The People’s Republic of China World Bank Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Foreign Economic and Technical Cooperation Center, Agriculture Commission of Hunan Province Hunan Research Institute for Nonferrous Metals April 2021 Project Name: Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Client: Foreign Economic and Technical Cooperation Center, Agriculture Commission of Hunan Province Assessment Unit: Hunan Research Institute for Nonferrous Metals Institute Qualification Certificate No.: G.H.P.Z.Y.Zi, No. 2711 Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Contents Chapter 1 Project Overview ....................................................................................................... 3 1.1 Project Background .......................................................................................................... 3 1.2 Lessons Learned from Projects ........................................................................................ 4 1.3 Category and Characteristics of the Project ..................................................................... 6 1.4 Thought on Environmental Assessment ........................................................................... 7 1.5 Assessment Standards ...................................................................................................... 9 1.6 Scope of Assessment ...................................................................................................... 13 1.7 Environmental Sensitive Sites........................................................................................ 13 Chapter 2 Laws, Regulations and Management Framework.................................................... 26 2.1 Applicable Laws, Regulations and Policies ................................................................... 26 2.2 Analysis of Compliance with the World Bank’s Safeguard Policies ............................. 31 2.3 Analysis of Differences between PRC National, Local Laws and Regulations and World Bank’s Safeguard Policies.................................................................................................... 33 Chapter 3 Project Content ........................................................................................................ 44 3.1 Project objectives ........................................................................................................... 44 3.2 Construction Content of the Project ............................................................................... 45 Chapter 4 Current Environment State ...................................................................................... 53 4.1 Natural Environment ...................................................................................................... 53 4.2 Ecological Environment ................................................................................................. 56 4.3 Social and Economic Environment ................................................................................ 59 4.4 Survey on Pollutant Source in Demonstration Area ...................................................... 71 4.5 Investigation and Assessment of Current Environmental Quality Status ...................... 90 4.6 Investigation and Evaluation of Rice in Demonstration Area ...................................... 100 4.7 Identification of Environmental Impact on Demonstration Area ................................. 106 Chapter 5 Analysis of Impacts on Environment and Mitigation Measures (ECOP and Specified Point Mitigation Measures) .................................................................................................... 113 5.1 Analysis on Impacts of the Project Civil Engineering Construction Activities and Mitigation Measures........................................................................................................... 113 5.2 Analysis on Surrounding and Upstream Pollution Sources and Mitigation Measures . 117 5.3 Analysis on Impacts of Agricultural Activities and Mitigation Measures ................... 126 Chapter 6 Analysis of Alternative Plans ................................................................................ 145 6.1 The Comparison and Selection with and without the Project ...................................... 145 6.2 Comparison and Selection of Demonstration Areas .................................................... 146 6.3 Project Village Area Selection ..................................................................................... 148 Chapter 7 Process of Public Participation .............................................................................. 150 1 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 7.1 Public Participation of Environmental Impact Assessment ......................................... 150 7.2 Information Release and Suggestion Feedback (Complaint) Mechanism during Project Implementation .................................................................................................................. 176 Chapter 8 Environmental Management Plan.......................................................................... 181 8.1 Purpose of Environmental Management ...................................................................... 181 8.2 Contents of Environmental Management Plan ............................................................. 181 8.3 Environmental Management System............................................................................ 181 8.4 Environmental Management Training.......................................................................... 190 8.5 Summary of Mitigation Measures for Environmental Impact ..................................... 192 8.6 Environmental Monitoring Plan ................................................................................... 197 8.7 Environmental Management Expenditure Estimation ................................................. 248 8.8 Information Management of EMP ............................................................................... 249 Chapter 9 Conclusion ............................................................................................................. 253 9.1 Project Brief Introduction............................................................................................. 253 9.2 Current Environmental Status ...................................................................................... 253 9.3 Environmental Impact Analysis and Mitigation Measures of Project.......................... 254 9.4 Public Consultation and Information Disclosure ......................................................... 255 9.5 Overall Conclusion....................................................................................................... 256 Appendix 1 ................................................................................................................................. 1 Environmental Protection Procedure for Small Civil Engineering Works ................................ 1 Appendix 2 ............................................................................................................................... 15 Environmental Protection Procedure for Field Irrigation Facility Construction ...................... 15 Appendix 3 ................................................................................................................................. 1 Environmental Protection Procedure for Agricultural Activities ............................................... 1 Appendix 4 Technical Plan to Be Adopted by Newly-added Demonstration Areas of Each Project County Appendix 5 Monitoring and Evaluation Result of Surface Water in Newly-added Demonstration Areas of Each Project County Appendix 6 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Demonstration Areas of each Project County Appendix 7 Selection Sheet of Project Towns of Each Project County Appendix 8 Comparison and Selection Sheet of Newly-added Demonstration Areas of Each Project County 2 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Attached Figure 1-1 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Yongding District Attached Figure 1-2 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Jishou City Attached Figure 1-3 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Yongshun County Attached Figure 1-4 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Cili County Attached Figure 1-5 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Huayuan County Attached Figure 1-6 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Anhua County Attached Figure 1-7 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Hengyang County Attached Figure 1-8 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Hengnan County Attached Figure 1-9 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Lengshuitan District Attached Figure 1-10 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Linwu County Attached Figure 1-11 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Qiyang County 2 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 1 Project Overview 1.1 Project Background Hunan Province is known as “a land of nonferrous metals”. Many farmlands are seriously polluted by nonferrous metals from industrial and mining waste water as well as dust fall during mining and smelting. In 2011, nonferrous metal pollution survey and monitoring were developed in rice growing areas of 1.8 million mu in surrounding areas of industrial and mining enterprises, irrigation areas and medium-large suburbs distributed in 45 districts and counties, and 12,000 soil samples were collected in all. According to the monitoring results, the heavy metals that pollute farmland mainly included Cd (cadmium), Pb (lead), Hg (mercury), As (arsenic), and Cr (chromium), especially Cd. In regard to the types of agricultural products, mainly rice and vegetables were polluted. In 2013, the reports about “cadmium-polluted rice storm” by some media aroused widespread attentions of society and high attention of government of all levels, caused huge impact on the rice industry in the whole southern China, and sounded the alarm for the issues on current agricultural production security and farmland protection. In recent years, the situation for grain sales in Hunan Province is very difficult. Being affected by the “cadmium-polluted rice storm”, grain merchants such as grain enterprises and the like do not actively purchase grains from farmers like before. On the one hand, the government emphasizes to grow more grains repeatedly orders to guarantee a steady rise in the total yield, on the other hand, the grains grown by the farmers cannot be sold. The grain production and sales is suffered from a serious setback, the benefits of the agricultural production and the grain processing enterprises are reduced, which as a strong impact on the enthusiasm of rice production, and there is a strong concern over this from the farmers. Given this, with the aims of curbing and controlling pollution of heavy metals and organic matters in agricultural producing areas, improving environments of agricultural producing areas, and guaranteeing food safety, 15 districts and counties in Hunan are selected as the representatives of sub-project counties being listed in the “Hunan Integrated Management of Agricultural Land Pollution Project” in the hilly and mountainous areas of Hunan after rapid risk analysis and research of Agriculture Commission of Hunan 3 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Province, these districts and counties have clear and controllable heavy metal pollution sources, draw attentions from local governments, attract a strong public participation willingness, and receive heavy metal pollution control in the earlier stage, and they provide reference and demonstration for other hilly and mountainous areas in Hunan to explore management modes for farmlands polluted by heavy metals. As the first batch of implementing sub-project counties, Yongding District, Hengyang County and Yongxing County obtained the approval from the the World Bank in January, 2017; and the remaining 12 sub-project counties of Baojing County, Jishou City, Yongshun County, Huayuan County, Cili County, Zhongfang County, Anhua County, Hengnan County, Yizhang County, Linwu County, Lengshuitan District and Qiyang County are implementing sub-project counties in the second batch obtained the approval from the the World Bank in December, 2018. During the implementation of the project, 11 project counties, including Jishou City, Huayuan County, Yongding District of Zhangjiajie City and Cili County of Xiangxi Autonomous Prefecture, Hengyang County and Hengnan County of Hengyang City, Lengshuitan District and Qiyang County of Yongzhou City, Anhua County and Linwu County of Chenzhou City, planned to add new demonstration areas on the basis of original approved ones. The project is Hunan Integrated Management of Agricultural Land Pollution Project in newly-added demonstration areas of 11 sub-project counties with World Bank Loan. Its objectives are to analyze risk factors of heavy-metal-polluted farmlands in newly-added demonstration areas, borrow and introduce heavy-metal-polluted farmland management experience at home and abroad, establish risk-based integrated management mechanism for polluted farmland, demonstrate and popularize the integrated management mode within the final selected demonstration farmland scope, and then realize safe agricultural production. 1.2 Lessons Learned from Projects Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan has implemented for two years since 2019. The implementation of the demonstration area has done a good job in the site selection, avoiding the demonstration 4 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report area where the pollution source is uncontrollable. By adopting the "VIP1" remediation mode, the cadmium content in rice in the implemented demonstration area was significantly reduced. So far, the rice in the implemented demonstration area can achieve the expected goal. A series of replicable and promotable pollution source control methods, monitoring schemes and technical paths of the implemented projects provide valuable experience for the newly-added demonstration areas, and particularly are of practical significance in technical scheme and project management, implementation and operation. The specific experience is as follows: (1) During the preparation stage of the project, the investigation of pollution sources shall be done well. After strict site selection and screening, the pollution sources in the selected demonstration areas are all historical pollution sources, and the upstream pollution sources have all been cut off. At present, there is no tailing pond, no waste residue stacking, and no problems left over by mining and separation. The uncontrollable area of pollution sources has been avoided to ensure that new heavy metal pollution will not be brought to the farmland in the demonstration area. (2) The project has developed a plausible monitoring plan, including the monitoring of irrigation water source, irrigation canal sediment, farmland soil, agricultural inputs (lime, organic fertilizer, soil conditioner, etc.). During the implementation of the project, according to the monitoring plan, the monitoring of each stage was carried out on time, and the monitoring data of irrigation water source, irrigation canal sediment, farmland soil and agricultural inputs were timely understood. Effective monitoring means were adopted to strengthen the control of pollution in the demonstration area, fully avoid new pollution to the demonstration area. Through two years of monitoring during the implementation of the project, it is found that the implementation of the project has little impact on the environment. (3) The Cd content in rice can be markedly reduced by adopting the "VIP" remediation mode, applying lime intensively, optimizing water management, increasing the 1 VIP: V refers to control of the rice species with high accumulation; I refers to improving water management in the field; P refers to soil acidification conditioning 5 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report application of soil conditioner (passivator, etc.) and other remediation technical measures after two years’ of project implementation. Although the soil in the implemented demonstration area still exceeds the standard, the cadmium content in the rice produced by the demonstration area is significantly reduced. So far, the rice quality in the implemented demonstration area can achieve the expected goal. (4) Strengthen policy control and carry out real-time detection of rice in each season. Sampling and testing shall be conducted before harvesting of rice in each season. According to the detection data of rice, the standard-exceeding rice is purchased by the local government of the demonstration area to store in special grain depot for industrial alcohol brewing. Since the implementation of the project for two years, the management and control measures for standard-exceeding rice are feasible, which ensures that the standard-exceeding rice does not flow into the edible rice market. Therefore, during the implementation the newly-added demonstration areas of Hunan Integrated Management of Agricultural Land Pollution Project, it’s necessary to summarize experience and lessons of previous Projects, learn from successful experience, prepare demonstration area address selection scheme and technical scheme, strengthen technical training for farmers in the demonstration area, conduct the monitoring of pollution source, soils, agricultural products, irrigation water, lime and organic fertilizers, avoid “simultaneous pollution and treatment” and secondary pollution, intensify the supervision on the process of Project implementation, launch supervision on key nodes in accordance with the project implementation plan, control such conditions as task implementation, fund utilization and work progress in a timely way, establish technical measure implementation supervision teams in all demonstration areas, and build job log and technical measure implementation supervision account, so as to ensure smooth practice of the project. 1.3 Category and Characteristics of the Project This project is a Class A project. The first batch of project has prepared environmental impact assessment results such as Environmental and Social Management Framework (ESMF), Terms of Reference (TOR), Pest Management Plan (PMP), etc. This time, according to the approved results in Environmental and Social Management Framework 6 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (ESMF), Environmental Impact Assessment Report (EIA) of new demonstration areas in 11 project counties have been prepared. The specific objective of the project is to analyze effective data including rice, agricultural internal and external pollution sources and agricultural production management in the newly-added demonstration areas of 11 sub-project counties, conduct soil pollution risk assessment, farmland pollution source risk assessment and farmland management risk assessment by combining with actual situation in the demonstration area, put forward corresponding risk management measures for different risk model combinations, finally, the comprehensive management mechanism of risk control is discussed to control the farmland risk of the project county, so as to achieve the purpose of safe production of qualified agricultural products. Main contents of the project include demonstration of farmland management based on risks, strengthening of agriculture environment monitoring and management, Project capability building, Project management and assessment. 1.4 Thought on Environmental Assessment (1) Collecting the monitoring data, irrigation water quality data and surrounding pollution source (including historical pollution source and present pollution source) data in the proposed demonstration area of sub-projects for data arrangement and analysis. Determine the proposed demonstration areas according to the demonstration area selection principles stated in the environmental and social management framework. (2) Compare in the targeted demonstration areas to determine the specific places for implementing the project; According to the degree of the soil pollution in farmland, comprehensive management technical scheme is selected, and the alternative scheme is analyzed from the aspects of technology maturity, construction difficulty, economic cost, farmers’ acceptance level and environmental impact. (3) Select appropriate assessment scope according to the actual conditions of the demonstration area after the demonstration area is determined. (4) Preliminarily analyze farmland soil pollution in the demonstration area through field survey, data collection and analysis, public consultation and information disclosure. 7 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (5) Collect monitoring data or conduct field monitoring according to monitoring data requirements determined in the Environment and Social Management Framework, and prepare field monitoring plan, including monitoring factor, distribution method, sampling quantity, and sampling and analysis method. (6) Conduct due diligence on heavy metal contamination within the assessment scope, including construction and operation of waste gas, wastewater and solid waste disposal facilities; check if concentration and discharge of waste gas and wastewater reach related standards, and if safety disposal is conducted for solid waste; set up environmental management organization and environmental management system. (7) By analyzing activities in the project (construction activities, agronomic activities and other activities), identify the environmental impacts (including positive and negative impacts) of each project activities, and propose mitigation measures. (8) Prepare Environmental Impact Assessment (EIA) of the demonstration area; during Project implementation, put forward a series of environmental influence mitigation measures, monitoring and organization construction measures, as well as environmental management, so as to eliminate or reduce adverse influence of the project on the environment; prepare plan to guarantee smooth implementation of the above measures. (9) Among the approved projects, a comprehensive pest management plan (separate edition) has been prepared for 15 project counties in the whole province. These 15 project counties have already covered the newly added demonstration areas, so no new PMP will be prepared for this batch of project. (10) Invite the public to fill in the participation questionnaires and convene field symposiums. Investigation scope of public investigation: demonstration areas and areas which may be influenced; objects of public investigation: important stakeholders, including the residents involved in the demonstration areas, the residents near the demonstration areas, public figures who pay close attention to the project, public groups in the demonstration areas including agricultural department, environmental protection department, water conservancy department, animal husbandry department, quality and 8 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report technology supervision department, safety supervision department, and industrial and mining enterprises, and related experts. Conduct two rounds of public consultation and information disclosure during assessment. The first round is after screening the environmental problems; the second round is in the completion stage of first draft of environmental assessment report. 1.5 Assessment Standards 1.5.1 Quality Standards (1) Ambient air: level-II stated in Quality Standards for Ambient Air (GB3095-2012). (This standard is formulated in order to protect and improve the living environment and the ecological environment as well as protect the human health. It stipulates the classification of ambient air functional zones, standard grading, pollutant items, average time and concentration limits, monitoring methods, effectiveness of data statistics, execution and supervision, etc. This standard is adopted for the ambient air assessment in the Hunan Integrated Management of Agricultural Land Pollution Project). (2) Surface water: type-II and type-III stated in Environmental Quality Standards for Surface Water (GB3838-2002); (This standard is formulated in order to prevent and control water pollution, protect surface water quality, protect the human health, and maintain a good ecological system, and it is divided into the basic item of surface-water environmental quality, the supplementary item of surface water source for centralized domestic drinking water and the specific item of the surface water source area for centralized domestic drinking water. This standard is executed for surface water protection in the Hunan Integrated Management of Agricultural Land Pollution Project). Irrigation water shall be subject to the Quality Standards for Farmland Irrigation Water (GB5084-2021). (This standard specifies the farmland irrigation water quality requirements as well as the standard implementation, sampling and test methods. It is applied to farmland irrigation water by using the water sources of surface water, underground water, treated municipal sewage and industrial wastewater with similar water quality of municipal sewage in China. This standard is strictly followed during the irrigation water assessment and management in the Hunan Integrated Management of 9 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Agricultural Land Pollution Project). (3) Acoustic environment: type-II standards stated in Quality Standards for Acoustic Environment (GB3096-2008). (This standard is formulated in order to prevent and control noise pollution, safeguard the acoustic environment quality for normal life, work and study of urban and rural residents. It specifies the ambient noise limits and the measuring methods for five types of functional zones in the acoustic environment. This standard is employed for acoustic environment quality and management in the Hunan Integrated Management of Agricultural Land Pollution Project). (4). The soil quality shall comply with the screening value standard in Table 1 of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018). (This standard specifies the maximum allowable concentration index values and the corresponding monitoring methods for pollutants in soils according to the application functions, the protection target and the main natures of soils. It is applied to the soils in farmlands, vegetable fields, tea gardens, orchards, paddocks, forest lands, natural reserves, etc. The evaluation of farmland soil in Hunan Integrated Management of Agricultural Land Pollution Project adopts the screening value standard in Table 1 of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018). (5) Agricultural products (rice samples): National Standards for Food Safety: Limits of Pollutants in Food (GB2762-2012). (This standard specifies the maximal residue limits of Pb (lead), Cd (cadmium), Hg (mercury), As (arsenic), Cr (chromium) and this standard is applied to the agricultural products (rice) in the Hunan Integrated Management of Agricultural Land Pollution Project). (6). The control value standard of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018) shall be implemented for irrigation canal sediment. If the sediment exceeds the control value, it shall be sent to the local landfill for filling. 1.5.2 Discharge Standards (1) Atmospheric pollutants: level-II stated in Comprehensive Standards for Discharge 10 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report of Atmospheric Pollutants (GB16297-1996). (This standard specifies the discharge limits for 33 types of atmospheric pollutants, and meanwhile it stipulates various reqreuiments during execution of the standard. For any activity concerning the discharge of atmospheric pollutants in the Hunan Integrated Management of Agricultural Land Pollution Project, it is required to implement this standard). (2) Water pollutants: level-I stated in Comprehensive Standards for Discharge of Sewage (GB8978-1996). (In order to implement the Environmental Protection Law of the People’s Republic of China, the Law of the People’s Republic of China on Prevention and Control of Water Pollution and the Marine Environmental Protection Law of the People’s Republic of China, control water pollution, maintain the good state of surface water and underground water quality in rivers, lakes, canals, channels, reservoirs, oceans, etc., protect the human health, maintain the ecological balance, and promote the development of national economy as well as urban and rural construction, this standard is formulated, and for any activity concerning the discharge of water pollutants in the Hunan Integrated Management of Agricultural Land Pollution Project, it is required to implement this standard). (3) Noises: Environmental Noise Discharge Standards in Construction Site (GB 12523-2011). (In order to implement the Environmental Protection Law of the People’s Republic of China and the Law of the People’s Republic of China on Prevention and Control of Ambient Noise Pollution, prevent and control noise pollution during the building construction as well as improve the acoustic environment quality, this standard is formulated, and for any activity concerning noise during the construction period in the Hunan Integrated Management of Agricultural Land Pollution Project, it is required to implement this standard). (4) Solid wastes: Standard for Pollution Control on Storage and Disposal Site for General Industrial Solid Wastes (GB 18599-2001) (revised in 2013). (In order to implement the Law of the People’s Republic of China on the Prevention and Control of Solid Waste Pollution, and prevent and control the secondary pollution in the general industrial solid waste storage and disposal sites, this standard is formulated. If any storage 11 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report and disposal of general solid wastes is involved in the Hunan Integrated Management of Agricultural Land Pollution Project, this standard is executed). Standard values of assessment factors: see Table 1-1. Table 1-1 Standard Values of Assessment Factors Name of standard Standard value Level-II stated in Item TSP SO2 NO2 Quality Standards for Hour average value (ug/m3) / 500 200 Ambient Air Annual average value 200 60 40 (GB3095-2012) (ug/m3) Type-II stated in NH3 Item pH COD TP Pb As Cd Cr Hg Environmental -N Quality Standards for Standard 0.000 Surface Water 6～9 15 0.5 0.1 0.01 0.05 0.005 0.05 value (mg/L) 05 (GB3838-2002) Type-III stated in NH3 Item pH COD TP Pb As Cd Cr Hg Environmental -N Quality Standards for Standard 0.000 Surface Water 6～9 20 1.0 0.2 0.05 0.05 0.005 0.05 value (mg/L) 1 (GB3838-2002) NH3- Quality Standards for Item COD SS Cd Pb As Hg Cr TP N Farmland Irrigation Standard Water (GB5084-2021) 150 80 0.01 0.2 0.05 0.001 0.1 / / value (mg/L) Screening value in Item pH Pb As Cd Cr Table 1 of ‘Soil ≤5.5 ≤80 ≤30 ≤0.3 ≤250 Environmental 5.5～ ≤100 ≤30 ≤0.4 ≤250 Quality Standard for 6.5 Standard Risk Control of Soil 6.5～ value ≤140 ≤25 ≤0.6 ≤300 Pollution of 7.5 (mg/kg) Agricultural Land (Trial)’ (GB ＞7.5 ≤240 ≤20 ≤0.8 ≤350 15618—2018). National Standards Total Inorganic Item Hg Cd Pb for Food Safety: chromium arsenic Limits of Pollutants in Standard Foods value 1.0 0.2 0.02 0.2 0.2 (GB2762-2012) (mg/kg) Type-II standards Item At daytime At night stated in Quality Standards for Type-2 60dB(A) 50dB(A) Acoustic Environment standards (GB3096-2008) Level-II stated in Item PM SO2 NOX Comprehensive Standards for Discharge Standard of Atmospheric value 120 550 240 Pollutants （mg/m3） (GB16297-1996) Level-I stated in Petrole Item pH SS Pb As Cd Cr Hg CODCr Comprehensive um Standards for Concentration Discharge of Sewage 6～9 70 5 1.0 0.5 0.1 1.5 0.05 100 limit (mg/L) (GB8978-1996) 12 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1.6 Scope of Assessment 1.6.1 Screening Methods (1) Include the area that may affect the newly-added demonstration areas into the assessment scope ① Identify the irrigation water source of the newly-added demonstration areas, and the surrounding potential surface water, groundwater and air pollution sources, including the industrial and mining enterprises involving discharge of heavy metals in upstream of the newly-added demonstration area, tailings reservoir, remaining historical pollution source, and slag heap, etc., and determine the areas that may affect the project, and include them into the assessment scope. ② Heavy metal pollution brought by agricultural productions, such as agricultural chemicals, chemical fertilizer, organic fertilizer, and agricultural wastes. ③ The upstream tailings reservoir sharing the same surface water system with demonstration area should be included into assessment scope. ④ The mountain pond and reservoir as irrigation water source of demonstration areas, as well as the upstream reservoir, river, and sediment in mountain pond shall be included into the assessment scope. (2) Include the area that may be affected by Project activities into the assessment scope Identify the project construction activity, agricultural activity (such as applying lime and organic fertilizer) and other Project activity, and determine the positive or negative influence area that they may cause, and include such area into the assessment scope. 1.6.2 Screening Results According to identification results and actual condition of each demonstration area, the assessment scope of the project is shown in the Attached Figures 1-1~1-12. 1.7 Environmental Sensitive Sites According to the field investigation of the demonstration areas and the activities in the 13 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report demonstration area, the identification of the environmental impact in the demonstration area is carried out, and for the results, see Table 4-2. For the confirmation of the environmental sensitive sites of the project, see Tables 1-1~1-11 and Attached Figures 1-1~1-11. 14 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 1-1 Environmental Sensitive Sites of the newly-added Demonstration Area in Yongding District Name Protection type Scale Remarks The annual average runoff is 13.12 billion m3. The drainage area is Lishui 18,496 square Yinjiaxi River Irrigation water source kilometers, including Demonstration of the demonstration 15,736 square area area kilometers in Hunan Mountain spring / water Wentang Mountain Irrigation water source Demonstration spring / of the demonstration Surface Area water area water The annual average runoff is 13.12 billion m3.The drainage area is Lishui 18,496 square Yanghuping River Irrigation water source kilometers, including Demonstration of the demonstration 15,736 square Area area Yongding kilometers in Hunan District Mountain spring / water Yuanguping Mountain Irrigation water source Demonstration spring / of the demonstration area water area Because there are many mountains and forest lands in Yongding District, the straws are disposed by adopting Forest land for straw disposal / the method of centralized gathering and in-place returning to the forest for coverage. A disposal company for standard-exceeding rice Xiangquan Winery / with Cd content >0.2mg/kg, 15 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report located in Yongding District With the total storage It can accept capacity of 3.957 out-of-limit heavy The refuse landfill in Yongding million m3 and the metal residues, and it is District refuse disposal capacity located in Xixiping of of 250 tons/day. Yongsding District It is used for recycling packing materials for Agricultural material recycling station agricultural inputs, and / in Yongding District located in the urban area of Yongding District. 265 poverty-stricken Poverty-stricken people families and 888 poverty-stricken people Table 1-2 Environmental Sensitive Sites in the Newly-added Area of Jishou City Demonstration Area Name Protection type Scale Remarks Aizhai Mountain Demonstration spring / Irrigation water source Surface Area water water Qianzhou Mountain Demonstration spring / Irrigation water source Area water Because there are many mountains and forest lands in Jishou city, the straws are Forest land for straw disposal / disposed by adopting the method of centralized gathering and in-place returning to the forest for coverage. Jishou A disposal company for City standard-exceeding rice with Cd Jishou Liquor Co., Ltd. / content >0.2mg/kg, located in Jishou City. With the total storage capacity of 2 million m3 It can accept out-of-limit heavy metal Jishou municipal refuse landfill and the residues, and located in Baxifu, Jishou refuse City disposal capacity of 300 16 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report tons/day. It is used for recycling packing Jishou municipal agricultural materials for agricultural inputs, and it / material recycling station is located in the urban area of Jishou City. Table 1-3 Environmental Sensitive Sites in the Newly-added Area of Yongshun County Demonstration Area Name Protection type Scale Remarks Shaba Mountain Demonstration spring / Irrigation water source Surface Area water water Xiqi Mountain Demonstration spring / Irrigation water source Area water Because there are many mountains and forest lands in Yongshun, the straws Forest land for straw disposal / are disposed by adopting the method of centralized gathering and in-place returning to the forest for coverage. A disposal company for Luohu Winery in Wanping Town / standard-exceeding rice with Cd content >0.2mg/kg Yongshun With the County total storage capacity of 2 It can accept out-of-limit heavy metal million Refuse landfill in Yongshun County residues, and located in Yongshun m3 and County the refuse disposal capacity of 100 tons/day. It is used for recycling packing Agricultural materials recycle station materials for agricultural inputs, and it / in Yongshun County is located in the urban area of Yongshun County. Table 1-4 Environmental Sensitive Sites of the Newly-added Demonstration Area in Cili County Name Protection type Scale Remarks 17 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Xiangshi Town Mountain Irrigation water source of / Demonstration spring water the demonstration area Area Sanhekou Town Mountain Irrigation water source of / Demonstration spring water the demonstration area Area It is an upstream As the reservoir in the tributary of Lishui approved demonstration Yangliupu River, with the area, the newly-add Surface Township Guantianrong watershed area of demonstration area and the water Demonstration Reservoir 12.3km2 and the approved demonstration Area total storage area shall share the same capacity of 1.88 irrigation water source million m3. Dongyueguan It is an upstream As the reservoir in the Town tributary of Lishui approved demonstration Demonstration River, with the area, the newly-add Area Zhuangta watershed area of demonstration area and the Tongjinpu Reservoir 15.8km2 and the Cili approved demonstration Town total storage County area shall share the same Demonstration capacity of 19.75 irrigation water source Area million m3. Due to the fact that Cili County has a great number of mountains and forests, the straws are disposed by Forest land for straw disposal / adopting the method of centralized gathering and in-place returning to the forest for coverage. A disposal company for Zhangjiajie Shengdi Wine Co., Ltd / standard-exceeding rice with Cd content >0.2mg/kg The refuse disposal It can accept out-of-limit Refuse landfill in Cili County capacity of 200 heavy metal residues, and tons/day located in Cili County It is used for recycling packing materials for Agricultural material recycling station in / agricultural inputs, and Cili County located in the urban area of Cili County. 18 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 1-5 Environmental Sensitive Sites of the Newly-added Demonstration Area in Huayuan County Name Protection type Scale Remarks Biancheng Surface Town Gaohe Agricultural land irrigation water Flow rate:2~5m3/s water Demonstration River source of Gaohe Village Area Due to the fact that there are many forest lands in Huayuan county, the straws are disposed by Forest land for straw disposal / adopting the method of centralized gathering and in-place returning to the forest for coverage. A disposal company for standard-exceeding rice with Cd Malichang Winery / content >0.2mg/kg, located in Huayuan Malichang Town, Huayuan County County. It covers an area of 153.6 mu, with the total total storage capacity of 0.952 It can accept out-of-limit heavy Town refuse landfill in Huayuan million m3 and the metal residues, and located in Yixi County refuse disposal Village, Huayuan Town, Huayuan scale is 70 County tons/day, and its service life is 20 years. It is used for recycling packing Agricultural materials recycle station materials for agricultural inputs, / in Huayuan County and it is located in the urban area of Huayuan County. Table 1-6 Environmental Sensitive Sites of the Newly-added Demonstration Area in Anhua County Name Protection type Scale Remarks Le’an Town Yishui Irrigation water source of Demonstration 2~5m3/s River demonstration area Anhua Surface Area County water Dafu Town Unknown Irrigation water source of Demonstration irrigation 1~3 m3/s demonstration area Area canal 19 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Qingtangpu Dongtian Irrigation Water Source of Demonstration 4~9 m3/s River Demonstration Area Area Because there are many mountains and forest lands in Anhua County, the straws are Forest land for straw disposal / disposed by adopting the method of centralized gathering and in-place returning to the forest for coverage. A disposal company for standard-exceeding rice with Cd Qinglong Wine Co., Ltd. / content >0.2mg/kg, located in Anhua County. It has a total storage capacity of It can accept out-of-limit heavy Refuse landfill in Anhua County 3.15 million m3 metal residues, and located in and the refuse Dongping Town, Anhua County. disposal scale is 220 tons/day. It is used for recycling packing Agricultural material recycling station in materials for agricultural inputs, / Anhua County and it is located in the urban area of Anhua County Table 1-7 Environmental Sensitive Sites of Demonstration Area in Hengyang County Name Protection type Scale Remarks Sanfu: Zhengshui River; Yanglin In Hengyang Yanglin: Demonstration County, the Shizhu Reservoir is the irrigation Area of length is 133 km, reservoir in the approved canal Fuxing of the rainwater demonstration area, the Surface water in Sanhu Town collecting area is newly-add demonstration area Water the Shizhu 2,336 km2, and and the approved Hengyang Reservoir the total annual demonstration area shall share County Qingli runoff volume is this irrigation water source 1,600 million m3. Demonstration Zhengshui Area of Xidu River Town With the planting It is the orientation of straws Honey pomelo planting base in area of 1000 removed from farmlands in Hengzhou hectares and Liangjiang Village, Yongning annual straw Village and Qunying Village 20 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report disposal capacity of Taiyuan Town. of 20,000 tons. A disposal company for standard-exceeding rice with Cd content >0.2mg/kg, Hunan Dinggu Wine Co., Ltd / located in Liansheng Village, Qingmu Village of Xidu Town. Covering a land It can accept out-of-limit of 236.47 mu, Lida refuse landfill in Hengyang heavy metal residues, and The refuse County located in Xidu Town, disposal capacity Hengyang County. of 300 tons/day It is used for recycling packing materials for Agricultural material recycling station / agricultural inputs, and in Hengyang County located in the urban area of Hengyang County. Table 1-8 Environmental Sensitive Sites of Demonstration Area in Hengnan County Name Protection type Scale Remarks Chaoyang Shantang and Village of Ouyanghai Irrigation water source of Xiangyang / irrigation demonstration area Demonstration canal water Area Huanghe Village of Surface Irrigation water source of Xiangyang Shangtang / water demonstration area Demonstration Area Quanchang Hengnan Village of Irrigation water source of County Quanxi Leishui River / demonstration area Demonstration Area With the planting It is the orientation of straws area of 253 Hengnan Xiangjian organic fruit, poultry removed from farmlands in the hectares and and agriculture fishery production and Demonstration Areas of annual straw marketing cooperative Xiangyang Town and disposal capacity Xiantang Town. of 10,000 tons. With the planting It is the orientation of straws Hengnan Jinxiangyan Planting and Raising area of 98 hectares removed from farmlands in the Cooperative and annual straw Demonstration Areas of disposal capacity Huaqiao Town, Chashi Town 21 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report of 5,000 tons. and Jiangkou Town. Xiangyang Community Demonstration Area, Quanxi Demonstration Area Hunan Lingjiu Wine Co., Ltd. An acquiring company for standard-exceeding rice with / Cd content >0.2mg/kg An acquiring company for standard-exceeding rice with Cd content >0.2mg/kg in Hunan Tianzhiheng Wine Co., Ltd. Xiangyang Community Demonstration Area, Quanxi Demonstration Area With the design of It can accept out-of-limit daily refuse heavy metal residues, and Maotang domestic refuse landfill in disposal of 100 located in Luobuchong Group, Hengnan County tons and storage Heshi Village, and Yunji capability of 1.5 Town. million m3 It is used for recycling packing materials for agricultural Agricultural material recycling station in / inputs, and it is located in the Hengnan County urban area of Hengnan County. Make a subsidy according to 6,000 Yuan/hectare. For annual crops, make a subsidy for one year; and Change of Restructuring of Change of cropping system of severely cropping system for palnting 53.33 mu of polluted area two-year or above crops, make sorghum and corn a subsidy until the grown year. The subsidy budget for change of cropping system is 601,900 Yuan. Table 1-9 Environmental Sensitive Sites of Demonstration Area in Lengshuitan District Name Protection type Scale Remarks As the reservoir in the approved It was completed Xianghuaba demonstration area, the in 1959, with the Village Dengjiachong newly-add demonstration area total storage Demonstration Reservoir and the approved demonstration Lengshuitan Surface capacity of Area 3 area shall share the same District Water 388,000 m irrigation water source Shixijiang Lanjiang A tributary of Irrigation Water Source of Village River Xiangjiang River Demonstration Area Demonstration 22 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Area Niujiaoba Shixijiang Irrigation Water Source of Demonstration / River Demonstration Area Area Its watermelon Lying in Yitang Town, it is the planting area is orientation of straws removed 6000 mu and Lengshuitan Five-Star Watermelon from the farmland in the annual straw Professional Cooperative demonstration areas of Puliqiao disposal capacity Town, Niujiaoba Town, and is over 20,000 Shanglingqiao Town. tons An acquiring company for standard-exceeding rice with Cd Yunxi Wine Co., Ltd. / content >0.2mg/kg, located in Lengshuitan District With the total storage capacity It can accept out-of-limit heavy Tantang refuse landfill in Lengshuitan of 10.75 million metal residues, and located in District m3 and the refuse Lanjiaoshan Town, Lengshuitan disposal capacity District. of 860 tons/day. Located in urban area of Agricultural material recycling station in Lengshuitan District, it is used / Lengshuitan District for recycling of packing materials for agricultural inputs. Table 1-10 Environmental Sensitive Sites of Demonstration Area in Linwu County Name Protection type Scale Remarks It is an irrigation water source, from the Wushui River is northern slope of Sanfengling in Linwu located in Linwu County, it flows through five counties of County, the length is Hunan Province, namely, Linwu County, Wushui 43.68km, the Wushui Yizhang County, Chenxian County, Demonstration rainwater collecting River Guiyang and Rucheng as well as Lechang, Area area is 1,138.92 km2, Ruyuan, Qujiang, Shaoguan urban area in and the total annual Guangdong Province, and it converges runoff volume is Linwu Surface with Zhenshui in Shazhouwei, Shaoguan 916.5 million m3. County water urban area. It is an irrigation source. Originates from Tiantouling, it flows into the county from It is 12.1km long Nanqiang Nanqiang Town, Linwu County, flows Renmin within Linwu County, Demonstration through Wushui Town and Fenshi Town in River and the rain collecting Area Linwu County, and flows out of the area is 36.24 km2. county in Wutangchong to flow into Yizhang. Shuidong Shuidong In Linwu County, the The irrigation water source and 23 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Demonstration River length is 38 km, the pollutant-holding water body in the Area rainwater collecting demonstration area of Shuidong Town area is 116.79 km2, originate from Kuandong Village of and the annual Yangtian Lake, enter Jinjiang Town of average runoff volume Linwu County, flow through Jinjiang is 521 million m3. Town and Shuidong Town of Linwu County, and flow out of the province at Wutangchong of Shuidong Town It is the orientation of straws removed from farmlands. Linwu Huijia Fruit Co., Linwu Huijia Fruit Co., Ltd. Linwu With the planting area Ltd. is located in Yafutang; Linwu Nongxiangsiyi Fruit Planting of 4900 mu and Changda Crispy Jujube Growing Professional Cooperative and Linwu annual straw disposal Professional Cooperative is located in Changda Crispy Jujube Growing capacity of 6533 tons. Yuping and Linwu Nongxiangsiyi Fruit Professional Cooperative Planting Professional Cooperative is located in Wushui Town. It is the orientation of straws removed With the planting area from the farmland. Hongyuan Fruit Hongyuan Fruit Co., Ltd. Linwu of 5400 mu and Industy is Shizipu Village, Nanqiang Xiangyuan Fruit Planting Professional annual straw disposal Town. Linwu Xiangyuan Fruit Planting Cooperative capacity of 7200 tons. Professional Cooperative is located in Xiangtang Village, Nanqiang Town. With the planting area It is the orientation of straws removed Linwu County Tianyuan Agricultural of 1500 mu and from farmlands in Huangjia Village, Technology Development Co., Ltd annual straw disposal Shuidong Town capacity of 2000 tons. An acquiring company for Linwu County GuyanWinery / standard-exceeding rice, located in Xiyao Township. Covering a land of It can accept out-of-limit heavy metal Nuisanceless domestic waste landfill in 206 mu, with the total residues, and located in Xiadong Village, Linwu County storage capacity of Linwu County. 1.85 million m3 Table 1-11 Environmental Sensitive Sites of Demonstration Area in Qiyang County. Name Protection type Scale Remarks The reservoir was completed in 1972, As the reservoir in the approved Xiaojia the normal total demonstration area, the newly-add Surface Dajiangbian Demonstration storage capacity is demonstration area and the approved water Reservoir Area 49.5 million m3, and demonstration area shall share the Qiyang the designed irrigation same irrigation water source County area is 168,400 mu. Because Qiyang has a lot of forest lands, the straws are disposed by Forest land for straw disposal / adopting the method of centralized gathering and in-place returning to the forest for coverage. 24 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report An acquiring company for standard-exceeding rice with Cd Qiyang Qiongniang Wine Co., Ltd. / content ＞0.2mg/kg, located in Wuxi Town, Qiyang County. The daily average landfill is 360 tons, the planned total floor It can accept out-of-limit heavy metal area is 307.5 mu, the residues, and located in Qiyang Urban refuse landfill in Qiyang County designed total storage County, the southwest suburb, Maozhu capacity is 453.5 m3, Town. and the service life is 30 years. It is used for recycling packing Agricultural material recycling station in materials for agricultural inputs, and it / Qiyang County is located in the urban area of Qiyang County. 25 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 2 Laws, Regulations and Management Framework 2.1 Applicable Laws, Regulations and Policies 2.1.1 Environment Protection Laws and Regulations (1) The Constitution of the People’s Republic of China (Amended in 2004): the Constitution Law of the PRC provides that all ethnic groups in China are equal. The state protects the legitimate rights and interests of each minority group, maintains and promotes the equality, unity and mutual help relationship among all ethnic groups. Any discrimination and suppression of any ethnic group is prohibited, and any disruption of unity among ethnic groups and ethnic division are prohibited. The state will facilitate each region inhabited by minority ethnic groups in the promotion of economic and cultural development consistent with the features and needs of each minority ethnic group. The policy of “regional autonomy” shall apply in areas populated by minority ethnic groups, and autonomous organs shall be established in such areas, which will exercise the autonomy powers. Each region in which minority ethnic group exercises autonomy powers shall be deemed an integral part of the PRC. Each minority ethnic group has the power to use and develop their own languages, and to maintain or transform their customs. Hunan Integrated Management of Agricultural Land Pollution Project shall be conducted in strict compliance with the requirements in the Constitution regarding equality among ethnic groups, and in a manner that fully respects the cultures, customs, religions and languages and characters in the minority ethnic group regions, and promotes the social and economic development in the minority ethnic group regions. (2) The Environment Protection Law of the People’s Republic of China enacted by the National People’s Congress, Standing Committee of the PRC dated January 1, 2015; this is a state law enacted to protect and improve environment, prevent and cure pollution and other public hazards, protect public health, promote ecological civilization, promote the economically and socially sustainable development. And Hunan Integrated Management of Agricultural Land Pollution Project must comply with the environment protection requirements in the law. (3) Environment Impact Assessment Law of the People’s Republic of China, amended 26 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report on July 2, 2016; It includes analysis, prediction and assessment of impact of planning and construction Projects on environment, counter-measures and actions to prevent or mitigate adverse environment impact, manners and policies applicable to follow-up and monitoring. This law provides that, any Project carried out in the territory of the PRC or other ocean areas under the jurisdiction of the PRC that may have any environmental impact shall be subject to environment impact assessment pursuant to this law. Hunan Integrated Management of Agricultural Land Pollution Project must be subject to the environment impact assessment pursuant to this law. (4) The Law of the People’s Republic of China on the Prevention and Control of Atmospheric Pollution, promulgated by the No. 31 President Order dated January 1, 2016 ;This law provides expressly and specifically for the supervisory and management policies and main legal system for atmospheric pollutants, the main measures, legal liabilities respecting prevention and control of atmospheric pollutants from combustion, pollutants released from vehicles and vessels, and released waste gas, dust, and odor pollutants. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the provisions in this law regarding prevention and control of atmospheric pollutants. (5) The Law of the People’s Republic of China on Prevention and Control Of Water Pollutants, promulgated by the No. 87 President Order dated June 1, 2008; This law aims to prevent and control water pollutants, protect and improve environment, protect the safety of drinking water, promote the comprehensive, sustainable economic and social development, which applies to the prevention and control of pollution of surface water in rivers, lakes, canals, channels, reservoirs and underground water in the territory of the PRC. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding prevention and control of water pollutants. (6) The Law of the People’s Republic of China on the Prevention and Control of Solid Wastes, amended on April 24, 2015; This law aims to prevent and control solid wastes pollution of the environment, protect the human health, protect ecological safety, promote economically and socially sustainable development, applies to the prevention and control 27 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report of pollution of solid wastes within the territory of the PRC. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding prevention and control of solid waste pollution. (7) The Law of the People's Republic of China on Prevention and Control of Pollution from Environmental Noise, promulgated by the No. 77 President Order on March 1, 1997; It aims to prevent and control noise pollution, protect and improve living environment, protect human health, promote the economic and social development, and it applies to the prevention and control of noise pollution within the territory of the PRC. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding prevention and control of environmental noise pollution. (8) The Law of the People’s Republic of China on the Protection of Cultural Relics (enacted on October, 2002): in order to strengthen the protection of cultural relics through regulation, this law provides that, in the protected areas and restricted areas for construction in cultural relics protection units, no facilities shall be constructed that may pollute such cultural relics protection units or the environment, nor shall any activities be permitted that may have any impact on the safety of such units and its environment. Any existing facilities that pollute the cultural relics protection untis and its environment shall be dealt with during specified period. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding cultural relics protection. (9) The Law of the People’s Republic of China on the Autonomy of Regions Populated by Minority Ethnic Groups (effective as of October 1, 1984): Regional Autonomy for Minority Peoples refers to the policy under which each region populated by minority ethnic group shall, under the uniform administration of the state, establish autonomous organs to exercise autonomous powers to implement the rule of autonomy for the region. Regional Autonomy embodies the state’s spirit of full respect and gu arantee to each ethnic group to manage its own internal affairs, and reflects the principle of promoting equality, unity and common prosperity among ethnic groups. Hunan Integrated Management of Agricultural Land Pollution Project must be carried out in a manner that fully respects the 28 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report autonomous rights of minority ethnic groups and does not interfere with their internal affairs. (10) The Labor Law of the People’s Republic of China (effective as of January 1, 1995): it aims to protect the legitimate rights and interests of employees, govern employment relationship, form and maintain a labor system that is consistent with the socialist market economy, and to promote the economic and social development. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding protection of employee interests. (11) The Labor Contract Law of the People’s Republic of China (effective as of January 1, 2008): it aims to improve the labor contract system, clarify rights and obligations of the parties to labor contracts, protect the legitimate interests of employees, form and promote harmonious and steady labor relationship. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding employee labor contracts. (12) The Employment Promotion Law of the People’s Republic of China (effective as of January 1, 2008): it aims to promote employment, promote the goal of economic growth and increase of employment, and promote the harmony and steadiness of the society. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding employment and training. (13) The Social Insurance Law of the People’s Republic of China (effective as of July 1, 2011): it aims to regulate the social insurance relationship, maintain the legitimate rights of citizens to participate in social insurance and their entitlements to social insurance benefits, and enable citizens to share the social development achievements and promote the social harmony and steadiness. Hunan Integrated Management of Agricultural Land Pollution Project must be compliant with the requirements in this law regarding social insurance. (14) The Thirteenth Five-year Plan for Minority Ethnic Groups (effective as of November 2016): this Plan aims to achieve the strategic target of construction of a well-off society in all aspects by taking into consideration the actual conditions of minority ethnic 29 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report groups and regions populated by minority ethnic groups in Hunan Province. This Plan, by adopting the approaches of “growth oriented in Projects, work by implementation of Projects, plan supported by Projects”, proposes policies and measures in 12 categories, 66 sub-items of policies on 8 aspects, including major construction Project, financial, tax, investment, land, ecology, industry, talents and “targeted aid” in less developed areas and other aspects. Hunan Integrated Management of Agricultural Land Pollution Project, shall be implemented consistent with and mutually supportive of the requirements in this Thirteenth Five-year Plan for Minority Ethnic Groups of Hunan. (15) Soil Pollution Prevention and Control Plan (dated May 31, 2016, issued by the State Council); this Plan aims to strengthen the prevention and control of soil pollutants, and gradually improve the soil environment quality. This Plan may serve as a reference in the preparation of agricultural land pollution management measures regarding Hunan Integrated Management of Agricultural Land Pollution Project. (16) Nation-wide Soil Pollution Survey Report (published by the Ministry of Environmental Protection and the Ministry of Land and Resources on April 17, 2014): from April 2005 until December 2013, China conducted the first national soil pollution survey and has obtained basic knowledge about the overall conditions of nation-wide soil environment and based on the survey results issued Nation-wide Soil Pollution Survey Report. Hunan Integrated Management of Agricultural Land Pollution Project has referenced the rating method for heavy metal pollution in this Report as the rating method for heavy metals other than cadmium. 2.1.2 Government Regulations The Thirteenth Five-year Plan of Hunan Province for National Economic and Social Development: Chapter Twelve of the Plan proposes to accelerate the pace of agricultural modernization, improve the agricultural product quality safety system, requires to implement a differentiated land administration system, and to determine land use size of various sorts in a reasonable manner, and to exert strict control of land use, and imposes differentiated overall pollutant release limits and environmental standards for different development priority zones. Hunan Integrated Management of Agricultural Land Pollution 30 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Project is included in Hunan Province’s Thirteen Five-year Plan in terms of the development targets set by the Plan, and the performance assessment is implemented. 2.1.3 Technical Guidelines and Regulations for Environmental Impact Assessment (1) Technical Guideline for Environmental Impact Assessment: General Principles (HJ 2.1-2016); (2) Technical Guideline for Environmental Impact Assessment: Atmospheric Environment (HJ 2.2-2018); (3) Technical Guideline for Environmental Impact Assessment: Surface Water Environment (HJ 2.3-2018); (4) Technical Guideline for Environmental Impact Assessment: Acoustic Environment (HJ 2.4-2009); (5) Technical Guideline for Environmental Impact Assessment: Ecological Impact (HJ 19-2011); (6) Technical Guideline for Environmental Risk Assessment of Construction Projects (HJ 169-2018). 2.2 Analysis of Compliance with the World Bank’s Safeguard Policies The World Bank has ten safeguard policies in social and environmental aspects. Whether the ten safeguard policies are involved in the project are identified according to the project nature, determined assessment scope and field investigation, with results shown in Table 2-1. Table 2-1 Analysis of Compliance of World Bank Safeguard Policies Involved in the project Applicable No. Safeguard policy Compliance or not 31 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report This Project, by adopting a risk-based comprehensive method, manages the agricultural land polluted by heavy metals and other pollutants, which applies to the safe agricultural product production of the Project counties of Hunan Province. The project aims to prove the efficacy of the risk-based method to manage polluted agricultural lands; therefore it has significantly positive environmental and social benefits. The project’s impact is primarily the impact OP/BP 4.01 created by activities of agricultural land irrigation canals and Environmental 1 other small-sized civil engineering activities. However, if lack Yes Impact of efficient management, the source of heavy metal pollutants Assessment will have substantial impact on the environment and residents’ health, and standard-exceeding agricultural products of the demonstration area, if entering into the market, will have negative impact on the society, and will raise the food safety concerns. As a result, this Project is clarified as category A pursuant to OP4.01 environmental impact assessment. The main contents and conclusions are included in the EIA of this project. Newly-added demonstration areas in each project county are OP/BP 4.04 2 mainly farming areas where the activities of human are No Natural Habitats frequent. They do not involve natural habitats. The policy is not used. The project will not support major OP 4.36 3 changes or degradation activities of important forest regions No Forests or related important natural habits determined by the policy. The project will support sustainable soil management practice to restore and maintain the soil quality, including chemical management. Therefore, Pest Management (OP4. 09) is related to the project. It’s necessary to prepare a pest management plan (PMP), which puts forward pest control and management method, and strengthen the method of integrated pest management (IPM) and recommended application scopes OP4.09 under various conditions, and to provide a list of fertilizers, 4 Pest insecticides and herbicides conforming to category Yes Management requirements recommended by the World Health Organization according to the project demands. PMP should also include training and monitoring programs for project stakeholders, and the implementation of training and monitoring programs should be included in the project cost budget. The PMP prepared for the first batch of sub-projects already covers the newly-added demonstration areas, so no new PMP will be prepared for this batch of sub-projects. OP 4.11 There is no cultural relics protection unit in the newly-added 5 No Material demonstration area. No occupation or removal of graves is 32 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Cultural involved; however, it’s necessary to adopt Disposal Resources Procedures of Cultural Relics Discovery. The construction of this project includes optimizing water management in field, etc. and does not involve the OP/BP 4.37 construction of reservoir dams at the place of water source. 6 Yes Safety of Dam The dams involved in the newly-added demonstration areas are all reservoir dams in the approved demonstration area, and there is no newly-added dam. OP/BP 4.10 The definition of ethnic minority by the World Bank is not 7 Indigenous applicable to the project, and the ethnic minority policy of the No Peoples World Bank is not involved in the project. The civil engineering under the project is to be conducted OP/BP 4.12 mostly in the project villages, and does not require land 8 Involuntary No expropriation or relocation, and does not involve involuntary Resettlement resettlement. OP7.50 Projects on The policy is not used, there is no international waterway 9 No International involved in this demonstration area. Waterways OP 7.60 The policy is not used; there is no international waterway 10 Projects in No involved in the demonstration area. Disputed Areas According to the above identification results, the applicable safeguard policies by the World Bank are as follows: (1) Action strategy/bank procedure of the World Bank: Environmental Impact Assessment (OP 4.01); (2) Action strategy/bank procedure of the World Bank: Pest Management (OP 4.09); (3) Action strategy/bank procedure of the World Bank: Safety of Dam (OP/BP 4.37). 2.3 Analysis of Differences between PRC National, Local Laws and Regulations and World Bank’s Safeguard Policies (1)Differences between PRC National, Local Laws and Regulations and World Bank’s Safeguard Policies ⚫ OP/BP4. 01 Environmental Assessment Generally, the World Bank’s requirements on Project environmental impact assessment are largely consistent with environmental impact assessment requirements in China, with certain differences with respect to focuses and procedures. The World Bank’s 33 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report provisions and requirements are more stringent than those in China, while China has special characteristics in environmental impact assessment. Classification is different. China stipulates in the List of Environmental Impact Assessment a method of quantitative index thresholds, based on which to determine the needs of preparation of environmental impact assessment reports/forms etc, and environmental impact assessment reports will be divided into 3 sub-categories. The World Bank adopts qualitative classification standards. According to the environmental assessment policy and after the judgments of the experts, the sub-projects are divided into three classes: A, B and C. Unlike China, which further distinguishes the work grades and then specifies the EIA scope, time period, content and method after the classification, the EIA work contents of Class A and Class B projects are basically the same according to the policy of the World Bank. Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan is categorized as Project of Category A, for which the EIA shall be conducted in accordance with requirements of the World Bank regarding Projects of Category A. The project impact areas and assessment scope may vary from Project to Project, and the World Bank will have a close look at the impact and potential impact of Projects. Therefore, environmental impact assessment of Newly-added Demonstration Areas of Hunan Integrated Management of Agricultural Land Pollution Project will be conducted by taking into consideration potential impact of the project on the environment, and EIA report shall list the preventive, mitigation or remedial actions proposed to be taken on adverse environmental impact assessment. The tools for environmental impact assessment are different. In China, there are planning EIA, EIA report and EIA form, and World Bank has strategic EIA, regional EIA, ESIA, ESMP, EMP, ESMP, ESMF, ECOP, and hazard and risk evaluation involved in due diligence. Hunan Integrated Management of Agricultural Land Pollution Project has prepared ESMF and ESIA, and ESIA has contained ESMP and ECOP. Public participation. The World Bank places high priority on information disclosure and public participation, and any Project subject to an EIA shall be subject to public 34 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report consultation. For category A Projects, public consultation shall be conducted at least twice, and after the completion of EIA summary and EIA report draft, all EIA reports shall be published in the local public places and media, disclosing the publication date, location and the manners of obtaining of all contents of the EIA (It is not allowed to only publish briefing) and the manner of providing feedback. Related Projects. The World Bank requires Projects or facilities that will be affected by or affect the project to be subject to a due diligence and impact analysis and provision of corresponding measures. During the EIA of the Hunan Integrated Management of Agricultural Land Pollution Project, due diligence for the pollution source that may have any impact on the project-covered regions shall be conducted and mitigation measures proposed. Alternative plan analysis. In China, EIA generally doesn’t require comparison and analysis of all plans for any Project in terms of environmental impact. Though Guideline for Environmental Impact Assessment requires an alternative plan analysis for Projects of category A, in practice, environmental impact assessment generally only relates to the discussion of reasonableness of plans selected after the feasibility study. The World Bank requires alternative plan analysis for all environmental impact assessments, and comparison shall be made for different plans, irrespective of Category A or Category B Projects, regarding the environmental impact, feasibility of mitigation of such impact, investments and operation expenses of mitigation actions, fitness for local conditions and requirements on training and monitoring etc. Those alternative plans may relate to different construction areas, different types of processes, raw materials and operation conditions, different mitigation actions, etc. The EIA for Hunan Integrated Management of Agricultural Land Pollution Project has conducted project counties comparison and selection, Project-covered region comparison and selection, and comparison and selection on Project’s presence or absence, which will provide reasonable basis for decision-making for the project. EMP, ESMP places high priority on the implementation of measures, and ESIA and EIA have special chapters and sections that require the monitoring of Projects during their 35 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report implementation. The latest technical guidelines in China require the monitoring of measures during the implementation of Projects, which is more in accord with the policies of the World Bank. ⚫ OP/BP4. 04 Natural Habitats The World Bank promotes the protection, maintenance and restoration of natural habitats and their functions, and expects borrowers to take preventive measures in natural resources management to ensure the sustainable development of the environment. If any Project contains natural habitat, the project shall arrange environmental protection experts to participate in the preparation, evaluation and inspection of the project, to ensure the preparation and implementation of sufficient impact mitigation measures. The World Bank will not fund any Project that may cause major transformation or deterioration of major natural habitats. China has enacted Regulation of the People's Republic of China on the Administration of Nature Reserves, Regulation on Management of Land in Nature Reserves, Regulation on Protection of Wild Plants and other regulations, and also will not support any Project that may cause any major transformation or deterioration of any major natural habitat. Demonstration Areas of Hunan Integrated Management of Agricultural Land Pollution Project are mainly farming lands with frequent human activities and do not involve natural habitats. ⚫ OP/BP4. 36 Forestry The World Bank raises the concerns on forestry for the purposes of reducing excessive deforestation, improve the environment conditions of forestry, promote afforestation, reduce poverty and promote economic development. The World Bank will not fund the deforesting trade or purchase of tools manufactured by the primary tropical rain forests. The lending by the World Bank in respect of forestry is based on the commitment of government to ensure the administration of the forestry and completion of targeted forestry protection. The Chinese government also makes great efforts in afforestation by adopting policies of forestry protection such as enacting the Forestry Law of the People’s Republic of China, strictly prohibiting the cutting of natural forests, primary forests, and promoting afforestation. Meanwhile, it has issued and implemented a 36 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report number of forest eco-engineering plans to protect eco-system. ⚫ OP/BP4. 09 Pest Management When assisting borrowers in prevention and control of pests that may affect the agricultural safety or public health, the World Bank supports the strategies of promoting ecologic and environmental control approaches to reduce the reliance on chemically synthesized pesticides. Under Projects fund by the World Bank, borrowers shall discuss the pest and inset control in light of the environmental impact assessment of such Projects. In the conduct of Project assessment of any Project that involves pest and disease control, the World Bank will conduct evaluation of the law framework and capacities of institutes of such nation and determine whether such nation may be able to promote and support the pest and disease control that is safe, efficient and environment-friendly. When necessary, the World Bank and borrowers will include certain contents in the project to enhance such capacities. In order to promote the professional prevention and control of crop disease and pest on a uniform basis, the World Bank adopts disease and pest control policies that endeavor to prevent the use and exposure to hazardous pesticides, and the World Bank will not finance any products that is categorized as IA or IB or listed as Category II by WHO. The PRC government has enacted the Uniform Management Regulation on Professional Crop Disease and Pest Prevention and Control, and promotes and supports the development of uniform professional prevention and control organizations, and promotes the professional prevention and control services on a uniform basis, and strives to promote the crop pest and disease prevention and control capacities, to safeguard food security, quality and safety of crops and safety of eco-system. Further, The Chinese government publishes a list of pesticides expressly prohibited and high toxic pesticides prohibited to be used on vegetables, fruit trees, tee trees, Chinese herbal medicines. The World Bank and China are consistent in terms of requirements on control of pests and diseases. ⚫ OP/BP4. 11 Material Cultural Resources Items subject to appraisal under the World Bank’s policies are wider than those in Chinese regulations, and ancestral halls, ancient wells, ancient houses that are not included in protected items in China may be subject to protection under World Bank regulations, 37 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report however the principles are consistent and the management of cultural relics are also consistent between the two. Therefore, the environmental impact assessment of Projects funded by the World Bank conducted by us will further clarify and expressly provide the definitions of material and cultural resources, and will be required to take corresponding protections regarding projects involving material and cultural resources. ⚫ OP/BP4.37 Safety of Dams The World Bank is concerned with the safety of the new dams funded by it and existing dams directly affiliated to the project funded by it. The World Bank requires borrowers to adopt and implement dam safety measures in connection with the dams’ and related buildings’ design, tendering, construction, operation and maintenance. The Chinese government also has strict requirements on dam safety issue, and has issued Regulation on Management of Reservoirs and Dams Safety, and proposes the principle of “safety first” in the construction and management of dams. Construction of dams shall be consistent with the dam safety technical standards enacted by the water authority under the State Council together with competent dam authority. Engineering design is required for the construction of any dam. The engineering design of dams shall be undertaken by the organizations that possess corresponding qualification certificate and a regular dam safety inspection and appraisal system must be conducted. The above requirements are in accord with the policies of the World Bank. ⚫ OP/BP4. 10 Indigenous Peoples The minority ethnic groups in China refer to ethnic groups other than the majority ethnic group in this multi-ethnic nation. In the People’s Republic of China, all the 55 statutorily defined ethnic groups other than Han people, the majority ethnic group, are deemed minority ethnic groups. Certain differences in definition of minority ethnic groups exist between the World Bank (Indigenous People, OP/BP4.10) and China. The World Bank defines minority ethnic group as having the following attributes: 1) The group alleges and is deemed by others to be specific cultural group in the region covered by the project. 2) Primarily attached to the ancestral domains and their natural resources in the region 38 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report covered by the project. 3) Have the traditional cultural, economic, social and political organizations that are distinguished from those of the mainstream society in the region covered by the project. 4) Have its own language that is different from the main language or official language used in the region covered by the project. As illustrated from the above definition of minority ethnic group given by the World Bank, such definition mainly applies to any minority ethnic group that is primarily attached to a certain region and has its own distinct culture and language, while the statutorily defined minority ethnic groups in China that are not primarily attached to a certain region as a group and have no substantial difference from the local major ethnic groups in terms of life style, language will not fall under the definition given by the World Bank regarding minority ethnic group (Indigenous People, OP/BP4.10). The definition of minority ethnic group given by the World Bank will not apply to Hunan Integrated Management of Agricultural Land Pollution Project. ⚫ OP4.12 Involuntary Resettlement In principle, the involuntary migration and resettlement policies in the World Bank Operation Guidance Principles, OP4.12, are not substantially different from those in China. In general, the land expropriation and migration & resettlement policies in the World Bank Operation Guidance Principles, OP4.12, are consistent with those in China in terms of purposes and general procedures. Both take efforts to avoid or minimize involuntary resettlement to ensure the long-term livelihood of prospective migrants, and take actions to restore the living standards of involuntary migrants to their previous standards. In connection with the implementation of involuntary resettlement, both parties focus both on compensation and restoration, supervision and evaluation. However, certain differences exist in terms of specific policies as set out below: Firstly, the World Bank’s policies on involuntary resettlement will cover associated Projects. In that regard, the World Bank raises concerns on not only involuntary resettlement covered by the loan Project but also on involuntary resettlement that are associated with the project, while in China the land expropriation, migration and 39 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report resettlement policies do not cover the associated Projects regarding the project. Secondly, differences regarding compensation paid to legal or illegal buildings and illegal occupants. Generally, under the policies in China, only legal affected buildings or migrants may be entitled to the compensation. In contrast, according to requirements of the World Bank, irrespective of whether the affected buildings or migrants or illegal occupants are recognized by law, they shall be entitled to compensation or will receive other necessary and appropriate resettlement allowance. Third, differences regarding compensation standards. The World Bank OP4.12 requires the compensation in the form of full replacement cost or by exchanging assets for the affected houses and other assets. However, the World Bank also provides that, if the resettlement cost can not be compensated in accordance with the regulations in the nation in which the project is located, then other necessary measures shall be taken to satisfy all replacement cost. This policy disallows the depreciation of asset value, therefore the compensation standards applicable to World-bank-funded Projects are generally higher than those applicable to domestic Projects. Fourth, differences in public participation. Policies and regulations enacted by the Chinese Government regarding public participation and consultation are rather unspecific. Other than for water power plant Projects, polices and regulations in China do not require participation by affected people in the migration plan. In comparison, the World Bank has express requirements regarding the public’s (especially affected people’s) participation in the project design, migration plan, implementation, monitoring and evaluation and the public complaint system, and includes it as a part of information disclosure. The World Bank encourages the project owners to prepare resettlement manuals and distribute them to the public (especially the affected people). Most of civil engineering conducted by Hunan Integrated Management of Agricultural Land Pollution Project is located in the project-covered villages and does not require land expropriation or relocation, and does not involve involuntary resettlement. ⚫ OP/BP7. 50 Projects on International Waterways In connection with each international waterway Project, the World Bank requires the 40 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report agreement or covenant entered into between the beneficiary state and other waterway owning states to include all related issues; and requires that other waterway owning states to give positive reply to the beneficiary state or the World Bank to express their affirmation, non-objection or support of the project or confirm that the project will not prejudice their interests, and that under all other circumstances, the project shall be evaluated by the personnel from the World Bank to make sure not to pose any substantial hazards to other waterway owning states or any major hazards out of water use to those states. In China, there is no law in that regard, so if any Project involves any international waterway, OP/BP7.50 of the World Bank International Waterway shall be referenced. ⚫ OP/BP7. 60 Projects in Disputed Areas The World Bank may fund any Project in a disputed area, as long as under the consent of the government of relevant state. In case of dispute resolution, the project contemplated to be carried out in State A will be conducted not to the detriment of the interests of State B. Currently, China has no such laws, so if any Project involves any disputed area, OP/BP7.60, Disputed Area Projects, shall be referenced. (2) Soil Environment Quality Standards Table 2-2 has listed the heavy metal content limits in agricultural land Soil Environment Quality Standards adopted by certain states and international organizations. The comparison reveals the risk screening value of cadmium as specified in Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial) (GB 15618—2018) (currently applicable to agricultural land in China) is 0.6 (6.5≤pH≤7.5), which is more stringent than international agricultural soil environment standard limits. The setting of standard and selection of control indices vary from country to country due to the differences in management structure, actual soil environment problems and economic and technical conditions, and the foundational work for such standard setting and such selection is large amount of basic study of soil environment and survey and monitoring of soil and related media pollution. Therefore, the soil environment standard adopted for this Project shall be prepared based on Chinese soil foundational study, in light 41 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report of the pollution status and management needs and the circumstances in China, and Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial) (GB 15618—2018), adopted in China shall apply to this Project. Table 2-2 Comparison on Farmland Soil Environmental Standard Heavy Metal Content Standard Limits Screening value (mg/kg) Item ≤5.5 5.5～6.5 6.5～7.5 >7.5 Cd 0.3 0.4 0.6 0.8 China As 30 30 25 20 Pb 80 100 140 240 Cr 250 250 300 350 Item Target value (mg/kg) Intervention value (mg/kg) Cd 0.8 12 Netherlands As 29 55 Pb 85 530 Cr 100 380 Item Heavy metal mass and concentration limit in soil (Soil pH6~7) /( mg/kg) European Cd 1~3 Union Pb 50~300 Cr - Medium Item Standard limit (mg/kg) Farmland Cu ≤125 Japan (dry As ≤15 farmland) Cd (content in rice) ≤0.4 (3) Food Safety Standard The contrast among CAC’s General Standard for Pollutant & Toxin in Food and Feed (CODEX STAN 193-1995) (CODEX STAN 193-1995), EC No. 1881/2006 and Chinese food safety standard, National Standards for Food Safety: Pollutant Limit in Foods regarding the standards of heavy metal content in food (Please refer to Table 2-3) shows that the cadmium content standard in rice provided in Chinese food safety standard complies with that in European Commission, and both are 0.2mg/kg and is more stringent than the standard adopted by CAC, 04mg/kg. Pollutant content limit in food is affected by impact of agricultural production and geographic location, features and control of food contaminants, environment pollution status, resident dietary and consumption patterns. The National Standards for Food Safety: 42 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Pollutant Limit in Foods adopted by the PRC, GB 2762-2012, is adopted by reference to CAC standard, after a risk evaluation based on the food Pollutant monitoring and overall dietary survey data in China as well as in light of the features of staple foods and heavy metal pollution in China. The main purpose of this Project is to lower the content of cadmium in rice produced in agricultural land in China, therefore the agricultural product safety standard adopted by this Project shall be subject to the National Standards for Food Safety: Pollutant Limit in Foods adopted by the PRC, GB 2762-2012. Table 2-3Comparison on Heavy Metal Content Limit in Food Food safety standard adopted by Type of Heavy metal content limit standard in food (mg/kg) major states and international agricultural Cd As Pb Cr Hg organizations product 0.5 (total 0.02 (total Rice 0.2 0.2 1.0 China arsenic) Mercury) National Standards for Food Not Grape 0.05 0.5 0.2 0.5 Safety: Pollutant Limit in Foods provided (GB 2762-2012) Not Orange 0.05 0.5 0.1 0.5 provided Codex Alimentarius Commission Not Not Not Rice 0.4 0.2 (CAC) provided provided provided General Standard for Pollutant Not Not Not Grape 1.0 0.2 and Toxins in Food and Feed provided provided provided (CODEX STAN 193-1995) Not Not Not Orange 1.0 0.1 (amended in 2013) provided provided provided Not Not Not Rice 0.2 0.2 provided provided provided European Union Not Not Not Grape 0.05 0.2 (EU) No 488/2014 provided provided provided Not Not Not Orange 0.05 0.1 provided provided provided 43 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 3 Project Content 3.1 Project objectives 3.1.1 Overall objective Through the analysis on valid data of newly-added demonstration areas of 11 project counties’ rice, endogenous and exogenous agriculture and agricultural production management etc. and in combination with the reality of the demonstration area, the soil pollution risk evaluation, the farmland pollution source risk evaluation and the agricultural management risk evaluation are conducted. The corresponding risk management measures are put forward according to different risk model composition. Finally, it is decided to adopt the integrated management mechanism of risk control to control the farmland risk of the project county to achieve the safety production of qualified agricultural products. 3.1.2 Specific Objectives 1. Based on the scientific pollution analysis method and the valid data of rice, endogenous and exogenous agriculture and agricultural production management, etc., clarify the pollution causes in the demonstration area , carry out the risk level assessment on the selected farmlands in the demonstration area, select applicable comprehensive technical management measures for demonstration, strengthen management and control of farmland pollution sources and farmland pollution risks, and increase the safe utilization level of agricultural resources. By 2022, it can maintain the good agricultural environment in the demonstration area, the heavy metal content of agricultural products basically reaches the standard; total cadmium in soil of the non-polluted farmland won’t increase, and total cadmium and available cadmium in soil of the polluted farmland gradually decreases. 2. Establish an agricultural environment monitoring network and warning system to enhance agricultural environment monitoring and management; develop farmland management tools focusing on risk control, and draw the farmland pollution risk map of the whole area; and formulate farmland environment protection rules, technical guidance, working guidance, etc., and gradually establish and improve laws and standards. 3. Through the technical trainings and propagandas to the government officials, the 44 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report agricultural environment monitoring personnel and the farmers in the demonstration area, demonstrate the feasible measures for farmland pollution management, promote the management and control ability of farmland pollution risks, enable the risks of farmlands in the project to be comprehensively managed and controlled, improve the farmland environment in the demonstration area, and realize a positive cycle of the ecological system. 4. By hiring experts to organize seminars, make the project indicators perfect, collect project data and evaluate, promote the management level of the project management department, finally establish the security system for safe production of agricultural products, and establish and apply land management measures. 3.2 Construction Content of the Project The project construction of newly-added demonstration areas content mainly includes four sections: farmland management demonstration based on risk, agricultural environment monitoring and management, project capability construction, and project management and evaluation. For activities in the project, see Table 3-1. Table 3-1 Activities in Hunan Integrated Management of Agricultural Land Pollution Project (The Third Batch of Subprojects) Amount No. Project activity Activity description (10,000 Source of fund yuan) Farmland management 1 demonstration based on risk Dense monitoring the selected demonstration areas (the density of monitoring point is one point every 50 mu or more, and it is required that there should be no less than 5 samples in each demonstration area; for World Bank Dense monitoring soil and agricultural products, monitor the heavy metal contents loan: 94.5%+ 1.1 and risk grade corresponding to each other; for sediments, monitor the heavy metal 551.37 supporting evaluation content, and for irrigation water, monitor water quality and the heavy funds: 5.5% metal content, etc.), carry out the risk level assessment according to the monitoring data, and determine the comprehensive risk management and control measures and schemes. Integrated risk Adopt targeted risk management and control measures based on analysis of effective data of rice, endogenous agriculture, exogenous agriculture 1.2 management and and agricultural production management in the project. For the specific control measures content, see 1.2.1 to 1.2.4. Engineering In newly-added demonstration areas of 11 project counties, build or World Bank 1.2.1 1,142.89 measures reconstruct 87.25km of channels (the length of single channel project is loan: 94.5%+ 45 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 500~1000m), 51 grit chambers (the length, width and height are supporting 2*2*1m), 43.73km of farm tracks, 3,000m of ecological interception funds: 5.5% ditches, 32 small impounding reservoirs and 1 electric pumping station in total. Reconstruct 14170m of irrigation channels, 1980m of farm tracks in 4 1.2.1.1 Yongding District newly-added demonstration areas There is no new construction project for the newly expanded areas in the 1.2.1.2 Jishou City old demonstration areas and there are only agronomic measures are implemented Reconstruct 12500m of irrigation channels, 4 grit chambers in the two 1.2.1.3 Yongshun County newly-added demonstration areas. In the one newly-added demonstration area and four old demonstration areas, a total of 34,880 m of irrigation channels have been reconstructed, 1.2.1.4 Cili County 5 grit chambers have been built, 27,250 m of farm tracks have been built, and 3000m of ecological interception ditches have been built. A new demonstration area is added, which does not involve engineering 1.2.1.5 Huayuan County measures. Two new demonstration areas have been added, and implementation area of the other project has been expanded, with a total of 8000m channels, 1.2.1.6 Anhua County 5500m farm tracks and 1 electric pumping station constructed or renovated. In the two demonstration areas, a total of 4000m of irrigation channels, 3 1.2.1.7 Hengyang County water conservancy supporting facilities and 600m of slope protection have been newly built or renovated. Build or reconstruct 2700m of irrigation channels, 26 grit chambers, 1.2.1.8 Hengnan County 3300m of farm tracks, 9 small impounding reservoirs in total three villages of the 2 newly-added demonstration areas. Build or reconstruct 8800m of irrigation channels, 16 grit chambers, 1.2.1.9 Lengshuitan District 5700m of farm tracks and 23 small impounding reservoirs in 3 demonstration areas. The implementation area of the original three demonstration areas has 1.2.1.10 Linwu County been expanded, all of which do not involve new construction project. A new implementation area of Xiaojia demonstration area has been 1.2.1.11 Qiyang County added and 2200m of farm tracks had been built. World Bank Agricultural Control high accumulation rice variety, optimize field moisture loan: 94.5%+ 1.2.2 management (flooding irrigation), soil acidification (pH value), apply 7,011.61 measures supporting organic fertilizer, apply soil passivator and remove straw from field. funds: 5.5% Popularize agricultural cleaning production, encourage farmers to apply World Bank Integrated pest organic fertilizer, reduce use amount of fertilizer, scientifically apply loan: 94.5%+ 1.2.3 pesticide, popularize professional unified green prevention and control on 216.9 management supporting pests of agricultural crops and popularize high effective, low toxic and funds: 5.5% low residue pesticide and modern plant protection machine. 1.2.4 Other measures Develop research on rice safety production appropriate technology in demonstration area on the basis of list emergency cadmium low accumulated rice variety recommended in Hunan Province to screen rice variety in demonstration area reasonably to determine cadmium World Bank (1) Variety screening loan: 94.5%+ accumulation index in main popularized rice variety in the area; when the 464.47 BCF index of rice variety is higher than Level-VI risk, its variety supporting cadmium accumulation risk is pretty high and control its access to funds: 5.5% demonstration area. Control of the For standard-exceeding rice, carry out acquisition by special enterprises, (2) the purchased rice is used as industry grains and feedstuff or used for standard-exceeding other industrial purposes. Make subsidies to the acquiring enterprises, 46 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report rice with the subsidy standard of 20% of purchase price Certification of place Subsidize the main body gaining no-pollution, green and organic food (3) of origin of certification of with subsidy standard of 5000/10000/20000 Yuan agricultural product respectively. Construction, publicity and Encourage demonstration area to construct, publicize and popularize (4) promotion expenses brand of agricultural product to improve economic value of product of agricultural product brand Employ professional supervision institutions and organize township and village personnel to supervise implementation of agricultural measures World Bank 1.3 Project supervision (apply lime, organic fertilizer, passivator, flooding irrigation and removal 399.72 loan: of straw from field) and supervision expenses shall be calculated based on 20 Yuan/mu/season. Strengthen agricultural 2 environmental monitoring and management Establishment of 2.1 agricultural Including sampling inspection van, desktop computer, sampler, GPS environment position indicator, settling barrel and digital altimeter, etc. monitoring database and early warning Preparation of Establish model based on various monitoring data in sub-project 1 to agricultural provide fundamental support for management of agricultural risk World Bank management tools 2.2 management and determine agricultural land and crop pollution risk level loan: 52.9%+ and agricultural risk 574.46 based on organic combination of effective data and management tools supporting drawing based on and formulate agricultural production risk map in the whole province. funds: 47.1% risk Develop and issue local regulatory systems and technical standards Development and related to prevention, control and rehabilitation of agricultural land and 2.3 issuing of local guide integrated management and control of agricultural land pollution policy and standard management and control in various demonstration counties Research on sustainable Research sustainable financing mechanism and ecological compensation investment and mechanism aiming at long-term agricultural land pollution management 2.4 financing mechanism and soil health recovery action so as to guarantee sustainable agricultural and ecological development in Hunan compensation mechanism Cultivate the management and technical capability of government officials, organize international and domestic studies and training; conduct training for environment monitoring personnel and farmers, and World Bank provide technical assistance for enterprises involved in heavy pollution; loan: 90% + 3 Capacity building 1,222.92 and conduct activities on project concepts and technical popularization in supporting the form of seminars, training, etc., and share and popularize project funds: 10% experience and technology by means of preparing video, paper documents, etc. Provide technical assistance and training for project management personnel (procurement, finance and security policy) to improve its World Bank Project management management capacity, purchase office equipment necessary for project loan: 23.4% + 4 737.51 and evaluation management institution as well as project daily management, supporting procurement and financial management, etc. Conduct project funds: 76.6% startup/completion seminars, and establish the Mis system; and collect 47 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report relevant information and data related to the environmental quality changes of farmlands in the project implementation process, and carry out monitoring and evaluation on the project implementation results. 3.3.1 Farmland Management Demonstration Based on Risk 3.3.1.1 Encrypted Monitoring and Risk Level Assessment Carry out an encrypted monitoring on soil, sediments, irrigation water, atmospheric sedimentation, agricultural products, plants, agricultural inputs, agricultural diseases and pests, etc. in each demonstration area according to the requirements in the monitoring scheme, and conduct the risk level assessment according to detection data. 3.3.1.2 Integrated Management Measures for Agricultural Land Risk Take specific risk management measures based on the analysis on effective data of rice, endogenous agriculture, exogenous agriculture and agricultural production management. (1) Engineering Measures Engineering measures mainly include channel engineering, ecological engineering and road engineering. The infrastructures of agricultural lands in the demonstration areas are rather complete and run well, but some irrigation channels for the agricultural lands are still earth channels, or are seriously damaged and required to be reconstructed; the heavy metal content of sediments in some channel exceeds the standard, sedimentation tanks are required to be built to settle sediments of irrigation water so as to prevent them from entering into the agricultural lands, and meet the requirement of optimizing agricultural land water management; and some infrastructures such as agricultural land tracks have imperfect supporting, which is not good for operations of mechanical field work suck as applying lime, removing straws out of the agricultural lands, etc. In newly-added demonstration area, build or reconstruct 87.25km of channels (the length of single channel project is 500~1000m), 51 grit chambers (the length, width and height are 2*2*1m), 43.73km of farm tracks, 3,000m of ecological interception ditches, 32 small impounding reservoirs and 1 electric pumping station in total. (2) Agronomic Measures 48 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Select 2995.31 hectares in the newly-added demonstration area, comprehensively demonstrate and popularize the measures of highly accumulative rice variety control, agricultural land water management optimization, soil acidification conditioning, applying organic manure, soil passivator application, etc., so as to guarantee the cadmium content of rice to be controlled within 0.2mg/kg and achieve the purpose of safe production of qualified agricultural products. (3) Other Measures These measures mainly include variety screening, standard-exceeding rice management and control, pollution-free and green agricultural product certification, agricultural product brand building, propaganda and promotion, etc. 3.3.1.3 Project Supervision Hire a competent agricultural supervision agency to organize personnel in towns and villages to supervise the implementation of agronomic measures (applying lime, manure and passivator as well as carrying out waterflooding to irrigate and removing rice straws out of the farmlands) in the project. 3.3.2Agricultural Environment Monitoring and Management 3.3.2.1 Establishment of Agricultural Environment Monitoring Database and Warning The PPMO establishes an agricultural environment monitoring and warning platform, establishes the agricultural land risk database, and forms the agricultural environment monitoring and warning system; it timely digitizes the monitoring results of the agricultural land pollutants monitoring points in the project counties, and carries out real-time warning on possible exogenous and endogenous pollution risks in the monitoring points; and it positions, monitors and evaluates the effect and benefits for integrated management of polluted agricultural lands for a long time, prevent the agricultural land pollution area from enlarging and aggravating in the extent, and provides guidance on integrated management and control of heavy metal pollution in the agricultural lands of the project counties as well as the adjustment of growing structure. 49 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 3.3.2.2 Formulate and Issue Local Regulations and Technical Standards Drafts According to the needs of the project, make and issue local regulations and technical standards drafts in some parts as well as establish and improve the standard system of regulations step by step. 1. Research and formulate the integrated management mechanism on agricultural land pollution risks, optimize farmland management for non-polluted farmlands, launch new agricultural technology, and prevent and restrict the generation of new pollution; and effectively carry out risk control on already polluted agricultural lands, stopping migration and transformation. 2. Formulate local laws and regulations as well as relevant plans for quality safety of agricultural products, and particularly propose the treatment schemes on standard-exceeding agricultural products. 3. Establish the county-level environmental supervision system. Supervise the input of agricultural land soil hazardous substances in the long term and set up early warning and prevention for external pollutants coming into the arable land. Make full use of the environmental supervision network to strengthen the construction of the agricultural land environmental protection law enforcement system. 4. Research and work out the eco-compensation mechanism required by effective control at various agricultural land pollution risks, including economic compensation, compensation ways, compensation objects and management methods. 3.3.3 Capability Building 3.3.3.1 Development of Management Capability 1. Investigation: it includes foreign and domestic investigations. It is organized by the PPMO in a unified manner to investigate and study the advanced heavy metal pollution treatment technology and experience in China and abroad. It is planned that during the five years of project implementation, 237 persons per day of abroad investigations and 2,360 people per day of domestic investigations participated in total for relevant managers in the 50 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report project countries. 2. Domestic training: it includes the training regarding to risk-based integrated agricultural land management, agricultural environment monitoring, pollution prevention, policy execution, purchasing, finance, etc., and there are 2422 persons per day in total. 3. Technical assistance: hire relevant technical experts to provide technical support to the project so as to guarantee smooth implementation of the project, and there are 2,400 persons per day in total. 3.3.3.2 Project Knowledge Management and Farmer Training 1. Information dissemination: make videos and paper documents etc. to publicize and summarize the project. 2. Farmer training: combine centralized training with on-site training to improve the farmers’ understanding on agricultural land heavy metal pollution and guarantee the effective publicity of the project-related technologies. 5,938 persons per day in total. 3.3.3.3 Discussion and promotion of achievements By preparing videos, paper documents, etc., summarize the experience obtained from the project implementation process, and popularize relevant technology, achievements to non-demonstration areas even other peripheral counties and cities in the manner of symposiums, document preparation, etc. 3.3.4 Project Management and Assessment 3.3.4.1 Project Management Project management includes technical assistance to the project, training on purchasing and financial management for managers, project management expenses and expenditures to start/complete the seminars, and costs to purchase relevant required office equipment. 3.3.4.2 Project Monitoring and Assessment Monitor and evaluate the project implementation achievements as well as the environmental, social impacts, etc., collect relevant information and data for project implementation, conclude experience and lessons, and organize the project startup 51 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mobilization meeting, the mid-term communication meeting, the project completion seminars, etc. 52 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 4 Current Environment State 4.1 Natural Environment 4.1.1 Geographical Location Hunan Province is located in central China and middle reaches of Yangtze River; as the major part is located in the south of Dongting Lake, it is named as “Hunan”; in addition, as the largest river Xiangjiang River flows through the whole province, it is short for “Xiang” whose capital is Changsha. Hunan is located in 108°47′E-114°15′E and 24°38′N-30°08′N. The straight-line distance from the east to the west is 667km and the straight-line distance between the south and north is 774km. Its total area is 211,800km 2, accounting for 2.2% of national land area. The heavy metal pollution of soil in Hunan Province is mainly shown as “one basin and two areas”. One basin: Xiangjiang River basin; two areas: south Hunan area and west Hunan area. The distributive characteristic of the project counties of Hunan Integrated Management of Agricultural Land Pollution Project are shown in Figure 4-1. Anhua County, Hengnan County, Yizhang County and Lengshuitan District in Yongzhou are located in “one basin” area of Xiangjiang River; Jishou City, Yongshun County, Baojing County, Huayuan County, Cili County and Zhongfang County of Huaihua City are located in west Hunan area; Yizhang County, Linwu County, Hengyang County, Hengnan County, Lengshuitan District and Qiyang County in Yongzhou City are located in south Hunan area. Refer to Figure 4-1. 53 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Figure 4-1 Map of Key Polluted Area in Hunan Province 4.1.2 Landform Hunan Province’s landforms are various but mainly mountains and hills.They could be divided roughly into “70% hills, 20% water and 10% field”; Mountain occupies 51.2% of total area of the whole province, hills and downlands occupy 29.3%, plains occupies 13.1% and water occupies 6.4%. Three sides of Hunan Province are surrounded by maintains to form asymmetric horseshoe shape from east, south and west sloping to northeast. The lowest point in Hunan is Huanggai Lake in Linxiang County with altitude of 24m; the highest point is Huping Mountain in Shimen with altitude of 2099m. 4.1.3 Climate Located in 25°N -30°N, Hunan has the subtropical monsoon humid climate with annual average temperature of 16-18℃ and annual average rainfall of 1200-1800mm. The climate characteristics could be summarized as: humid climate, distinguished four seasons, sufficient heat; centralized rainfall, changeable temperature in spring, dryness in summer and autumn, short chilly period and long hot period. 54 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 4.1.4 Surface Water Hunan has blue mountains and green rivers with dense river network and developed water system. The total length of rivers inside Hunan is over 99,300km, the basin area is nearly 210,000km2 and its annual average runoff is 162.3 billion m3. The total volume of runoff of Xiangjiang River accounts for 41%, Yuanjiang River accounts for 24.2%, Zishui River accounts for 13.4%, Lishui River accounts for 8.3% and other lake systems account for 13.1%. There are 5,341 rivers with the length over 5km and the area of fresh water reaches13,500km2; Dongting Lake is the second largest freshwater lake in China; Xiangjiang River, Zishui River, Yuanshui River and Lishui River cover the whole province. Among them, Xiangjiang River is one of seven branches of the Yangtze River and the total amount of natural water resource in the whole Hunan Province is the largest in nine provinces of south China. Except extremely few rivers in south and east Hunan Province belong to the Pearl River and Ganjiang River system, other rivers all belong to Yangtze River. The Province’s water system is mainly represented by Xiangjiang River, Zishui River, Yuanshui River and Lishui River as well as Dongting Lake; they converge into Dongting Lake from the west, south and east to form a fan-shape water system. The highest level and the maximum flow of river generally occur in April and June; the lowest level of all the rivers occurs in November - February in the next year. 4.1.5 Basic Condition of Dams Dam safety analysis and evaluation have been carried out in the first and second batch of sub-projects of Hunan Integrated Management of Agricultural Land Pollution Project, the list of 36 reservoir dams triggering the World Bank’s dam safety policy OP4.37 in the Hunan Integrated Management of Agricultural Land Pollution Project and the safety and management on the dams have been expounded, and the 2015 Dam Safety Evaluation Report of Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (the first batch of sub-projects) and the General Dam Safety Evaluation Report of the Second Phase Project on Hunan Integrated Management of Agricultural Land Pollution have been submitted. 55 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report In the two years since the implementation of the project, the provincial PMO has recruited senior dam safety experts in China to inspect and evaluate the dam safety of the reservoirs involved in the project and put forward opinions and suggestions. The specific tasks of the experts are as follows: 1) To review the reports and information on dam safety provided by every PMO and the dam management unit. 2) To conduct on-site inspections on dams included in the World Bank’s dam safety policy every year. 3) To put forward evaluation opinions and suggestions on the safety status and operation and maintenance status of each dam, and put forward reinforcement opinions and suggestions to remove danger for the dams that need to be reinforced. 4) To assist the provincial PMO to make the annual dam safety report once a year, which includes the safety evaluation content and examination conclusion on each reservoir dam, reinforcement construction to remove danger, operation and maintenance, dam emergency plan, suggestions, etc. According to the opinions and suggestions on dam reinforcement to remove danger, PMO of every county has completed reinforcement to remove danger for the dams included and carried out regular maintenance. Up to now, the dams involved in the project are running well and there has been no dam safety failure. Some irrigation water sources in the newly added demonstration areas of Hengyang County, Cili County, Lengshuitan District and Qiyang County are reservoirs, all of which are among the 36 reservoirs of the project that has been approved for the first and second batches. No new reservoir dam has been added in the newly added demonstration areas. Therefore, new dam safety evaluation report is not required for this batch of project. 4.2 Ecological Environment 4.2.1 Soil Type As natural conditions in Hunan Province are complicated and its east, south and west are surrounded by maintains; its north is the lake plain while central downland Basin is staggered with huge topographic change. The patent soil materials are diverse and it enjoys 56 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report a long history in agriculture; both horizontal and vertical band spectrum distribution principle and various structural forms of regional distribution exist in soil distribution. The soil in the whole province is divided into zonal soil and azonal soil. There are 9 soil types, 24 sub-types, 111 soil debris and 418 soil species. The zonal soil is mainly red soil and yellow soil which is mainly divided by Donglu Line, Xuefeng Mountain, Wulingyuan; the east side of this line is mainly red soil while its west is yellow soil. The azonal soil is mainly moisture soil, rice soil, limestone soil, purple soil, etc. Red soil is the main soil in Hunan whose area is about 36.3% of total land area of Hunan Province; generally, its soil layer is deep with strong acidity and small organic matter; it is sufficient in Fe and Al while it lacks nutrient and fertility is low. It is mainly distributed in hills and mountains in the east of Xuefeng Mountain, Wuling and Xiangjiang River and Zishui River area, which is suitable for developing oil tea, tea, orange and other cash crops. The area of yellow soil accounts for 15.4% of total land area in Hunan Province, which is mainly distributed in Xuefeng Mountain and Nanling Mountain area. The soil presents acid reaction whose natural fertility is higher than that of red soil. Moisture soil is formed by river and lake sediments with deep soil layer, appropriate texture, rich nutrient and wide adaptability and the major part has been cultivated as rice soil. Moisture soil (excellent dry soil) only occupies 2.5% of total land area of Hunan Province. Rice soil is the main agricultural soil in Hunan Province, accounting for 19% of the total land area. Generally, it is clearly-layered with plough pan. The content of organic matter is 2.3%, and the iron is with strong activity. Rice soil and moisture soil are distributed in Dongting Lake area and costal area of Xiangjiang River, Zishui River, Yuanshui River and Lishui River, which are suitable for developing rice, cotton, fiber crops, rape and other cash crops. The area of limestone soil accounts for 6.9% of total land area of Hunan Province, which is mainly distributed in Wuling Mountain area in northwest Hunan and limestone area in central and south Hunan; the topsoil is nearly neutral with bountiful content of limestone which is suitable for growth of tung tree, sapium sebiferum, raw lacquer and cypress. The area of purple soil is about 1,333,300 hectares, mainly distributed in Hengyang Basin and Yuanma Basin and accounting for 6.3% of total land area in Hunan Province. Purple soil is full of 57 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report phosphorus and potassium, suitable for growth of cash crops. 4.2.2 Soil Organic Matter The content of organic matter in soil of typical agricultural land in Hunan Province is pretty bountiful. The content of organic matter of topsoil 0-20cm of typical agricultural land in Hunan Province is mainly in Level-I, II and III. Its scope of content is 8-66.1g/kg with average value of 30.43g/kg. The content of organic matter≥20g/kg accounts for 88.8%; the content of organic matter≥30g/kg accounts for 44.4%; the content of organic matter<20g/kg accounts for 11.2%. The scope of organic matter of underearth 20-100cm soil is 3.9-41.9g/kg with average content of 11.91 g/kg; the content of organic matter is mainly distributed in 6-19.9g/kg. 4.2.3 Content of Nitrogen, Phosphorus and Potassium in Soil The total nitrogen content of typical agricultural land soil 0-20cm and 20-100cm in Hunan Province is 1.79g/kg and 0.82g/kg respectively. The average content of total phosphorus of typical agricultural land soil 0-20cm and 20-100cm is 0.56g/kg and 0.44g/kg respectively. The scope of content of effective phosphorus in 0-20cm soil of agricultural land topsoil is among 2.53-92.2 mg/kg with average content of 17.01mg/kg; the scope of content of effective phosphorus in 20-100cm soil in bottom layer is among 1.9-29.9 mg/kg with average content of 8.2 mg/k. The average content of all potassium of typical agricultural land topsoil 0-20cm of Hunan Province is 17.13g/kg; the average content of all potassium of 20-100cm soil is 17.17g/kg. 4.2.4 Soil pH The typical agricultural land topsoil in Hunan Province is mainly acid soil, and the range of pH value is 5-7, while the subsoil is mainly micro-acid soil to micro-alkaline soil. There are two possible main reasons resulting in soil acidification in Hunan Province: Atmospheric environmental pollution results in the increase of acid sedimentation so the speed of soil acidification in the area influenced by acid sedimentation is accelerated; inappropriate agricultural measures accelerate soil acidification. 4.2.5 Agricultural ecology There are many people in Hunan while the land is limited so the pressure on 58 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report protection of cultivated land and occupation complement balance is huge; in addition, the multiple crop index of cultivated land and the stock capacity is large; productive infrastructure is generally old and transport infrastructure in some villages is still weak. Meanwhile, water loss and soil erosion, water and soil pollution and other problems are very prominent due to excessive exploitation of natural resources and excessive application of fertilizer, pesticide, agricultural film and other chemical products which not only makes field weaker and weaker, but results in serious non-point pollution and white pollution; in addition, industrial pollution and domestic sewage pollution are serious, so agricultural environment problems are becoming more and more serious, which seriously endangers sustainable agricultural development and quality and security of agricultural products; in particular, the influence of “rice contaminated by Cadmium” accident in 2012 on grain production in Hunan is not completely eliminated until now. 4.3 Social and Economic Environment 4.3.1 Social and Economic Environment in the Whole Province (1) Population and Administrative Division By the end of 2019, the province’s permanent population was 69.184 million. And the urban population is 39.587 million. The province governs 13 cities, 1 autonomous prefecture and 122 counties (cities and districts), including 36 municipal districts, 18 county-level cities and 68 counties (including 7 autonomous counties). There are 403 sub-districts, 1138 towns, 309 townships and 83 ethnic townships in the province, with a total of 1933 township level divisions, with towns accounting for 79.7% of the total number of townships. (2) Economic Condition The GDP in 2019 was 3975.21 billion yuan, an increase of 7.6% over the previous year. The added value in the first industry was 364.69 billion Yuan, with the growth of 3.2%; in the secondary industry 1494.7 billion Yuan, growth of 7.8%; in the tertiary industry 2115.82 billion Yuan, growth of 8.1%. The total regional output value per capita was 57,540 Yuan with the growth of 7.1% calculated based on permanent resident 59 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report population. (3) Overview of Agricultural Production In 2017, it realized an added value of RMB 385.02 billion in the agricultural, forestry, animal husbandry and fishing industries in the whole year with a growth rate of 3.5% compared with same period last year. Among them, the added value of agriculture was 212.4 billion yuan, an increase of 3.6%; the added value of forestry was 31.92 billion yuan, an increase of 9.4%; the added value of animal husbandry was 91.63 billion yuan, a decrease of 2.2%; the added value of fishery was 28.75 billion yuan, an increase of 7.1%. The grain planting area in Hunan Province was 4.6164 million hectares in 2019 with the reduction of 0.1315 million hectares compared with last year. Among them, summer grain crops cover 102,500 ha, a decrease of 21,200 ha; early season rice covers 1,094,600 ha, a decrease of 143,600 ha; autumn grain crops cover 3,419,300 ha, an increase of 33,300 ha. In terms of autumn grain crops, middle season rice and single-season late rice cover 1,602,100 ha, an increase of 129,600 ha; double-season late rice covers 1,158,500 ha, a decrease of 139,800 ha. Annual grain yield was 29.748 million tons with the reduction of 1.6%. Among which the summer grain output was 413000 tons with the reduction of 19.6%; that of early rice was 6.614 million tons with the reduction of 12.5%; the autumn grain was 22.721 million tons with the growth of 2.5%. The planting area of cotton in the whole year was 63000 hectares with the reduction of 900 hectares; that of sugar material was 7400 hectares with the growth of 30 hectares; that of oil material was 1365500 hectares with the growth of 20800 hectares; that of vegetable was 1313200 hectares with the growth of 48300 hectares. The cotton production is 82 thousand tons, representing a decrease of 4.5% than last year; the oil crops have increased 2.0% to 2.392 million tons; 184 thousand tons of flue-cured tobacco have been produced, with a decrease of 2.5%; tea production has grown 8.7% to 234 thousand tons and 39.694 million tons of vegetables have been yielded with a growth of 3.9%. The annual total output of pork, cattle, sheep and poultry was 4.568 million tons, a decrease of 15.3% over the previous year. Of which, the pork production has plunged 22.0% to 3.485 million tons, the beef production has grown 6.1% to 190 thousand tons, the 60 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mutton production has increased 6.7% to 159 thousand tons and the poultry production has soared 22.9% to 734 thousand tons. There were 48.129 million live pigs, a decrease of 19.7%; 1.625 million cattle, an increase of 6.4%; and 9.715 million sheep, an increase of 6.6%. At the end of the year, there were 26.983 million live pigs in stock, a decrease of 29.4% over the previous year; 2.48 million fertile sows in stock, a decrease of 34.5%; 4.104 million cattle in stock, an increase of 6.5%; 7.122 million sheep in stock, an increase of 6.6%. The total production of poultry and eggs has increased 8.8% to 1.147 million tons. The milk production has grown 1.6% to 63 thousand tons. And the aquatic products have grown 3.0% to 2.544 million tons. 30.2 thousand hectares of effectively irrigated farmland and 38.7 thousand hectares of water-saving irrigated area have been newly added this year. 75 thousand sites of water conservation projects have broken ground with a total fund of 26.7 billion yuan. It have finished 1.02 billion cubic meters of water conservation earthwork and renovated 5445.8 kilometers of rural roads. 4.3.2 Social Economic Condition of Project Counties (1) Analysis of Social-economic Status of Yongding District In 2019, the GDP of Yongding District is 22.957 billion yuan, with a year-on-year growth of 7.8%, which is 1.7%, 0.2% and 0.2 percentage points higher than the average level of the whole country, the whole province and the whole city respectively. Viewing the industries respectively, the first industry has accomplished an added value of 2.194 billion yuan, the second industry has gained an added value of 3.416 yuan and the tertiary industry has fulfilled an added value of 17.347 billion yuan. The growth rates are 3.2%, 6.7% and 8.5% respectively. The contribution rates to GDP of the three industries are respectively 3.46%, 13.27% and 83.27%, driving up the GDP for 0.3, 1.0 and 6.5 percentage points respectively. The structure of the three industries was adjusted from 8.8:15.5:75.7 to 9.5:14.9:75.6. The total regional output value per capita was 48,474 Yuan with the growth of 6.4% calculated based on permanent resident population. At the end of 2019, the total number of registered residence households in Yongding District was 193948, and the total registered residence population was 481342. Among 61 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report them, there were 199928 urban residents, 281414 rural residents, 244723 men, 236619 women, 89208 persons aged 60 and over. By the end of the year, there were 477800 permanent residents and a total of 179800 households, Of which, the male and female populations are respectively 243700 and 234100. 275300 people have gained permanent urban residence while 202500 people have lived in rural areas lastingly. The urbanization rate has reached 57.62%. In 2019, there were 5024 births and 2872 deaths, with a mortality rate of 6.05 ‰, a natural population growth rate of 5.8 ‰, and a sex ratio of 112.7. In 2019, the total output value of agriculture, forestry, animal husbandry and fishery service industry in Yongding District was 3607.18 million yuan, a year-on-year increase of 3.4%; the sown area of grain crops was 415000 mu, a decrease of 1.1%. Among them, the planting area of rice is 237900 mu, the corn planting area is 91000 mu, and the potato planting area is 25200 mu. The main planting structure is single cropping system, and the main ways are rice-rape and rice-vegetable. The total grain yield has been up to 145.534 thousand tons, registering an increase of 1.6%. Vegetable planting area was 205400 mu, an increase of 0.5%, and vegetable output was 382676 tons, an increase of 2.4%. In the 5 risk factors including cadmium, arsenic, mercury, lead and chromium, as demonstrated by the monitoring data of earth-cultivated crops, the rice of Yongding District might be polluted by heavy metals, and cadmium proves the major one to blame. (2) Analysis of Social-economic State of Jishou City In 2019, Jishou City has fulfilled a gross regional product of 19355.6 million yuan, representing a growth of 7.2% than last year. Of which, the first industry added a value of 837.73 million yuan with a growth of 3.6%, the second industry added a value of 6808.96 million yuan with a growth of 3.2% and the tertiary industry added a value of 11708.91 million yuan with a growth of 9.9%. The total regional output value per capita was 53,766 Yuan with the growth of 5.1% calculated based on permanent resident population. By the end of 2019, 312.4 thousand people have gained registered residence in Jishou City, with an increase of 0.26% than last year. The number of permanent residents has reached 361.8 thousand with a growth of 1.01%. The total urban population of this city is 268.4 thousand, with an urbanization rate of 74.18% and a growth of 0.12 percentage point. 62 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report The birth rate of the city is 11.55‰, with a drop of 1.82 ‰. And the mortality rate is 6.89‰, with an increase of 1.4 ‰. The natural population growth rate has reduced 3.21 ‰ to 4.67‰. In 2019, the planting area of grain crops in Jishou City was 8754 hectares, a decrease of 1.5% year on year. Among them, the sown area of rice was 5607 hectares, a decrease of 1.9%; the sown area of corn was 1390 hectares, a decrease of 1.1%; the sown area of beans was 590 hectares, an increase of 1.7%; the sown area of potato was 1153 hectares, a decrease of 1.4%. The sown area of oilseeds was 4507 hectares, a decrease of 1.0%. The vegetable planting area is 6080 hectares, which is basically the same as that of the previous year. The tea planting area has surged 38.3% to 5873 hectares. The area of kiwifruit orchard was 457 hectares, a decrease of 12.8%, and that of citrus orchard was 4597 hectares, a decrease of 23.9%. Jishou City has 10823 hectares of arable land and 7758 hectares of basic farmland. In 2019, the total grain output of Jishou City was 48171 tons, a year-on-year decrease of 0.4%. Among them, the output of rice is 36050 tons, a decrease of 0.2%; the corn output is 6120 tons, a decrease of 1.6%; the output of beans is 1001 tons, a decrease of 1.5%; the output of potato is 4970 tons, a decrease of 0.5%. The oilseeds production was 6431 tons, a decrease of 2.9%. The vegetable output was 101965 tons, the growth rate was basically the same in the same period. Tea output was 1350 tons, an increase of 43.9%. The yield of kiwi fruit was 3980 tons, a decrease of 2.7%; the yield of citrus fruit was 87828 tons, a decrease of 9.7%. It is shown by soil agricultural product monitoring data that among five risk factors of cadmium, arsenic, mercury, lead and chromium, heavy metal pollution risk exists in rice in Jishou with main risk factor of cadmium. (3) Analysis of Social-economic State of Yongshun County With economic development lagging behind, this county is weak in industry and finance in Xiangxi Prefecture. In 2019, 45 poverty-stricken villages and 19414 people were lifted out of poverty, thus the whole county achieved poverty-elimination In 2019, the GDP of Yongshun County was 8.64 billion yuan, an increase of 6.7% 63 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report over the previous year. Among them, the first industry was 1.923 billion Yuan, with the growth of 3.0%; the secondary industry was 1.536 billion Yuan, with the reduction of 1.2%; tertiary industry was 5.181 billion Yuan, with the growth of 10.8%. According to the resident population, the per capita GDP was 19372 yuan, and the three industrial structure of the county was adjusted from 23.7:21.9:54.4 to 22.3:17.8:59.9. In 2019, the sown area of crops in Yongshun County is 980700 mu, an increase of 0.15%, and the total grain output is 218000 tons, an increase of 2.97%; The total output of rice was 142014 tons, an increase of 0.34%; the total output of corn was 36987 tons, an increase of 13.36%; the output of sweet potato was 7948 tons, an increase of 0.91%; the output of potato was 27680 tons, an increase of 5.58%; the output of soybean was 3131 tons, an increase of 5.99%; the output of mung bean was 148 tons, an increase of 0%; the total output of oil was 18864 tons, an increase of 1.68%; the total output of peanut was 4644 tons, an increase of 2%; the total output of rapeseed was 14206 tons, an increase of 1.59%; The total output of vegetables was 126965 tons, an increase of 3.32%. The total area of fruit is 168,000 mu, and the total output is 168,619 tons, an increase of 1.9%. As the Yongshun County is in mountain area, and rice planting is generally single cropping with main planting type of “rice-rape” and “rice-idle”. It is shown in the inspection result of soil heavy metal pollution of agricultural land in Yongshun County that heavy metal pollution exists in partial agricultural land soil in Yongshun County to different degrees with main pollution risk element of cadmium. (4) Analysis of Social-economic State of Cili County In 2019, the GDP of Cili County was 17828.53 million yuan, an increase of 7.4% over the previous year. Among them, the added value of the first industry was 3168.3 million yuan, an increase of 3.4%; the added value of the second industry was 3110.78 million yuan, an increase of 6.8%; the added value of the industry was 1461.13 million yuan, an increase of 7.5%; the added value of the construction industry was 1651.61 million yuan, an increase of 6.1%; the added value of the tertiary industry was 11549.45 million yuan, an increase of 8.7%. The per capita GDP of the whole county is 28,834 yuan. The added value of the first, second and tertiary industries accounted for 17.8:17.4:64.8 of the county’s 64 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report GDP. At the end of 2019, the total number of households in Cili County was 240,637, with a total registered population of 690,390, of which 353,916 were males and 336,474 were females. The ratio of male to female is about 105:100. At the end of the year, the urban registered population was 154,470, an increase of 8.8%, and the rural population was 535,920. In 2019, the output value of planting industry in Cili County is 2889.79 million yuan, and the added value is 2087.08 million yuan, an increase of 4.2%. The grain planting area of the county is 875200 mu, and the total grain output reaches 316600 tons, with a year-on-year increase of 3.6%; the oil planting area is 342600 mu, with a year-on-year increase of 0.5%, and the oil production is 38200 tons, with a decrease of 8.4%; the vegetable planting area is 164000 mu, with a year-on-year increase of 1.5%, and the output is 283300 tons, with a year-on-year increase of 1.6%. At the end of the year, the area of tea garden was 22200 mu, and the output of tea was 2088 tons, an increase of 9.3%. The area of orchard was 202900 mu, and the output of fruit was 196800 tons, an increase of 1.7%. The main planting type is single cropping with main form of rice-vegetable, rice-fertilizer, rice-rape and rice-idle, etc. It is shown in the inspection result of soil heavy metal pollution of agricultural land in Cili County that heavy metal pollution exists in partial agricultural land soil in Cili County to different degrees with main pollution risk elements of cadmium and arsenic. (5) Analysis of Social-economic State of Huayuan County Huayuan County is located in central Xiangxi Tujia and Miao Autonomous Prefecture with total land area of 1109.35km2 and there are 12 townships, 217 villages and 24 communities (neighborhood committee). The total population is 312,500 with agricultural population of 266,600 and rural labor of 143,000. Total area of cultivated land is 24712.21 hectares (among them: paddy field is 11900.47 hectares and dry soil is 12811.74 hectares). In 2019, the total production output was 7212.15 million Yuan; the total output of agriculture, forestry, animal husbandry and fishery industry was 14638.49 million Yuan; the per capita disposable income of rural residents was 9,510 Yuan. 65 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Except producing grain crop, the county also produces one-year cash crops and fruits; among them, grain crops mainly include rice, corn, sweet potato, and soybean, etc.; the one-year cash crops mainly include rape, peanut, vegetables, flue-cured tobacco and artemisia apiacea, etc.; fruits mainly include orange, pear and kiwifruit, etc.. Rice, rape, vegetable and other crops are mainly planted here with main planting types of rice, rape-rice, rice-fertilizer and rice-vegetable. In 2019, the county’s annual crop planting area was 464,406 mu, grain crop planting area was 269,697 mu, corn planting area was 63,523 mu, bean planting area was 27,446 mu, potato planting area was 22,768 mu; the planting area of oil crops, tobacco leaves, Chinese medicinal materials, vegetables and fruits were 61,171 mu;, 21,800 mu;, 12937 mu;, 71563 mu and 4898 mu respectively. The total annual grain output was 91578 tons, including 81745 tons of cereal. The area of 1483.3 hectares of agricultural land is within the qualified requirement, accounting for 6.0% of total agricultural land; the area of 8542.6 hectares is slightly polluted, accounting for 34.8%; the area of 3983.2 hectares is mildly polluted, accounting for 16.2%; the area of 3461.3 hectares is polluted at middle level, accounting for 14.1%; the area of 7087.3 hectares is seriously polluted, accounting for 28.9%. (6) Analysis of Social-economic State of Anhua County Anhua County is located in the north of central Hunan, in the north of Xuefeng Mountains and in the middle reaches of Zishui River. It is 123.764 kilometers long from east to west and 73.461 kilometers wide from north to south, with a total area of 4,950.25 square kilometers, making it the third largest county in Hunan Province. At the end of 2019, the county’s population registered at public security organs was 1.0088 million, and the permanent population was 861,000, of which the urban permanent population was 333,900, and the urbanization rate was 38.78%. In 2019, the regional GDP reached 23.218 billion yuan, a year-on-year increase of 6.7%. Among them, the added value in the first industry was 4.461billion Yuan, with the growth of 3.1%; added value in the second industry was 7.689 billion Yuan, with the growth of 7.8%; added value in the tertiary industry was 11.068 billion Yuan, with the growth of 7.2%. The ratio of three industries was 19.2: 33.1: 47.7; the proportion of first 66 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report industry increased by 2.9 percentage points; the proportion of second industry decreased by 0.7 percentage points, and the proportion of tertiary industry decreased by 2.2 percentage points. Contribution rates of three industries on economic growth were 8.6%, 42.9% and 48.5% respectively. GDP growth driven by three industries was 0.6%, 2.9% and 3.3% respectively. The per capita GDP was 26,986 yuan calculated based on permanent resident population. It realized a total output value of RMB 8.124 billion in the agricultural, forestry, animal husbandry and fishing industries with a growth rate of 3.3% compared with same period last year. The grain sown area was 656000 mu with total grain output of 229000t. There were 611300 live pigs sold, a decrease of 20% over the previous year; 26300 cattle, an increase of 6.5%; and 365900 sheep, an increase of 8.1%. 3.3786 million poultry were sold, an increase of 5.1%; the total output of aquatic products was 16200 tons, a decrease of 1.9%. The development of distinctive agriculture was further strengthened. It is shown by the result of soil agricultural product monitoring data in 2015 and 2017 that among five risk factors of cadmium, arsenic, mercury, lead and chromium, heavy metal pollution risk exists in partial rice in Anhua County and the risk factor is cadmium. (7) Analysis of Social-economic State of Hengyang County The total population with household registration of the county was 1.24 million (statistics of public security registered residence, same below) in the end of 2019 with the reduction of 5700 compared with the last year. In the whole year, there were 12282 births, with a birth rate of 9.62 ‰, increase 0.62 ‰; 7374 deaths, with a death rate of 5.78 ‰, increase 2.08 ‰; and the natural growth rate of population was 3.85 ‰, decrease 0.48 ‰. Sex ratio at birth was 109.02 (take women as 100) At the end of year, the permanent population is 1.0374 million, decreasing by 11400 people. Of them, the urban population is 0.4579 million and the rural population is 0.5795 million. The urbanization rate is 44.14%, decreasing by 0.94%. The annual gross regional product (GDP) was 34.894 billion yuan, an increase of 7.8%. From the perspective of different industry, the added value in the first industry was 6.371 billion Yuan, with the growth of 2.8%; added value in the second industry was 67 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 12.519 billion Yuan, with the growth of 7.9%; added value in the tertiary industry was 16.004 billion Yuan, with the growth of 10.0%. The grain sown area of the year was 90910 hectares, of which 83990 hectares were planted for rice, 43220 hectares were planted for oil, 4450 hectares were planted for cotton, and 5810 hectares were planted for vegetables. The annual total grain output was 618000 tons, including 578900 tons of rice, 5157 tons of cotton, 68712 tons of oil and 200421 tons of vegetables. The planting type is divided into triple cropping, double cropping and single cropping. Rice planting varieties include Xiangzaoxian 45, Xiangwanxian 13, Huanghuazhan, and the like. (8) Analysis of Social-economic State of Hengnan County In 2019, the permanent population was 915,900, of which the urban population was 380,100, and the urbanization rate was 41.5%. The birth rate was ‰, death rate was 2.87‰, natural growth rate was 6.44‰ and sex ratio at birth was 113.06. In 2019, the Gross Domestic Product (GDP) reached 34.109 billion Yuan with the year-on-year growth of 8.0%. Among them, the added value in the first industry was 6.421 billion Yuan, with the growth of 2.6%; added value in the secondary industry was 11.473 billion Yuan, with the growth of 7.9%; added value in the tertiary industry was 16.215 billion Yuan, with the growth of 10.4%. The regional per capita GDP was (current price of GDP) 37,241 Yuan with the growth of 5.6% calculated based on permanent resident population. The annual grain planting area was 1.3627 million mu, including 5100 mu for wheat, 1.2631 million mu for rice, 24800 mu for corn and 49000 mu for cotton. Oil planting area is 533300 mu and sugar planting area is 399 mu, an increase of 0.3%. The annual grain output was 625400 tons, including 210000 tons of early rice, 134800 tons of middle season rice and 242700 tons of late season rice. The planting type is divided into triple cropping, double cropping and single cropping. Rice planting varieties include Xiangzaoxian 45, Xiangwanxian 13, Huanghuazhan, and the like. (9) Analysis of Social-economic State of Lengshuitan District 68 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report In 2019, the total GDP in the district reached 33.511 billion Yuan with the year-on-year growth of 7.3%. Among them, the added value in the first industry was 3.474 billion Yuan, with the year-on-year growth of 3.5%; added value in the second industry was 8.928 billion Yuan, with the year-on-year growth of 7.1%; added value in the tertiary industry was 21.109 billion Yuan, with the growth of 8.0%. The per capita GDP was 61,425 Yuan with the growth of 7.5% calculated based on permanent resident population. The total population with household registration in the public security system in the district was 561600 at the end of 2019 in 196,000 households; among them, there were 290,000 males and 271,600 females. The date of birth in the district was 10.7‰ with the growth of 2.12‰; the mortality rate was 5.89‰ with the growth of 1.06‰ and natural growth rate was 4.89‰. The permanent resident population was 553,700 at the end of the year in 192,200 households, including urban population of 384,600 and rural population of 169,100; the urbanization rate was 69.46%. The total sown area of crops in the whole year is 1321033 mu, including 804144 mu of grain crops with an output of 340459 tons, 97386 mu of oil crops with an output of 12387 tons, and 4571 mu of cotton with an output of 434 tons. The main grain crop in Lengshuitan District is rice. The planting type is divided into double cropping and single cropping. Rice planting varieties include Xiangzaoxian 45, Xiangwanxian 13, Huanghuazhan, and the like. (10) Analysis of Social-economic State of Linwu County The total regional output value was 14218.72 million Yuan with the growth of 7.9% compared with the last year calculated by comparable price. The GDP per capita was 40,953 Yuan with the growth of 9.1% calculated based on permanent resident population. An increase of 3423 Yuan over the last year. From the perspective of different industry, the added value in the first industry was 1444.25 million Yuan, with the growth of 3.6%; added value in the second industry was 6048.87 million Yuan, with the growth of 8.0%; added value in the tertiary industry was 6725.6 million Yuan, with the growth of 8.9%. The permanent resident population was 347,200 at the end of the year, including rural population of 161,900 and urban population of 185,300. The urbanization rate was 53.4%, 69 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 4.7 percentage points higher than at the beginning of the year. Grain planting area of the county was 21,500 ha, with the growth of 0.6% compared with the last year; the total grain output was 120,400 tons with the growth of 0.4%. Among them, the rice planting area was 14930 hectares, a decrease of 0.9%; the rice output was 89000 tons, a decrease of 0.8%. The vegetable planting area was 77600 hectares, an increase of 1.3%; the vegetable output was 243000 tons, an increase of 1.9%. The orchard covers an area of 25300 hectares and the fruit output is 48400 tons. (11) Analysis of Social-economic State of Qiyang County In 2019, the GDP reached 33.206 billion Yuan with the growth of 7.2% compared with the last year. Among them, the added value in the first industry was 5.092 billion Yuan, with the growth of 3.1%; added value in the second industry was 9.717 billion Yuan, with the growth of 7.9%; added value in the tertiary industry was 18.343 billion Yuan, with the growth of 7.9%. The per capita GDP was 38,769.7 Yuan calculated based on annual average annual average annual average permanent resident population. The three industrial structures of the Qiyang County are 15.34: 29.42: 55.24. The industrial added value accounted for 20.68% of the GDP of the district. The contribution rate of primary industry, secondary industry and tertiary industry to economic growth is 6.63%, 34.87% and 58.5%. The contribution rate of industry to economic growth is 28.23%. The first, second and tertiary industries respectively led to GDP growth of 0.48%, 2.51% and 4.21%. In 2019, the added value of the first industry in Qiyang County was 5.092 billion yuan, an increase of 3.1%. In 2018, the grain planting area of Qiyang County was 89753.8 hectares, a decrease of 0.81% over the previous year. Among them, the sown area of rice was 77156.8 hectares; the sown area of oil plants was 22500.73 hectares, an increase of 0.4% over the previous year; the sown area of cotton was 461.8 hectares; and the sown area of vegetables was 25462.07 hectares. The total grain output of the whole year was 571500 tons, a year-on-year decrease of 0.53%. Oil production was 42300 tons, an increase of 0.44% year on year; cotton production was 551 tons, a decrease of 4.84% year on year; tobacco production was 159 tons, a decrease of 0.63% year on year; tea production was 261 tons, 70 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report an increase of 0.38% year on year; fruit production was 183300 tons, an increase of 0.6%; vegetable production was 779100 tons. In 2019, the grain planting area of Qiyang County was 89400 hectares, a decrease of 0.39% over the previous year. Among them, the cotton planting area was 450 hectares, a decrease of 3.32% over the previous year; the sugar planting area was 820 hectares, an increase of 2.32% over the previous year; the oil planting area was 22200 hectares, a decrease of 1.35% over the previous year; the tobacco planting area was 40 hectares, a decrease of 2.85% over the previous year; the vegetable planting area was 26230 hectares, an increase of 3.0% over the previous year. The total grain output in 2019 was 572000 tons, a decrease of 0.23% over the previous year. The oil production was 40600 tons, a decrease of 4.0% over the previous year, of which the rapeseed production was 28600 tons, a decrease of 7.62% over the previous year. The output of cotton was 541 tons with the reduction of 1.81% over the previous year; The output of tobacco was 155 tons with the reduction of 2.52% over the previous year; The output of tea was 269 tons with the reduction of 3.07% over the previous year; The output of vegetable was 80.26 tons with the reduction of 3.01% over the previous year; 4.4 Survey on Pollutant Source in Demonstration Area 1. Pollutant source (1) Yongding District Yongding District is located in the interior of Wuling Mountain. Limestone is the main parent material of soil, and there are many kinds of soil. The main source of heavy metal pollution in cultivated land is the discharge of waste residue and wastewater from historical industrial and mining. Yongding District is rich in mineral resources. Discharge of waste water, residues and waste gas generated by smelting enterprise has become main factors influencing regional environmental quality. Waste water generated by industrial enterprises was directly discharged into nearby river without being processed or reaching standard after being processed, which polluted the environment. In addition, the problem that cultivated land and water resource polluted by heavy metal residues resulted from closing smelting enterprise and sporadic mining sites under the role of blowing, raining 71 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report and leaching is prominent which threatens water quality and production of agricultural products. Main source of heavy metal pollution in cultivated land in Yongding District is the emission of “the three wastes” generated by historical mining enterprises with pollution channel that pollutant enters into irrigation water and sewage irrigation results in pollution of heavy metal in soil. The current agricultural land pollution of newly-added demonstration areas in Yongding District is historical pollutant source of smelting enterprises with main part of sediment introduction through on-site survey, public consultation and material collection and analysis; in addition, waste gas containing heavy metal emitted by historical smelting enterprises is settled on soil. After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (2) Jishou City The metal and mineral resources in Jishou are bountiful, especially for production of manganese ore. In the past, residues of smelting plants, electrolytic manganese enterprises and other enterprises involved in heavy metal pollution are directly piled openly without proper treatment; as time goes by, the bottom layer of slagheap and surrounded soil are polluted by heavy metal under the role of rain and filtration liquid. During the smelting process of nonferrous metal, large amount of heavy metal, suspended substances and acid are included in generated waste water; waste water containing heavy metal is directly discharged into Donghe River and Wanrong River due to backward processing process which pollutes rivers; while Donghe River and Wanrong River are irrigation water sources of major cultivated lands in Jishou so agricultural land soils are polluted; in addition, the background value of heavy metal in soil in Jishou City is pretty high, resulting in heavy metal in large area of soil exceeding standard. The current agricultural land pollution of newly-added area in old demonstration area in Jishou City is historical pollutant source of smelting enterprises with main part of 72 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report sediment introduction through on-site survey, public consultation and material collection and analysis; in addition, waste gas containing heavy metal emitted by historical smelting enterprises is settled on soil. After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (3) Yongshun County There were coal ore exploitation, iron ore exploitation and smelting and other mining enterprises involved in emission of heavy metal pollution along the history of Yongshun County, Xiangxi Autonomous Prefecture. The mining, mineral processing and smelting all have a long history. At different stages of historical development, due to the restriction of technical conditions, knowledge level, supervision and other factors, the heavy metals in the discharged wastewater are deposited in the sediment of the ditch channel. The heavy metals in the waste gas settle in the soil and water through the atmosphere and enter the surface water, soil and underground water along with the surface runoff. The non-degradable nature of the discharged heavy metals causes them to accumulate gradually in the environment and accumulate over time, increasing the concentration of heavy metals in the soil, sediment and water and increasing the pollution, thus causing heavy metal pollution accidents. The current agricultural land pollution of newly-added demonstration area in Yongshun County is historical mining which is brought by sediment introduction through on-site survey, public consultation and material collection and analysis; in addition, waste gas containing heavy metal emitted by historical smelting enterprises is settled on soil. These historical pollutant sources are closed and left ore residues are cleared when they are closed through on-site survey; now, there is no tailings reservoir or residue piling as well as left issues of mining and mineral processing, which won’t result in new heavy metal pollution to downstream agricultural land. (4) Cili County 73 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report In Cili County, the proportion of industrial activity and agricultural activity in heavy metal pollution risk is large along the history. Following main resources contribute to heavy metal pollution in agricultural land: residues of mining enterprises piled openly, direct discharge of waste water into water without being processed and emission of waste gas and dust. In industrial source, residues are openly piled without being properly processed; as the time goes by, soil in bottom layer of slagheap and surrounded soil is polluted by heavy metal pollution with the role of rain wash and filtration liquid; when it is piled for long term, dust shall be generated due to dry surface which shall damage the atmospheric environment. With the role of surrounded mineral enterprises, discharged dust containing heavy metal shall enter into surface soil with dry and wet sedimentation of dust. Heavy metals as well as SO2, sulfuric acid mist and other pollutants are included in dust emitted by enterprises involved in heavy metal enterprises which shall make rainfall acidized and dissolved part of heavy metal higher. As the process of processing technology of waste water is simple and the effect is unstable in the past, waste water discharged by mineral enterprises shall pollute water; in addition, the utilization of surface water polluted by heavy metal as irrigation water pollutes agricultural land, resulting in heavy metals in agricultural crops exceeding standard. The current agricultural land pollution of newly-added demonstration area and newly-added area of old demonstration area in Cili County is historical mining and smelting pollutant source which is brought by sediment through on-site survey, public consultation and material collection and analysis; in addition, waste gas containing heavy metal emitted by historical smelting enterprises is settled on soil. These historical pollutant sources are closed and left ore residues are cleared when they are closed through on-site survey; now, there is no tailings reservoir or residue piling as well as left issues of mining and mineral processing, which won’t result in new heavy metal pollution to downstream agricultural land. (5) Huayuan County Huayuan County is located in central section of Wuling Mountain with bountiful 74 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mineral resources in side the county; in particular, the reserves of manganese ore and lead zinc ore are huge. There were at most over 200 small and micro mining and smelting enterprises or individual workshops with free sewage discharge whose annual emitted amount of “three wastes” is over 10,000t. Waste water, residue and waste gas emission generated by smelting enterprises inside the county has become important factor influencing regional environmental quality. Waste water generated by mining of some historical industrial ore was directly discharged into nearby river without being processed or reaching standard after being processed, which polluted the environment. In addition, the problem that cultivated land and water resource polluted by heavy metal residues resulted from closing mineral processing site and sporadic mining sites under the role of blowing, raining and leaching is prominent which threatens water quality and production of agricultural products. Main source of heavy metal pollution in cultivated land in Huayuan County is the emission of “the three wastes” generated by historical mining and mineral processing with pollution channel that pollutant enters into irrigation water and historical sewage irrigation results in pollution of heavy metal in soil. The current agricultural land pollution of selected demonstration area in Huayuan County is historical pollutant source of smelting enterprises of lead zinc ore which is brought by sediment through on-site survey, public consultation and material collection and analysis; in addition, waste gas containing heavy metal emitted by historical smelting enterprises is settled on soil. After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (6) Anhua County Smelting, coal ore, tungsten ore, brickfield, processing, production and other small and micro enterprises or individual workshops emerged with reform and opening up since 1980s; there were 60 free sewage discharge production sites at peak period before and after 2010 with annually discharged “three wastes” over 50,000t. Among them, pollution caused 75 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report by “the three wastes” discharged by gold smelting, mining sulphur pentoxide, manganese zinc and copper smelting, paper-making, plastics processing and other industries is pretty serious. Sewage production enterprises with pretty large scope are mainly in Kuixi Town closed to Xupu, Qingtang Town closed to Lianyuan and Dongping Town closed to county. When previous enterprises and small workshops pollute surrounded cultivated land in discharging residues, discharged waste water flows into nearby river and then flows into Zishui River as irrigation water source to further pollute more agricultural land. In addition, in the past 30 years, large amount of calcium phosphate fertilizers were applied to agricultural land; calcium superphosphate and phosphate rock powder with poor quality in phosphate fertilizer contained cadmium with low content which made pollution of heavy metal in agricultural land heavier. The current agricultural land pollution of selected demonstration area in Anhua County is historical pollutant source of coal ore and zinc lead ore which is brought by sediment through on-site survey, public consultation and material collection and analysis; in addition, waste gas containing heavy metal emitted by historical smelting enterprises is settled on soil. After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (7) Hengyang County Hengyang County is typical of years of mining and separation and metallurgy in the reach of Xiangjiang River. There are hundreds of large and small mines and operations in the County, resulting in many sources of pollution. Heavy metals in the discharged liquid waste that deposited in the bottom sediments of the ditches and channels in various development stages due to factors including technical conditions, level of awareness, degree of supervision efforts, etc. Heavy metals in the waste gas precipitated through air into the soil and water body and then flow with surface runoff into the surface water, soil and groundwater. Heavy metals discharged were not degradable so that they accumulated 76 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report in the environment as time went by. Besides, the background value of heavy metals in the soil in the County is relatively high, resulting in excessive heavy metals in a large area of soil. In industrial source, residues of mining, smelting and other industries involved in heavy metal pollution enterprises are directly piled openly without being properly handled; with the time goes by, soil in bottom layer of slagheap and surrounded soil is polluted by heavy metal pollution with the role of rain wash and filtration liquid. When residues are piled for long term, dust shall be generated due to dry surface which damages atmospheric environment; in addition, it shall enter into surface soil with dry and wet sedimentation of smelting dust with dust containing heavy metal discharged by smelting plant. During the smelting process of nonferrous metal, large amount of heavy metal, suspended substances and acid are contained in generated waste water; waste water containing heavy metal is directly discharged into Zhengshui River due to backward processing process which pollutes rivers; while Zhengshui River are irrigation water sources of major cultivated lands in Hengyang County so agricultural land soils are polluted. In addition, in the past period of time, local farmers used sediment of Zhengshui River as organic fertilizer and applied it to farmland, resulting in excessive heavy metals in farmland soil. Taking Xiangjiang River Basin in Hunan Province as an example, the annual discharge of heavy metal cadmium from mining and smelting is as high as 148 tons. At present, most heavy metal-related enterprises have been shut down and no new pollution will be generated. However, problems left over from history have caused excessive heavy metals in farmland soil and crops, requiring relatively high cost for the treatment. Hengyang County, as a “national model county for grain production”, has applied 6,000 tons of superphosphate annually in the past 30 years. The superphosphate with poor quality in phosphate fertilizer and cadmium contained in powdered rock phosphate may contribute to heavy metal pollution in farmland. In addition, according to statistics, 119 farms within 500m of the Zhengshui River are counted, and the discharge of the farm waste is also an important factor of the risk of farmland pollution. At present, environmental protection department has closed 21 large-scale farms, and the remaining 98 77 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report large-scale farms have been listed in the treatment plan. All the farms are up to standard in 2016, and those failing to meet the standards will be closed. Through on-site reconnaissance, public consultation and data collection and analysis, farmland pollution in Qingli Demonstration Area selected in Hengyang County is mainly the historical pollution sources of pharmaceutical enterprises and farms. In the history of Sanhu Town Demonstration Area, there have been 2 small recycled paper mills, 3 illegal indigenous method vanadium refining enterprises and other factories and mines. After on-site investigation in each demonstration area, these historical polluting enterprises have been shut down, and their slags and residues have been cleared up; now, there is no tailings reservoir or residue piling as well as left issues of mining and mineral processing, which won’t result in new heavy metal pollution to downstream agricultural land. (8) Hengnan County There are many non ferrous, metallurgy and chemical enterprises in Hengnan County since 1950s. There are over 70 smelting mineral enterprises inside the county; in addition, partial mineral enterprise pollution brought from upstream of Leishui River results in “three wastes” pollution of mineral enterprise to different degrees and the pollution has been spread from urban to rural area. As production management of some enterprises is nonstandard and sewage prevention and governance is not useful, illegal sewage discharge cannot be banned, resulting in soil pollution in the area around mineral enterprises and irrigated by Leishui River is very severe. Through on-site reconnaissance, public consultation and data collection and analysis, farmland pollution in Xiangyang Demonstration Area (Chaoyang Village and Huanghe Village) is mainly the historical pollution of Xiangjiang River water. In recent years, Xiangjiang River water is no longer used for irrigation as a result of changing irrigation water sources. Therefore, pollution sources are basically controlled and no new pollution will be caused. Farmland pollution in Quanxi Demonstration Area (Quanchang Village) is mainly due to the backward flowing of Leishui River caused by two consecutive years of floods in 2006 and 2007, which stayed in the demonstration area for half a month, bringing a lot of silt and pollutants and polluting the farming layer. At the same time, due to the 78 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report excessive fertilization of regional farmland, most of the pesticides used are pesticides with high contents of arsenic, lead, mercury, and cadmium, resulting in increasing soil pollution. These historical pollutant sources are closed through on-site survey; now, there is no tailings reservoir or residue piling as well as left issues of mining and mineral processing, which won’t result in new heavy metal pollution to downstream agricultural land. (9) Lengshuitan District The development of industrial and urban construction in Lengshuitan District is rapid since reform and opening up that various plants are constructed along two banks of Xiangjiang River continuously and over 150 institutions with pollutant emission constructed in narrow corridor inside the area; there are 25 drain outlets along the river and discharge amount of sewage and waste water is 20 million tons each year. Mineral resources in Lengshuitan District are pretty bountiful and there are many smelting enterprises inside the area. Discharge of waste water, residues and waste gas generated by smelting enterprise has become main factors influencing regional environmental quality and some suburb areas are used for piling domestic garbage and industrial residues. Waste water generated by industrial enterprises was directly discharged into nearby river without being processed or reaching standard after being processed, which polluted the environment. In addition, agricultural land pollution and water resource pollution of heavy metal residues left by closed smelting enterprises under the role of blowing, raining and leaching is prominent which greatly threatens water quality and production of agricultural product; dust containing heavy metal discharged by smelting plant enters into surface soil with dry and wet sedimentation of smelting dust. The main source of heavy metal pollution in agricultural land in Lengshuitan District is discharge of “three wastes” generated by historical smelting enterprises with main pollution channel of water type and atmospheric dust fall and main pollutants of cadmium as well as arsenic, mercury and lead, etc. The current agricultural land pollution of selected demonstration area in Lengshuitan District is historical pollutant source of iron core and manganese ore exploitation which is brought by sediment through on-site survey, public consultation and material collection and analysis. After on-site investigations, all these historical pollution sources had been 79 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (10) Linwu County Linwu County has long history in mining industry for many years; during the peak period, there are over 400 various mining tunnels and 480 mineral processing plants and attached slot with many pollutant sources. Heavy metals in discharged waste water are deposited in sediment of channel which flow into surface water and soil with surface runoff due to restriction of technical conditions, recognition level, supervision force and other elements in different historical development levels. In the past, residues of mining, mineral processing, and other industries involved in heavy metal pollution enterprises are directly piled openly without being properly handled; with the time goes by, soil in bottom layer of slagheap and surrounded soil is polluted by heavy metal pollution with the role of rain wash and filtration liquid. Discharged heavy metal is gradually accumulated in the environment due to its non-degradability; in addition, the background value of heavy metal in soil in the county is pretty high, resulting in heavy metal in large area of soil exceeds standard. Discharge of waste water, residues and waste gas generated by mining and separation enterprises has become main factors influencing regional environmental quality. The current agricultural land pollution of selected demonstration area in Linwu County is historical pollutant source of mineral processing of lead zinc ore which is brought by sediment through on-site survey, public consultation and material collection and analysis. These historical pollutant sources are closed and left ore residues are cleared when they are closed through on-site survey; now, there is no tailings reservoir or residue piling as well as left issues of mining and mineral processing, which won’t result in new heavy metal pollution to downstream agricultural land. (11) Qiyang County There are bountiful mineral resources in Qiyang County which is called “the land of nonferrous metal” with main mineral resources of coal, iron, manganese, antimony, zinc 80 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report and tin ore. Exploitation of iron ore, manganese ore, tin ore and other metal mineral involved in heavy metal pollution occurred in the history with distribution of 48 ores whose mining and mineral processing history is long. Heavy metals in discharged waste water are deposited in sediment of channel and heavy metals in waste gas are deposited in soil and water through atmospheric sedimentation due to restriction of technical conditions, recognition level, supervision force and other elements in different historical development levels. They enter into surface water, soil and ground water with surface runoff and discharged heavy metals are gradually accumulated in environment as they are not degradable so that heavy metal concentration in soil, sediment and water is risen continuously and pollution is gradually aggravated so as to result in heavy metal pollution accident. The current agricultural land pollution of selected demonstration area in Qiyang County is historical pollutant source of iron, manganese and tin ore exploitation which is brought by sediment through on-site survey, public consultation and material collection and analysis. These historical pollutant sources are closed and left ore residues are cleared when they are closed through on-site survey; now, there is no tailings reservoir or residue piling as well as left issues of mining and mineral processing, which won’t result in new heavy metal pollution to downstream agricultural land. 2. Governance of pollutant source (1) Yongding District In recent years, Yongding District has been developed for an eco-tourism city, and heavy metal-related enterprises and sporadic mining sites have all been closed. In addition, pollution and sporadic waste residues left over from closed enterprises has been treated by reuse or landfill, soil covering and greening. After closing enterprises involved in heavy metal pollution and scattered mining points, surface water basically meets the standard and conforms to Standards for Quality Standards for Farmland Irrigation Water. Through selection, it is found pollutant source of newly-added demonstration areas in Yongding District is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and 81 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. (2) Jishou City Aiming at serious situation of heavy metal pollution, Jishou City adopts various measures to form the resolution that “manganese and zinc enterprises completely exit from Jishou” and puts forward the target that “be provincial ecological city and national ecological city”. In 2011, 7 enterprises, including Debang Chemicals, Tiantang Chemicals and Hexi Power Station Chemical Plant, were closed. In 2012, 4 enterprises, including Rongjiang Manganese, were closed; in addition, 6 manganese residue reservoirs in 3 enterprises, Debang Chemicals, Hexi Power Station and New Century Manganese, were closed. In 2013, New Tianran Chemicals and manganese residue base of Yaohua Manganese were closed; in 2014, reservoir closing was adopted for Tiantian Manganese and Pingshan Slope without main tailings. Through making efforts, the integrated governance of electrolytic manganese industry and metal pollution prevention project in Jishou is finally completed. The city invested 107.66 million Yuan with 11 electrolytic manganese enterprises closed, 10 manganese residue reservoirs closed, 7 initial dams reinforced, 7 flood discharge systems constructed, 15km reservoir-loop flood interception ditch constructed, 15.34km dam slope intercepting ditch constructed, 7 filtration liquid collection processing systems established, 5000t waste slags around 12.6km river cleaned and 37,800 m2 ecological scenery renovated. Ecological environment in Jishou is obviously improved as manganese zinc enterprises are comprehensively closed. After closing enterprises involved in heavy metal pollution and scattered mining points, surface water basically meets the standard and conforms to Quality Standards for Farmland Irrigation Water. Through selection, it is found pollutant source of newly-added area of old demonstration area of Jishou City is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. 82 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (3) Yongshun County Coal ore exploitation existed in upstream of newly-added demonstration area in Yongshun County along the history while there was no smelting enterprise in surrounded area and upstream area without tailings reservoir through on-site survey and material collection and analysis. Coal mining has been closed, slag has been cleared, and no new heavy metal pollution will be caused to agricultural land downstream. (4) Cili County In recent years, Cili County is listed into one of 138 integrated heavy metal pollution management areas by Ministry of Environmental Protection and one of 28 heavy metal pollution counties in Hunan Province due to exploitation and processing of nickel-molybdenum ore inside the county and former Shimen arsenic disulfide ore, which result in pretty serious heavy metal pollution. According to Integrated Pollution Prevention Plan of Heavy Metals in Hunan Province, Cili County has started heavy metal pollution prevention since 2011 and it has invested special fund over 60 million Yuan to organize integrated governance in nickel-molybdenum ore, residue and waste water governance in Daxu Ore Area and exert other efforts on preventing heavy metal pollution. During the governance period, Cili County governs nickel-molybdenum ore pollution in two steps: centralized governance and separated governance. It invests over 16 million Yuan to implement tailings centralized processing plant governance project in Dahu Ore Area of nickel-molybdenum ore and 28.5 million Yuan to implement centralized governance project of historical left heavy metal tailings in Baizhuyu, Dahu Ore Area of nickel-molybdenum ore. Meanwhile, the county also develops deep governance project and clean production review in waste water and waste gas of enterprises involved in processing of heavy metal nickel-molybdenum ore. It supervises Xingda Smelting Company to invest over 9 million Yuan to complete deep governance project of waste water and waste gas and clean review; in addition, Hunan Zhongjie Technology Development Co., Ltd. invests 9.515 million Yuan to complete deep governance project of waste water and waste gas. Moreover, the county also invests 3.27 million Yuan to implement safe water drinking project in the area polluted by arsenic in Cili which 83 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report effectively solves safe water drinking of nearly 2000 people in Lingkuang, Xingming and Guangkou Village in Guotaiqiao Township; in addition, the county integrates 8 nickel molybdenum mines into 4 mines. Through selection, it is found pollutant source of selected demonstration areas in Baojing County is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. (5) Huayuan County During the “12th Five Year Plan” period, 46 enterprises involved in heavy metal in Huayuan County were monitored with emphasis; among them, 16 enterprises had qualified discharge while 13 enterprises have stopped production for long term. 21 key discharge reduction projects on prevention of heavy metal pollution were implemented, including 19 projects with structural adjustment and 2 projects of pollutant source governance. Huayuan County further digs out potential on reducing heavy metal pollution and enhances efforts on structural adjustment and pollution governance on the basis of completing planned projects that it has closed 41 projects involved in heavy metal. In 2015, the qualification rate of heavy metal pollutant of urban centralized surface drinking water source (Jiaming section) in the whole year was 100%; the qualification of key heavy metal pollutant of national controlled section of surface water (Zhangpima and Biancheng section) was improved compared with previous year (qualification rate of Zhangpima Section was 100%; the qualification rate of Biancheng Section was improved from 16.7% in the previous year to 58.3%); the qualification rate of atmospheric environmental quality index of key area (Wangcheng Village) was stable (qualification rate was 100%). Currently, there are 79 tailings dams inside the county, which have adopted effective governance measures based on related requirements of environmental protection department. After closing enterprises involved in heavy metal pollution and scattered mining points, surface water basically meets the standard and conforms to Quality Standards for Farmland Irrigation Water. 84 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Through selection, it is found pollutant source of Huayuan Town Demonstration Area, Longtan Town Demonstration Area, Malichang Town Demonstration Area and Mao’er Township Demonstration Area in Huayuan County is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. (6) Anhua County Confronting serious influence of heavy metal pollution in soil, Anhua County Government has started to govern heavy metal pollution. Firstly, it closes coal ore, antimony ore, tungsten ore and other small processing plants and dozens of various sewage discharge production sites. Secondly, 200 livestock farms along Zijiang River and its branches are relocated; circular utilization or qualified discharge of waste water is realized through construction of pollution prevention measures and technological renovation; related enterprises have set up pollution prevention measures to realize circular utilization or “zero discharge” of waste water, comprehensively reduce dust and raise dust and comprehensively dispose and utilize waste materials and residues so that water quality of Zishui River and its branches, Xishui River, unknown river, Oblique Weir and other rivers and reservoirs around the demonstration area becomes better. After closing enterprises involved in heavy metal pollution and scattered mining points, surface water basically meets the standard and conforms to Quality Standards for Farmland Irrigation Water. Through selection, it is found pollutant source of Kuixi Town Demonstration Area, Changtang Town Demonstration Area, Qingtang Town Demonstration Area, Jiangnan Town Demonstration Area and Dongping Town Demonstration Area in Anhua County is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. (7) Hengyang County In the face of the serious impact of heavy metal pollution in soil, in recent years, the 85 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report man-made pollution problem has been vigorously remedied. (1) The paper mill of the county, the nitrogen fertilizer plant of the county, three small waste plastic processing plants, three zinc oxide plants and small paper mills and dozens of other sewage production sites have been shut down. (2) 38 farms on both sides of the main stream of Xiangjiang River have been relocated. (3) For 26 stone enterprises in Jingtou Town and 13 ceramic sand washing enterprises in Jiepai Town, waste water have been recycled or discharged up to standard through the construction of pollution prevention facilities and technological transformation. (4) 39 mining and processing enterprises, 13 large-scale breeding farms and 5 plastic making enterprises were comprehensively renovated in respect of environment. After the renovation, relevant enterprises established pollution prevention and control facilities to achieve waste water recycling or "zero discharge". Dust and raise dust are reduced in an all-round way, and waste and residue are disposed and utilized comprehensively. The water quality of Wushui River, Yinxi River, Niuxing Mountain, Oblique Weir and other rivers and reservoirs has been significantly improved. At the same time, in recent years, the provincial government has attached great importance to the control of heavy metal pollution in the Xiangjiang River Basin and invested a lot of manpower and material resources. With the joint efforts of governments at all levels, the water quality and environment in the Xiangjiang River Basin has been greatly improved. Through the implementation of the above control measures, the monitoring factors of the main irrigation water source, the Zhengshui River, in Hengyang County meet the requirements of Quality Standards for Farmland Irrigation Water (GB5084-2021). (8) Hengnan County Hengnan County Party Committee and Government pay high attention to governance of heavy metal and other pollution types in cultivated land and have issued Notice on Further Strengthening Environmental Protection Governance of Enterprises Involving in Heavy Metal (N.B.T. [2011] No.77) to strengthen effort on pollution governance of 86 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report enterprises in mine mineral processing, smelting, chemical and other heavy pollution industries. It develops soil environmental pollution and risk search in the whole county; requires 45 illegal and “fifteen small” enterprises to establish governance standing book and correct with limited term; stops production and governs 7 enterprises without complete environmental protection procedures including Hongfeng Fuli Chemicals and 6 enterprises without environmental protection procedures; closes 6 enterprises involved in heavy metal of lead, zinc, indium and vanadium, including Yanxing, Xusheng, Rongxing, Haofengnian, Hengxiang and Rongxing; removes 2 enterprises with serious sewage discharge and strong public response, namely Quanxi Mudouchong Papermaking Plant and Diping Livestock Farm. It removes 35 poultry and sensitive water net cage farmers along “Xiangjiang River, Zishui River, Yuanshui River and Lishui River” as well as enterprises with serious sewage discharge in Diping Farm. Xiangyang Demonstration Area changed its irrigation water system. Huanghe Village intends to use the ponds in the hill and Ouyanghai Irrigation Canal as the source of irrigation water. Chaoyang Village intends to use the ponds in the hill in the Village for irrigation. The farmland pollution in the Quanxi Demonstration Area (Quanchang Village) was the result of the backward flow of the Leishui River. Thanks to the cleanup and governance over recent years, mud, pollutants and introduced organisms caused by major flooding in the past have been almost cleared away and will not cause any new pollution. (9) Lengshuitan District Governmental departments in Lengshuitan District strengthen governance on enterprise pollution in mine exploitation, smelting, chemical and other heavy pollution enterprises. They have closed 147 illegal sewage discharge enterprises, including Huaqiao Smelting Plant, Electroplating Plant of Running Water Company, Electroplating Plant of Material Bureau, Qishantou Manganese Ore, Haomen Ceramic Plant, Renwan Lake Ceramic Plant, Shanglingqiao Oil Smelting Plant, Lantian Chemical Plant, Lixiangyang Copper Sulfate Plant, Hongfa Smelting Co., Ltd., Tianyuan Chemicals, Tiancheng Chemicals, Xiyanghong Smelting Plant and Five Star Antimony Product Plant, whose 87 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report pollution is serious without the hope to be governed in 1998-2014. They strictly control environment access of high pollution and high risk industry in sensitive area and it is not allowed to construct chemical pulping, paper making, tanning and projects of external drainage pollutant with involvement of heavy metal within 20km along two banks of main stream of Xiangjiang River. Projects with low pollution, water conservation and integrated resource utilization without pollution are encouraged to be developed; in addition, enterprises are encouraged to conduct deep governance and improve circular utilization rate of industrial water on the basis of stabilizing qualified discharge. In 2015, left residues of Lengshuitan Lantian Chemical Plant and other enterprises involved in heavy metal after they are closed were governed in 2015 and they have passed provincial acceptance. After being governed for many years, water quality of Lengshuitan District is maintained within the national Level-II water quality standard and atmospheric environmental quality is maintained within the national Level-II standard. After closing enterprises involved in heavy metal pollution and scattered mining points, surface water basically meets the standard and conforms to Quality Standards for Farmland Irrigation Water. Through selection, it is found pollutant source of Xianghuaba Village Demonstration Area, Niujiaoba Demonstration Area and Shixijiang Demonstration Area in Lengshuitan District is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. (10) Linwu County Linwu County is one of key areas of heavy metal governance in Hunan Province and all areas involved in heavy metal pollution have been completely included into national governance planning. Ministry of Land and Resources, Ministry of Supervision and Ministry of Environmental Protection listed and supervised Sanshiliuwan in 2005. Sanshiliuwan Area in Linwu County was listed as one of key governance areas of heavy metal pollution in Xiangjiang River basin in March 2011 after being approved by the State Council. Municipal Party Committee and Government started to implement “shock 88 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report treatment” for Sanshiliuwan, Xianghualing and surrounded ore districts since 2006. Thousands of mining and separation enterprises in the mining area have been shut down for centralized rectification. So far, the original 222 sewage-discharging enterprises in Linwu County have been closed down, leaving only 26 now. By the end of July 2015, the county had received 28 special fund projects for heavy metal pollution control. By the end of 2019, all projects had been completed and passed the acceptance. Small mineral processing plants in over 10km along Ganxi River are completely removed and clean river replaces original dark and rotten sewage. Water quality of Ganxi River, Wushui River, Houzi River, Puxia River and other outbound sections has reached standard of Level-III water quality of surface water in normal weather. Through selection, it is found pollutant source of Wushui Demonstration Area, Nanqiang Demonstration Area and Shuidong Demonstration Area in Linwu County is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. (11) Qiyang County Governmental departments in Qiyang County supervise related enterprises to construct and update sewage disposal facilities; close 41 various sewage discharge production sites, including 33 papermaking plants and 8 small plastic plants; remove 54 farms at two banks of main stream of Xiangjiang River; realize circular utilization or qualified discharge of waste water for 5 rare earth smelting plants, eliminating 19 small smelting furnaces and 9 cement vertical kiln enterprises through setting up pollution prevention facilities and technology renovation; supervise Baoda, Kaisheng and other enterprises to construct and update sewage processing facility. Related enterprises have set up pollution prevention measures to realize circular utilization or “zero discharge” of waste water, comprehensively reduce dust and raise dust and comprehensively dispose and utilize waste materials and residues so that water quality of Wushui River, Yinxi River, Niuxing Mountain, Oblique Weir and other rivers and reservoirs around the demonstration area becomes better. After closing enterprises involved in heavy metal pollution and scattered 89 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mining points, surface water basically meets the standard and conforms to Quality Standards for Farmland Irrigation Water. Through selection, it is found pollutant source of Xiaojia Demonstration Area and Baishui Demonstration Area in Qiyang County is clear and controllable without atmospheric pollution, tailings reservoir, mineral waste residues and other pollutant sources as well as left problems of mining and mineral processing, which basically won’t result in new heavy metal pollution to downstream agricultural land. 4.5 Investigation and Assessment of Current Environmental Quality Status 4.5.1 Investigation and Assessment of Current Surface Water Environment Status The monitoring results of surface water quality in new newly-added demonstration areas of each project county are shown in Appendix 5. (1) Distribution of Monitoring Points In order to investigate and have knowledge of the water quality of irrigation water sources in the newly-added demonstration areas, the CPMO of each project county entrusted the monitoring unit to monitor the irrigation water sources. (2) Time of Monitoring The monitoring time is from May 2019 to December 2020 (3) Monitoring Factor Water quality monitoring factors: pH, CODCr, TP, NH4-N, As, Pb, Cd, Cr6+ and Hg. (4) Assessment Standards Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). (5) Assessment Results Yongding District: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Yongding District all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III 90 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report in Environmental Quality Standards for Surface Water (GB3838-2002). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Jishou City: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Jishou City all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Yongshun County: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Yongshun County all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Cili County: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Cili County all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) Huayuan County: it can be known from monitoring result that monitoring factors of water quality, namely CODCr, Cd, Pb, As, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Huayuan County all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Anhua County: it can be known from monitoring result that monitoring factors of 91 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Anhua County all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Hengyang County: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in Fuxing Demonstration Area and Qingli Demonstration Area in Hengyang County all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Hengnan County: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in Xiangyang Demonstration Area (Chaoyang Village, Huanghe Village) and Quanxi Demonstration Area (Quanchang Village) in Hengnan County all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Lengshuitan District: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in Xianghuaba Demonstration Area and Shixijiang Demonstration Area in Lengshuitan District all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Linwu County: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Linwu County all meet requirements as 92 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). Qiyang County: it can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in various newly-added demonstration areas in Qiyang County all meet requirements as specified in Quality Standards for Farmland Irrigation Water (GB5084-2021) and Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). 4.5.2 Investigation and Assessment of Current Soil Environment Status (1) Distribution of Monitoring Points In order to investigate and have knowledge of the content of heavy metals in the soil of the demonstration area of the project county, the monitoring units of the agricultural bureau of each project county monitored the soil of the demonstration area. (2) Time of Monitoring The monitoring time is from June 2019 to December 2020. (3) Monitoring Factor Cadmium (Cd), arsenic (As), lead (Pb) and chromium (Cr) (4) Assessment Standards Screening value of ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018). (5)Assessment Results According to the monitoring results, the evaluation results of heavy metal content in farmland soil of newly-added demonstration areas in each project county are as follows Yongding District: the cadmium content in farmland soil in all newly added demonstration areas in Yongding District generally is higher than the screening value of "Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)" (GB15618-2018). Among them, the average cadmium content in farmland soil in Yuanguping Demonstration Area is 0.49 mg/kg, and the cadmium content in soil is 93 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mainly between 0.3 and 1.0 mg/kg, which is higher than the screening value. The average cadmium content in farmland soil in Yinjiaxi Demonstration Area is 0.39mg/kg, and the cadmium content in soil is mainly between 0.3 and 1.0 mg/kg, which is higher than the screening value. The average cadmium content in soil in Yanghuping Demonstration Area is 0.34mg/kg, and the cadmium content in soil is mainly between 0.3 and 0.8 mg/kg, which is higher than the screening value. The average cadmium content in soil in Wentang Demonstration Area is 0.36mg/kg, and the cadmium content in soil is mainly between 0.3 and 1.0 mg/kg, which is higher than the screening value. In addition, the monitoring factors Pb, As and Cr of farmland soil in each newly added demonstration area in Yongding District is not higher than the required screening values in "Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)" (GB15618-2018). Jishou City: the cadmium content in the newly added farmland soil in the old demonstration areas of Jishou City is generally higher than the screening value but is lower than the requirements of the control value. Among them, the cadmium content of farmland soil in the newly added area of Qianzhou Demonstration Area is mainly between 0.3 and 1.0 mg/kg, and the cadmium content of soil is higher than the screening value requirements. The cadmium content of farmland soil in the newly added area of Aizhai Demonstration Area is mainly between 0.3 and 1.0 mg/kg, and the cadmium content of soil is higher than the screening value requirements. In addition, the monitoring factors Pb, As and Cr of farmland soil in each demonstration area of Jishou City is not higher than the required screening values in "Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)" (GB15618-2018). Yongshun County: the cadmium content in farmland soil in all newly added demonstration areas of Yongshun County is generally higher than the screening value but is lower than the requirements of the control value. Among them, the average content of cadmium in the soil of the Shaba Demonstration Area is 0.382 mg/kg, and the content of cadmium in the soil is mainly between 0.3 and 1.0 mg/kg, which is higher than the screening value. The average content of cadmium in the soil of the Xiqi Demonstration Area is 0.373 mg/kg, and the content of cadmium in the soil is mainly between 0.3 and 1.0 94 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mg/kg, which is higher than the screening value. In addition, the monitoring factors Pb, As and Cr of farmland soil in each demonstration area of Yongshun County is not higher than the required screening values in "Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)" (GB15618-2018). Cili County: the cadmium content in the newly added farmland soil in each demonstration area of Cili County is generally higher than the requirements of the screening value. Among them, the cadmium content in farmland soil in Dongyueguan Town Demonstration Area is mainly between 0.3 and 0.8 mg/kg, and the cadmium content in soil is higher than the requirements of the screening value. The cadmium content in farmland in Yangliupu Township Demonstration Area is higher than the standard. The cadmium content in farmland soil in the demonstration area was mainly between 0.3 and 1.0 mg/kg, and the cadmium content in soil is higher than the requirements of the screening value. The cadmium content of farmland soil in Tongjinpu Town Demonstration Area is mainly between 0.3- 1.0 mg/kg, and the cadmium content of soil is higher than the screening value. The cadmium content of farmland soil in Sanhekou Town Demonstration Area is mainly between 0.3- 1.0 mg/kg, and the cadmium content of soil is higher than the screening value. The cadmium content of farmland soil in Xiangshi Town Demonstration Area is mainly between 0.3- 1.0 mg/kg, and the cadmium content of soil is higher than the screening value. In addition, the monitoring factors Pb, As and Cr of farmland soil in each demonstration area of Cili County is not higher than the required screening values in "Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)" (GB15618-2018). Huayuan County: according to the monitoring results, cadmium is generally higher than the standard in farmland soil in the demonstration area of Biancheng Town to be added in Huayuan County. The results showed that the pH of farmland soil in Biancheng Town Demonstration Area was 6.48 ~ 7.33; the total cadmium content was 0.49 ~ 4.36mg/kg, exceeding the standard by 0.63 ~ 13.53 times; the lead content was 63 ~ 168mg / kg, not exceeding the standard; the mercury content was 0.0951 ~ 0.168mg/kg, 95 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report not exceeding the standard; the arsenic content was 5.8 ~ 19.5mg/kg, not exceeding the standard; the total chromium content was 45 ~ 87mg / kg, not exceeding the standard. Anhua County: according to monitoring result, Cd & As contents in agricultural soil in all newly-added demonstration areas in Anhua County generally exceeds the standard; among them, Cd content in agricultural land in Dafu Town Demonstration Area is between 0.191~6.5mg/kg, exceeding the standard by 0.01-20.7 times with the exceeding ratio being 92%; As content is between 3.93~61.60 mg/kg, exceeding the standard by 0.002-1.46 times with the exceeding ratio being 23%; Cd content in agricultural land in Le’an Town Demonstration Area is between 0.145~1.29mg/kg, exceeding the standard by0.01-3.3 times with the exceeding ratio being 62.6%; Cd content in agricultural land in newly added area of Qingtang Town Demonstration Area is between 0.135~3.04mg/kg, exceeding the standard by 0.003-9.1 times with the exceeding ratio being 83.3%; Hengyang County: Yanglin Demonstration Area of Fuxing Village of Sanhu Town: the content of cadmium is higher than the standard and the content of chromium, lead and arsenic in farmland soil have reached the screening value of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), among which the soil cadmium content is 0.24-0.82 mg/kg, the over-limit ratio is 50%, and the times of over-limit is 0.03-1.05 The content of cadmium, arsenic and lead in Qingli Demonstration Area of Xidu Town has not reached the screening value of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), in which the soil cadmium content is 0.38-4.40 mg/kg, the over-limit ratio is 80%, and the times of over-limit is 0.27-13.67 times; The content of Pb is 52.7-288mg/kg, the over-limit ratio is 20%, and the times of over-limit is 0.15-2.6 times; The arsenic content is 13.6-47.6 mg/kg, the over-limit ratio is 13.33%, and the times of over-limit is 0.27-0.58 times. Hengnan County: cadmium, lead and arsenic in farmland soil in Xiangyang Demonstration Area have not reached the screening value of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), among which the soil cadmium content is 0.608 ~ 14.60 mg/kg, the 96 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report over-limit ratio is 100%, and the times of over-limit is 0.66-23.33 times; The lead content is 43.1 ~ 648mg/kg, the over-limit ratio is 37.5%, and the times of over-limit is 0.49-3.63 times; The arsenic content is 6.04 ~ 147.69 mg/kg, the over-limit ratio is 37.5%, and the maximum times of over-limit is 0.02-3.92 times. In Quanxi Demonstration Area (Quanchang Village), the content of cadmium is higher than the standard and the content of chromium, lead and arsenic have reached the screening values of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), in which the soil cadmium content is 0.627 ~ 3.57 mg/kg, the over-limit ratio is 100%, and the times of over-limit is 1.09-7.93 times. Lengshuitan District: the content of cadmium is higher than the standard in farmland soil of Niujiaoba Demonstration Area and the content of chromium, lead and arsenic have reached the screening values of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), in which the cadmium content in soil is 0.26-0.69 mg/kg, the over-limit ratio is 38.9%, and the times of over-limit is 0.025-0.08 times. The content of cadmium in farmland soil in Shixijiang Demonstration Area is higher than the standard and the content of chromium, lead and arsenic have reached the screening values of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), in which the cadmium content in soil is 0.27-0.46 mg/kg, the over-limit ratio is 33.3%, and the times of over-limit is 0.03-0.15 times. The content of cadmium in farmland soil in Xianghuaba Demonstration Area is higher than the standard and the content of chromium, lead and arsenic have reached the screening values of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), in which the cadmium content in soil is 0.1-0.92 mg/kg, the over-limit ratio is 86.2%, and the times of over-limit is 0.03-0.53 times. Linwu County: cadmium, chromium, lead and arsenic in farmland soil in the newly-added area of Wushui Town Demonstration Area, Nanqiang Town Demonstration Area have all reached the screening values of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018). 97 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Qiyang County: cadmium, chromium, lead and arsenic in farmland of newly-added project villages in Xiaojia Demonstration Area have all reached the screening values of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018). 4.5.3 Inspection and Assessment of the Current States of Irrigation Canal Sediment See Appendix 6 for the monitoring results of the current states of the irrigation canal sediment in the newly added demonstration areas of each project county. (1) Investigation Object Irrigation canal sediments in the demonstration areas. (2) Assessment Standards Execute ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018) (3) Assessment Results Yongding District: as per the monitoring results and refer to ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the sediment of irrigation canal in four newly-added demonstration areas of Yongding District can all meet the control value requirements. Jishou District: as per the monitoring results and refer to ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the sediment of irrigation canal in newly-added area of two old demonstration areas of Jishou District can all meet the control value requirements. Yongshun County: as per the monitoring results and refer to ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the sediment of irrigation canal in 2 newly-added demonstration areas of Yongshun County can all meet the control value requirements. Cili County: as per the monitoring results and refer to ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the sediment of irrigation canal in the newly-added demonstration area of Cili County can meet the control value 98 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report requirements. Huayuan County: as per the monitoring results and refer to ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the sediment of irrigation canal in the newly-added demonstration area of Huayuan County can meet the control value requirements. Anhua County: as per the monitoring results and refer to ‘Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the sediment of irrigation canal in each newly-added demonstration area of Anhua County can all meet the control value requirements. Hengyang County: as per the monitoring results, the pH value of Yanglin Demonstration Area of Fuxing of Sanhu Town (6 monitoring points) is 6.0 ~ 8.4. Compared with the ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the content of lead, chromium, cadmium and arsenic is lower than the standard. Qingli Demonstration Area of Xidu Town: as per the monitoring results, the pH value of sediment of irrigation canal in Qingli Demonstration Area (3 monitoring points) is 5.0 ~ 7.9. Compared with the ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the content of lead, chromium, cadmium and arsenic is lower than the standard. Hengnan County: as per the monitoring results and compared with the ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the content of lead, chromium, cadmium and arsenic of sediment of Xiangyang Demonstration Area is lower than the standard. Lengshuitan District: as per the monitoring results and compared with the ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the content of lead, chromium, cadmium and arsenic of sediment of Xianghuaba Demonstration Area and Shixijiang Demonstration Area is lower than the standard. 99 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Linwu County: Compared with ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the content of the monitoring factors of irrigation canal sediment in Wushui Demonstration Area and Nanqiang Demonstration Area of Wushui County is lower than the agricultural land soil control value standard. Qiyang County: Compared with ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the content of the monitoring factors of irrigation canal sediment in Xiaojia Demonstration Area is lower than the agricultural land soil control value standard. 4.6 Investigation and Evaluation of Rice in Demonstration Area (1) Investigation Object Rice samples collected in the newly-added demonstration areas. (2) Assessment Standards National Standards for Food Safety: Contaminant Limit in Foods (GB2762-2012) (standard value: Pb: 0.2mg/kg, inorganic As: 0.2mg/kg, total Cr: 1.0mg/kg, Hg: 0.02mg/kg, Cd: 0.2mg/kg). (3) Monitoring Results Yongding District: the rice risks in the newly added demonstration areas in Yongding District mainly include combined pollution of cadmium and arsenic and single pollution of cadmium. Among them, the risk of rice in Yuanguping Demonstration Area is combined pollution of cadmium and arsenic, the average cadmium content of rice is 0.24 mg/kg, and the cadmium content of rice is mainly between 0.2 and 0.4 mg/kg; The average arsenic content in rice is 0.26 mg/kg, and the arsenic content in rice is mainly between 0.2 and 0.4 mg/kg. The risk of rice in Yinjiaxi Demonstration Area is combined pollution of cadmium and arsenic, the average cadmium content of rice is 0.25 mg/kg, and the cadmium content of rice is mainly between 0.2 and 0.4 mg/kg; The average arsenic content in rice is 0.30 mg/kg, and the arsenic content in rice is mainly between 0.2 and 0.4 mg/kg. The risk of rice in Yanghuping Demonstration Area is combined pollution of cadmium and arsenic, the 100 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report average cadmium content of rice is 0.25 mg/kg, and the cadmium content of rice is mainly between 0.2 and 0.4 mg/kg; The average arsenic content in rice is 0.26 mg/kg, and the arsenic content in rice is mainly between 0.2 and 0.4 mg/kg. The risk of rice in Wentang Demonstration Area is single pollution of cadmium, with an average cadmium content of 0.25 mg/kg, and the cadmium content of rice is mainly between 0.2 and 0.4 mg/kg. Jishou City: Main risks of rice in the newly-added area of the previous demonstration areas in Jishou City include cadmium-arsenic pollution and arsenic pollution. Main risk of rice in the newly added area in the Qianzhou Demonstration Area includes arsenic pollution and the arsenic content in rice is mainly between 0.2 and 0.4 mg/kg. Main risk of rice in the newly added area in the Aizhai Demonstration Area includes cadmium-arsenic pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg; arsenic between 0.2 and 0.4 mg/kg. Yongshun County: Main risks of rice in the newly-added demonstration areas in Yongshun County include cadmium-arsenic- lead pollution and cadmium-arsenic pollution. Among them, the risk of rice in the Shaba Demonstration Area includes cadmium-arsenic-lead pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg, arsenic between 0.2 and 0.4 mg/kg and lead between 0.2 and 0.4 mg/kg. The risk of rice in the Xiqi Demonstration Area includes cadmium-arsenic pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg and arsenic between 0.2 and 0.4 mg/kg. Cili County: Main risks of rice in the newly added area in the Demonstration Area of Cili County include cadmium-arsenic pollution and cadmium pollution. Main risks of rice in the newly added area in the Dongyueguan Town Demonstration Area include cadmium-arsenic pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg and arsenic between 0.2 and 0.4 mg/kg. Main risks of rice in the newly added area in Yangliupu Township include cadmium-arsenic pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg and arsenic between 0.2 and 0.4 mg/kg. Main risks of rice in the newly added area in Tongjinpu Town include cadmium-arsenic pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg and arsenic between 0.2 and 101 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 0.4 mg/kg. Main risks of rice in the newly added area in Sanhe Town include cadmium pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg. Main risks of rice in the newly added Xiangshi Town include cadmium pollution and the cadmium content in rice is mainly between 0.2 and 0.4 mg/kg. Huayuan County: There is a risk of heavy metal (lead) pollution with rice in the Demonstration Area of Biancheng Town and the contents of cadmium, arsenic, mercury, chromium, etc. are within the limit, among which cadmium is monitored to be 0.002-0.048mg/kg and this reaches the standard. Monitoring points where lead is monitored to be 0.02-0.2 mg/kg account for 91.3% and those be above 0.2 mg/kg 8.7%. Anhua County: The rice in Dafu Town Demonstration Area was polluted by Cd and As. Monitoring points where Cd is monitored to be ＜0.2mg/kg account for 60.2%, those be 0.2-0.4mg/kg 15.9%, 0.4-0.6mg/kg 8.0% and ＞0.6mg/kg 15.9%. Monitoring points where As is monitored to be ＜0.2mg/kg account for 79.6% and those be 0.2-0.4mg/kg 20.4%. The rice in Le’an Town Demonstration Area was polluted by Cd and As. Monitoring points where Cd is monitored to be ＜0.2mg/kg account for 64.8%, those be 0.2-0.4mg/kg 28.6% and 0.4-0.6mg/kg 6.6%. Monitoring points where As is monitored to be ＜0.2mg/kg account for 89.0% and those be 0.2-0.4mg/kg 11.0%. The rice in newly added area of Qingtang Town Demonstration Area was polluted by Cd and As. Monitoring points where Cd is monitored to be ＜0.2mg/kg account for 50.0%, those be 0.2-0.4mg/kg 38.3%, 0.4-0.6mg/kg 8.3% and ＞ 0.6mg/kg 3.3%. Monitoring points where As is monitored to be ＜0.2mg/kg account for 91.7% and those be 0.2-0.4mg/kg 8.3%. Hengyang County: A total of 32 rice samples were collected in the Sanhu Fuxing Yanglin Demonstration Area, the tests and analysis of which show that there is a risk of heavy metal (cadmium) pollution in the area. Monitoring points where cadmium is monitored to be <0.2mg/kg account for 9.38%, those to be between 0.2 and 0.4mg/kg 53.1% and those to be between 0.4 and 0.6mg/kg 37.5%. A total of 15 rice samples were collected in the Xidu Qingli Demonstration Area where there is a risk of heavy metal (cadmium, arsenic and lead) pollution. Monitoring points where cadmium is monitored to be <0.2mg/kg account for 13.3%, those to be between 0.2 and 0.4mg/kg 66.7%, those to be 102 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report between 0.4 and 0.6mg/kg 13.3% and those to be above 0.6mg/kg 6.7%. Monitoring points where As is monitored to be <0.2mg/kg account for 93.3%, those to be between 0.2 and 0.4mg/kg 6.7%. Monitoring points where Pb is monitored to be <0.2mg/kg account for 93.3%, those to be between 0.2 and 0.4mg/kg 6.7%. Hengnan County: There is a risk of heavy metal (cadmium, arsenic and lead) pollution in the rice in Chaoyang Village of Xiangyang Demonstration Area and monitoring points where cadmium is monitored to be 0.2 and 0.4mg/kg account for 12.5%, those to be between 0.4 and 0.6mg/kg 37.5% and those to be between 0.6 and 0.9mg/kg 50%. Monitoring points where As is monitored to be <0.2mg/kg account for 25%, those to be between 0.2 and 0.4mg/kg 75%. Monitoring points where Pb is monitored to be <0.2mg/kg account for 87.5%, those to be between 0.2 and 0.4mg/kg 12.5%. There is a risk of heavy metal (cadmium, arsenic and lead) pollution in the rice in Huanghe Village of Xiangyang Demonstration Area and monitoring points where cadmium is monitored to be <0.2mg/kg account for 25%, those to be above 0.6mg/kg 75%, those where arsenic is monitored to be below 0.2mg/kg 75% and those to be between 0.2-0.4mg/kg 25%. Monitoring points where lead is monitored to be below 0.2mg/kg account for 62.5% and those to be between 0.2 and 0.4mg/kg 37.5%. There is a risk of heavy metal (cadmium, arsenic and lead) pollution in the rice in Quanchang Village of Quanxi Demonstration Area and monitoring points where cadmium is monitored to be below 0.2mg/kg account for 60% and those to be between 0.2-0.4mg/kg 30%. Monitoring points where cadmium is monitored to be between 0.4-0.6mg/kg account for 10%. Monitoring points where As is monitored to be below 0.2mg/kg account for 30% and those to be between 0.2-0.4mg/kg 70%. Monitoring points where lead is monitored to be below 0.2mg/kg account for 90% and those to be between 0.2 and 0.4mg/kg 10%. Lengshuitan: A total of 36 rice samples were collected in the Niujiaoba Demonstration Area where there is a risk of heavy metal (cadmium and arsenic) pollution. Monitoring points where cadmium is monitored to be below 0.2mg/kg account for 61.1%, those to be between 0.2 and 0.4mg/kg 30.6%, those to be between 0.4 and 0.6mg/kg 5.6% and those to be above 0.6mg/kg 2.7%. Monitoring points where As is monitored to be below 0.2mg/kg 103 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report account for 55.6% and those to be between 0.2-0.4mg/kg 44.4%. A total of 21 rice samples were collected in the Shixijiang Demonstration Area where there is a risk of heavy metal (cadmium and arsenic) pollution. Monitoring points where cadmium is monitored to be below 0.2mg/kg account for 52.4% and those to be between 0.2 and 0.4mg/kg 33.3%. Monitoring points where cadmium is monitored to be between 0.4-0.6mg/kg account for 14.3%. Monitoring points where As is monitored to be below 0.2mg/kg account for 85.7% and those to be between 0.2-0.4mg/kg 14.3%. A total of 29 rice samples were collected in the Xianghuaba Demonstration Area where there is a risk of heavy metal (cadmium and arsenic) pollution. Monitoring points where cadmium is monitored to be below 0.2mg/kg account for 62.1% and those to be between 0.2 and 0.4mg/kg 34.5% and those to be between 0.4-0.6mg/kg 3.4%. Monitoring points where As is monitored to be below 0.2mg/kg account for 86.2% and those to be between 0.2-0.4mg/kg 13.8%. Linwu County: A total of 4 rice samples were collected in the newly-added area in the Wushui Town Demonstration Area where there is a risk of heavy metal (cadmium and arsenic) pollution. Monitoring points where cadmium is monitored to be below 0.2mg/kg account for 50% and those to be between 0.2 and 0.4mg/kg 50%. Monitoring points where arsenic is monitored to be below 0.2mg/kg account for 25% and those to be between 0.2 and 0.4mg/kg 50%. A total of 15 rice samples were collected in the newly added area in the Nanqiang Town Demonstration Area where the monitoring results show that there is no risk of heavy metal (cadmium and arsenic) pollution. A total of 4 rice samples were collected in Shuidong Demonstration Area where there is a risk of heavy metal (cadmium and arsenic) pollution. Monitoring points where cadmium is monitored to be below 0.2mg/kg account for 75% and those to be between 0.2 and 0.4mg/kg 25%. Monitoring points where arsenic monitored to be between 0.2 and 0.4mg/kg 100%. Qiyang County: there is risk of rice in Xiaojia Demonstration Area being polluted by heavy metal cadmium. Monitoring points where cadmium is monitored to be between 0.2 and 0.4mg/kg (low risk-medium risk) account for 43.3%, those to be 0.4-0.6mg/kg (high risk) 16.7% and those to be ＞0.6mg/kg (extremely high risk) 13.33%. In addition, 26.7% of the points were monitored to be qualified. 104 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 105 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 4.7 Identification of Environmental Impact on Demonstration Area Refer to Table 4-2 for environmental impact identification in demonstration area. Table 4-2 Identification Table for Environmental Impact in Demonstration Area No. Project activity Activity description Potential environmental impact Mitigation measures Sensitive points involved 1 Demonstration of agricultural land based on risk ⚫ Unit accepting inspection sample shall be qualified inspection lab Dense monitoring is conducted for selected demonstration ⚫ Irrigation water source, areas based on the requirement in monitoring plan ⚫ Sampling in demonstration area canal and sediments of (density of monitoring point is about every 50mu and and samples shall be analyzed and irrigation water source and there shall be no less than 5 samples in each monitoring in qualified inspection lab. canal Dense demonstration area; monitor heavy metal content in soil Waste liquid and solid wastes during ⚫ Surrounded potential monitoring and Safely handle waste liquid and solid 1.1 and agricultural product and they shall be correspond to chemical analysis process may be surface water, ground water risk grade wastes generated in inspection lab. each other; monitoring heavy metal content in sediments generated while they shall be handled and atmospheric pollutant evaluation and monitor water quality and heavy metal content of based on national management source, including mineral irrigation water); evaluate risk grade based on monitoring specification in inspection lab with little enterprises involved in heavy data and determine integrated risk management and influence on environment. metal discharge in upstream control measures. of demonstration area, tailings, left historical pollutant source and slag dump Adopt targeted risk management and control measures Integrated risk based on analysis of effective data of rice, endogenous management 1.2 agriculture, exogenous agriculture and agricultural and control production management in the project. Refer to 2.1-2.4 measures for specific contents. 106 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report ⚫ Belong to small civil engineering construction activity; the project is located around agricultural land; there is no environmental sensitive area in project and surrounded area. The scale of the project is very small. The ⚫ Villager, school and construction personnel is no more than other sensitive points around 5-10 at most so it is unnecessary to ⚫ Spray water and reduce dust Build or reconstruct 87.25km of channels (the length of small civil engineering construct construction camps; in generation; single channel project is 500~1000m), 51 grit chambers activity addition, land requisition, relocation and ⚫ Arrange construction time Engineering (the length, width and height are 2*2*1m), 43.73km of ⚫ Landfills that receive 1.2.1 minority are not involved. Raise dust, reasonably; measures farm tracks, 3,000m of ecological interception ditches, 32 the bottom sediments in the noise, waste water and solid wastes may ⚫ Construction machines shall small reservoirs and 1 electric pumping station in the irrigation canals(exceeding be generated during the construction conform to national health protection newly-added demonstration areas. the soil control value) process, while the influence is standard; momentary in small scope of construction area which shall be disappeared after the construction is finished. ⚫ Irrigation canal dredging is involved in sediments which may be suffered from heavy metal pollution. ⚫ All agricultural measures shall be ⚫ Set application amount of lime, done inside the field without land organic fertilizer and soil passivator Combination of measures such as highly accumulative ⚫ Villager, school and requisition, relocation and minority. based on soil characteristics and risk rice species control, optimized field water management other sensitive points ⚫ Waterflooding irrigation during degree in different demonstration Agricultural (waterflooding and irrigation), soil acidification influenced by lime 1.2.2 the grain-filling and heading period can areas based on monitoring result of measures conditioning (pH value), organic fertilizer application, soil application; reduce the heavy metal absorption by soil; passivator application, removing straws out of farmlands, ⚫ Orchard and forest rice. ⚫ Special agricultural lime shall be etc. receiving straw; ⚫ Apply lime to adjust pH value of selected for applied lime with soil and reduce absorption of crops on certificate on key index verification of 107 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report heavy metal. However, the excessive product quality issued by authorized application of lime may result in soil institution; the content of calcium hardening. If protection measures are oxide shall be 70% in CaO. Operators not adopted, lime application may result must wear protective clothes and in poor influence on health of lime apply lime with the wind direction (it application personnel. is inappropriate to apply when wind ⚫ The application of soil passivator power is above Level-4); can reduce activity of heavy metal in ⚫ Applied passivator must be soil. agricultural pesticides allowed to be ⚫ The application of organic applied in agricultural land by national fertilizer can improve physicochemical agricultural department to guarantee property of soil, while the application of new heavy metal pollution won’t be unqualified organic fertilizer may result brought; in secondary pollution of soil in ⚫ Advocate to use commercial agricultural land. organic fertilizer and select ⚫ By removing straws out of the commercial organic fertilizer which agricultural lands, heavy metal in straws has conducted field test and passed can be removed out of the agricultural secondary pollution evaluation to lands, which facilitates to reduce heavy determine product security with metal in agricultural land soil. Handle product registration; in addition, the potential environmental influence in the heavy metal content in commercial field after removing straw from field. organic fertilizer must conform to Organic Fertilizer (NY 525-2012); ⚫ Use removed straws for orchard and forest coverage. Popularize agricultural cleaning production, encourage ⚫ Be favorable for reducing use ⚫ Clean and recycle packaging of farmers to apply organic fertilizer, reduce use amount of amountof chemical pesticides; agricultural inputs in time; send to Integrated pest Recovery unit of packaging of 1.2.3 fertilizer, scientifically apply pesticide, popularize popularize agricultural, physical and local unit specially recycling management agricultural inputs professional unified green prevention and control on pests biological prevention measures and low packaging of agricultural inputs; of agricultural crops and popularize high effective, low toxic and low residue chemical ⚫ Develop pest monitoring 108 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report toxic and low residue pesticide and modern plant pesticides which are favorable for ⚫ Develop training on pest protection machine. ecological and environmental protection prevention knowledge for agricultural of demonstration area. Handle potential technical personnel and farmers. environmental impact of packaging of agricultural inputs. 1.2.4 Other measures Carry out the rice safety and reasonable technology research in the demonstration area based on the list of low emergency cadium accumulation rice varieties recommended in Hunan Province, conduct a reasonable screening on the rice varieties entering into the Variety ⚫ No environmental impact. (1) demonstration area, confirm the cadium accumulation Subsidize seed cost Price of agricultural product screening ⚫ Influence product price index of the rice varieties which are mainly popularized in the area, and when the BCF index of a rice variety is higher than level-Ⅵ risk, the cadium accumulation risk of this variety is deemed high,and should be prevented fron entering into the demonstration area. ⚫ Farmers do not cooperate. Planting other crops requires change of planting habits and techniques. Make a subsidy according to 6,000 Although the project management Yuan/hectare. For annual crops, make offices and the project team have a subsidy for one year; and Change of Change of already carried out in-depth The newly added demonstration areas almost do not cropping system for planting two-year Income of farmers involved in (2) cropping investigation and analysis, there involve any restructuring or above crops, make a subsidy until change of cropping system system may still be some farmers who are the grown year. The subsidy budget not willing cooperate in the for change of cropping system is process. 7,611,800 Yuan. ⚫ The issue of distribution and management of subsidies for change of cropping system. 109 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Consensus has been reached on subsidy standards, but more farmers are worried about the transparency of the subsidy. ⚫ Labor supply problem. At present, many villages are “empty villages” because young and middle-aged laborers are all working outside. Planting of fruits and seedlings requires more laborers, which may face the problem of insufficient labor. ⚫ Rice can be stored after being inspected; ultra standard rice shall be purchased by designated enterprise based on national protection price or market price and stored by special ⚫ Plant with industrial Rice that exceeds the standard shall be purchased by warehouse; utilization of ⚫ Heavy metal pollution risk exists Control of the special grain reserve depots for industrial use and ⚫ Inspect heavy metal content in standard-exceeding rice (such for reutilizing residues after industrial (3) standard-exceed subsidies will be provided to such purchasers. Such residues after industrial utilization of as alcohol plant, etc.) utilization of standard-exceeding rice ing rice subsidy shall be granted as per 20% of the national standard-exceeding rice and safely ⚫ Refuse landfill while the risk is small. purchase price of the year. handle residues of heavy metal by receiving standard-exceeding adopting sanitary landfill and other residues of heavy metal methods; ⚫ Compile Management and Control Program on Rice with Standard-exceeding Heavy Metal Certification of Subsidize the main body gaining no-pollution, green and (4) place of origin organic food certification with subsidy standard of ⚫ No negative environmental impact ⚫ of agricultural 5000/10000/20000 Yuan respectively. 110 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report product Construction, publicity and Encourage demonstration area to construct, publicize and (5) promotion fee popularize brand of agricultural product to improve ⚫ No negative environmental impact of agricultural economic value of product product brand Employ professional supervision institutions and organize township and village personnel to supervise implementation of agricultural measures (lime Project 1.3 application, organic fertilizer, passivator, flooding ⚫ No negative environmental impact supervision irrigation and removal of straw from field) and supervision fee shall be calculated based on 20 Yuan/mu/season 2 Strengthen agricultural environmental monitoring and management Establishment of agricultural Including sampling inspection vans, desktop computers, 2.1 environment ⚫ Belong to soft topic research samplers, GPS position indicators, settling barrels, digital monitoring without negative environmental impact. altimeters. database and early warning Preparation of Establish models according to monitoring data in the agricultural sub-project 1, provide a basic support to risk management management of farmlands, combine with management tools according ⚫ Belong to soft topic research 2.2 tools and to valid data, determine the contaminated risk level of without negative environmental impact. agricultural risk farmlands and crops in the area, and prepare the drawing based agricultural production risk map in the whole province. on risk Development Develop and issue local regulatory systems and technical ⚫ Belong to soft topic research 2.3 and issuing of standards related to prevention, control and rehabilitation without negative environmental impact. local policy and of agricultural land and guide integrated management and 111 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report standard control of agricultural land pollution management and control in various demonstration counties Research on sustainable Research sustainable financing mechanism and ecological investment and compensation mechanism aiming at long-term agricultural financing ⚫ Belong to soft topic research 2.4 land pollution management and soil health recovery mechanism and without negative environmental impact. action so as to guarantee sustainable agricultural ecological development in Hunan compensation mechanism Cultivate management and technical capacity of governmental officers and organize international and domestic observation and training; develop training on environmental monitoring personnel and farmers and Capacity provide technical assistance for enterprises involved in 3 ⚫ No negative environmental impact building heavy metal pollution with total 178150 persons/days. Develop project idea and technique popularization activity in the form of seminar, training and other forms; share and publicize project experience and technology by making video and paper materials. Provide technical assistance and training for project management personnel (procurement, finance and security policy) to improve its management capacity, purchase office equipment necessary for project management Project institution as well as project daily management, 4 management ⚫ No negative environmental impact procurement and financial management fee. Conduct and evaluation project start/completion seminar and establish Mis system; collect change of agricultural land environmental quality and other related information and data during the project implementation process to monitor and evaluate 112 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report project implementation result. The design dimension of sedimentation basin is 2×2×1.0 m with cast-in concrete structure and cast C20 reinforcement concrete with wall thickness of 120mm and baseboard thickness of 120mm. The bottom elevation shall be away from canal bottom elevation at least 300mm. 113 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 5 Analysis of Impacts on Environment and Mitigation Measures (ECOP and Specified Point Mitigation Measures) 5.1 Analysis on Impacts of the Project Civil Engineering Construction Activities and Mitigation Measures The civil engineering construction activities of the integrated management Project of agricultural land pollution in Project Counties can be divided into two categories: ①Small-scale civil engineering construction including the front sedimentation basin, electric pumping station construction, impounding reservoir, motor-pumped well and small-scale field road maintenance (Reinforce the pavement level off only, and no increase the width and length of road); ②The field irrigation canal construction including the drainage canal and irrigation canal renovation and the ecological intercepting ditch construction. The project civil engineering activities have impact on water environment, atmospheric environment, acoustic environment and ecological environment during construction. The civil construction activities of the project counties are small-scale civil construction activities. The project is located around agricultural lands and there is no environmentally sensitive area inside or around the demonstration area. The scale of the project is very small. The number of construction workers for the project is not more than 5 – 10. There is no need to build construction camps, and land acquisition, demolition and ethnic minorities are not involved. Dust, noise, waste water, solid waste, etc. may be produced during the construction process, but these effects are temporary and little. They are limited to a very small area of the construction area, and the impact disappears immediately after the construction is finished. 5.1.1 Analysis on Impacts of Water Environment during Construction Waste water during construction mainly includes construction wastewater and domestic sewage of constructors. The construction waste water of this project mainly includes water seepage of foundation pit excavation, concrete mixing waste water, concrete curing waste water, 114 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report sand and gravel washing waste water, machinery oil-bearing waste water, etc. During channel engineering construction, the amount of waste water generated is relatively small, and the pollution factors of waste water are mainly SS, petroleum, cod, etc. The main pollutants of domestic sewage are COD, BOD5 and SS. The project’s construction personnel rely on nearby villages for food and lodging. According to the actual living conditions in the local villages, domestic sewage is collected in septic tanks and regularly removed for use as agricultural fertilizer. The arbitrary discharge of construction wastewater without any treatment will cause a certain amount of pollution to soil and surface water. Especially in rainy weather, it will have a greater influence on the surface water environment, but it will not bring heavy metal contamination. During the channel construction process, the sediment in the water will be disturbed and the SS concentration in the water will rise, which will have a short-term impact on the downstream water environment and agricultural land irrigation. Such projects should avoid the irrigation period of agricultural land. Reasonable construction methods need to be adopted to shorten the construction time as much as possible, and minimize the impact on water. 5.1.2 Analysis on Impacts of Ambient Air during Construction The project construction has concentrated impact on ambient air. The ambient air pollution mainly comes from the construction dust. During the construction, canal excavation, dregs transportation and loading, site clean-up and field construction will produce raised dust. The construction sites of the project are dispersed and the scale of the construction site in each demonstration area is small. Therefore, the construction dust produced is only in a small amount. Usually it only has some impact on the constructors. After the watering and dust suppression measures are taken, its impact on the regional environment is slight. 5.1.3 Analysis on Impacts of Acoustic Environment during Construction Noise during construction period mainly includes noise from construction site and 115 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report traffic noise during transport of materials. The Noise on the Construction Site The noises on the construction site mainly include the mechanical equipment noise and the impact noise during material loading such as shoveling and transportation, concreting, earth-rock filling as well as aggregated rock and gravel loading etc. Since the construction machinery is in mobile outdoor operation and has no sound insulation measures, it will have some impacts on the residents living around the construction site. The Traffic Noise The truck will be mainly used as the transportation vehicle during the construction. The maximum noise intensity of a truck can reach 90dB (A). The construction sites of the project are dispersed, the work amount of each demonstration area is small and there are not so many transportation vehicles. Therefore, the traffic noise in the construction transportation is intermittent and transient. The work amount in each demonstration area of the project is small and dispersed, the noises produced during the construction is intermittent and transient. In addition, the construction is only conducted during the daytime and the construction sites are normally over 200m away from the centralized settlement of the village. Therefore, the impact of the noises is slight. By strengthening management and taking corresponding environmental control measures, its impact can be minimized. 5.1.4 Analysis on Impacts of Solid Wastes during Construction The solid wastes during the construction are mainly the temporarily stockpiled dregs for foundation excavation during the renovation of drainage and irrigation canals and the construction of front sedimentation basins, ecological intercepting ditches and field road maintenance as well as the domestic wastes produced by the constructors. If no preventive measures are taken to the dregs, they will affect the landscape. In rainy seasons, they will cause water and soil loss; in windy and dry weather, they will produce flying dust. If the domestic wastes are not treated in time, they will breed mosquitoes in mild temperature and cause a stink and transmit diseases, thus having adverse impacts on 116 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report the surrounding environment. The drainage channel and irrigation channel project mainly consists of the reconstruction and hardening of the original channel and reinforcement is conducted by “masonry + concrete”. The design volume of the front sedimentation tank is 4m3, and the quantity of work is small, so that the excavation can be used for canal construction; the ecological intercepting ditch is mainly built based on the original ditch. Water purification, sediment and floating objects interception can be achieved through planting aquatic plants and setting up multi-stage intercepting dams in the passing ditch. The field roads to be maintained in each project county are relatively short and it will not increase the width and length of the road surface. The road surface is sand and gravel road surface. Earth and stone work can be balanced in each section. The sub-demonstration areas of each project county are mountainous and hilly areas, and the quantities of each project site are not large. The excavated muck can be leveled and absorbed in situ; the amount of domestic waste generated by construction personnel is small, which is collected centrally on the construction site and cleaned and transported away by the construction party in a timely manner, thus having little impact on the surrounding environment. 5.1.5 Analysis on Impacts on Ecological Environment during Construction The construction work of this project mainly includes drainage channel, irrigation channel reconstruction, sedimentation tank construction and field road maintenance. The drainage channel and irrigation channel of this project are reconstructed from the original drainage channel and no additional land will be used. Maintenance of field roads does not increase the width and length of roads and does not involve land acquisition. The land for the pre-settling tank is very small, and it is planned to be built on vacant land in the demonstration area, which does not involve land acquisition. During the construction period, the storage of construction sites, temporary storage yards of muck and construction building materials will need temporary land occupation, which will affect the ecological factors such as vegetation and soil environment within the scope of its 117 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report influence. Occupation of the construction site, mechanical rolling and personnel activities can destroy the surface vegetation and soil structure and reduce the ecosystem function. During excavation and filling, a certain area of surface vegetation will be stripped off from the land, which will easily cause local surface vegetation damage, while waste soil stacking will inevitably cause soil erosion. Therefore, temporary soil erosion will be caused during the construction of the project. There is no large area of land occupied in this project. After the construction period, the temporary construction area can be reclaimed and planted immediately, which has little impact on land utilization. 5.1.6 Mitigation Measures to Impacts of the project Civil Engineering Construction on Environment For the mitigation measures to impacts of the project civil engineering construction on environment, please see the following appendixes: Appendix 1 Environmental Protection Procedure of Small-scale Civil Engineering Construction ECOP Appendix 2 Environmental Protection Procedure of Field Irrigation Facility Construction ECOP 5.1.7 Impact Analysis and Mitigation Measures of Project Construction Activities on Specific Points Newly added demonstration areas in this Project shall be away from sensitive sites including schools, densely populated residential areas, etc. Sensitive sites are not applied to construction activities. The bottom sediments in the irrigation canals in the newly added demonstration areas in all project counties meet the control value in the Soil Environmental Quality – Standard for Risk Control of Soil Pollution of Agricultural Land (Trial) (GB 15618-2018) and no cleanup is required. Therefore, no specific sites are applied to construction activities in the newly added demonstration areas in all project counties. 118 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 5.2 Analysis on Surrounding and Upstream Pollution Sources and Mitigation Measures 5.2.1 Investigation and Analysis on Surrounding and Upstream Pollution Sources (1) Yongding District The current agricultural land pollution of newly-added demonstration areas in Yongding District is historical pollutant source of smelting enterprises with main part of sediment introduction through on-site survey, public consultation and material collection and analysis; in addition, waste gas containing heavy metal emitted by historical smelting enterprises is settled on soil. After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (2) Jishou City Through on-site reconnaissance, public consultation and data collection and analysis, the agricultural land pollution in the selected demonstration area of Jishou City belongs to historical pollution source, mainly brought in by sediment, followed by the settlement in soil of heavy metal-containing waste gas discharged by smelting enterprises. In past, in the surrounding and upper reaches of the Qianzhou Demonstration Area, there were heavy metal-related emission enterprises such as Jishou Branch of Baojing Jianlei Mining Co., Ltd., Xiangxizhou Jinquan Printing Co., Ltd., Datang Mining Co., Ltd., and Rongjiang Manganese Co., Ltd. (these heavy metal-related enterprises were shut down from 2010 to 2015 and when these enterprises was shut down, the plant equipment and slag field had been cleaned up, and there were no residue left on site). In past, in the surrounding area of the Aizhai demonstration area, there were private vanadium mining activities (they were in small scale and forced to be shut down by the government in 2010. Slag has been cleaned up after shut down, and there is no residue left on site). After 119 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (3) Yongshun County Coal ore exploitation existed in upstream of demonstration area along the history while there was no smelting enterprise in surrounded area and upstream area without tailings ponds through on-site survey and material collection and analysis. Coal mining has been closed, slag has been cleared, and no new heavy metal pollution will be caused to agricultural land downstream. Pollution sources in the demonstration area are clear and controllable. (4) Cili County In past, there were mining enterprises involving heavy metal pollution, such as nickel-molybdenum ore, coal mine and realgar mining in Cili County in Zhangjiajie City. The mining, mineral processing and smelting all have a long history. At different stages of historical development, due to the restriction of technical conditions, knowledge level, supervision and other factors, the heavy metals in the discharged wastewater are deposited in the sediment of the ditch channel. The heavy metals in the waste gas settle in the soil and water through the atmosphere and enter the surface water, soil and underground water along with the surface runoff. The non-degradable nature of the discharged heavy metals causes them to accumulate gradually in the environment and accumulate over time, increasing the concentration of heavy metals in the soil, sediment and water and increasing the pollution, thus causing heavy metal pollution accidents. In the upper reaches of Sanhe Town demonstration area, there was realgar mining in history.There were no smelting enterprises in the periphery and the upper reaches and there is no tailings reservoir. Realgar mining has been closed and slag has been cleared. No new heavy metal pollution will be caused to the agricultural land in the lower reaches. 120 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report In the upper reaches of Tongjinpu Town demonstration area, there was coal mining in history. There were no smelting enterprises in the surrounding and upper reaches or tailings reservoir. Coal mining had been closed and slag had been cleaned up. No new heavy metal pollution would be caused to the agricultural land in the lower reaches. In the upper reaches of Dongyueguan Town demonstration area, there was a history of nickel-molybdenum mining. There were no smelting enterprises or tailings reservoir. Nickel-molybdenum mining had been closed and slag had been cleared. No new heavy metal pollution would be caused to the agricultural land downstream. In past, there were nickel-molybdenum mining activities in the upper reaches of the Gaoqiao Demonstration Area. There are no smelting enterprises in the periphery and the upper reaches or tailings reservoir, nickel-molybdenum mining has been closed, slag has been cleared, and no new heavy metal pollution will be caused to the agricultural land in the lower reaches. In past, there were nickel-molybdenum mining activities in the upper reaches of Yangliupu Township Demonstration Area. There are no smelting enterprises or tailings reservoir. Nickel-molybdenum mining has been closed and slag has been cleared. No new heavy metal pollution will be caused to downstream agricultural land. (5) Huayuan County Through on-site reconnaissance, public consultation and data collection and analysis, the agricultural land pollution in the selected demonstration area of Huayuan County belongs to historical pollution source, mainly brought in by sediment, followed by the settlement in soil of heavy metal-containing waste gas discharged by smelting enterprises. Xinxiang Mining Company (having a lead-zinc mine and a separation plant, which were closed in 2015 and the equipment in the plant area and slag yard were cleaned up without any residue left on site) existed in the past in the upper reach of the Biancheng Town Demonstration Area. After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be 121 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report caused to the downstream agricultural land. (6) Anhua County Through on-site reconnaissance, public consultation and data collection and analysis, agricultural land pollution in the selected demonstration area of Anhua County belongs to a historical pollution source, mainly brought in by sediment, followed by settlement in soil of heavy metal-containing waste gas discharged by smelting enterprises. There once was a coal mine in the upper reach of the Le’an Town Demonstration Area (which was closed in the 1990s due to resource exhaustion, with residues cleaned up). Except for that, there are no other enterprises involving heavy metal discharge. There once was a private mining operation of antimony sulfide ores in the upper reach of the Dafu Town Demonstration Area (which was mined for a short period of time between 1993 and 1998 and has been closed without any residue left on site) and a antimony flotation plant (which produced from 1993 to 2003 and was shut down in 2003 when the plant equipment and slag yard were cleaned up without any residue left on site). There once were two coal mines in the upper reach of the Qingtang Town Demonstration Area (which were shut down in 2000-2002 due to resource exhaustion, and residues have been almost cleaned up). Apart from those above, there are no other enterprises involving heavy metal discharge. After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. (7) Pollution Sources in Hengyang County Demonstration Area and its Surroundings Hengyang County is typical of years of mining and separation and metallurgy in the reach of Xiangjiang River. There are hundreds of large and small mines and operations in the County, resulting in many sources of pollution. Heavy metals in the discharged liquid waste that deposited in the bottom sediments of the ditches and channels in various 122 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report development stages due to factors including technical conditions, level of awareness, degree of supervision efforts, etc. Heavy metals in the waste gas precipitated through air into the soil and water body and then flow with surface runoff into the surface water, soil and groundwater. Heavy metals discharged were not degradable so that they accumulated in the environment as time went by. Besides, the background value of heavy metals in the soil in the County is relatively high, resulting in excessive heavy metals in a large area of soil. Site surveys, public consultation and data collection and analysis show that the source of farmland pollution in the Qingli Demonstration Area in Hengyang County was mainly the pharmaceutical company and the livestock farms. The pharmaceutical company, the previous synthetic drug manufacturer, was built in 1977 and stopped production in 1997. Main products included phenylacetamide and phenylacetic acid. There was no effective environmental protection measure in the production process and about 3,000 tons of organic wastes were not safely disposed of when production stopped. Therefore, frequent rain wash year after year caused severe impacts on soil, air and the Zhengshui River. The People’s Government of Hengyang County commissioned a qualified agency to dispose of the organic wastes and conduct site remediation to step by step restore the surrounding ecological environment. There is no residue left on site and it is almost impossible to cause any new heavy metal pollution to the farmlands in the lower reach. Inadequate environmental protection measures in the relevant livestock farms caused the waste water to be discharged directly to severely impact the surface water in the region. In 2016, the Hengyang County Government shut down the livestock farms in the region and carried out a comprehensive improvement of the regional environment, which will not cause new heavy metal pollution to the farmlands in the lower reach. The Sanhu Town Demonstration Area uses the Zhengshui River as a source of irrigation water. There were once two small-size recycled paper mills, three illegal indigenous method vanadium refining plants, etc. Illegal indigenous method vanadium 123 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report refining operations can be traced back to the 1980s, whose annual processing capacity was less than 10,000 tons. Indigenous method vanadium refining mainly produces waste water and residue containing contamination factors including, lead, cadmium, chromium, arsenic, vanadium, etc. to cause pollution to Zhengshui River. In 2008, the two indigenous method vanadium refining operations were shut down by the law enforcement agency of Hengyang County, with the plant equipment and the slag yard cleaned up where there was no residue left and almost no new heavy metal pollution will be caused to the farmlands in the lower reach. (8) Hengnan County Site surveys, public consultation and data collection and analysis show that the farmland pollution in the Xiangyang Demonstration Area (Chaoyang Village, Huanghe Village) was mainly that of the Xiangjiang River carried over from the past and that the farmland pollution in the Quanxi Demonstration Area (Quanchang Village) was mainly the result of the backward flow of the Leishui River caused by major flooding consecutively in two years (2006 and 2007). Water flowed backward stayed in the Demonstration Area for up to half a month, resulting in a great deal of mud and pollutants that contaminated the plowing layer. Now the Xiangyang Demonstration Area has changed its irrigation water system. Huanghe Village intends to use the ponds in the hill and Ouyanghai Irrigation Canal as the source of irrigation water. Chaoyang Village intends to use the ponds in the hill in the Village for irrigation. The farmland pollution in the Quanxi Demonstration Area (Quanchang Village) was the result of the backward flow of the Leishui River. Thanks to the cleanup and governance over recent years, mud, pollutants and introduced organisms caused by major flooding in the past have been almost cleared away and will not cause any new pollution. (9) Lengshuitan District Through on-site reconnaissance, public consultation and data collection and analysis, the agricultural land pollution in the selected demonstration area of Lengshuitan District belongs to a historical pollution source, mainly brought in by sediment. There once was a 124 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report State-owned coal mine – Hongqi Coal Mine in the upper reach of the Xianghuaba Village Demonstration Area (which was closed in 2000, with residues cleaned up and there is no residue left on site). There once was a State-owned coal mine – Lingling Coal Mine in the upper reach of the Shixijiang Demonstration Area (which was closed in 2012, with residues cleaned up and there is no residue left on site). There were small-size coal mine operations in the upper reach of the Niujiaoba Demonstration Area, which were all closed in 2012. As required by the government, the closed mines cleaned up the residues and there is no residue left on site. And it is almost impossible to cause any new heavy metal pollution to the farmlands in the lower reach. (10) Linwu County Through on-site reconnaissance, public consultation and data collection and analysis, the current agricultural land pollution in Linwu County Demonstration Area belongs to a historical pollution source, mainly brought in by sediment. Site survey shows that these once-existing sources of pollution were all stopped and no new heavy metal pollution will be caused to the farmlands in the Demonstration Area. (11) Qiyang County Through on-site reconnaissance, public consultation and data collection and analysis, agricultural land pollution in the selected demonstration area of Qiyang County belongs to historical pollution source, mainly brought in by sediment. The Xiaojia Demonstration Area uses Dajiangbian Reservoir as the source of irrigation. There once were iron and manganese ore mines in Dajiang Forest Farm east of the Dajiangbian Reservoir (which were in operation in the 1990s at a capacity of 5,000 to 10,000 tons per year. It was closed at the end of the 1990s. Site survey shows that slags of the iron and manganese ore mines have been cleaned up). After on-site investigations, all these historical pollution sources had been shut down and the slag left behind has been cleaned up during the shutdown. There is no tailings reservoir, no waste residue piled up, and there is no problem left over from mining and mineral processing. Basically, no new heavy metal pollution will be caused to the downstream agricultural land. 125 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 5.2.2 Mitigation Measures (1) Regular water quality monitoring of irrigation water shall be conducted to master changes in irrigation water quality, and ensure that the water quality of agricultural land irrigation water in the demonstration area meets the standards. Once the water quality exceeds the standards, emergency treatment measures shall be taken. Clean and up-to-standard irrigation water sources shall be used, and irrigation can be carried out by water diversion from reservoirs with up-stream water quality up to the standards. (2) Renovation of irrigation drains to meet the water quality and quantity requirements of agricultural land irrigation in the demonstration area. (3) The newly added demonstration areas in the project counties including Yongshun County, Cili County, Hengnan County, Lengshuitan District, etc. intend to build settling ponds. The sedimentation basin shall be managed by special personnel arranged by PMO, and the sediment shall be monitored and cleaned regularly every year. Bottom sediments settled are generally solid wastes. When the heavy metal content in the sediments exceeds the control value in the ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618-2018), they will be transported by special vehicles to the landfill to avoid environmental pollution See Picture 5-1 for the typical front sedimentation basin. 126 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Picture 5-1 Typical Front Sedimentation Basin 5.3 Analysis on Impacts of Agricultural Activities and Mitigation Measures Among the agricultural activities in project counties, the environmental impacts include flooding irrigation, lime sprinkling (PH value adjusted by soil acidification), organic fertilizer application, soil passivator application, etc. Impacts on specific points include: straw removal from fields and management and control of over-standard rice. All agricultural activities in project counties are carried out on agricultural land and do not involve land acquisition, demolition or ethnic minorities. 127 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 5.3.1Analysis of Common Environmental Impacts of Agricultural Activities 5.3.1.1 Impact Analysis of Waterflooding Irrigation During the implementation of the project, waterflooding irrigation during rice filling and heading can reduce the absorption of heavy metals of rice. The irrigation water source in project counties is sufficient. Although waterflooding irrigation temporarily increased irrigation water during rice filling and heading, it had little influence on regional agricultural irrigation compared with sufficient irrigation water source in the region. The impact of flooded irrigation on the environment of this project is positive. 5.3.1.2 Impact Analysis of Lime Application Lime dosage is generally selected scientifically based on soil PH and soil texture. See Table 5-2 for agricultural lime dosage standards during the implementation of the project. Table 5-2 Agricultural Lime Dosage Standard (Unit: kg / mu) Dosage (kg / mu) Soil texture pH value The first year The second year 3rd year ＜4.5 400 400 200 4.5-5.5 300 300 150 Clay 5.5-6.5 200 200 100 6.5-7.5 100 100 100 ＞7.5 0 0 0 ＜4.5 350 350 175 4.5-5.5 250 250 125 Loam 5.5-6.5 150 150 75 6.5-7.5 100 100 50 ＞7.5 0 0 0 ＜4.5 300 300 150 4.5-5.5 200 200 100 Sandy soil 5.5-6.5 100 100 50 6.5-7.5 100 100 50 ＞7.5 0 0 0 128 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report After lime is applied, the concentration of heavy metal ions in irrigation water will be reduced, and the pH value will still meet the requirements of reclaimed water in Standards for Quality Standards for Farmland Irrigation Water (GB 5084-2005). The lime applied shall meet the following standards: quicklime (CaO content > 70 %): dolomite (CaO + MgO content > 45 %): limestone (CaCO3 content > 45 %) is a composite product with a ratio of 1: 3: 6. the proportion of quicklime is small, which can effectively prevent burns on crops and personnel during the application. After applying lime composite material, when the soil PH reaches 6.5 during crop harvest in this season, it needs to stop applying for one year. The soil in the Demonstration Area is weakly acidic with varied degree of acidification, so the applying of lime can decrease the soil acidity and increase microbial activity. Lime is an excellent material for neutralizing soil acidity, which can promote the precipitation of Cd and Pb in soil, inhibit the activity of heavy metals in soil, and reduce the Cd content in rice. After lime is applied, the PH value of the soil can be improved, which is also beneficial to the activities of microorganisms (microorganisms like the near-neutral soil environment). Dry powder lime is applied to agricultural land through the combination of lime spreader and manual spreading. Lime dust pollution will inevitably occur to local ambient air during the spreading process. The affected area is small and the influence time is short, which mainly affects lime spreader and has little influence on surrounding residents. When applying quicklime, the lime spreader must do a good job of protection and be required to wear protective clothing and masks to ensure safety. 5.3.1.3 Impact Analysis of Soil Remediation Agent Use The passivation and restoration agents applied are all agricultural agents registered by the national agricultural department and allowed to be applied to agricultural land, which can ensure that no new heavy metal pollution is brought in. At present, the passivation materials used in the remediation of heavy metal pollution in agricultural land soils at home and abroad mainly include: (1) clay minerals; 129 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (3) phosphorus-containing materials; (4) silicon calcium material; (5) metal oxides, such as iron oxide, ferrous sulfate, ferric sulfate, goethite, manganese oxide, potassium manganese ore, etc. (6) organic materials; (7) industrial wastes, etc. In the actual use of agricultural land, industrial waste should be avoided as much as possible as a passivating and repairing agent, so as not to bring new secondary pollution to agricultural land soil or destroy soil structure, physical and chemical properties and environmental quality, thus bringing unpredictable adverse effects on the long-term environmental quality of agricultural land. Judging from the current use effect, the effective state reduction rate of heavy metals such as Cd and Pb can reach 10 % 30 % after passivation and restoration of agricultural land soil, and the content reduction rate of Cd and Pb in crops (rice and vegetable aboveground) can reach 30 % 70 %. Combined with agricultural control measures, the restoration efficiency can reach 90 % at the highest, and the stability of passivation and restoration of heavy metals such as Cd and Pb in general soil can reach more than 3 years. Moreover, in many cases, with the extension of restoration time, the effect of passivation and restoration of heavy metals in soil is obviously enhanced. The organic passivator is helpful to restore the soil micro-ecological environment system and reduce the biological availability of toxic metals in the soil, thus reducing the toxicity to crops. In the remediation of heavy metal pollution in agricultural land soil, special attention should be paid to the negative effects that a large amount of passivating agent may have on soil environmental quality. In particular, after the use of the passivating agent, it is necessary to strengthen the comprehensive monitoring and evaluation of the stability of the passivating agent itself, the long-term stability of the passivated / stabilized heavy metals, the long-term effects of the passivating agent on soil texture, physical and chemical properties, and environmental quality, as well as the effects of the passivating remediation on crop growth, yield, and quality, etc. 5.3.1.4 Effect Analysis of Organic Fertilizer Application Organic fertilizer is rich in organic substances and nutrients needed for crop growth, 130 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report which can not only provide nutrients needed for crop growth and improve soil, but also improve crop quality, increase crop yield, promote high and stable yield of crops, maintain soil fertility, and at the same time improve fertilizer utilization rate and reduce production cost. Making full and reasonable use of organic fertilizer can increase crop yield, increase soil fertility, improve agricultural product quality, and improve the availability of soil nutrients. There are many raw materials for organic fertilizer production, which can be divided into the following categories: ① agricultural wastes, such as straw, soybean meal, cotton meal, etc. ② livestock and poultry manure, such as chicken manure, cattle, sheep, horse manure, and rabbit manure; ③ industrial wastes such as distiller’s grain, vinegar residue, cassava residue, sugar residue, furfural residue, etc. ④ domestic waste, such as kitchen waste, etc. ⑤ municipal sludge, such as river silt, sewer silt, etc. There are many sources of organic fertilizer raw materials, while heavy metal-rich straw, livestock manure containing heavy metal feed, municipal sludge, etc. may bring heavy metal elements into organic fertilizer. Once organic fertilizer with excessive heavy metal content is applied to agricultural land, it may lead to an increase in the content of heavy metal elements in the soil, resulting in secondary pollution. Therefore, the heavy metal content of the organic fertilizer applied in the Demonstration Area must be lower than the standard of Organic Fertilizer (NY 525 2012). If livestock manure is used as the organic fertilizer, the heavy metal content of the feed used to feed livestock must meet the requirements of Hygienic Standard for Feeds (GB 13078 2001). In view of livestock excrement produced by surrounding farmers’ farming industry, the project office needs to strengthen supervision. Livestock excrement that does not have detection or exceed the standard cannot enter agricultural land in order to prevent the introduction of new heavy metal pollution. 5.3.1.5 Analysis of Fertilizer Application Impact The application of chemical fertilizer has a great influence on the heavy metals in soil, especially Cd, while the application of phosphate fertilizer has the greatest 131 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report contribution to Cd heavy metals. Relevant research shows that phosphate fertilizer application is the main way to import Cd into paddy fields without considering the effects of rainfall, dust, irrigation, pesticides and other Cd inputs into paddy fields, as well as surface runoff, underground runoff and other Cd outputs. Although single application of high Cd phosphate fertilizer can control the Cd content in rice grains not exceeding the standard in a short period of time, it increases the risk of Cd pollution in soil. High Cd phosphate fertilizer must be used in combination with lime and other modifiers in rice production. Therefore, low-cadmium fertilizer products should be selected to reduce the risk of cadmium pollution of fertilizer to paddy soil, and phosphate fertilizer should also be selected to ensure the soil environment and food safety when the compound fertilizer is used simultaneously. 5.3.1.6 Impact Analysis of Pesticide Application According to the data provided by the agriculture bureaus of 12 project counties, the frequency of agricultural pesticides used in each project county is 2 to 3 times / quarter. In 2015, 3,100 tons of chemical pesticides were used in the project counties, 60 tons of biological pesticides were used, and the proportion of biological pesticides was 1.9 %. After on-site investigation and verification by the agriculture bureau of the project county, the pesticides applied in the agricultural land of the project county at present are all qualified pesticides that meet the national standards and basically do not bring heavy metal pollution to the agricultural land. During the implementation of the project, the agricultural department of the project county will guide and supervise the selection and spraying of pesticides so that the Demonstration Area can use pesticides scientifically and reasonably. The project office commissioned Hunan Plant Protection Station to prepare a “management plan for the prevention and control of diseases, insect pests and weeds” based on the plant protection policy of “prevention first and comprehensive prevention”. The plan insists on and implements the concepts of “public plant protection” and “green 132 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report plant protection” and summarizes and puts forward the prevention and control methods for common diseases and insect pests of major crops such as rice, corn, potato, citrus, grape, vegetables, cotton, rape, tea and the like related to the project. Under the premise of protecting the ecological environment, the control plan emphasizes the natural control function, promotes the use of agricultural, physical and biological control methods to control diseases and insect pests, coordinates the use of appropriate chemical control technical measures, reduces the dependency on agricultural chemicals, controls the disease and insect pests below the allowable level of economic harm, and obtains the best economic, social and ecological benefits. (1). Main method recommended by disease and pest control plan ① Physical prevention method a. The phototaxis of pests is used to trap and kill pests. b. Heat energy, such as hot water is used to soak seeds to kill latent pathogenic bacteria in seeds. c. Cut off and burn plant diseases and insect pests. d. Eliminate pests and diseases in orange orchard, and reduce overwintering base. ② Biological control method a. Protect and utilize natural enemies. b. Use biological agents and products. c. Create a suitable environment for natural enemies and increase the number of natural enemies. ③ Chemical Control Method a. The list of pollution-free pesticides recommended for this project is shown in Table 5-5 for the use of high efficiency, low-toxicity and low-residue pesticides. b. Promote the application of pesticide reduction and synergistic spray additives to effectively reduce pesticide consumption. c. For insect source areas and occurrence center areas where insect population density is relatively high, high-efficiency and low-dose pesticide control shall be used in 133 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report a timely manner in the young stage of pests to ensure that the best effect can be achieved in each application of pesticide. It is strictly prohibited to use pesticides that kill natural enemies in the late stage of pest rampant. d. Ensure safety interval of pesticide application. e. Safe pesticide application equipment and methods are adopted to improve pesticide utilization efficiency and pest control effect. f. Strengthen publicity, education and training on the safe and reasonable use of pesticides, strictly abide by the regulations on the use of pesticides, pay attention to safety, including wearing protective clothing correctly and mastering the common sense of first aid in pesticide poisoning. g. Do a good job in the safe storage of agricultural chemicals (e.g. stay away from children and food, etc.). h. Properly dispose pesticide waste and packaging materials, and do not wash pesticide application equipment in natural waters. (2) List of Recommended Pollution-Free Pesticides Table 5-3 List of Recommended Pollution-Free Pesticides Tox Safety interval Plant Control object Recommended species icit (day) y Propiconazole (10 % or 20 % suspending agent) U 21 Isoprothiolane (40 %, and wettable powder) Ⅲ 28 Azoxystrobin (over 25%, emulsifiable concentrate) U 21 Rice blast Bacillus Subtilis (above 100 billion PIB / g, wettable U 20 powder) Trifloxystrobin (above 75 %, water dispersible granules) U 21 Kasugamycin+Zinc thiazole U 21 Hexaconazole (10 %, suspending agent and water U 28 Rice dispersible granule) Tebuconazole (43%, suspending agent) U 21 Thifluzamide (over 24%, suspending agent) U 14 Banded Azoxystrobin (over 25%, emulsifiable concentrate) U 21 sclerotial Epoxiconazole (over 12.5%, suspending agent) U 21 blight Jinggangmycin (above 20 %, water-soluble powder) U 14 Jinggang+Wax Bud Bacteria (over 12.5%, suspending U 14 agent) Phenazino-1-Carboxylic Acid (over 1%, suspending U 14 134 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report agent) Difenoconazole+Propiconazole (30 %, water dispersible Ⅲ 28 granules, emulsifiable concentrate) Trifloxystrobin (above 75 %, water dispersible granules) U 21 Epoxiconazole (over 12.5%, suspending agent) U 20 Tebuconazole (43%, suspending agent) U 60 Propiconazole (25%, emulsifiable concentrate) U 28 Difenoconazole+Propiconazole (30 %, water dispersible False smut Ⅲ 28 granules, emulsifiable concentrate) Jinggang+Wax Bud Bacteria (over 12.5%, suspending U 14 agent) Trifloxystrobin (above 75 %, water dispersible granules) U 21 Pymetrozine ( above 25 %, suspending agent, wettable U 14 powder and water dispersible granules) Buprofezin (25 %, suspending agent and wettable U 14 powder) Thiamethoxam (25%, water dispersible granules) U 28 Rice Imidacloprid (10 %, 20 %, wettable powder, water planthopper dispersible granules, suspending agent, microemulsion, Ⅲ 21 seed dressing agent) Chromafenozide (10%, suspending agent) U 20 Dinotefuran (above 25%, wettable powder) U 21 Pymetrozine·Nitenpyram (over 80%, water dispersible U 30 granules) Chlorantraniliprole (over 20%, suspending agent) U 7 Flubenzamides (over 20%, suspending agent) U 14 Tetrachloroacetamide (over 10%, suspending agent) U 30 Indoxacarb (over 15%, emulsifiable concentrate) U 28 Spinetoram+Methoxyfenozide (34%, suspending agent) U 21 Rice leaf Bacillus Thuringiensis (above 8000 iu / mg, wettable folder Ⅲ 14 powder) Emamectin Benzoate (2 %, water dispersible granules and U 21 microemulsion) Spinetoram+Methoxyfenozide (34%, suspending agent) U 21 Metaflumizone (22%, suspending agent) U 21 Chlorantraniliprole (over 20%, suspending agent) U 7 Chilo Flubenzamides (over 20%, suspending agent) U 14 suppressalis Spinetoram+Methoxyfenozide (34%, suspending agent) U 21 Tetrachloroacetamide (over 10%, suspending agent) U 30 Pretilachlor (above 30 %, containing safety agent, U - emulsifiable concentrate and emulsion in water) Bensulfuron Methyl (over 10%, wettable powder) U - Directly-planted weed Penoxsulam (over 2.5%, oil suspending agent) U - paddy field Cyhalofop-butyl (above 10 %, emulsifiable concentrate U - and aqueous emulsion) Bensulfuron-Methyl+Pretilachlor (20%, wettable U - 135 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report powder) Oxazolamide (above 10%, emulsifiable concentrate and U - oil suspension) Bensulfuron-methyl (above 10 %, suspending agent and U - oil suspending agent) Bentazone (45%, water aqua) Ⅲ - Bispyribac-sodium (above 10 %, suspending agent and U - oil suspending agent) Butachlor (above 50 % emulsifiable concentrate, Ⅲ - suspending agent and emulsion in water) Pretilachlor ( over 50 % emulsifiable concentrate, U - suspending agent and emulsion in water) Throw-planting Mefenacet (more than 50% emulsifiable concentrate, U - (mechanized suspending agent and emulsion in water) weed transplanting) Bensulfuron Methyl (over 10%, wettable powder) U - paddy field Pyrazosulfuron-Ethyl (over 10%, wettable powder) U - Cyhalofop-butyl (above 10 %, emulsifiable concentrate U - and aqueous emulsion) Bispyribac-sodium (above 10 %, suspending agent and U - oil suspending agent) Butachlor (above 50 % emulsifiable concentrate, Ⅲ - suspending agent and emulsion in water) Pretilachlor ( over 50 % emulsifiable concentrate, U - Transplanted suspending agent and emulsion in water) weed paddy field Bensulfuron Methyl (over 10%, wettable powder) U - Pyrazosulfuron-Ethyl (over 10%, wettable powder) U - Cyhalofop-butyl (above 10 %, emulsifiable concentrate U - and aqueous emulsion) Mancozeb (over 80%, wettable powder) U 14 Copper Calcium Sulphate (77%, wettable powder) Ⅲ 32 Thiodiazole-copper (20%, suspending agent) U 14 Scab Chlorothalonil (over 75%, wettable powder) U 21 Azoxystrobin (over 25 % emulsifiable concentrate) U 14 Difenoconazole (10%, water dispersible granules) U 28 Zinc Thiazole (over 20%, suspending agent) U 21 Thiodiazole-copper (20%, suspending agent) U 14 Cupric Hydroxide (46 %, wettable powder and water Canker Ⅲ 30 Orange dispersible granules) Resin Acid Copper Salt (20%, wettable powder) U 14 Copper Calcium Sulphate (77%, wettable powder) Ⅲ 32 Propineb (over 70%, wettable powder) U 21 Thiophanate-Methyl (over 70%, wettable powder) U 21 Bromothalonil (25%, emulsifiable concentrate) Ⅲ 21 Anthracnose Prochloraz (20%, emulsifiable concentrateand emulsion U 14 in water) Azoxystrobin (over 25 % emulsifiable concentrate) U 14 Chlorothalonil (over 75%, wettable powder) U 21 136 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Captan (over 80%, water dispersible granules) U 21 Resinosis Prochloraz (20%, emulsifiable concentrateand emulsion (sand paper U 14 in water) russet) Mancozeb (over 80%, wettable powder) U 14 Big (small) 0.1% Abamectin Bait concentrate U 14 fruit fly Spirodiclofe (24%, suspending agent) U 30 Propargite (over 73%, emulsifiable concentrate) Ⅲ 30 Abamectin+Propargite, E.C.( (40%, emulsifiable Red spider Ⅲ 30 concentrate) Abamectin+Pyridaben (10.5%, Micro emulsifiable Ⅲ 21 concentrate and emulsifiable concentrate ) Fenpyroximate (5%, emulsifiable concentrate) U 15 Phyllocoptrut Spirodiclofe (24%, suspending agent) U 30 a oleivora Abamectin+Propargite, E.C.( (40%, emulsifiable Ⅲ 30 concentrate) Buprofezin (25%, wettable powder) U 35 Scale bug Buprofezin (18%, suspending agent) U 35 Machine oil (94%, emulsifiable concentrate) Ⅲ 30 Chlorbenzuron (over 25%, suspending agent) U 21 Leaf miner Diflubenzuron (25%, wettable powder) U 28 Chlorfluazuron (over 5%, emulsifiable concentrate) U 21 Glyphosate (above 30%, water aqua, soluble powder U - and soluble granule) Orange orchard weed Flumioxazin (over 20%, water aqua) U - Flumioxazin (over 50%, wettable powder) U - Carbendazim (over 80%, wettable powder) U 41 Dimethachlon (40%, wettable powder) U 25 Oilseed rape Stalk break Prochloraz (20%, emulsifiable concentrateand emulsion U 21 in water) Improve crop Modifier 0.136% VitaCat U - resistance Diseases 63% Polyol-Type Nonionic Surfactant U - Auxiliariy insect pests Ethoxy ModifiedTtrisiloxane U - and weeds Monosilicic Acid U - (3) Monitoring and Training Plan for Diseases and Insect Pests Monitoring is carried out by the municipal and district (county) level agricultural technology extension service centers, project offices and owners together in the villages and towns of the project implementation area. Once diseases and insect pests are discovered, they must be reported and handled in a timely manner. The personnel dispatched by the World Bank should provide help to establish an appropriate monitoring system and sampling procedures as early as possible, and provide training in the 137 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report implementation and analysis of the monitoring system. For the specific pest management information of this project, please refer to the Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan for Pest Management Plan. 5.3.1.7 Analysis on the Impact of Agricultural Materials and Wastes During the implementation of the project, a small amount of agricultural materials and wastes such as agricultural films and packaging materials for agricultural inputs will be produced in the Demonstration Area. If they are discarded and left in the soil at will, the decomposition of soil humus will be affected, and the ventilation and water permeability of the soil will also be affected, resulting in the destruction of soil structure, the low content of nutrient elements and the reduction of the ability to maintain water and fertilizer. Therefore, it is necessary to remove and recycle agricultural films and packaging materials for agricultural inputs in time to prevent pollution to the environment of product origins. This project intends to set up a collection pond for agricultural packaging waste in each Demonstration Area, requiring farmers to collect and temporarily store the used waste agricultural films, agricultural chemical packaging materials, etc. in the collection pond. At the same time, it will connect with the recycle bin of agricultural materials packaging materials in each project county. The project office will regularly transport the agricultural materials packaging wastes from the collection point to the recycle bin of agricultural materials packaging materials in the project county. The recycle bin of agricultural materials packaging materials in the project county will entrust a qualified unit to handle them in a unified way. Through the above measures, the agricultural material waste of this project can be properly disposed with little impact on the environment. 5.3.2 Mitigation Measures for Common Impacts of Agricultural Activities Please refer to the following annex for details of mitigation measures for common 138 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report environmental impacts of agricultural activities: Annex 3 Environmental Protection Procedure for Agricultural Activities ECOP 5.3.3 Analysis of Impact of Agricultural Activities on Specific Points and Mitigation Measures 5.3.3.1 Impact Analysis and Mitigation Measures of Straw Removal from Field When the Cd content of rice straw (straw) is more than 1.5 mg / kg, if the straw returns to the field, it will not help to reduce the Cd content in the agricultural land and affect the effect of the project implementation. As for the area with Cd content of straw above than 1.5 mg / kg in the Demonstration Area, straw removal measures were taken to remove it from agricultural land in order to curb the Cd pollution in agricultural land. This project adopts PPP mode of operation mechanism and incentive mechanism, through subsidies to farm operators or specialized harvest cooperatives, adjusts the harvest mode for straw utilization (semi feeding harvest to ensure the removal and utilization of the entire grass), and adds chopped straw bales (straw picking and bundling machines can be purchased) to realize the removal of crop straws from the field in the Demonstration Area. The straw to be removed should adopt the principle of adjusting measures to local conditions and comprehensive utilization. In view of the characteristics of mountainous areas and woodlands in the project county, the straw should be disposed and utilized by means of centralized collection and on-site return of forest cover. The project office needs to strengthen supervision to ensure the smooth progress of straw removal and proper disposal. According to the relevant research conclusions of domestic agricultural research institutions, the Cd content of contaminated straw is generally 1.5 to 10 mg / kg. Even if such rice straw is moved to forest land, it will not cause Cd pollution in forest land soil. Rice straw removed from the field in some project counties can be moved to forest land for consumption, and the impact on forest land soil is acceptable. In some project counties, this kind of rice straw is moved to orchards. According to related agricultural 139 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report research, the orchard soil will not exceed the secondary soil standard and will not cause Cd pollution in soil within 100 years. Therefore, rice straw removed from the field in some project counties can be moved to orchards for consumption, and the impact on orchard soil is acceptable. By adopting above measures, it can be ensured that the rice straw will be moved to the field in areas where the rice straw exceeds the standard, and the straw after being moved to the field will be used or properly treated, which will have little impact on the environment. 5.3.3.2 Control Scheme and Influence Analysis of Standard-exceeding Rice In order to strengthen the control of rice with Cd and other heavy metals exceeding the standard, and to ensure that the contaminated rice does not circulate freely in the field of grain circulation, the control plan for the contaminated rice has been formulated. A scheme for controlling the rice that exceeds the standard shall cover purchasing by the government for special grain reserve depots and liquor making. Residues such as distillers’ grains are all landfilled without going into the food chain. Scheme for Controlling Standard-exceeding Rice-Winery Brewing (1) Control Scope Standard-exceeding rice produced in the following demonstration areas: Yongding District, Jishou City, Yongshun County, Cili County, Huayuan County, Anhua County, Hengyang County, Hengnan County, Lengshuitan City, Linwu County and Qiyang County. (2) Cooperative Participating Unit County agriculture bureau, county grain storage warehouse, towns and townships in each Demonstration Area, village (residential committees), professional cooperative of rice planting, farmers in the Demonstration Area, Xiangquan Winery, Jishou Liquor Co., Ltd, Wanping Luohu Winery, Zhangjiajie Shengdi Liquor Co., Ltd, Huayuan Malichang Winery, Anhua Qinglong Liquor Co., Ltd, Hunan Dinggu Liquor Co., Ltd, Hunan Lingjiu Liquor Co., Ltd, Lengshuitan Yunxi Liquor Co., Ltd, Linwu Guyan Winery, Qiyang Qiongniang Liquor Company and other units are the cooperation units for solving the 140 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report contaminated rice caused by Cd pollution. (3) Control Mode and Operation Steps ① Control Mode The county agriculture bureau on behalf of the government has signed contaminated rice purchase agreements with county grain storage warehouses, rice planting cooperatives and farmers in the Demonstration Area respectively. It has also signed contaminated rice disposal agreements with Xiangquan Winery, Jishou Liquor Co., Ltd, Wanping Luohu Winery, Zhangjiajie Shengdi Liquor Co., Ltd, Huayuan Malichang Winery, Anhua Qinglong Liquor Co., Ltd, Hunan Dinggu Liquor Co., Ltd, Hunan Lingjiu Liquor Co., Ltd, Lengshuitan Yunxi Liquor Co., Ltd, Linwu Guyan Winery, Qiyang Qiongniang Liquor Company. The villages, towns and villages (or cooperatives) of each Demonstration Area will assist in the process of purchasing rice that exceeds the standard to ensure that all rice that exceeds the standard will be purchased without omission. ② Operating Procedure A. Sampling and Inspection According to the features of the project counties as mountainous areas, it is advisable to select one rice sample for every 30-50 Chinese mu and about 120-150 rice samples are selected in each project county. It is preferable to select samples in the yellow-ripe stage after rice ripens. Samples will be tested by a relevant testing agency after they are threshed and dried. B. Confirmation of contaminated rice According to the test results, rice with Cd content above or equal to 0.2 mg / kg was confirmed as contaminated rice according to the relevant national standards. C. Purchase and Temporary Storage of contaminated rice County agriculture signed an agreement with xx grain storage warehouse on behalf of the government to purchase contaminated rice. The purchase price shall be based on the corresponding purchase price stipulated by the state in the year. The purchased contaminated rice will be stored separately and temporarily in a special warehouse in xx grain reserve warehouse. D. Sales and Processing of contaminated rice In order to reduce the losses caused by the purchase of rice with over-standard Cd 141 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report content, such rice can be sold to the Tujia Brewery for direct processing into edible liquor. The county agriculture bureau, on behalf of the project county government, signed the Rice with Over-Standard Cd Content Treatment Agreement with the Tujia Brewery. The brewery can process the rice with Cd content exceeding standard into edible liquor separately. The selling price can be appropriately subsidized according to the quantity of rice accepted by the brewery and the price of rice purchased with reference to the liquor produced by the enterprise. At the same time, the winery used rice with over-standard Cd content to make wine and tested Cd and other heavy metals in white wine. Distiller’s grains are disposed of in landfill. The project offices of each project county shall provide appropriate subsidies in the form of technical assistance for the relevant testing costs and research costs of distiller’s grains used for products and their accessories and for the treatment methods of distiller’s grains. 2. Environmental Impact of Contaminated Rice Control For rice with Cd content above 0.2 mg / kg, Yongding District, Jishou City, Yongshun County, Cili County, Huayuan County, Zhongfang County, Anhua County, Hengyang County, Hengnan County, Lengshuitan City, Linwu County, Qiyang County choose nearby Xiangquan Winery, Jishou Liquor Co., Ltd, Yongshun Xiongge Liquor Co., Ltd, Zhangjiajie Shengdi Liquor Co., Ltd, Huayuan Malichang Winery, Anhua Qinglong Liquor Co., Ltd, Hunan Dinggu Liquor Co., Ltd, Hunan Lingjiu Liquor Co., Ltd, Lengshuitan Yunxi Liquor Co., Ltd, Linwu Guyan Winery, Qiyang Qiongniang Liquor Company. Special enterprises will purchase such rice as raw materials for liquor making. Heavy metals do not have volatility during liquor making and will not enter liquor. Cd in rice is mainly concentrated in by-product distiller’s grains. In order to ensure that they do not enter food chain, all distiller’s grains will enter county refuse landfills. Currently, the over-standard multiple of standard-exceeding rice is relatively low. According to foreign standards, it is not over-standard and the content of distiller’s grains is also relatively low. After the above measures are taken, the impact on the environment is acceptable. 142 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report According to environmental impact assessments, it is recommended that such distiller’s grains must be transported to various county refuse landfills for sanitary landfill. (1) Yongding District Yongding District landfill site is located in Xixiping, Yongding District. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. It covers an area of 3.957 million m 3, with the refuse disposal scale being 250 tons/day, and its service life is 30 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Baojing County. (2) Jishou City Jishou City landfill site is located in Baxifu, YJishou City. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. It covers an area of 2 million m 3, with the refuse disposal scale being 300 tons/day, and its service life is 30 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Jishou City. (3) Yongshun County Yongshun County landfill site is located in Linxi Town, Yongshun County. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. It covers an area of 2 million m3, with the refuse disposal scale being 200 tons/day, and its service life is 30 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Yongshun County. (4) Cili County 143 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Cili County landfill site is located in Lingyang Town of Cili County. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. It covers an area of 2 million m 3, with the refuse disposal scale being 200 tons/day, and its service life is 30 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Cili County. (5) Huayuan County Refuse landfill in Huayuan County is located in Huayuan Town, Huayuan County. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. The total storage capacity of the waste treatment plant is 0.952 million cubic meters; the scale of waste treatment is 70 tons / day, and the scale of landfill leachate treatment is 50 tons/day. Its service life is 20 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Huayuan County. (6) Anhua County The waste landfill site of Anhua County is located in Dongping Town of Anhua County. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. Its total storage capacity is 3.15 million m3 and the refuse disposal scale is 220 tons/day, and its service life is 30 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Anhua County. (7) Hengyang County Hengyang Lida landfill site is located in Xidu Town, Hengyang County. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. With the refuse disposal of 300 tons 144 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report and storage capability of 1.5 million m3 The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Hengyang County. (8) Hengnan County Hengnan Maotang household refuse landfill is in Luobuchong Group, Heshi Village, Yunji Town. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. At present, with the design of daily refuse disposal of 100 tons and storage capability of 1.5 million m3.The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the Maotang domestic waste landfill site in Hengnan County. (9) Lengshuitan District Lengshuitan District Tantang refuse landfill is located in Lanjiaoshan Town, Lengshuitan District. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. The total storage capacity of it is 10.75 million m3 and the refuse disposal scale is 860 tons/day, and its service life is 30 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Lengshuitan District. (10) Linwu County Landfill in Linwu County is located in Majia Village, Wushui Town of east Linwu County. It is a circular quasi-aerobic sanitary landfill and adopts horizontal anti-seepage technology. The total storage capacity of the waste treatment plant is 1.85 million cubic meters; the scale of domestic waste treatment is 160 tons / day and meets the construction specifications and requirements of the landfill site. It can be used for about 23 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the landfill site in Linwu County. 145 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (11) Qiyang County Refuse landfill site in Qiyang County is located in Maozhu Town of southwest suburb of Qiyang County. The landfill site has undergone anti-corrosion and anti-seepage treatment to meet the construction specifications and requirements of the landfill site. The daily average landfill is 360 tons, the planned total floor area is 307.5 mu, the designed total storage capacity is 453.5 m3, and the service life is 30 years. The amount of distiller’s grain produced by standard-exceeding rice is very small in the project, and the content of other heavy metals is also low, which has little influence on the Urban refuse landfill site in Qiyang County. Through the above measures, the contaminated rice in the demonstration areas can obtain effective control and utility and their by-product can be settled properly to cause no harm to the environment. 146 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 6 Analysis of Alternative Plans 6.1 The Comparison and Selection with and without the Project The comparative analysis of with or without the project is mainly from environmental profit and loss and social economy and is shown in Table 6-1. Table 6-1 Comparison and Selection List of with Project and without Project Classification Implement the project plan Without plan of this project ⚫ The construction of the project conforms to the 13th Five-Year Plan outline for the national economic and social development of Hunan Province. ⚫ Reduce heavy metal content in agricultural ⚫ Maintain the current products and protect the health of farmers and environmental situation and do not consumers. Main produce environmental impact caused ⚫ Is conducive to the sale of agricultural advantages by agricultural activities such as products and safeguard the vital interests of project construction and lime farmers. application. ⚫ It is of great significance to ensure the safety of national agricultural products, maintain social stability, improve the ecological environment and promote the sustainable development of regional agricultural economy. ⚫ Long-term consumption of ⚫ Dust produced by engineering agricultural products with excessive construction, waste soil (slag) after foundation heavy metals is harmful to human excavation and backfill have short-term adverse health and may cause skin, nervous effects on the environment, but such effects can system, kidney and blood system be avoided and reduced by taking diseases. corresponding environmental protection ⚫ This poses a serious challenge to measures, and the impact during the the safety of food production and construction period is relatively small and only poses a serious threat to the temporary. sustainable development of Main ⚫ Application of lime may cause changes in agriculture. disadvantages soil structure and physical and chemical ⚫ Grain contaminated by heavy properties, and improper application of lime metals is difficult to sell, which affects may affect the health of operators. However, farmers’ economic income. these effects can be mitigated by determining ⚫ There are many migrant workers the application amount of lime according to in the Demonstration Area. Poor different textures and PH values, choosing households are trapped in a poverty agricultural special lime, and applying it by cycle dominated by traditional professionals or lime planters. agricultural management and planting ⚫ Farmers’ demands for new farming skills patterns. There is a lack of useful may be uncomfortable in the short term. experience in controlling heavy metal pollution in agricultural land. Comprehensive Project construction plan is better than without plan analysis Agricultural land in Hunan Province has been polluted by heavy metals to varying degrees. The quality of soil environment and its safety performance are declining day by day, which directly threatens the quality and safety of agricultural products and 147 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report endangers the health of the masses. Even if there is no project plan, and there is no environmental impact caused by small-scale civil construction activities and agricultural activities such as lime application, heavy metal pollution in agricultural products in Hunan Province will still exist and will continue. The problem of excessive heavy metals in agricultural products consumed by ordinary people will still be harmful to the health of ordinary people. The sales volume of heavy metal-polluted agricultural products will still be affected, affecting the vital interests of the vast majority of farmers. Although the project construction plan will bring about certain environmental impact, the impact can be avoided and reduced by adopting corresponding environmental protection measures. Moreover, the impact during the construction period is relatively small and temporary. The implementation of the project can improve food security and the quality of life of the people. It is a project beneficial to the people’s livelihood and brings long-term social and environmental benefits. Therefore, the project construction plan is obviously superior to no plan, and the project construction is very necessary. 6.2 Comparison and Selection of Demonstration Areas 6.2.1 Selection Principle of Demonstration Areas 1. Principle of centralization and contiguity The Demonstration Area should be centralized and contiguous with unified planning and reasonable layout. The whole village (district) should be promoted together. The implementation of the project has good scale benefits, and the major grain producing areas should be given appropriate priority. 2. Pollution Source is Clear and Controllable The causes and sources of heavy metals and other pollutants in the arable land and soil in the Demonstration Area need to be clearly identified. The information on pollutant types and pollution levels is accurate, and the main pollution sources are controllable or cut off. 3. Principle of Regional Representativeness The main agricultural land type of the demonstration area should be paddy field, the 148 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report main pollution type heavy metal contamination, and the main heavy metal contamination Cd pollution. 4. Principle of Typicality The demonstration area should be typical, and the project implementation should have large investment benefits, impacts, and demonstration effects. 5. Principle of Sustainability It’s necessary to conduct infrastructure construction and adopt comprehensive agricultural measures in the demonstration area, so as to alleviate heavy metal contamination, control agricultural non-point source pollution, increase yield and improve efficiency, and realize sustainable agricultural, economic and social development in the demonstration area. 6、Principle of Stability The local government should lay large emphasis on the project; the personnel allocation should be reasonable; the project units (farmers or enterprises) should be active. 6.2.2 Selection of Project Towns and Townships The specific project implementation area is determined, through comprehensive consideration of the area of the Demonstration Area as well as the concentrated contiguous area, the type of main agricultural land, whether it belongs to the main grain producing area, the type of heavy metal pollution, whether the pollution source is clear and controllable, the importance of the local government and the intensity of farmers’ willingness to participate in the selection of the Demonstration Area. In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through evaluation and screening, a total of 47 project villages and towns were selected from 12 project counties. The comparison 149 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report results are summarized in Table 6-2, and the screening table of specific project villages and towns is shown in Attachment 7. Table 6-2 Summary of Comparison and Selection Results of Villages and Towns in the Project Serial Project county Project township and town No. Yongding Maoyanhe Town, Luoshui Township, Jiaoziya Town, Yinjiaxi Town, 1 District Xinqiao Town, Wangjiaping Town, Yuanguping town 2 Jishou City Aizhai Town, Qianzhou Sub-district Yongshun 3 Shaba Town, Xiqi Township County Xiangshi Town, Sanhekou Town, Yangliupu Township, Dongyueguan 4 Cili County Town, Tongjinpu Town Huayuan 5 Biancheng Town County 6 Anhua County Le’an Town, Dafu Town and Qingtang town Hengyang 7 Xidu Town, Sanhu town County Hengnan 8 Xiangyang Community, Quanxi Town County Lengshuitan 9 Xianghuaba Town, Niujiaoba Town, Shixijiang Town District 10 Linwu County Wushui Town, Shuidong Town, Nanqiang Town 11 Qiyang County Xiaojia Town 6.3 Project Village Area Selection According to the feasibility study report of the project, after field survey of the project villages and towns, based on the diversity of PH value, pollution type and degree, organic matter content and other factors, considering the investment limit and the degree of enthusiasm of participants, the polluted agricultural land of representative villages was selected as the implementation Demonstration Area in the project villages and towns to demonstrate and explore the comprehensive management of the polluted agricultural land in the whole region. Through evaluation and selection, demonstration areas were selected. The comparison results are summarized in Table 6-3, and the selection table of specific Demonstration Areas is shown in Annex 8. Table 6-3 Summary of Comparison and Selection Results of Demonstration Areas 150 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Serial Project county Demonstration Area No. Yongding Yuanguping Demonstration Area, Yinjiaxi Demonstration Area, 1 District Yanghuping Demonstration Area, Wentang Demonstration Area 2 Jishou City Qianzhou Demonstration Area, Aizhai Demonstration Area Yongshun 3 Shaba Demonstration Area and Xiqi Demonstration Area County Xiangshi Town Demonstration Area, Sanhekou Town Demonstration 4 Cili County Area, Yangliupu Township Demonstration Area, Dongyueguan Town Demonstration Area, Tongjinpu Town Demonstration Area 5 Huayuan County Biancheng Town Demonstration Area Le’an Town Demonstration Area, Dafu Town Demonstration Area, 6 Anhua County Qingtang Town Demonstration Area Hengyang Yanglin Demonstration Area of Fuxing of Sanhu Town, Qingli 7 County Demonstration Area of Xidu Town Xiangyang Demonstration Area (including Chaoyang Village and 8 Hengnan County Huanghe Village), Quanxi Demonstration Area (Quanchang Village) Xianghuaba Demonstration Area (including Datangqian Village, Lengshuitan Xiangjiang Village and Chunguang Village), Shixijiang (including Zhuxi 9 District Village Demonstration Area), Niujiaoba Demonstration Area (Including Xiangshanjie and Yangsi Temple) Wushui Demonstration Area, Shuidong Demonstration Area, Nanqiang 10 Linwu County Demonstration Area 11 Qiyang County Xiaojia Demonstration Area 151 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 7 Process of Public Participation 7.1 Public Participation of Environmental Impact Assessment 7.1.1 Purpose of Public Participation and Identification of Stakeholders 7.1.1.1 Purpose of Public Participation Public participation and information disclosure form a two-way communication between Project owner and the public through environmental impact assessment work. They are an important constituent part of environmental impact assessment of the construction Project and they are crucial for improvement of decision-making. The purposes of public participation and information disclosure include: Release Project related information to Project region and people paying attention to construction of this Project; enable the public to get to know the main conditions, construction and operation characteristics of the project as well as major environmental problems related to the project; help assessment personnel find the problems and confirm that all major environmental problems resulting from the project are already analyzed and evaluated in the Environmental Impact Report; confirm feasibility of environmental protection measures as well as carry out and implement optimized measure schemes. Public consulting has emphasized on the importance of connection and communication between parties involved in the project and the public. It can directly reflect the public opinions and enable the decision-making department to timely spot potential problems and timely modify and perfect design scheme so as to fundamentally solve the problems complained by the public, gradually make Project planning, design, environmental monitoring and management more complete and reasonable and strive to obtain optimized unification in terms of environmental benefits, social benefits and economic benefits. 7.1.1.2 Identification of Stakeholders According to assistance objectives of World Bank, all directly or indirectly benefited or damaged individuals and organizations within the project affected regions are all stakeholders of the project. According to feasibility study report, agricultural land pollution in Demonstration areas is administered by adopting measures such as agricultural improvement, land remediation and supporting of rural cooperative. The main stakeholders 152 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report involved mainly include: (1) Farmer households in demonstration areas: Farmer households in Demonstration areas are the directly benefited or damaged subjects in the project. Agricultural land heavy metal contamination administration will have an influence on land use and agricultural measures. (2) Agricultural cooperatives: Agricultural cooperatives in Demonstration areas are also directly benefited or damaged subjects in the project. Agricultural land heavy metal contamination administration will have an influence on their management and cultivation model to different extents. (3) Relevant government departments. Agricultural land pollution administration involves relevant departments such as agricultural department, environmental protection department and water conservancy department. (4) The winery disposal the contaminated rice in the demonstration area. In order to strengthen the management and control on the rice with excessive heavy metals, such as the cadmium etc., to ensure that the rice with the excessive heavy metal will not be circulated in the food fields at random, and to manage and control the rice with excessive heavy metal, county government where the project is located will purchase these rices specially to make wine for wineries, meanwhile the vinasse and other residues etc. shall be sent to the refuse landfill for treatment in the counties where the project is located, and it is forbidden to let them flow into the food chain. These enterprises are the direct benefited or damaged subjects of the project. (5) Vulnerable group. Vulnerable groups refer to social groups among residents who become vulnerable due to their social participation ability, social security, poverty, etc., lack the ability to respond to social changes, and are at a disadvantage in the society. Vulnerable groups of this project mainly include the following types: poor households enjoying a guaranteed living benefit, women, etc. In this part, appeals and expectations of farmer households, agricultural cooperatives, relevant departments of the government and vulnerable groups in demonstration areas for the project are intensively analyzed. 153 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 7.1.2 Negotiation Methods and Contents According to the requirements of Law of the People’s Republic of China on Environmental Impact Assessment, Interim Measures for Public Participation of Environmental Impact Assessment issued by Ministry of Environmental Protection of the state as well as business policy of the World Bank (OP4.01), we carry out two rounds of public negotiation and information disclosure during the process of assessment. The first round is carried out after screening and selection of environmental problems and before final determination of environmental impact assessment outline, while the second round is carried out in the stage when the first draft of Environmental Impact Report is completed. Besides, public participation and information disclosure will also be continuously carried out during Project implementation. 7.1.2.1 Negotiation Methods Methods for public participation negotiation mainly include: (1) Convening of symposiums in demonstration areas; (2) Visit some people in demonstration areas; (3) Carry out public opinion census in form of questionnaire survey; (4) NGO: Forms including convening of symposium or telephone interview are adopted. The negotiation work with the public shall be conducted in all the demonstration areas; and it is required to take the change of cropping system of the negotiation work participated by the public as the key emphasis for the demonstration area with the change of cropping system demands. 7.1.2.2 Negotiation Contents Contents of the symposium and mass visit: construction conditions of this Project as well as main contents involving environmental protection are mainly introduced to participants and participants’ ideas and suggestions on Project construction and environmental protection are heard. In order to promote the participation of vulnerable groups, the project design made guiding provisions for poor households, women and other vulnerable groups to participate in the project activities. Each community shall absorb a 154 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report certain proportion of poor farmers to take part in the project. To ensure that the voice of vulnerable groups can be reflected, the village project team shall contain representatives of women and poor households. In the process of public questionnaire survey, the opinions of local poor households and women must be solicited. 7.1.3 Public Participation Investigation 7.1.3.1 First Round of Public Investigation Activities Table 7-1 First round of public investigation activities Serial Negotiation Time Form Location Contents No. object Learn the current situation of the local Competent agricultural condition, and consult the agricultural project condition in the local area, and listen department of to the opinion on the project by the Yongding District agricultural competent department. . Relevant competent Agricultural departments of Learn the basic condition of the local Bureau of Symposium government of industrial and mining enterprises involving Yongding Yongding District the heavy metal, the water quality condition District in charge of of the local irrigation water source and the environmental current security status of the local protection, water agricultural products, and listen to the conservancy, opinions on the project by the competent 1. March security and department of the government. Yongding 2020 quality District supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local Symposium township agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local Competent agricultural condition, and consult the agricultural project condition in the local area, and listen department of to the opinion on the project by the Jishou City agricultural competent department. . Relevant Agricultural Learn the basic condition of the local 2. Jishou March competent Symposium Bureau of industrial and mining enterprises involving City 2020 departments of Jishou City the heavy metal, the water quality condition government of of the local irrigation water source and the Jishou City in current security status of the local charge of agricultural products, and listen to the environmental opinions on the project by the competent protection, water department of the government. conservancy, 155 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Serial Negotiation Time Form Location Contents No. object security and quality supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local township Symposium agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local Competent agricultural condition, and consult the agricultural project condition in the local area, and listen department of to the opinion on the project by the Yongshun County agricultural competent department. . Relevant competent Agricultural departments of Learn the basic condition of the local Bureau of Symposium government of industrial and mining enterprises involving Yongshun Yongshun County the heavy metal, the water quality condition County in charge of of the local irrigation water source and the environmental current security status of the local protection, water agricultural products, and listen to the conservancy, opinions on the project by the competent 3. March security and department of the government. Yongshun 2020 quality County supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local Symposium township agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local agricultural condition, and consult the project condition in the local area, and listen Competent to the opinion on the project by the agricultural agricultural competent department. . department of Cili Especially for the demonstration area with Agricultural 4. Cili April County the cropping system change demands, it is Symposium Bureau of Cili County 2020 required to listen to the opinions on the County cropping system change by the agricultural competent department. Relevant Learn the basic condition of the local competent industrial and mining enterprises involving departments of the heavy metal, the water quality condition government of of the local irrigation water source and the 156 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Serial Negotiation Time Form Location Contents No. object Cili County in current security status of the local charge of agricultural products, and listen to the environmental opinions on the project by the competent protection, water department of the government. Especially conservancy, for the demonstration areas to be reformed, security and listen to the opinions of the relevant quality competent government departments on the supervision reform. Posting of Post the project announcement in the announcement bulletin board of the government Local residents, Learn the current situation of the local poor households, agricultural condition, and consult the cooperatives and project condition in the local area. township Especially for the demonstration area with Symposium government the cropping system change demands, it is Demonstration required to listen to the opinions of the local areas residents on the cropping system change by the agricultural competent department. Learn the enterprises removed or closed involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local agricultural condition, and consult the project condition in the local area, and listen Competent to the opinion on the project by the agricultural agricultural competent department. . department of Especially for the demonstration area with Huayuan County the cropping system change demands, it is required to listen to the opinions on the cropping system change by the agricultural Agricultural competent department. Bureau of Relevant Learn the basic condition of the local Symposium Huayuan competent industrial and mining enterprises involving County departments of the heavy metal, the water quality condition government of of the local irrigation water source and the Huayuan County current security status of the local 5. in charge of agricultural products, and listen to the March Huayuan environmental opinions on the project by the competent 2020 County protection, water department of the government. Especially conservancy, for the demonstration areas to be reformed, security and listen to the opinions of the relevant quality competent government departments on the supervision reform. Posting of Post the project announcement in the announcement bulletin board of the government Local residents, Learn the current situation of the local poor households, agricultural condition, and consult the Demonstration cooperatives and project condition in the local area. areas township Especially for the demonstration area with Symposium government the cropping system change demands, it is required to listen to the opinions of the local residents on the cropping system change by the agricultural competent department. 157 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Serial Negotiation Time Form Location Contents No. object Learn the enterprises removed or closed involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local agricultural condition, and consult the project condition in the local area, and listen Competent to the opinion on the project by the agricultural agricultural competent department. . department of Especially for the demonstration area with Anhua County the cropping system change demands, it is required to listen to the opinions on the cropping system change by the agricultural competent department. Agricultural Relevant Learn the basic condition of the local Symposium Bureau of competent industrial and mining enterprises involving Anhua County departments of the heavy metal, the water quality condition government of of the local irrigation water source and the Anhua County in current security status of the local charge of agricultural products, and listen to the environmental opinions on the project by the competent protection, water department of the government. Especially conservancy, for the demonstration areas to be reformed, 6. Anhua April security and listen to the opinions of the relevant County 2020 quality competent government departments on the supervision reform. Posting of Post the project announcement in the announcement bulletin board of the government Local residents, Learn the current situation of the local poor households, agricultural condition, and consult the cooperatives and project condition in the local area. township Especially for the demonstration area with Symposium government the cropping system change demands, it is Demonstration required to listen to the opinions of the local areas residents on the cropping system change by the agricultural competent department. Learn the enterprises removed or closed involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local Competent agricultural condition, and consult the agricultural project condition in the local area, and listen department of to the opinion on the project by the Hengyang County agricultural competent department. . Agricultural 7. Relevant Learn the basic condition of the local April Bureau of Hengyang Symposium competent industrial and mining enterprises involving 2020 Hengyang County departments of the heavy metal, the water quality condition County government of of the local irrigation water source and the Hengyang County current security status of the local in charge of agricultural products, and listen to the environmental opinions on the project by the competent protection, water department of the government. 158 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Serial Negotiation Time Form Location Contents No. object conservancy, security and quality supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local township Symposium agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local Competent agricultural condition, and consult the agricultural project condition in the local area, and listen department of to the opinion on the project by the Hengnan County agricultural competent department. . Relevant competent Agricultural departments of Learn the basic condition of the local Bureau of Symposium government of industrial and mining enterprises involving Hengnan Hengnan County the heavy metal, the water quality condition County in charge of of the local irrigation water source and the environmental current security status of the local protection, water agricultural products, and listen to the conservancy, opinions on the project by the competent 8. April security and department of the government. Hengnan 2020 quality County supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local township Symposium agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Competent Learn the current situation of the local agricultural agricultural condition, and consult the department of project condition in the local area, and listen Lengshuitan to the opinion on the project by the District agricultural competent department. Agricultural 9. Relevant Learn the basic condition of the local March Bureau of Lengshuitan Symposium competent industrial and mining enterprises involving 2020 Lengshuitan District departments of the heavy metal, the water quality condition District government of of the local irrigation water source and the Lengshuitan current security status of the local District in charge agricultural products, and listen to the of environmental opinions on the project by the competent protection, water department of the government. 159 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Serial Negotiation Time Form Location Contents No. object conservancy, security and quality supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local township Symposium agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local Competent agricultural condition, and consult the agricultural project condition in the local area, and listen department of to the opinion on the project by the Linwu County agricultural competent department. Relevant competent Agricultural departments of Learn the basic condition of the local Symposium Bureau of government of industrial and mining enterprises involving Linwu County Linwu County in the heavy metal, the water quality condition charge of of the local irrigation water source and the environmental current security status of the local protection, water agricultural products, and listen to the conservancy, opinions on the project by the competent 10. April security and department of the government. Linwu 2020 quality County supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local township Symposium agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. Learn the current situation of the local Competent agricultural condition, and consult the agricultural project condition in the local area, and listen department of to the opinion on the project by the Qiyang County agricultural competent department. Agricultural 11. Relevant Learn the basic condition of the local April Committee of Qiyang Symposium competent industrial and mining enterprises involving 2020 Qiyang County departments of the heavy metal, the water quality condition County government of of the local irrigation water source and the Qiyang County in current security status of the local charge of agricultural products, and listen to the environmental opinions on the project by the competent protection, water department of the government. 160 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Serial Negotiation Time Form Location Contents No. object conservancy, security and quality supervision Posting of Local residents, Post the project announcement in the announcement poor households, bulletin board of the government cooperatives and Learn the current situation of the local township Symposium agricultural condition, and consult the government project condition in the local area. Demonstration Learn the enterprises removed or closed areas involving the heavy metal pollutant discharge surrounding the demonstration Surrounding Symposium area and the winery purchasing the enterprises contaminated rice in the demonstration area, and learn the environmental appeal of these enterprises and the influences on the project. On-the-Spot Photos of the First Round of Public Investigation Activities: a. Symposium of the demonstration area b. Symposium of the demonstration area 7.1.3.2 Second Round of Public Investigation Activities Table 7-2 Second Round of Public Investigation Activities Serial No. Time Form Location Negotiation object Contents No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Relevant competent 1. departments of December Yongding government of Consult the local situation of 2020 District Agricultural Yongding District in the project and listen to the Bureau of charge of views of the agricultural Symposium Yongding environmental competent departments and District protection, water other relevant government conservancy, security authorities on the project. and quality supervision 161 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Jishou City and relevant Consult the local situation of government the project and listen to the Agricultural competent views of the agricultural Symposium Bureau of departments in charge competent departments and Jishou City of environmental other relevant government 2. Jishou December protection, water authorities on the project. City 2020 conservancy, security and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Yongshun County and Consult the local situation of Agricultural relevant government the project and listen to the Bureau of competent views of the agricultural Symposium 3.Yongshun December Yongshun departments in charge competent departments and County 2020 County of environmental other relevant government protection, water authorities on the project. conservancy, security and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives Demonstration households, Interview and related enterprises, and areas cooperatives and optimize the relevant contents enterprises of project design and construction. 162 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Cili County and relevant Consult the local situation of government the project and listen to the Agricultural competent views of the agricultural Symposium Bureau of Cili departments in charge competent departments and County of environmental other relevant government 4. Cili December protection, water authorities on the project. County 2020 conservancy, security and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Huayuan County and Consult the local situation of Agricultural relevant government the project and listen to the Bureau of competent views of the agricultural Symposium Huayuan departments in charge competent departments and 5. County of environmental other relevant government December protection, water Huayuan authorities on the project. 2020 conservancy, security County and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of 6. Anhua December Posting of Demonstration Local residents environmental impact of the County 2020 announcement areas newly-added demonstration area. 163 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Agricultural competent departments of Huayuan County and Consult the local situation of relevant government the project and listen to the Agricultural competent views of the agricultural Symposium Bureau of departments in charge competent departments and Anhua County of environmental other relevant government protection, water authorities on the project. conservancy, security and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Hengyang County and Consult the local situation of Agricultural relevant government the project and listen to the Bureau of competent views of the agricultural Symposium Hengyang departments in charge competent departments and 7. County of environmental other relevant government November protection, water authorities on the project. Hengyang 2020 County conservancy, security and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. 8. Agricultural November competent Hengnan Consult the local situation of 2020 departments of County Agricultural the project and listen to the Hengnan County and Bureau of views of the agricultural Symposium relevant government Hengnan competent departments and competent County other relevant government departments in charge authorities on the project. of environmental protection, water 164 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report conservancy, security and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Lengshuitan District Consult the local situation of and relevant Agricultural the project and listen to the government Bureau of views of the agricultural Symposium competent Lengshuitan competent departments and departments in charge 9. District other relevant government December of environmental Lengshuitan authorities on the project. 2020 protection, water District conservancy, security and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Linwu County and relevant Consult the local situation of government the project and listen to the 10. Linwu November Agricultural competent views of the agricultural County 2020 Symposium Bureau of departments in charge competent departments and Linwu County of environmental other relevant government protection, water authorities on the project. conservancy, security and quality supervision Local residents, poor Visit the site to understand the Demonstration households, demands and suggestions of Interview areas cooperatives and local residents, cooperatives enterprises and related enterprises, and 165 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report optimize the relevant contents of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. No feedback was received on the announcement of Posting of Demonstration Local residents environmental impact of the announcement areas newly-added demonstration area. Agricultural competent departments of Qiyang County and Consult the local situation of relevant government the project and listen to the Agricultural competent views of the agricultural Symposium Committee of departments in charge competent departments and Qiyang County 11. of environmental other relevant government December protection, water authorities on the project. Qiyang 2020 conservancy, security County and quality supervision Visit the site to understand the demands and suggestions of Local residents, poor local residents, cooperatives households, Interview and related enterprises, and cooperatives and Demonstration optimize the relevant contents enterprises areas of project design and construction. Issue the questionnaire to Questionnaire Local residents investigate the opinion on the survey project by the local resident. On-the-Spot Photos of the Second Round of Public Investigation Activities: b. Site-visit and symposium of the a. Symposium of the demonstration area demonstration area 166 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report c. Questionnaire survey in the demonstration d. Agricultural land irrigation canal in the area demonstration area 7.1.3.3 Public Participation Questionnaire In order to listen to the ideas and suggestions of people affected by the project on Project construction and environmental protection, questionnaires are given out to relevant personnel in all demonstration areas in 12 project counties, including major agricultural planting households, individual planting households, village cadres, poor households, women, other farmers and enterprise employees. Applicable questionnaire shall be designed according to Project characteristics. There are 236 questionnaires in total. The statistics of basic information of the respondents are shown in Table 7-3. The results of questionnaire survey are shown in Table 7-4. The statistical data in the statistical table of basic information of respondents indicates that the ratio of female respondents takes up 22% and the ratio of respondents aged 41-60 takes up 61%, thus relatively favorably representing the basic features of affected people. The questionnaires filled out by these personnel can basically reflect the actual conditions and ideas of these groups. Statistics of each question raised in the questionnaire are gathered and relevant analysis is conducted. See Table 7-4 for details. Table 7-3 Statistical table of basic information of respondents involved in public opinion questionnaire of environmental impact assessment Sex Age Education Above Senior Junior Above Primary Male Female 18~40 41~60 junior high high 60 school college school school Number of persons 185 51 37 144 55 13 52 129 42 (person) Ratio (%) 78 22 16 61 23 6 22 55 18 Table 7-4 List of statistical results and analysis of public opinion questionnaire of environmental impact assessment Investigation No. of No. Option Ratio % Analysis and conclusion content persons Yes 158 66.95% Respondents understand or heard about the project Do you understand Heard of before 52 22.03% 1 conditions, indicating that the this Project? publicity efforts of the project No idea 26 11.02% should be better. 167 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Investigation No. of No. Option Ratio % Analysis and conclusion content persons Bulletin board 162 68.64% Majority of respondents get to TV/newspaper/ know the project from the How do you get to 34 14.41% network bulletin board, indicating that 2 know information the announcement of the project of this Project? Local residents 31 13.14% has already become effective. Others 22 9.32% (Remark: Multiple choices) Approve 236 100.00% What attitude do No one disagrees on Project 3 you adopt towards Disapprove 0 0.00% construction. this Project? No idea 0 0.00% What’s your Reasonable 227 96.19% opinion on site No one thinks that the project 4 Unreasonable 0 0.00% selection of the site selection is unreasonable. project? No idea 9 3.81% What kind of Promoting 222 94.07% influence of effect Project Obstructing Great majority of people think 3 1.27% construction will effect that Project construction will 5 be imposed on No influence 9 3.81% promote development of local local economic economy. development in No idea 2 0.85% your opinion? Which aspect of Water 141 59.75% Project environment About half number of construction will Atmospheric 19 8.05% respondent think that the project be under most environment 6 has the biggest influence on influence of Ecological 71 30.08% water environment. (Remark: Project environment Multiple choices) construction in your opinion? Others 24 10.17% Reduction of agricultural soil 138 58.47% pollution Improvement What are the main of Most respondents think that environmental farm-oriented 49 20.76% reduction of pollution is the 7 benefits of this irrigation major environmental benefit of Project in your quality this Project. (Remark: Multiple opinion? Improvement choices) of quality and safety of 100 42.37% agricultural products What is the biggest Improvement 100 42.37% About half of the respondents influence on the of income believe that the implementation interests of Environmental 80 33.90% of the project will promote the 8 yourself and local improvement increase of local residents’ residents after income or the food security. construction of this Food safety 98 41.53% (Remark: Multiple choices) Project Are you satisfied Satisfied 146 61.86% Most of the respondents are 9 with status quo of Dissatisfied 75 31.78% satisfied with the local current 168 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Investigation No. of No. Option Ratio % Analysis and conclusion content persons local environmental quality, a small environmental part of them is not satisfied, and quality? this shows that there are No idea 15 6.36% environmental problems in the implementation area of the project. Water pollution 166 70.34% Most of the respondents believe What is the major that the local water pollution is Atmospheric local 22 9.32% the most remarkable problem, pollution 10 environmental and the construction of the problem in your Noise 2 0.85% project will greatly improve the opinion? Ecological local water environment. 64 27.12% destruction (Remark: Multiple choices) Heavy metal 131 55.51% Most respondents think that contamination What is the major Pesticide heavy metal contamination is environmental 73 30.93% the largest land environment pollution 11 problem existing in Excessive problem at present, indicating cultivated land at fertilizer 40 16.95% that the construction contents of present? application this Project are well-targeted. (Remark: Multiple choices) Others 8 3.39% Agricultural 139 58.90% What is the soil pollution problem you want Production The project will effectively 12 to solve most in 76 32.20% realize this objective. (Remark: technologies current agricultural Product sales 28 11.86% Multiple choices) production? Others 9 3.81% What change will Improved 203 86.02% Majority of respondents thinks take place to the that the improvement of Project yield of grain Reduced 4 1.69% will improve the yield. 13 crops after Unchanged 21 8.90% Safeguarding of grain yield of implementation of farmers is the key to ensure the project? No idea 8 3.39% smooth Project implementation. What change will Improved 228 96.61% take place to the Reduced 0 0.00% Majority of respondents think quality of the implementation of the 14 agricultural project will improve quality and products after Unchanged 6 2.54% safety of agricultural products. implementation of the project? How about your Relatively 103 43.64% About half of the respondents opinion on local complete believe that the local agriculture and Relatively agricultural and water irrigation 15 water conservancy simple and 109 46.19% facility is rather simple, and this irrigation crude shows that the local irrigation facilities? No irrigation 24 10.17% facilities are weak. facility Do you already Fully mastered 57 24.15% Most of the respondents believe 16 master various Probably that they grasp the basic farm related skills for 154 65.25% irrigation system construction learned 169 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Investigation No. of No. Option Ratio % Analysis and conclusion content persons construction and and the relevant maintenance maintenance of skills, but still a small part of Not mastered 25 10.59% field irrigation them does not grasp the relevant system? skills. Are you willing to Yes 211 89.41% participate in the Respondents are willing to take whole process of No 6 2.54% part in the whole process of Project design, design, construction and construction and implementation of field 17 implementation if irrigation system, indicating field irrigation No idea 20 8.47% relatively high degree of system is designed concern of locals for irrigation and constructed system. locally? Have you ever No 55 23.31% Most of the respondents have participated in accepted the agricultural training on 1-2 times 93 39.41% training, and it is required to 18 agricultural 3-5 times 63 26.69% strengthen the relevant training knowledge? in the construction process of Above 5 times 26 11.02% the project. Fully manual 75 31.78% planting Manual planting + Most respondents adopt Limited 112 47.46% planting method of manual agricultural planting + limited agricultural What is your crop machinery 19 machinery or total manual planting method? Agricultural planting, indicating relatively machinery + 41 17.37% weak agricultural machinery Limited manual construction at present. planting Fully agricultural 9 3.81% machinery Farm manure 70 29.66% A small part of the respondents use the compound and Compound micronutrients fertilizer, a small fertilizer and 90 38.14% part of the investigators use the trace fertilizer farmyard manure, another small Testing soil for part of the investigators use the Types of chemical formulated 36 15.25% soil testing and formula 20 fertilizers applied fertilization fertilizer or the mixed fertilizer, by you this shows that the local soil testing and formula fertilizer Mixed has certain foundation, which is 67 28.39% fertilization beneficial for the implementation of the project. (Remark: Multiple choices) Recommended On the selection of the fertilizer How do you by agricultural 137 58.05% and pesticide, most of the choose chemical 21 technical staff respondents depend on the fertilizers and Recommended recommendation of the pesticide? 59 25.00% by dealers technicians in agriculture. 170 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Investigation No. of No. Option Ratio % Analysis and conclusion content persons Based on (Remark: Multiple choices) experience (or 46 19.49% recommended by neighbors) Based on labels (advertisements 2 0.85% ) Pesticide store 218 92.37% How do you Direct sales Most of the respondents acquire chemical 22 from 8 3.39% purchase the fertilizer and fertilizers and manufacturer pesticide in the pesticide shop. pesticide? Itinerant vendor 10 4.24% Ask those who used chemical 35 14.83% fertilizers About half of the respondents What is the basis before. can determine the dosage of the guiding your usage Based on 77 32.63% fertilizer according to the 23 of chemical experience guidance of the technicians in fertilizers at Label 39 16.53% agriculture. (Remark: Multiple present? instructions choices) Guidance by agricultural 105 44.49% technical staff Based on 72 30.51% experience About half of the respondents How do you Label 36 15.25% can determine the using number determine using instructions of the fertilizer according to the 24 frequency of Guidance by guidance of the technicians in chemical fertilizers agricultural 112 47.46% agriculture. (Remark: Multiple and pesticide? technical staff choices) Recommended 32 13.56% by dealers How about the 1-2 times 85 36.02% Pesticide is relatively frequently frequency of use of 3-4 times 129 54.66% used in Demonstration areas 25 pesticide in each 5-6 times 18 7.63% and plant diseases and insect round of crop pests are relatively serious. planting? Above 6 times 4 1.69% Hand-operated 63 26.69% sprayer Knapsack 106 44.92% About half number of sprayer How do you spray respondents use knapsack 26 Power sprayer 68 28.81% pesticide? sprayers. (Remark: Multiple Unified choices) prevention and 2 0.85% control company Which work shall Publicity and About half number of 106 44.92% 27 be mainly education respondents think that publicity, strengthened in the Training 125 52.97% education and relevant training 171 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Investigation No. of No. Option Ratio % Analysis and conclusion content persons next step in order Organization shall be strengthened, which is to ensure and also a highlight in the successful implementation 29 12.29% early-stage work of the project. implementation of of monitoring (Remark: Multiple choices) the project? and assessment Others 1 0.42% What are your opinions and Main opinions and suggestions: It is expected that the project can be suggestions on implemented as soon as possible with guaranteed quality and quantity. 28 Project Meanwhile, environmental protection work shall be properly conducted. construction and The normal lives of surrounding people shall not be affected during environmental construction period. protection work? Main difficulties and hopes: It is expected that the project would have What are relatively good continuity and the economic subsidy can be improved in a difficulties and proper manner; it will bring obvious economic benefits to villagers, hopes during 29 especially for poor households, women and other groups; project publicity implementation shall be enhanced to enable more people to get involved in the project as and construction of well as play a demonstrative role for local agricultural development through the project? favorable implementation effect. 7.1.4 Information Disclosure and Feedback 7.1.4.1 Site Announcement Site announcement refers to posting of paper announcement in bulletin boards of township governments and village committees where the project is implemented as other densely-populated areas. 7.1.4.2 Contents of Announcement According to the requirements of Law of the People’s Republic of China on Environmental Impact Assessment, Interim Measures for Public Participation of Environmental Impact Assessment issued by Ministry of Environmental Protection of the state as well as business policy of the World Bank (OP4.01), we carry out two rounds of information disclosure during the process of assessment. The first round is carried out after screening and selection of environmental problems and before final determination of environmental impact assessment outline, while the second round is carried out in the stage when the first draft of Environmental Impact Report is completed. Contents of announcement are shown as follows: ① Overview of construction Project; ② Work procedures and main contents of assessment; 172 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report ③ Scope of solicitation of public opinions and main matters; ④ Specific solicitation of public opinions; ⑤ The way and deadline that the public look up the environmental impact report. ⑥ Starting and ending dates for the public to put forward their opinions; ⑦ Contact information, including mailing addresses, postal codes, contact number, fax number, contact persons, emails, etc. of development organization and environmental impact assessment organization. 7.1.5 Summarization of Opinions and Feedback of Public Participation Table 7-5 Summary sheet of Opinions and Feedback of Public Participation Public opinions Corresponding Feedback in Environmental Impact Report Land leveling and digestion are carried out locally upon muck 1. About control of construction excavation of Project points; the household garbage of garbage construction personnel are centrally collected on the construction site and timely cleared and transported. PMO is responsible for uniformly establishing scheme and organizing training for agricultural technical service providers and 2. About Project implementation field schools, and publicity and training for poor households and effect women shall particularly be strengthened. Through good implementation effect, it can bring obvious economic benefits for villagers, especially for poor households, women and other groups. Agricultural land irrigation water source detection points are set up at the main irrigation water inlet of cultivated land in 3. About water pollution problems Demonstration area to detect the water quality of irrigation water source during key water demand period of grain planting so as to ensure provision of basis for safety of irrigation water quality. Liming personnel shall properly conduct protection work and 4. Safety management and properly wear protective clothes and masks during application of personnel’s health issues quick lime to ensure safety of personnel and seedlings. Maintain and rebuild the irrigation canal that can not meet the 5. Related to the irrigation irrigation demands in the demonstration area, so as to meet the measures demands of farmers on the irrigation canal and water source. 173 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Public opinions Corresponding Feedback in Environmental Impact Report In order to strengthen the management and control on the rice with excessive heavy metals, to ensure that the contaminated rice will not be circulated in the food fields at random, and to manage and control the contaminated rice, the wineries in the counties where Related to the management and the demonstration area is located will purchase the rice to make control of contaminated rice wine. The vinasse and other residues etc. shall be sent to the refuse landfill for treatment in the counties where the project is located, and it is forbidden to let them flow into the food chain. 7.1.6 Brief Summary of Public Participation Table 7-6 Summary Sheet of Public Participation Feedback on Form of public Participating Time Location Contents Public participation objectives opinions The First Round of Summary Sheet of Public Participation: Learn the current situation of the local agricultural condition, and consult the project condition in Play a the local area, and listen to the demonstrative opinion on the project by the role for local Competent agricultural competent agricultural agricultural department. Especially for the development department of demonstration area with the through Counties cropping system change demands, favorable it is required to listen to the implementation opinions on the cropping system effect. change by the agricultural competent department. Agricultural Symposium bureaus of all Learn the basic condition of the counties local industrial and mining March Relevant enterprises involving the heavy to competent metal, the water quality condition Play a April departments of of the local irrigation water source demonstrative 2020 government of and the current security status of role for local Counties in the local agricultural products, agricultural charge of and listen to the opinions on the development environmental project by the competent through protection, water department of the government. favorable conservancy, Especially for the demonstration implementation security and areas to be reformed, listen to the effect. quality opinions of the relevant supervision competent government departments on the reform. Local residents, Play a poor households, Post the project announcement in demonstrative Posting of Demonstration cooperatives and the bulletin board of the role for local announcement areas township government agricultural government development 174 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Feedback on Form of public Participating Time Location Contents Public participation objectives opinions through favorable implementation effect. Through good Learn the current situation of the implementation local agricultural condition, and effect, it can consult the project condition in bring obvious the local area. Especially for the economic demonstration area with the benefits for Symposium cropping system change demands, villagers, it is required to listen to the especially for opinions of the local residents on poor the cropping system change by households, the agricultural competent women and department. other groups. The water Learn the enterprises removed or quality of local closed involving the heavy metal irrigation water pollutant discharge surrounding source is Surrounding Symposium the demonstration area, and learn already enterprises the environmental appeal of these controlled and enterprises and the influences on the project the project. demand can be satisfied. The Second Round of Summary Sheet of Public Participation: Agricultural competent Optimize the departments of contents of each county and Consult the local situation of the project design relevant project and listen to the views of and government the agricultural competent construction; Agricultural competent departments and other relevant act as a model Symposium bureaus of all departments in government authorities on the for the local counties charge of project. Especially the opinions agricultural environmental and suggestions on the development protection, water implementation content and through good conservancy, construction of the project. implementation security and effects. quality Novem supervision ber to Optimize the Decem contents of ber project design 2020 Conduct site surveys and field and visits to have a good construction; understanding of the demands and publicity and suggestions of local residents, training for cooperatives and related poor Local residents, businesses. Particularly, for Demonstration households and Interview poor households, demonstration areas where areas women shall be cooperatives engineering works or strengthened; restructuring is required, hear the through good opinions of local residents, implementation cooperatives, etc. about such effect, it can engineering works or bring obvious restructuring. economic benefits for villagers, 175 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Feedback on Form of public Participating Time Location Contents Public participation objectives opinions especially for poor households, women and other groups. Agricultural land irrigation water source detection points are set up at the main irrigation water inlet of cultivated land in Demonstration area to detect Issue the questionnaire to Questionnaire the water Local residents investigate the opinion on the survey quality of project by the local resident. irrigation water source during key water demand period of grain planting so as to ensure provision of basis for safety of irrigation water quality. Conduct the relevant measures through the removing or closing the enterprises Investigate the enterprises involving the removed or closed involving the heavy metal heavy metal pollutant discharge pollutant Surrounding Interview surrounding the demonstration discharge enterprises area, and learn the environmental surrounding the appeal of these enterprises and the demonstration influences on the project. area, so as to ensure that the irrigation water quality in the demonstration area free from of contamination. Table 7-7 Summary Sheet of Information Disclosure Time of Place of Form of Disclosed contents Organizer disclosure disclosure disclosure The First Round of Summary Sheet of Public Participation and Information Disclosure: March to Government Posting of Agricultural bureau of counties Post the project (Agricultural Bureau of April 2020 bulletin announcement announcement in the Yongding District, Agricultural 176 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Time of Place of Form of Disclosed contents Organizer disclosure disclosure disclosure board bulletin board of the Bureau of Jishou City, government, publishing Agricultural Bureau of the overview of the Yongshun County, Agricultural construction project and Bureau of Cili County, the main contents. Agricultural Bureau of Huayuan County, Agricultural Bureau of Anhua County, Agricultural Bureau of Hengnan County, Agricultural Bureau of Hengnan County, Agricultural Bureau of Lengshuitan District, Agricultural Bureau of Lengshuitan District, Agricultural Bureau of Linwu County, Agricultural Committee of Qiyang County) The Second Round of Summary Sheet of Public Participation and Information Disclosure: Environmental impact Agricultural bureau of counties of the project, key (Agricultural Bureau of points of measures, EIA Yongding District, Agricultural conclusions, and Bureau of Jishou City, publication of EIA Brief Agricultural Bureau of Yongshun County, Agricultural Edition; scope of public Bureau of Cili County, participation and main Agricultural Bureau of Huayuan November to matters; contact County, Agricultural Bureau of Demonstrati Posting of December information including Anhua County, Agricultural on areas announcement Bureau of Hengnan County, 2020 mailing addresses, Agricultural Bureau of Hengnan postal codes, contact County, Agricultural Bureau of number, fax number, Lengshuitan District, contact persons, emails, Agricultural Bureau of etc. of development Lengshuitan District, organization and Agricultural Bureau of Linwu County, Agricultural Committee environmental impact of Qiyang County) assessment organization Approaches such as convening of symposium, interview, granting of questionnaires and site announcement are adopted to get to know the opinions and suggestions of the public. The information collected through various approaches is utilized to enable the public in the demonstration areas to generally get to know the conditions of this project, properly conduct environmental protection work and make the project to generate social, environment and economic benefits as early as possible. 177 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 7.2 Information Release and Suggestion Feedback (Complaint) Mechanism during Project Implementation 1. Information release The effective information release mechanism is established for this project in order to make the affected people quickly obtain the information in the project implementation process and ensure the interests of affected groups to be fully considered in the project construction and operation process. The information release mechanism is as follows: Stage 1: small-scale civil construction activities For construction of small-scale civil activities (such as irrigation canal renovation, etc.), the construction unit shall publish the project information to the affected residents in the vicinity in the form of posting notices. All the construction sites shall be posted with relevant project information, including but not limited to: ① Project overview; ② Construction plans; ③ Main construction activities; ④ Major environmental problems and mitigation measures; ⑤ Name and telephone number of the construction units and the supervision unit, and so on. The construction unit and the supervision unit shall regularly communicate with the nearby residents to minimize the adverse impact on them. All construction units shall provide training to workers on surrounding relationship maintenance, communication, local customs and code of conduct. All complaints, problems and related matters shall be included in the feedback report and submitted to the supervision unit and the construction unit for review; complaints to be corrected and treated must be communicated to the concerned party in order to ensure the complainant to be satisfied. The environmental protection problems should be properly solved through consulting the local environmental protection administration department. Stage 2: agronomic activities 178 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report For execution of agronomic activities (such as liming, etc.), the construction unit shall publish the project information to the affected residents in the vicinity in the form of posting notices. Notices of relevant project information shall be posted conspicuously around the agricultural land where all agronomic activities are carried out, and the information includes but not limited to: ① Project overview; ② Implementation plans of agronomic activities; ③ Main activity amounts (e.g. lime application amount); ④ Major environmental problems and mitigation measures; ⑤ Name and telephone number of the implementation units and the supervision unit, and so on. The construction unit and the supervision unit shall regularly communicate with the nearby residents to minimize the adverse impact on them. All construction units shall provide training to workers on surrounding relationship maintenance, communication, local customs and code of conduct. All complaints, problems and related matters shall be included in the feedback report and submitted to the supervision unit and the implementation unit for review; complaints to be corrected and treated must be communicated to the concerned party in order to ensure the complainant to be satisfied. The environmental protection problems should be properly solved through consulting the local environmental protection administration department. Stage 3: agricultural product detection during implementation After agricultural product detection results come out each year during project implementation, the county will hold a public-participation field investigation meeting and inform the project basic situations and agricultural product detection results to the related farmers and rural cooperatives. If the heavy metal content in agricultural products exceeds the standards, the agricultural products exceeding the standards will be purchased in a unified way and safely disposed according to the subsidy policies formulated in the project implementation plan. Meanwhile, opinions and suggestions given by the stakeholders such 179 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report as farmers, rural cooperatives, and so on in the demonstration area should be collected, corresponding countermeasures or measures shall be prepared based on their opinions and suggestions, and improvement should be made in the subsequent implementation of the project. 2. Suggestion feedback (complaint) mechanism A suggestion feedback (complaint) mechanism should be established in order to effectively solve the problems arising from the project implementation process in a timely manner and ensure the smooth progress of the project. After receiving the environmental complaint or the rectification notice of administrative department, the construction unit or the implementation unit shall organize a visit and investigation with the relevant departments such as the county PMO and other relevant departments, and make rectification according to the actual situation. Meanwhile, the rectification plan will be publicized to solve the environmental protection disputes. After receiving the rectification notice, the rectification should be completed within 3 working days (the rectification will be completed within 10 working days in case of coordination of the management organization). The feedback mechanism is described as follows: The public can give advice by sending letters, faxes or E-mails to the construction unit or the implementation unit; and give feedback opinions through the county PMO and the petition handling office. Measures should be taken to ensure the transparency and effectiveness of the appeal channels, and specific requirements are described as follows: (1) If residents are affected in any aspect of the environment, they can appeal to the county PMO, and the office will decide to handle the appeal within 2 weeks. (2) If residents are still not satisfied with the decision of the county project management office, they may, upon receipt of the decision, appeal to the administrative organ having jurisdictions by levels for arbitration according to the Administrative Procedure Law of the People’s Republic of China. (3) If residents who are still dissatisfied with the arbitration decision, they may, upon receipt of the arbitration decision, bring a suit in a civil court in accordance with the civil procedure law. 180 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (4) Residents may appeal (bring an action) against any aspect of environmental management, including compensation standards. (5) The way of appeal shall be informed to the residents so that they fully understand that they have the right to appeal. (6) No fees shall be charged by the organ handling the residents’ complaints, and the expenses incurred in the complaints shall be paid by the construction unit or the implementation unit. (7) All appeals should be normatively recorded, tracked and periodically reported; Record contents include: the appeal record sheet mainly includes: the basic information of the complainant, the basic information of the complaint matter, the appeal matter and the respondent, solutions and the effect achieved. Tracking contents include: whether the petitioner’s appeal has been handled, whether the complainant is satisfied with the treatment results, and so on. Periodic reports include: the complaints should be periodically reported to the upper level in writing and written into the follow-up project implementation plan. The project undertaker or the construction unit shall arrange the full-time environmental protection personnel to specialize in collecting and receiving the dissatisfaction and complaints from the affected population. The principal name, office address and contact number of the project undertaker or the construction unit shall be announced. According to the public’s feedback opinions, the mitigation measures should be adjusted purposefully and the environmental management activities should be further improved in line with the environment monitoring report, inspection reports of the regulatory authority, and the environmental management plans. In case of any significant deviation from the contents of the environmental management and social plans during inspection, or any great negative environment impact caused by project changes, or any significant increase of population due to adverse environmental impacts, the project management office will promptly consult the environmental agency and the World Bank and set up an environmental assessment team to 181 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report conduct additional environmental assessment, and also carry out additional public consultation if necessary. The revised environmental management plans shall also be notified to the implementation agency and the contractors. Carry out according to the revised content. 182 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 8 Environmental Management Plan 8.1 Purpose of Environmental Management Environmental management is a part of project management as well as an important link in the effective implementation of environmental protection and social risk prevention work of the project. Purpose of environmental management of the Hunan Integrated Management of Agricultural Land Pollution Project lies in guaranteeing the smooth implementation of various environmental protection measures and social risk prevention measures of the project, to mitigate the adverse impact of project implementation on the environment and enable the harmony among environmental protection, social sustainable development and economic development. 8.2 Contents of Environmental Management Plan Environmental management plan of the project is prepared based on environmental impact assessment and its contents mainly include environmental management system and responsibilities, environmental management training, environmental protection measures and social risk prevention measures proposed for the adverse impacts identified in environmental impact assessment and investment estimation of environmental management. 8.3 Environmental Management System 8.3.1 Setting of Environmental Management Organization The setting of environmental management organization of the project is specified in Table 8-1 and Figure 8-1. Table 8-1 Composition of environmental management system Nature of Name of organization Responsibilities of the organization organization ◼ Provide comprehensive and macroscopic guidance for implementation and coordination of relevant policies as well Provincial project joint as solving of relevant difficulties, supervise project meeting implementation, review and approve project plan, seek for supporting capital, implement inter-department coordination and help solve difficulties existing in project implementation. Management organization Take charge of overall coordination and management of the project to ensure smooth implementation of relevant policies in environmental management plan, which mainly includes: Provincial PMO ◼ Check and coordinate with the work of each local environmental management department. ◼ Take charge of arranging survey activities of environmental experts of World Bank. 183 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report ◼ Summarize reports of each sub-project in different stages and submit them to World Bank for review. ◼ Report work to World Bank on a regular basis. ◼ Coordinate with County PMO to process complaints and grievances Take charge of implementation and management of each sub-project to ensure smooth implementation of relevant policies in environmental management plan, which mainly includes: ◼ Supervise and urge the project implementer to implement the County PMO environmental management plan. ◼ Prepare staged report of environmental management of the project. ◼ Report work to provincial PMO on a regular basis. ◼ Take charge of processing complaints and grievance Supervise and check implementation of environmental World Bank management plan. The governmental administration organization conducts whole-process environmental supervision management of project Environmental protection activities according to law, including examination and approval of bureau environmental impact assessment report, provision of guidance, and remediation acceptance. For the demonstration area organized and implemented by professional agricultural cooperatives, each project administrative village shall establish a project quality supervision team consisting of village committee members, representatives of farmers, women’s representatives, representatives of poor Supervision farmer households and representatives of vulnerable target groups organization (minority representatives shall be included in areas inhabited by the minority nationalities). Responsibilities: 1. supervise projects implemented by farmer specialized cooperatives and Third-party supervision agriculture-related enterprises together with the agriculture organization supervision company entrusted by County PMO; 2. assist PMO at each level in collecting monitoring and assessment data as required; For the demonstration area organized and implemented by village committee, a village project implementation team shall be established, to specifically organize the implementation of various works and various agronomic measures. Supervision of project quality shall be implemented by the agriculture supervision company entrusted by County PMO Project implementation Take charge of project implementation and execution of Implementation organization established by environmental protection measures and social risk prevention organization project implementation measures township of each county Implement environmental impact identification, prepare specific Preparation Environmental environmental impact assessment document and provide stage consultant environmental consulting and technical support upon the entrustment of project environmental management organization. Consulting Implement staged assessment and summary on environmental service impact of project implementation on a regular basis, submit the organization Implementa Environmental report on the execution of EMP in the implementation stage tion stage consultant (twice a year) and provide environmental consulting and technical support upon the entrustment of project environmental management organization. Environmental monitoring Undertake professional environmental monitoring tasks upon the organization entrustment of project environmental management organization. Framework of environmental management organization of the project is as shown in Figure 8-1. 184 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Figure 8-1 Framework Diagram of Environmental Management Organization of the Project 8.3.2 Responsibilities and Personnel Allocation of Each Organization of Environmental Management System The environmental management system adopted in “Integrated Management Project of Polluted agricultural land of Hunan Province with World Bank Loan” includes project management organization, supervision organization, implementation organization and consulting service organization. All these organizations commonly constitute a complete environmental management system of the project. However, each of them undertakes different work contents and has different scopes of responsibility. The project is launched under the organization and leadership of provincial PMO and each project county (municipal) government to ensure the compliance of project construction with requirements stipulated by China and the World Bank concerning work procedure and implementation of pollution prevention and control measures and social risk prevention measures, etc. Responsibilities and personnel allocation of each organization in this project are as shown in Table 8-2 below. Table 8-2 Responsibilities of Relevant Organizations in Each County in Environmental 185 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Management System Name of Type of Personnel Responsibilities of the organization organization organization allocation 1. Carry out whole-process environmental supervision management of the project according to law, ①Environmental including approval of project environmental impact Supervision Protection Bureau 1 assessment report (including environmental organization of Project County assessment work of sub-projects), and environmental supervision management in stages such as project construction and operation. 1. Prepare and supervise the implementation of Environmental Management Plan; 2. Supervise and urge the coordination and implementation of domestic environmental management requirements and environmental ②Provincial management requirements of World Bank; project joint Management 3. Submit relevant reports to World Bank every half a 2~3 meeting and organization year; provincial PMO 4. Check environmental management work of PMO at each level; 5. Coordinate with other relevant departments to solve major environmental problems; 6. Entrust hired environmental and social expert group to check the project. 1. Prepare and supervise the implementation of sub-project environmental management rules and regulations; 2. Organize the preparation of approval application of domestic environmental impact assessment documents; 3. Urge the project design to meet environmental impact assessment requirements; 4. Include environmental protection measures in this environmental management plan in Project construction contract; ③PMO of Management 5. Hire, supervise and coordinate with Project 1-2 Project Counties organization supervisor (qualification, responsibilities and management); 6. Organize the implementation of environmental management training plan; 7. Properly keep records on complaints during Project construction and operation process, sort such records, answer handling results to the public and solve the problems complained by the public; 8. Submit reports (statements) to provincial PMO every quarter; 9. Accept the inspection of environmental work (including Project inspection of World Bank) 1. The World Bank assigns an inspectorate every year to conduct special inspection of Project Supervision implementation; ④World Bank 1~2 organization 2. Check execution conditions of loan agreement of this Project and implementation conditions of Environmental Management Plan. ⑤Provision of Environmental 1. Carry out on-the-spot survey of each Project and 3 construction impact conduct environmental assessment; 186 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Project assessment 2. Take charge of compiling contents of Environmental environmental organization Management Plan. impact assessment qualification certificate 1. Carry out site inspection of construction site and contractor and assist provincial PMO in checking environmental protection work of Project points; Consulting 2. Guide environmental impact assessment unit and ⑥Environmental service 2 implementation unit to properly design and consultants organization implement environmental protection measures, submit a draft report to provincial PMO and put forward suggestions and opinions on implementation of environmental protection. 1. Carry out environmental monitoring in Project ⑦Environmental Consulting construction period and operation period according monitoring service 1-2 to Environmental Monitoring Plan, keep such organization organization conditions in the archives and report to each county (municipal) PMO. 1. Formulate each environmental protection measure in construction period; 2. Accept supervision and inspection from World Bank ⑨Civil work and environmental protection departments at all contractors, levels regarding environmental protection; implementation Implementation 3. Establish a feedback mechanism and complete Some organization and organization rectification within 3 working days after receiving farmers of each notice of rectification (rectification shall be project site completed within 10 working days if management organization is demanded to coordinate); 4. Complete construction checklist together before construction and submit it to county (district) PMO. 1. Supervise projects implemented by farmer professional cooperatives and agriculture-related ⑩Third party Supervision enterprises together with the agriculture supervision supervision Some organization company entrusted by County PMO organization 2. Assist PMO at each level in collecting monitoring and assessment data as required 8.3.3 Environmental Management Tasks in Each Project Stage Project environmental management involves different work contents in different Project implementation stages as shown in Figure 8-2。 The most important task of environmental management plan is to ensure that each environmental protection measure put forward is practically and effectively implemented, including: ①Include environmental protection measures and social risk prevention measures in environmental management plan into project design and construction contract; ②Implementation of environmental protection measures by the construction unit during construction period; ③Project acceptance, supervision and management of Project operation period, mechanism of environmental management plan inspection, reporting 187 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report mechanism and filing mechanism. The timeliness of work is reflected through inspection of daily work. 8.3.4 Public Appeal and Feedback Mechanism In order to ensure the issues occurring in the implementation of the project to be effectively and timely addressed and ensure the smooth implementation of the project, a public appeal and feedback mechanism shall be established. 8.3.4.1 Grievance and Complaint Handling Organization In order to better protect local environmental quality condition and the interests of surrounding residents, each County PMO shall establish a leading group for handling complaints against environmental impact. The team leader shall be concurrently acted by the principal related personnel of each County PMO. Complaint handling office shall be set under the leading group for handling complaints and shall be set at each County PMO. Telephone number, fax, address, e-mail, etc. of complaint handling organization shall be 188 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report made public through bulletin board, etc. to allow affected persons to file a grievance against any environmental issue at any time. Daily complaints shall be collected and sorted by complaint handling office and shall be summarized by complaint handling office. Complaints and grievances raised by the masses shall be recorded and processed by specifically designated person in each county. In addition, the grievance and complaint system in China is fairly complete, and the grievance channel is very smooth. Specialized office for letters and calls and bureau for letters and calls are set under various government departments, such as environmental protection bureau, bureau of civil affairs and finance bureau. The masses may file a grievance directly to office for letters and calls and bureau for letters and calls. 8.3.4.2 Complaint and Grievance Procedures Detailed complaint and grievance processing procedures are as follows: 1） Grievance Uptake and Receipt When an affected person believes in any aspect that his/her rights are infringed on, he/she may file a complaint to the complaint handling office in writing or orally. In case of oral complaint, members of complaint handling office shall make detailed records. 2） Grievance Sorting, Processing, Investigation and Action The complaint handling office shall organize and sort complaints and investigate the cause and impact of grievance incidents as well as the responsible party. Based on the above investigation results, the complaint handling office will determine further actions to be taken and the time schedule for implementing the actions, determine measures to mitigate and address the impact of the incident, and meanwhile propose preventive measures to prevent occurrence of such incident and determine the channel of complaint and properly match with the channel. Complaints against environmental issues: grievance handling organization shall submit processing opinions within two weeks. Where the complainant is dissatisfied with the opinions of the complaint handling office, he/she may file a complaint to the county or municipal environmental protection bureau in writing within 1 month after the receipt of processing opinions; and relevant county or municipal environmental protection bureau 189 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report shall make processing opinions within the statutory time limit. Where the complainant is still dissatisfied with the processing opinions of county or municipal environmental protection bureau, he/she may file a complaint to its superior environmental protection authority after the receipt of processing opinions. Complaint against social issues: Phase 1: an affected person may raise his/her grievance to relevant village committee /community neighborhood committee or town government/ sub-district office through oral or written grievance. In case of oral grievance, the village committee/community neighborhood committee or village or town government/sub-district office must maintain a written records and shall make a clear reply within 2 weeks; Phase 2: In case of dissatisfaction with the processing decision made in Phase 1, the affected person may file an oral or written grievance to the town where the village is located after the receipt of the decision; in case of oral grievance, the town shall process and make written records. The town must make a processing decision within 2 weeks; Phase 3: where an affected person is still dissatisfied with the decision of the town, he/she may file a grievance to the complaint handling office of County PMO. County/District PMO shall make a processing decision within 2 weeks; Phase 4: In case of dissatisfaction with the decision of County/District PMO, after the receipt of the decision of PMO, he/she may file a grievance to provincial PMO. Provincial PMO shall make a processing decision within 2 weeks; Phase 5: In case of dissatisfaction with the processing result of provincial PMO, after the receipt of the decision of provincial PMO, he/she may file a lawsuit to civil court according to civil procedure act; where the affected person is still dissatisfied with the decision made in Phase 2, after the receipt of the decision, he/she may appeal to the administrative organ with jurisdiction level by level for arbitration according to the Administrative Procedure Law of PRC. Where the affected person is still dissatisfied with the arbitration decision, after the receipt of the arbitration decision, he/she may file a lawsuit to civil court according to the civil procedure law. 3） Monitoring and Tracking Grievance Regularly review feedback received, cases resolved and GR trends in Project management meetings. 190 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 4） Communication for Effective GRMs 8.3.4.3 Contents and Method of Reply to Grievance (1) Contents of reply ① Brief narration of the grievance of the complainant. ② Findings of investigation of facts. ③ National regulations, principles and standards on environmental protection ④ Processing opinions and specific basis. (2) Method of reply to grievance ① For complaint against individual phenomenon, reply shall be made in written materials directly delivered to the complainant. ② For frequent complaints, relevant village committee shall be notified through convening residents’ meeting or issuing documents. No matter which reply method is adopted, reply materials must be delivered to each County PMO. 8.3.4.4 Recording, Tracking and Feedback of Grievance and Complaint During project implementation and operation, each County PMO must properly carry out registration and management of complaint materials and processing results and submit such materials to provincial PMO in writing once a month. Provincial PMO shall check the processing and registration of complaints on a regular basis. In order to completely record the processing of complaints of complainants and relevant issues, County PMO developed a registration form for processing of complaints and grievances of complainants. The format of the registration form is specified in Table 8-3. Table 8-3 Registration form of complaints and grievances Receiving unit: Time: Place: Name of Content of Proposed Required solution Actual processing complainant: grievance resolution Complainant Recorder (signature) (signature) 191 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Note: 1. The recorder shall accurately record the contents and requirements of the grievance of complainant. 2. Grievance process shall not be subject to any interference and obstacles. 3. Proposed solution shall be sent to the complainant within the specified time. 8.3.4.5 Contact Details for Expressing Complaints and Grievances Each County PMO shall specifically arrange personnel to collect and process the complaints and grievances of complainants. Names, addresses and contact details of principals are listed in Table 8-4. Table 8-4 Information of Organizations and Personnel for Processing Complaints and Grievances of Complainants Organization for processing Contact Address Tel. complaints and grievances person Agricultural and Rural Work Yongding District PMO Hu Wenling 13637440869 Bureau of Yongding District Jishou City PMO Yang Jun No. 4, Beijixin Road, Jishou Ciyu 13574330547 Foreign Capital & Foreign Aid Chen PMO of Yongshun County, the Yongshun County PMO 13787433288 Shengshuang People’s Government of Yongshun County Yang Agricultural and Rural Work Cili County PMO 13974477800 Hongquan Bureau of Zhongfang County No. 108, Jianshe Middle Road, Huayuan County PMO Shi Junlin (+86-743) 7223811 Huayuan Town, Huayuan County Peng No. 194, Yingchun Road, Anhua Anhua County PMO 13787376160 Xiumiao County Liu No. 206, Zhengyang Avenue, Hengyang County PMO 13973415242 Kangxing Hengyang County Yin 208, Yunji Avenue, Hengnan Hengnan County PMO 13974721668 Xiangyang County No. 579, Wutong Road, Lengshuitan District PMO Wen Jun 15807480337 Lengshuitan District Chen Nearby Linwu County Linwu County PMO 13975595524 Xiangwu Government Wuxi Middle Road, Qiyang Qiyang County PMO Li Haiying +86-746-3222305 County, Yongzhou City 8.4 Environmental Management Training 8.4.1 Training Purpose The purpose of environmental management training is to ensure smooth and effective launch of environmental management work, enable relevant personnel to be familiar with 192 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report contents and procedures of environmental management, improve environmental management capacity of environmental management personnel and ensure effective implementation of each environmental protection measure and social risk prevention measures. The main object of environmental capacity construction is environmental and social managers. Training of environmental managers is a constituent part of technical support of the project. During the implementation of project, the training courses also train construction party and workers. Before commencement of project construction, all construction units and operation units are required to participate in mandatory environment, health and safety training. 8.4.2 Training Objects Training objects include all members of environmental management offices at each level (provincial, municipal and county-level), project owner, representatives of environmental monitoring organization, main construction party, project point implementation organization, representatives of planting households, etc. 8.4.3 Training Contents 1. Mastery and application of environmental policies of World Bank and domestic environmental protection laws and regulations as well as environmental standards; 2. Environmental management model of loan project of World Bank and environmental terms in loan agreement; 3. Project environmental management plan; 4. Project environmental management provisions; 5. Responsibilities and mutual relations of environmental management personnel, environmental monitoring personnel and contractor; 6. Environmental management work report and environmental monitoring report. 8.4.4 Environmental Management Training Plan and Fund Environmental management training and funds of “Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects)” are detailed in Table 8-5. 193 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-5 Table of Capacity Building and Training Plan Amount Serial Construction Unit price Unit Qty (10,000 Remarks No. content (Yuan) yuan) Ability enhancement 1 of government 2,093 Such work is uniformly officials implemented by provincial PMO. Person/ The training refers to domestic and 1.1 Abroad survey 711 5,500 391.05 foreign training mainly about day risk-based land management, Person/ monitoring of agricultural 1.2 Abroad training 1,018 5,500 559.9 day environment, prevention of Person/ pollution, and policy execution and 1.3 Domestic survey 7,080 1,100 778.8 compliance. The training objects are day provincial and county-level Person/ agriculture, environmental 1.4 Domestic training 7,265 500 363.25 protection and land and resources day departments, development and Training of reform commissions, financial agricultural departments and government Person/ 2 environment 7,200 500 360 officials recommended by other day organizations. monitoring personnel Person/ Training of framers in the 3 Training of farmers 178,150 100 1,781.5 day demonstration area Discussion and Promotion of project achievements, 4 promotion of / 930 information disclosure, publicity and achievements issuing of materials 8.5 Summary of Mitigation Measures for Environmental Impact See Table 8-6 for the summary of mitigation measures for the common environmental impacts of this Project; see Table 8-7 for the summary of the mitigation measures for the special environmental impacts of this Project. 194 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-6 List of Common Mitigation Measures for Environmental Impacts Implement Impact ation Supervision Potential impact Mitigation measures factors organizatio organization n ⚫ Select advanced and reliable low-noise equipment during equipment type selection; ⚫ Construction time shall be reasonably arranged and it is prohibited to construct during lunch break and at night; ⚫ Foundation damping treatment shall be conducted for machinery Environmental Noise during construction period mainly equipment generating relatively big noise, or vibration damping Protection includes noise from construction site and traffic support shall be set up to bind up damping materials; Department of noise during transport of materials. The noise ⚫ Noise generated during vehicle transport may have a certain impact on Hunan Acoustic County from construction site mainly includes noise acoustic environment sensitive points along the line. Transport time Province and environment PMO generated by construction machinery equipment shall be reasonably arranged and the quantity of cars and driving County and noise generated due to material loading, density in the construction area shall be compressed as much as Environmental unloading and collision. possible. Measures such as speed restriction and horning prohibition Protection shall be imposed on construction machinery such as vehicles; Bureau ⚫ All machinery equipment shall be effectively maintained and repaired on a regular basis to ensure that the equipment is in good condition and the purposes of noise reduction and extension of equipment use life are realized. ⚫ Most earthwork and stonework excavated from channels are used to During construction of irrigation facilities, field backfill for the purpose of land leveling and ridge building; field farm farm tracks and small civil engineering works, tracks are constructed around existing ridges and all earthworks are raising dust will be generated due to pavement reused in the field; Environmental excavation, transport, loading and unloading of ⚫ Activities such as roadbed excavation and filling shall be avoided Protection spoils, and site trimming and construction. during windy and rainy days; Department of Construction waste gases mainly refer to waste ⚫ Stacking and storage of powdery construction materials used in the Hunan Atmospheric County gases generated by fuel oil consuming project, such as cement, lime and sand, etc., shall be strictly managed Province and environment PMO construction machinery and tail gas generated by and the surfaces shall be covered. Watering measure shall be adopted County transport vehicles. The emission volume of these when necessary; Environmental pollutants is limited and usually only has a ⚫ Project construction shall be implemented in different sections and Protection certain impact on construction personnel. The different areas to reduce scope of raising dust; measures such as Bureau influence of such pollutants on regional watering shall be adopted to reduce pollution of raising dust; environment is very small. ⚫ Construction machinery and vehicles with good operating condition shall be selected and used; 195 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report ⚫ Overhaul and maintenance of construction vehicles shall be strengthened. It is strictly prohibited to use vehicles beyond the period of intended use and with tail gas exceeding the standard. Construction vehicles with low oil consumption and small exhaust shall be used as much as possible and high-quality fuel oil shall be selected and used as much as possible to reduce emission of hazardous gases from machinery and vehicles. ⚫ Channel construction shall be better conducted in non-irrigation period. Temporary water passage may be built when necessary; ⚫ Sedimentation basin shall be set up on construction site. The construction wastewater shall be collected and deposited through sedimentation basin and then reused for construction as much as possible; Construction production wastewater and ⚫ Temporary latrine pits are set up within construction site. Excrements Environmental domestic sewage are mainly included. are cleared on a regular basis and then used as farm manure according Protection Construction wastewater mainly includes to actual living conditions in rural regions; Department of concrete maintenance wastewater and aggregate ⚫ Construction management shall be strengthened and deflation, water Hunan Water flushing water. Although the volume of this part emission, liquid dripping and liquid leakage of construction County Province and environment of wastewater generated is small, it contains a machinery shall be strictly controlled; drainage system and water PMO County certain amount of oil contamination and conservancy measures shall be properly implemented in temporary Environmental sediments which may cause certain pollution to soil stacking area to prevent stacking of spoils from resulting in water Protection soil, surface water and underground water if not and soil loss to influence water environment; Bureau properly treated and discharged at will. ⚫ Each construction unit must implement each treatment measure for handling of construction production wastewater and domestic sewage to ensure that the wastewater is properly treated and disposed; ⚫ Environmental protection education for construction personnel shall be strengthened and environment awareness of construction personnel shall be improved. The construction personnel shall not throw or dump wastes and sewage at will. The main sources of solid wastes generated ⚫ The household garbage shall be collected using garbage cans and bags Environmental during construction period include foundation set up on construction site and then uniformly cleared and transported Protection excavation, spoil (slag) after backfilling, and to household garbage landfill in the towns where the project is located Department of County Solid waste household garbage generated by the construction for treatment and disposal; Hunan PMO personnel. If the building garbage generated ⚫ Spoil (slag) can be used for land leveling and backfill as well as Province and during construction period is not timely paving of road foundation without having to go far. No water slag County disposed, it will not only influence landscape but yard is separately set up in order to reduce land occupation. Environmental 196 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report also generate raising dust under windy and dry Protection weather conditions; if household garbage is not Bureau timely treated, mosquitoes will be bred, and stink will be generated and diseases will be spread under moderate temperature, which will have an adverse influence on surrounding environment. Once cultural relics and historic sites are discovered during construction process, relevant personnel shall immediately inform local cultural relics Cultural County Provincial preservation department and timely and properly protect the site. relics PMO PMO Construction can be resumed only after the cultural relics department properly handles the cultural relics and historic sites discovered. 197 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-7 Summary of Mitigation Measures of Specific Environment Sensitive Places Potential Specific environmental sensitive places environmental Mitigation measures influence ◆ Forbid the standard-exceeding rice to enter the grain market, and set up purchasing stations for special collection and storage; ◆ For rice with cadmium content >0.2mg/kg, sign contract with these companies including Baojing Tujiaren Brewery, Jishou Liquor Co., Ltd., Disposal of standard-exceeding rice: Yongshun Xiongge Wine Co., Ltd., Huayuan Malichang Winery, Xiangquan Winery, Jishou Liquor Co., Ltd, Wanping Risks and social Zhangjiajie Shengdi Liquor Co., Ltd., Huaihua Huangxi Daqu Wine Co., Luohu Winery, Zhangjiajie Shengdi Liquor Co., Ltd, impacts of improper Ltd., Anhua Qinglong Liquor Co., Ltd., Hunan Lingjiu Liquor Co., Ltd., Huayuan Malichang Winery, Anhua Qinglong Liquor Co., disposal of rice with Yizhang Baishidu Winery, Linwu Guyan Winery, Lengshuitan Yunxi Ltd, Hunan Dinggu Liquor Co., Ltd, Hunan Lingjiu Liquor standard-exceeding Liquor Co., Ltd., and Qiyang Qiongniang Liquor Co., Ltd. and so on. As a Co., Ltd, Lengshuitan Yunxi Liquor Co., Ltd, Linwu cadmium raw material for brewing, cadmium in rice is mainly enriched in Guyan Winery, Qiyang Qiongniang Liquor Company by-product, that is, vinasse. ◆ The by-product vinasse of rice with over-standard cadmium must be properly disposed by sanitary landfill or other measures. ◆ Develop subsidy programs to ensure that the income of farmers in the demonstration area will not be reduced. 198 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 8.6 Environmental Monitoring Plan 8.6.1 Purpose and Principle of Monitoring The purpose of establishment of environmental monitoring plan is to supervise the implementation of each measure so as to adjust environmental protection action plan according to monitoring results and provide basis for implementation time and implementation scheme of environmental protection measures. The purpose of environmental monitoring is to comprehensively and timely master the pollution trends of proposed Project, get to know the degree of change of local environmental quality due to Project construction, scope of influence and environmental quality trends during Project operation, and timely feedback information to the competent department so as to provide scientific basis for environmental management of the project. The environmental monitoring plan of the proposed Project can be uniformly entrusted by PMO of each project county. The entrusted party shall have monitoring qualification and shall take charge of acquiring and analyzing monitoring data, issuing environmental analysis report, and submitting the report to the entrusting unit which shall submit duplicate to the World Bank. The responsibilities of monitoring plan organization of the project are shown in Table 8-9 below. Table 8-9 List of responsibilities of monitoring plan organization Implemented item Responsible unit Local environmental monitoring station or company with Acquisition of monitoring data monitoring qualification is entrusted. Data analysis The monitoring unit is responsible for acquiring and analyzing data. Preparation of environmental The monitoring unit issues an analysis report according to report monitoring data. The above-mentioned monitoring plan can be uniformly entrusted by PMO of each project county. The entrusted environmental monitoring station shall sort and analyze monitoring data implemented, issue an environmental analysis report, and submit the report to the entrusting party which shall submit a duplicate to World Bank every quarter according to monitoring plan. After submission of environmental analysis report, PMO of each project county will uniformly manage and file the report as collected Management plan material indicating environmental impact in Project implementation stage for the purpose of Project completion acceptance. 199 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 8.6.2 Monitoring Organization The management organization is recommended to entrust local environmental monitoring station or social environmental monitoring organization with monitoring qualification to execute monitoring plan. The construction unit shall sign monitoring contract for construction period with the monitoring unit before construction, and sign monitoring contract for operation period with the monitoring unit before the project is put into use. 8.6.3 Environmental Monitoring Plan Sensitive points with relatively obvious pollution will be determined as monitoring points according to predicted results of environmental impact. Based on pollution conditions during Project implementation period, relatively significantly affected irrigation surface water body, soil, agricultural products, and organic fertilizers and pesticide applied are selected as monitoring contents. The monitoring factors are determined according to characterization factors of the project. Monitoring analysis method of relevant Project of the state is adopted. National standards determined during environmental impact assessment are executed as assessment standards. Project monitoring contents are determined according to characteristics of Project and environment. See Table 8-10~8-21。 1. Arrangement of Monitoring Point of Irrigation Surface Water Body (1). Point Arranging Principle Agricultural land irrigation water source detection points are set up in river sections around main irrigation water inlet of cultivated land in demonstration area, main irrigation water inlets of main canals/branch canals and small reservoir in each key reservoir level by level. Irrigation water drainage sampling is carried out at ground drain of demonstration area and irrigation water recession outlet. And dense points are set up near irrigation water outlets of "suspected key polluted water sources" and suspected inlets of new pollution . Under any circumstances, points must be set in the places where water body is well-mixed to ensure the representativeness of samples. Select or specifically set sample markers for easy identification at the determined sampling points and shores, and use GPS positioning 200 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report to ensure that the water samples are taken from the same location. (2). Monitoring Time and Frequency Monitoring year: Monitoring should be carried out in the first and third year of project implementation. Frequency: For single cropping rice, the monitoring frequency is three times in a year (single cropping rice: in May, July and September); For double cropping rice, the monitoring frequency is four times in a year (double cropping rice: in March, May, July and September). (3). Surface Water Monitoring Factors pH、Cd、Pb、As、Hg、Cr6+、CODCr、NH3-N、TP (one time only) 2. Monitoring of Sediment in Irrigation Water Source (1). Point Arranging Principle Set the sediment monitoring point at each detection point of the irrigation water sources on the agricultural lands, and make sure they are corresponded to the monitoring sampling points of irrigation surface water. Collect one sample at each sediment monitoring point. (2). Monitoring Time One time in the first year and one time at the end of the project implementation (evaluation of the implementation effect). (3). Monitoring Factors pH, total Cd, Pb, As, Hg, Cr, and water-soluble Cd. 3. Monitoring of Sediment in Sedimentation Basin (1). Point Arranging Principle One sample is acquired for each sedimentation basin using quartering method. (2). Monitoring Time Once a year. (3). Monitoring Factors pH, total Cd, Pb, As, Hg, Cr, and water-soluble Cd. 4. Arrangement of Soil Monitoring Points 201 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (1). Point Arranging Principle The monitoring points for soil and agricultural products shall be in accordance with the data requirements of “5+ mu” for each governance unit, and no less than 5 samples for each demonstration area. Grid method should be used for points setting, and typical plots with soil in good natural conditions, flat ground, relatively stable factors, and an area greater than 1300 ㎡ should be selected as monitoring and sampling sites. Sampling plots should not be set near residences, ditches, dunghills, waste piles and graves, as well as areas with subordinate landscape features such as slopes and marsh lands, and should be more than 50m away from roads or railways. Meanwhile, contaminated plots should not be deliberately avoided or approached. For orchards with straw returned, the soil and products are sampled and monitored in the same way. Monitoring Items and Frequency A. Soil monitoring in the entire demonstration area ① pH, available Cd: once a year. ② Total amount of Cd, As, Pb, Hg and Cr: monitored twice, that is, one time in the first year and one time at the end of the project implementation (for the evaluation of the implementation effect). ③ Organic matter and cation exchange capacity (CEC): monitored in the first year, only once. B. Soil monitoring in selected demonstration agricultural lands During the implementation process, two blocks (1,000 mu is appropriate for each block, and choose the high-risk area as far as possible) should be selected in the project counties as demonstration plots, where soil sampling and detection should be carried out in one-to-one correspondence with agricultural products. ① Detection items: pH, total amount of Cd, As, Pb, Hg and Cr, and available Cd. ② Detection frequency: single cropping rice: once a year; double-reason rice: twice a year. 5. Heavy Metal Detection of Agricultural Products (1). Sampling Principle 202 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report The sampling point of agricultural products shall be as correspondent to soil heavy metal monitoring sampling points as possible. More than five composite samples shall be acquired from every agricultural product. (2). Detection Time Samples should be taken at the harvest period, and the frequency is once a year for single cropping rice and twice a year for double cropping rice. (3). Monitoring Factors Cd, Pb, As, Hg, Cr. 6、Detection of Fertilizers and Other Agricultural Inputs (1). Compound and phosphate fertilizers ① Sampling Principle Three samples should be collected. ② Detection Time One time in first year. ③ Detection Factors Cd, Pb, As, Hg, Cr. (2). Organic Fertilizer ① Sampling Principle Three samples are acquired from each batch of organic fertilizers. ② Detection Time Before application, each batch of organic fertilizer should be detected. ③ Detection Factors Cd, Pb, As, Hg, Cr, easily-oxidized organic carbon and total carbon. (3) Other agricultural inputs such as lime, passivating agents, etc. ① Sampling Principle Three samples should be collected for each batch of passivating agents. ② Detection Time Before application, each batch of other agricultural inputs should be detected. ③ Detection Factors 203 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Cd, Pb, As, Hg, Cr. 7. Monitoring of Plant Diseases and Insect Pests (1). Use of pesticide Record types of pesticide used in Demonstration area as well as pesticide application frequency and dosage. The monitoring frequency is once a year; (2). Conditions of agricultural land ecosystem Monitor morbidity of plant diseases and insect pests, quantity of injurious insects and quantity of natural enemies; The monitoring frequency is 4 times per year (seedling period, adult-plant period, fruiting period, and harvesting and picking period); (3). Pesticide residues of crops Detect pesticide residues of agricultural products. More than five composite samples shall be acquired from each agricultural product with monitoring frequency of 1 time per year for each harvest season. 8. Balance Monitoring Set up project control plots based on the needs of the project implementation and cadmium balance analysis. The demonstration area of each town should have 5 control plots (hills), and the total area of each control plot (hill) should be more than 1300 ㎡, with the blank control area of less than 130 ㎡. (Build a strong soil layer in the control hill and reinforce it regularly to prevent the water in the areas where agronomic measures are taken from mixing into the blank control area. When agronomic measures are carried out in the control hill, professional agricultural technicians must be on site to direct the operation, so as not to produce concomitant effects on the blank control area). Soil: Collect 1 basic sample from each typical field, monitor it once a year, and detect Cd, As, Pb, Hg and Cr. Plants: sample number: products (rice and rice straw) are sampled once a season per hill, and the soil is sampled once a year per hill; for each time, the sample should be collected from both the demonstration area (non-blank control area) and the blank control area. 204 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Irrigation water: in the above-mentioned selected fields (2 hills in each demonstration area, altogether 6 hills) of balance monitoring point, one mixed sample should be collected each time the irrigation water enters, and 4 samples should be collected per hill every year (the sample should be collected from the inlets in field boundary where no cross-streaming or cross-irrigation exists). Dry and wet deposition of the atmosphere: conduct continuous monitoring for 3 years and collect the sample once every six months with the simple sedimentation tank collection method. Fertilizer: use the detection data of fertilizer monitoring to count the amount of heavy metals from the fertilizers in the field. 9. Monitoring of the By-product Vinasse of Wine-making by Rice with Over-standard Cadmium Monitor Cd, As, Pb, Hg and Cr; collect three samples from each batch of vinasses and conduct detection for each batch. The environmental monitoring plans for the 11 counties are detailed in Table 8-10 to Table 8-20. 205 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-10 Environmental Monitoring Plan of Yongding District Estimated Monitoring Monitoring Arrangement of monitoring point Executive standards and unit price Expense Monitoring Supervision Monitoring frequency item parameters positions (quantity) specifications (Yuan per (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for third year of project As、Hg、Cr6+、 demonstration area, main irrigation the Environment Quality Qualified Provincial Surface water implementation. CODCr、 water inlets of main canals/branch Monitoring of Water for 520 56,640 organization and county for irrigation Frequency: The monitoring NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted PMOs frequency in a year should (one time only) reservoir level by level. Irrigation (NY/T396-2000) be 3 times (single cropping water drainage sampling is carried out rice: May, July, at ground drain of demonstration area September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Technical Specification for Sediment of Pb, As, Hg, Cr, Qualified Provincial and make sure they are corresponded to stage of project Soil Environmental irrigation and 432 5,760 organization and county the monitoring sampling points of implementation (for the Monitoring water source water-soluble entrusted PMOs irrigation surface water. Collect one evaluation of the (HJ/T 166-2004) Cd. sample at each sediment monitoring implementation effect). point. Technical Specification for Sediment in pH, Cd, Pb, As, Collect one sample in each Qualified Provincial Soil Environmental sedimentation Hg, Cr, sedimentation basin by method of Once a year 432 15,552 organization and county Monitoring basin available Cd quartering entrusted PMOs (HJ/T 166-2004) pH, available The monitoring points for soil and Once a year 100 60,400 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first Technical Specification for Qualified Provincial of 5+ mu for each governance unit, and year, and one at the final Soil Total amount Soil Environmental organization and county no less than 5 samples for each stage of project Cd, Pb, As, Hg, Monitoring (HJ/T 166-2004) 300 60,400 entrusted PMOs demonstration area. Grid method implementation (for the Cr should be used for points setting, and evaluation of the typical plots with good natural implementation effect). 206 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report conditions, flat ground, relatively Organic matter stable factors, and an area greater than Only once in the first year 100 10,066.67 and CEC 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Soil of pH, total Cd, Samples should be taken at Technical Specification for Qualified Provincial the the high-risk area as far as possible) demonstration As, Pb, Hg, Cr, harvest season, once a year Soil Environmental 418.5 33,480 organization and county and set a point every 30-50 mu in the field available Cd for single cropping rice Monitoring (HJ/T 166-2004) entrusted PMOs mountainous area, and every 50-100 mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); National Standards for Food The product sampling point should Samples should be taken at Safety: Determination of correspond to the monitoring sampling harvest season, once per Total Mercury and Organic Qualified Provincial Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as harvest season in a year and Mercury in Foods (GB 352 212,608 organization and county products Cr possible, and more than five mixed –once a year for single 5009.17-2014); National entrusted PMOs samples should be collected for each cropping rice. Standards for Food Safety: sample. Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified Provincial compound and Cd, Pb, As, Hg, Collect three samples Only once in the first year / 500 500 organization and county phosphate Cr entrusted PMOs fertilizers Organic Cd, Pb, As, Hg, Collect three samples for each batch of The cadmium content of the Qualified Provincial Twice a year 500 6,000 fertilizer Cr fertilizers. organic fertilizer should be organization and county 207 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report detection controlled below 1mg/kg, entrusted PMOs and the proportion of easily-oxidized organic carbon content in total carbon content should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified Provincial inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per / 500 6,000 organization and county lime, Cr passivating agents. purchase batch. entrusted PMOs passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate of pesticides; Monitoring in each demonstration area pests and diseases, number incidence rate Monitoring of should be focused on agricultural of pests and their natural National Standards for Food of pests and Qualified Provincial plant diseases products, and more than five samples enemies should be Safety: Maximum Residue diseases, / 100,000 organization and county and insect of each agricultural product should be monitored once a year. The Limit of Pesticide in Foods number of pests entrusted PMOs pests collected for detection of pesticide amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per harvest agricultural season every year. product output and pesticide residues Balance Soil: Cd, As, Set 2 representative demonstration One basic sample is Technical Specification for Qualified Provincial 300 3,600 monitoring Pb, Hg and Cr areas, and select 3 typical fields in each collected for each typical Soil Environmental organization and county 208 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report demonstration area. field, once a year. Monitoring (HJ/T 166-2004) entrusted PMOs Collect the above-ground part of rice in Qualified Provincial Plants: Cd, As, 3 to 5 samples, once a year mature stage, with 5 to 7 pieces for / 352 3,520 organization and county Pb, Hg and Cr for single cropping rice each sample. entrusted PMOs Irrigation Technical Specification for water: pH、Cd、 the Environment Quality Qualified Provincial Collect one mixed sample of each Pb、As、Hg、 Collect 8 samples each year Monitoring of Water for 472 7,552 organization and county irrigation water intake. Cr6+、CODCr、 Agricultural Use entrusted PMOs NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring for (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified Provincial 2 years, collecting one Specifications for deposition of demonstration area, and there are two 600 3,200 organization and county sample every 3 months in a Environmental Air Quality the atmosphere points in total. entrusted PMOs year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product vinasse of Qualified Provincial Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each wine-making / 500 6,000 organization and county Cr vinasse. batch by rice with entrusted PMOs over-standard Cadmium 501300 Sub-total Yuan 78300 Sampling expense and others Yuan 579600 Total monitoring expense Yuan 209 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-11 Environmental Monitoring Plan of Jishou City Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified Surface water implementation. Provincial and CODCr、 water inlets of main canals/branch Monitoring of Water for 520 21,800 organization for irrigation Frequency: The county PMOs NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: May, at ground drain of demonstration area July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Technical Specification for Sediment of Pb, As, Hg, Cr, Qualified and make sure they are corresponded to stage of project Soil Environmental Provincial and irrigation and 432 6,460 organization the monitoring sampling points of implementation (for the Monitoring county PMOs water source water-soluble entrusted irrigation surface water. Collect one evaluation of the (HJ/T 166-2004) Cd. sample at each sediment monitoring implementation effect). point. Technical Specification for Sediment in pH, Cd, Pb, As, Collect one sample in each Qualified Soil Environmental Provincial and sedimentation Hg, Cr, sedimentation basin by method of Once a year 432 6,164 organization Monitoring county PMOs basin available Cd quartering entrusted (HJ/T 166-2004) pH, available The monitoring points for soil and Once a year 100 22,400 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first year, and one at the final Technical Specification for Total amount of 5+ mu for each governance unit, and Qualified Provincial and Soil no less than 5 samples for each stage of project Soil Environmental organization Cd, Pb, As, Hg, 300 22,400 county PMOs demonstration area. Grid method implementation (for the Monitoring (HJ/T 166-2004) entrusted Cr should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively Only once in the first year 100 7,900 210 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report and CEC stable factors, and an area greater than 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Qualified the the high-risk area as far as possible) at harvest season, once a Provincial and demonstration As, Pb, Hg, Cr, Soil Environmental 418.5 25,110 organization and set a point every 30-50 mu in the year for single cropping county PMOs field available Cd Monitoring (HJ/T 166-2004) entrusted mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); National Standards for Food The product sampling point should Samples should be taken Safety: Determination of Total correspond to the monitoring sampling at harvest season, once per Mercury and Organic Qualified Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as Provincial and harvest season in a year Mercury in Foods (GB 352 166,848 organization products Cr possible, and more than five mixed county PMOs and –once a year for single 5009.17-2014); National entrusted samples should be collected for each cropping rice. Standards for Food Safety: sample. Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified compound Cd, Pb, As, Hg, Provincial and Collect three samples Only once in the first year / 500 375 organization and phosphate Cr county PMOs entrusted fertilizers Organic The cadmium content of the Qualified Cd, Pb, As, Hg, Collect three samples for each batch of Provincial and fertilizer Twice a year organic fertilizer should be 500 4,500 organization Cr fertilizers. county PMOs detection controlled below 1mg/kg, and entrusted 211 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report the proportion of easily-oxidized organic carbon content in total carbon content should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per Provincial and / 500 4,500 organization lime, Cr passivating agents. purchase batch. county PMOs entrusted passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring of should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified plant diseases products, and more than five samples natural enemies should be Safety: Maximum Residue Provincial and diseases, / 7,500 organization and insect of each agricultural product should be monitored once a year. Limit of Pesticide in Foods county PMOs number of pests entrusted pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Qualified Soil: Cd, As, Provincial and Balance areas, and select 3 typical fields in each collected for each typical Soil Environmental 300 2,700 organization Pb, Hg and Cr county PMOs monitoring demonstration area. field, once a year. Monitoring (HJ/T 166-2004) entrusted Plants: Cd, As, Collect the above-ground part of rice in 3 to 5 samples, once a year / 352 2,640 Qualified Provincial and 212 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Pb, Hg and Cr mature stage, with 5 to 7 pieces for for single cropping rice organization county PMOs each sample. entrusted Irrigation Technical Specification for the water: pH、Cd、 Environment Quality Qualified Collect one mixed sample of each Collect 8 samples each Provincial and Pb、As、Hg、 Monitoring of Water for 472 5,664 organization irrigation water intake. year county PMOs Cr6+、CODCr、 Agricultural Use entrusted NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring for (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified 2 years, collecting one Specifications for Provincial and deposition of demonstration area, and there are two 600 2,400 organization sample every 3 months in Environmental Air Quality county PMOs the atmosphere points in total. entrusted a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product vinasse of Qualified Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each Hygienic Standard for Feeds Provincial and wine-making 500 4,500 organization Cr vinasse. batch (GB 13078-2001) county PMOs by rice with entrusted over-standard Cadmium 231400 Sub-total Yuan 58700 Sampling expense and others Yuan 290100 Total monitoring expense Yuan 213 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-12 Environmental Monitoring Plan of Yongshun County Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified Surface water implementation. Provincial and CODCr、 water inlets of main canals/branch Monitoring of Water for 520 26,820 organization for irrigation Frequency: The county PMOs NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified and make sure they are corresponded to stage of project Provincial and irrigation and Environmental Monitoring 432 8,004 organization the monitoring sampling points of implementation (for the county PMOs water source water-soluble (HJ/T 166-2004) entrusted irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial and sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 2,592 organization county PMOs basin available Cd quartering (HJ/T 166-2004) entrusted pH, available The monitoring points for soil and Once a year 100 41,650 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Total amount Technical Specification for Soil Qualified no less than 5 samples for each stage of project Provincial and Soil Cd, Pb, As, Hg, Environmental Monitoring 300 41,650 organization demonstration area. Grid method implementation (for the county PMOs Cr (HJ/T 166-2004) entrusted should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively stable factors, and an area greater than Only once in the first year 100 7,775 and CEC 214 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Soil Qualified the the high-risk area as far as possible) at harvest season, once a Provincial and demonstration As, Pb, Hg, Cr, Environmental Monitoring 418.5 37,665 organization and set a point every 30-50 mu in the year for single cropping county PMOs field available Cd (HJ/T 166-2004) entrusted mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as Provincial and per harvest season in a Mercury and Organic Mercury 352 136,708 organization products Cr possible, and more than five mixed county PMOs year and –once a year for in Foods (GB 5009.17-2014); entrusted samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified compound and Cd, Pb, As, Hg, Provincial and Collect three samples Only once in the first year / 500 375 organization phosphate Cr county PMOs entrusted fertilizers The cadmium content of the organic fertilizer should be Organic Qualified Cd, Pb, As, Hg, Collect three samples for each batch of controlled below 1mg/kg, and Provincial and fertilizer Twice a year 500 4,500 organization Cr fertilizers. the proportion of county PMOs detection entrusted easily-oxidized organic carbon content in total carbon content 215 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per Provincial and / 500 4,500 organization lime, Cr passivating agents. purchase batch. county PMOs entrusted passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring of should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified plant diseases products, and more than five samples natural enemies should be Safety: Maximum Residue Provincial and diseases, / 7,500 organization and insect of each agricultural product should be monitored once a year. Limit of Pesticide in Foods county PMOs number of pests entrusted pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Soil: Cd, As, Provincial and areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 2,700 organization Pb, Hg and Cr county PMOs demonstration area. field, once a year. (HJ/T 166-2004) entrusted Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Plants: Cd, As, Provincial and monitoring mature stage, with 5 to 7 pieces for year for single cropping / 352 2,640 organization Pb, Hg and Cr county PMOs each sample. rice entrusted Irrigation Collect one mixed sample of each Collect 8 samples each Technical Specification for the Qualified Provincial and 472 5,664 water: pH、Cd、 irrigation water intake. year Environment Quality organization county PMOs 216 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Pb、As、Hg、 Monitoring of Water for entrusted Cr6+、CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified for 2 years, collecting one Specifications for Provincial and deposition of demonstration area, and there are two 600 2,400 organization sample every 3 months in Environmental Air Quality county PMOs the atmosphere points in total. entrusted a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product vinasse of Qualified Cd, As, Pb, Hg, Collect three samples for each batch of Hygienic Standard for Provincial and wine-making Monitor once for each batch 500 4,500 organization Cr vinasse. Feeds (GB 13078-2001) county PMOs by rice with entrusted over-standard Cadmium 337700 Sub-total Yuan 48500 Sampling expense and others Yuan 386200 Total monitoring expense Yuan 217 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-13 Environmental Monitoring Plan of Cili County Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified Surface water implementation. Provincial and CODCr、 water inlets of main canals/branch Monitoring of Water for 520 86,820 organization for irrigation Frequency: The county PMOs NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified and make sure they are corresponded to stage of project Provincial and irrigation and Environmental Monitoring 432 17,504 organization the monitoring sampling points of implementation (for the county PMOs water source water-soluble (HJ/T 166-2004) entrusted irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial and sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 2,592 organization county PMOs basin available Cd quartering (HJ/T 166-2004) entrusted pH, available The monitoring points for soil and Once a year 100 76,100 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Total amount Technical Specification for Soil Qualified no less than 5 samples for each stage of project Provincial and Soil Cd, Pb, As, Hg, Environmental Monitoring 300 76,100 organization demonstration area. Grid method implementation (for the county PMOs Cr (HJ/T 166-2004) entrusted should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively stable factors, and an area greater than Only once in the first year 100 5,600 and CEC 218 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Soil Qualified the the high-risk area as far as possible) at harvest season, once a Provincial and demonstration As, Pb, Hg, Cr, Environmental Monitoring 418.5 37,665 organization and set a point every 30-50 mu in the year for single cropping county PMOs field available Cd (HJ/T 166-2004) entrusted mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as Provincial and per harvest season in a Mercury and Organic Mercury 352 118,272 organization products Cr possible, and more than five mixed county PMOs year and –once a year for in Foods (GB 5009.17-2014); entrusted samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified compound and Cd, Pb, As, Hg, Provincial and Collect three samples Only once in the first year / 500 375 organization phosphate Cr county PMOs entrusted fertilizers The cadmium content of the organic fertilizer should be Organic Qualified Cd, Pb, As, Hg, Collect three samples for each batch of controlled below 1mg/kg, and Provincial and fertilizer Twice a year 500 4,500 organization Cr fertilizers. the proportion of county PMOs detection entrusted easily-oxidized organic carbon content in total carbon content 219 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per Provincial and / 500 4,500 organization lime, Cr passivating agents. purchase batch. county PMOs entrusted passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring of should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified plant diseases products, and more than five samples natural enemies should be Safety: Maximum Residue Provincial and diseases, / 7,500 organization and insect of each agricultural product should be monitored once a year. Limit of Pesticide in Foods county PMOs number of pests entrusted pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Soil: Cd, As, Provincial and areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 2,700 organization Pb, Hg and Cr county PMOs demonstration area. field, once a year. (HJ/T 166-2004) entrusted Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Plants: Cd, As, Provincial and monitoring mature stage, with 5 to 7 pieces for year for single cropping / 352 2,640 organization Pb, Hg and Cr county PMOs each sample. rice entrusted Irrigation Collect one mixed sample of each Collect 8 samples each Technical Specification for the Qualified Provincial and 472 5,664 water: pH、Cd、 irrigation water intake. year Environment Quality organization county PMOs 220 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Pb、As、Hg、 Monitoring of Water for entrusted Cr6+、CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified for 2 years, collecting one Specifications for Provincial and deposition of demonstration area, and there are two 600 2,400 organization sample every 3 months in Environmental Air Quality county PMOs the atmosphere points in total. entrusted a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product vinasse of Qualified Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each Hygienic Standard for Feeds Provincial and wine-making 500 4,500 organization Cr vinasse. batch (GB 13078-2001) county PMOs by rice with entrusted over-standard Cadmium 455400 Sub-total Yuan 73500 Sampling expense and others Yuan 528900 Total monitoring expense Yuan 221 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 9-14 Environmental Monitoring Plan of Huayuan County Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project Surface As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified implementation. Provincial and water for CODCr、 water inlets of main canals/branch Monitoring of Water for 520 49,920 organization Frequency: The county PMOs irrigation NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified and make sure they are corresponded to stage of project Provincial and irrigation and Environmental Monitoring 432 17,280 organization the monitoring sampling points of implementation (for the county PMOs water source water-soluble (HJ/T 166-2004) entrusted irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial and sedimentatio Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 25,920 organization county PMOs n basin available Cd quartering (HJ/T 166-2004) entrusted pH, available The monitoring points for soil and Once a year 100 34,650 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Total amount Technical Specification for Soil Qualified no less than 5 samples for each stage of project Provincial and Soil Cd, Pb, As, Hg, Environmental Monitoring 300 34,650 organization demonstration area. Grid method implementation (for the county PMOs Cr (HJ/T 166-2004) entrusted should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively Only once in the first year 100 5,775 and CEC stable factors, and an area greater than 222 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Soil Qualified the the high-risk area as far as possible) at harvest season, once a Provincial and demonstratio As, Pb, Hg, Cr, Environmental Monitoring 418.5 20,925 organization and set a point every 30-50 mu in the year for single cropping county PMOs n field available Cd (HJ/T 166-2004) entrusted mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as Provincial and per harvest season in a Mercury and Organic Mercury 352 121,968 organization products Cr possible, and more than five mixed county PMOs year and –once a year for in Foods (GB 5009.17-2014); entrusted samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of compound Qualified Cd, Pb, As, Hg, Provincial and and Collect three samples Only once in the first year / 500 375 organization Cr county PMOs phosphate entrusted fertilizers The cadmium content of the Organic organic fertilizer should be Qualified Cd, Pb, As, Hg, Collect three samples for each batch of Provincial and fertilizer Twice a year controlled below 1mg/kg, and 500 4,500 organization Cr fertilizers. county PMOs detection the proportion of entrusted easily-oxidized organic carbon 223 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report content in total carbon content should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified inputs such Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per Provincial and / 500 4,500 organization as lime, Cr passivating agents. purchase batch. county PMOs entrusted passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified of plant products, and more than five samples natural enemies should be Safety: Maximum Residue Provincial and diseases, / 7,500 organization diseases and of each agricultural product should be monitored once a year. Limit of Pesticide in Foods county PMOs number of pests entrusted insect pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Soil: Cd, As, Provincial and areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 2,700 organization Pb, Hg and Cr county PMOs demonstration area. field, once a year. (HJ/T 166-2004) entrusted Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified monitoring Plants: Cd, As, mature stage, with 5 to 7 pieces for year for single cropping / 352 2,640 organization Provincial and Pb, Hg and Cr county PMOs each sample. rice entrusted Irrigation Collect one mixed sample of each Collect 8 samples each Technical Specification for the 472 5,664 Qualified Provincial and 224 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report water: pH、Cd、irrigation water intake. year Environment Quality organization county PMOs Pb、As、Hg、 Monitoring of Water for entrusted Cr6+、CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified for 2 years, collecting one Specifications for Provincial and deposition of demonstration area, and there are two 600 2,400 organization sample every 3 months in Environmental Air Quality county PMOs the atmosphere points in total. entrusted a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product vinasse of Qualified Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each Provincial and wine-makin / 500 4,500 organization Cr vinasse. batch county PMOs g by rice entrusted with over-standar d Cadmium 345900 Sub-total Yuan 101400 Sampling expense and others Yuan 447300 Total monitoring expense Yuan 225 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 9-15 Environmental Monitoring Plan of Anhua County Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified Provincial Surface water implementation. CODCr、 water inlets of main canals/branch Monitoring of Water for 520 46,800 organization and county for irrigation Frequency: The NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted PMOs monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified Provincial and make sure they are corresponded to stage of project irrigation and Environmental Monitoring 432 4,320 organization and county the monitoring sampling points of implementation (for the water source water-soluble (HJ/T 166-2004) entrusted PMOs irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 11,664 organization and county basin available Cd quartering (HJ/T 166-2004) entrusted PMOs pH, available The monitoring points for soil and Once a year 100 37,050 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Total amount Technical Specification for Soil Qualified Provincial no less than 5 samples for each stage of project Soil Cd, Pb, As, Hg, Environmental Monitoring 300 37,050 organization and county demonstration area. Grid method implementation (for the Cr (HJ/T 166-2004) entrusted PMOs should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively Only once in the first year 100 6,175 and CEC stable factors, and an area greater than 226 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Soil Qualified Provincial the the high-risk area as far as possible) at harvest season, once a demonstratio As, Pb, Hg, Cr, Environmental Monitoring 418.5 25,110 organization and county and set a point every 30-50 mu in the year for single cropping n field available Cd (HJ/T 166-2004) entrusted PMOs mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Provincial Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as per harvest season in a Mercury and Organic Mercury 352 130,416 organization and county products Cr possible, and more than five mixed year and –once a year for in Foods (GB 5009.17-2014); entrusted PMOs samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of compound Qualified Provincial Cd, Pb, As, Hg, and Collect three samples Only once in the first year / 500 375 organization and county Cr phosphate entrusted PMOs fertilizers The cadmium content of the Organic organic fertilizer should be Qualified Provincial Cd, Pb, As, Hg, Collect three samples for each batch of fertilizer Twice a year controlled below 1mg/kg, and 500 4,500 organization and county Cr fertilizers. detection the proportion of entrusted PMOs easily-oxidized organic carbon 227 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report content in total carbon content should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified Provincial inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per / 500 4,500 organization and county lime, Cr passivating agents. purchase batch. entrusted PMOs passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring of should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified Provincial plant diseases products, and more than five samples natural enemies should be Safety: Maximum Residue diseases, / 7,500 organization and county and insect of each agricultural product should be monitored once a year. Limit of Pesticide in Foods number of pests entrusted PMOs pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Provincial Soil: Cd, As, areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 2,700 organization and county Pb, Hg and Cr demonstration area. field, once a year. (HJ/T 166-2004) entrusted PMOs Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Provincial monitoring Plants: Cd, As, mature stage, with 5 to 7 pieces for year for single cropping / 352 2,640 organization and county Pb, Hg and Cr each sample. rice entrusted PMOs Irrigation Collect one mixed sample of each Collect 8 samples each Technical Specification for the 472 5,664 Qualified Provincial 228 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report water: pH、Cd、irrigation water intake. year Environment Quality organization and county Pb、As、Hg、 Monitoring of Water for entrusted PMOs Cr6+、CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified Provincial for 2 years, collecting one Specifications for deposition of demonstration area, and there are two 600 2,400 organization and county sample every 3 months in Environmental Air Quality the atmosphere points in total. entrusted PMOs a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product Qualified Provincial vinasse of Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each Hygienic Standard for Feeds 500 4,500 organization and county wine-making Cr vinasse. batch (GB 13078-2001) entrusted PMOs by rice with over-standard Cadmium 333400 Sub-total Yuan 101300 Sampling expense and others Yuan 434700 Total monitoring expense Yuan 229 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 9-7 Environmental Monitoring Plan of Hengyang County Estimated Monitoring Monitoring Arrangement of monitoring point Executive standards and unit price Expense Monitoring Supervision Monitoring frequency item parameters positions (quantity) specifications (Yuan per (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified Provincial Surface water implementation. CODCr、 water inlets of main canals/branch Monitoring of Water for 520 31,500 organization and county for irrigation Frequency: The NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted PMOs monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified Provincial and make sure they are corresponded to stage of project irrigation and Environmental Monitoring 432 6,000 organization and county the monitoring sampling points of implementation (for the water source water-soluble (HJ/T 166-2004) entrusted PMOs irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 32,400 organization and county basin available Cd quartering (HJ/T 166-2004) entrusted PMOs pH, available The monitoring points for soil and Once a year 100 62,300 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first Technical Specification for Soil Qualified Provincial of 5+ mu for each governance unit, and year, and one at the final Soil Total amount Environmental Monitoring organization and county no less than 5 samples for each stage of project Cd, Pb, As, Hg, (HJ/T 166-2004) 300 62,300 entrusted PMOs demonstration area. Grid method implementation (for the Cr should be used for points setting, and evaluation of the typical plots with good natural implementation effect). 230 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report conditions, flat ground, relatively Organic matter stable factors, and an area greater than Only once in the first year 100 5,900 and CEC 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Soil Qualified Provincial the the high-risk area as far as possible) at harvest season, once a demonstration As, Pb, Hg, Cr, Environmental Monitoring 418.5 11,000 organization and county and set a point every 30-50 mu in the year for single cropping field available Cd (HJ/T 166-2004) entrusted PMOs mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Provincial Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as per harvest season in a Mercury and Organic Mercury 352 398,100 organization and county products Cr possible, and more than five mixed year and –once a year for in Foods (GB 5009.17-2014); entrusted PMOs samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified Provincial compound Cd, Pb, As, Hg, Collect three samples Only once in the first year / 500 2,000 organization and county and phosphate Cr entrusted PMOs fertilizers The cadmium content of the Organic Qualified Provincial Cd, Pb, As, Hg, Collect three samples for each batch of organic fertilizer should be fertilizer Twice a year 500 6,000 organization and county Cr fertilizers. controlled below 1mg/kg, and detection entrusted PMOs the proportion of 231 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report easily-oxidized organic carbon content in total carbon content should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified Provincial inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per / 500 3,500 organization and county lime, Cr passivating agents. purchase batch. entrusted PMOs passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring of should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified Provincial plant diseases products, and more than five samples natural enemies should be Safety: Maximum Residue diseases, / 7,500 organization and county and insect of each agricultural product should be monitored once a year. Limit of Pesticide in Foods number of pests entrusted PMOs pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Provincial Soil: Cd, As, areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 2,800 organization and county Pb, Hg and Cr Balance demonstration area. field, once a year. (HJ/T 166-2004) entrusted PMOs monitoring Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Provincial Plants: Cd, As, mature stage, with 5 to 7 pieces for year for single cropping / 352 2,800 organization and county Pb, Hg and Cr each sample. rice entrusted PMOs 232 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Irrigation Technical Specification for the water: pH、Cd、 Environment Quality Qualified Provincial Collect one mixed sample of each Collect 8 samples each Pb、As、Hg、 Monitoring of Water for 472 4,500 organization and county irrigation water intake. year Cr6+、CODCr、 Agricultural Use entrusted PMOs NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified Provincial for 2 years, collecting one Specifications for deposition of demonstration area, and there are two 600 3,600 organization and county sample every 3 months in Environmental Air Quality the atmosphere points in total. entrusted PMOs a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product vinasse of Qualified Provincial Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each wine-making / 500 3,000 organization and county Cr vinasse. batch by rice with entrusted PMOs over-standard Cadmium 645200 Sub-total Yuan 148000 Sampling expense and others Yuan 793200 Total monitoring expense Yuan 233 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 9-8 Environmental Monitoring Plan of Hengnan County Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified Provincial Surface water implementation. CODCr、 water inlets of main canals/branch Monitoring of Water for 520 82,500 organization and county for irrigation Frequency: The NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted PMOs monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified Provincial and make sure they are corresponded stage of project irrigation and Environmental Monitoring 432 23,000 organization and county to the monitoring sampling points of implementation (for the water source water-soluble (HJ/T 166-2004) entrusted PMOs irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 119,000 organization and county basin available Cd quartering (HJ/T 166-2004) entrusted PMOs pH, available The monitoring points for soil and Once a year 100 72,000 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Total amount Technical Specification for Soil Qualified Provincial no less than 5 samples for each stage of project Soil Cd, Pb, As, Hg, Environmental Monitoring 300 72,000 organization and county demonstration area. Grid method implementation (for the Cr (HJ/T 166-2004) entrusted PMOs should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively Only once in the first year 100 12,000 and CEC stable factors, and an area greater than 234 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Soil Qualified Provincial the the high-risk area as far as possible) at harvest season, once a demonstration As, Pb, Hg, Cr, Environmental Monitoring 418.5 30,750 organization and county and set a point every 30-50 mu in the year for single cropping field available Cd (HJ/T 166-2004) entrusted PMOs mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Provincial Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as per harvest season in a Mercury and Organic Mercury 352 348,300 organization and county products Cr possible, and more than five mixed year and –once a year for in Foods (GB 5009.17-2014); entrusted PMOs samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified Provincial compound and Cd, Pb, As, Hg, Collect three samples Only once in the first year / 500 1000 organization and county phosphate Cr entrusted PMOs fertilizers The cadmium content of the organic fertilizer should be Organic Qualified Provincial Cd, Pb, As, Hg, Collect three samples for each batch of controlled below 1mg/kg, and fertilizer Twice a year 500 6,625 organization and county Cr fertilizers. the proportion of detection entrusted PMOs easily-oxidized organic carbon content in total carbon content 235 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified Provincial inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per / 500 6,625 organization and county lime, Cr passivating agents. purchase batch. entrusted PMOs passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring of should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified Provincial plant diseases products, and more than five samples natural enemies should be Safety: Maximum Residue diseases, / 15,000 organization and county and insect of each agricultural product should be monitored once a year. Limit of Pesticide in Foods number of pests entrusted PMOs pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Provincial Soil: Cd, As, areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 3,950 organization and county Pb, Hg and Cr demonstration area. field, once a year. (HJ/T 166-2004) entrusted PMOs Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Provincial Plants: Cd, As, monitoring mature stage, with 5 to 7 pieces for year for single cropping / 352 3,875 organization and county Pb, Hg and Cr each sample. rice entrusted PMOs Irrigation Collect one mixed sample of each Collect 8 samples each Technical Specification for the Qualified Provincial 472 8,325 water: pH、Cd、 irrigation water intake. year Environment Quality organization and county 236 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Pb、As、Hg、 Monitoring of Water for entrusted PMOs Cr6+、CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified Provincial for 2 years, collecting one Specifications for deposition of demonstration area, and there are two 600 3,525 organization and county sample every 3 months in Environmental Air Quality the atmosphere points in total. entrusted PMOs a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Fertilizer Use the detection data of fertilizers / / organization / entrusted Monitoring of the by-product vinasse of Qualified Provincial Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each Hygienic Standard for Feeds wine-making 500 6,525 organization and county Cr vinasse. batch (GB 13078-2001) by rice with entrusted PMOs over-standard Cadmium 815000 Sub-total Yuan 184800 Sampling expense and others Yuan 999800 Total monitoring expense Yuan 237 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 9-9 Environmental Monitoring Plan of Lengshuitan District Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in Technical Specification for the third year of project As、Hg、Cr 、 6+ demonstration area, main irrigation Environment Quality Qualified Surface water implementation. Provincial and CODCr、 water inlets of main canals/branch Monitoring of Water for 520 51,200 organization for irrigation Frequency: The county PMOs NH3-N、TP canals and small reservoir in each key Agricultural Use entrusted monitoring frequency in a (one time only) reservoir level by level. Irrigation (NY/T396-2000) year should be 3 times water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July, September). and irrigation water recession outlet. Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified and make sure they are corresponded to stage of project Provincial and irrigation and Environmental Monitoring 432 8,000 organization the monitoring sampling points of implementation (for the county PMOs water source water-soluble (HJ/T 166-2004) entrusted irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial and sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 45,000 organization county PMOs basin available Cd quartering (HJ/T 166-2004) entrusted pH, available The monitoring points for soil and Once a year 100 65,100 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Total amount Technical Specification for Soil Qualified no less than 5 samples for each stage of project Provincial and Soil Cd, Pb, As, Hg, Environmental Monitoring 300 65,100 organization demonstration area. Grid method implementation (for the county PMOs Cr (HJ/T 166-2004) entrusted should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively Only once in the first year 100 5,600 and CEC stable factors, and an area greater than 238 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1300 ㎡ should be selected as monitoring and sampling sites. Choose two blocks (1,000 mu is appropriate for each block, and select Samples should be taken Soil of pH, total Cd, Technical Specification for Soil Qualified the the high-risk area as far as possible) at harvest season, once a Provincial and demonstration As, Pb, Hg, Cr, Environmental Monitoring 418.5 10,800 organization and set a point every 30-50 mu in the year for single cropping county PMOs field available Cd (HJ/T 166-2004) entrusted mountainous area, and every 50-100 rice mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as Provincial and per harvest season in a Mercury and Organic Mercury 352 401,900 organization products Cr possible, and more than five mixed county PMOs year and –once a year for in Foods (GB 5009.17-2014); entrusted samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified compound and Cd, Pb, As, Hg, Provincial and Collect three samples Only once in the first year / 500 2,000 organization phosphate Cr county PMOs entrusted fertilizers The cadmium content of the organic fertilizer should be Organic Qualified Cd, Pb, As, Hg, Collect three samples for each batch of controlled below 1mg/kg, and Provincial and fertilizer Twice a year 500 8,000 organization Cr fertilizers. the proportion of county PMOs detection entrusted easily-oxidized organic carbon content in total carbon content 239 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per Provincial and / 500 5,000 organization lime, Cr passivating agents. purchase batch. county PMOs entrusted passivating agents, etc. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate Monitoring of should be focused on agricultural number of pests and their National Standards for Food of pests and Qualified plant diseases products, and more than five samples natural enemies should be Safety: Maximum Residue Provincial and diseases, / 7,500 organization and insect of each agricultural product should be monitored once a year. Limit of Pesticide in Foods county PMOs number of pests entrusted pests collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Soil: Cd, As, Provincial and areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 3,000 organization Pb, Hg and Cr county PMOs demonstration area. field, once a year. (HJ/T 166-2004) entrusted Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Plants: Cd, As, Provincial and monitoring mature stage, with 5 to 7 pieces for year for single cropping / 352 2,600 organization Pb, Hg and Cr county PMOs each sample. rice entrusted irrigation water: Collect one mixed sample of each Collect 8 samples each Technical Specification for the Qualified Provincial and 472 5,600 pH、Cd、Pb、 irrigation water intake. year Environment Quality organization county PMOs 240 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report As、Hg、Cr6+、 Monitoring of Water for entrusted CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified for 2 years, collecting one Specifications for Provincial and deposition of demonstration area, and there are two 600 3,600 organization sample every 3 months in Environmental Air Quality county PMOs the atmosphere points in total. entrusted a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Provincial and Fertilizer Use the detection data of fertilizers / / organization county PMOs entrusted Monitoring of the by-product vinasse of Qualified Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each Hygienic Standard for Feeds Provincial and wine-making 500 4,500 organization Cr vinasse. batch (GB 13078-2001) county PMOs by rice with entrusted over-standard Cadmium 694500 Sub-total Yuan 180000 Sampling expense and others Yuan 874500 Total monitoring expense Yuan 241 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 9-19 Environmental Monitoring Plan of Linwu County Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in third year of project Technical Specification for the As、Hg、Cr6+、 demonstration area, main irrigation implementation. Environment Quality Qualified Surface water Provincial and CODCr、 water inlets of main canals/branch Frequency: The Monitoring of Water for 520 9,218 organization for irrigation county PMOs NH3-N、TP canals and small reservoir in each key monitoring frequency in a Agricultural Use entrusted (one time only) reservoir level by level. Irrigation year should be 3 times (NY/T396-2000) water drainage sampling is carried out (single cropping rice: at ground drain of demonstration area May, July and and irrigation water recession outlet. September). Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified and make sure they are corresponded to stage of project Provincial and irrigation water and Environmental Monitoring 432 2,553 organization the monitoring sampling points of implementation (for the county PMOs source water-soluble (HJ/T 166-2004) entrusted irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial and sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 3,318 organization county PMOs basin available Cd quartering (HJ/T 166-2004) entrusted pH, available The monitoring points for soil and Once a year 100 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Total amount Technical Specification for Soil Qualified no less than 5 samples for each stage of project Provincial and Soil Cd, Pb, As, Hg, Environmental Monitoring 300 26,629 organization demonstration area. Grid method implementation (for the county PMOs Cr (HJ/T 166-2004) entrusted should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively Only once in the first year 100 and CEC stable factors, and an area greater than 242 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 1300 ㎡ should be selected as monitoring and sampling sites. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as Provincial and per harvest season in a Mercury and Organic Mercury 352 43,262 organization products Cr possible, and more than five mixed county PMOs year and –once a year for in Foods (GB 5009.17-2014); entrusted samples should be collected for each single cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of compound and Cd, Pb, As, Hg, Collect three samples Only once in the first year / 500 phosphate Cr fertilizers The cadmium content of the organic fertilizer should be controlled below 1mg/kg, and Qualified Provincial and the proportion of organization 1,920 county PMOs easily-oxidized organic carbon entrusted Organic Cd, Pb, As, Hg, Collect three samples for each batch of content in total carbon content fertilizer Twice a year 500 Cr fertilizers. should be no more than 15%. detection Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). 243 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Other agricultural Qualified inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per Provincial and / 500 1,773 organization lime, Cr passivating agents. purchase batch. county PMOs entrusted passivating agents, etc. Set 2 representative demonstration areas, and select 3 typical fields in each Qualified Cd, Pb, As, Hg, demonstration area. Collect the Provincial and Plants Once a season. / 300 21,272 organization Cr above-ground part of rice in mature county PMOs entrusted stage, with 5 to 7 pieces for each sample. Type of pesticides, frequency and The type, frequency and amount to be amount to be used of used of pesticides; incidence rate pesticides; Monitoring in each demonstration area of pests and diseases, incidence rate should be focused on agricultural number of pests and their National Standards for Food Monitoring of of pests and Qualified products, and more than five samples natural enemies should be Safety: Maximum Residue Provincial and plant diseases diseases, / 2,954 organization of each agricultural product should be monitored once a year. Limit of Pesticide in Foods county PMOs and insect pests number of pests entrusted collected for detection of pesticide The amount of pesticide (GB2763-2014) and their residues in agricultural products residues in agricultural natural products should be enemies; monitored once per agricultural harvest season every year. product output and pesticide residues Set 2 representative demonstration One basic sample is Technical Specification for Soil Qualified Soil: Cd, As, Provincial and areas, and select 3 typical fields in each collected for each typical Environmental Monitoring 300 1,064 organization Pb, Hg and Cr county PMOs demonstration area. field, once a year. (HJ/T 166-2004) entrusted Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Plants: Cd, As, Provincial and monitoring mature stage, with 5 to 7 pieces for year for single cropping / 352 1,040 organization Pb, Hg and Cr county PMOs each sample. rice entrusted irrigation water: Collect one mixed sample of each Collect 8 samples each Technical Specification for the Qualified Provincial and 520 945 pH、Cd、Pb、 irrigation water intake. year Environment Quality organization county PMOs 244 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report As、Hg、Cr6+、 Monitoring of Water for entrusted CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified for 2 years, collecting one Specifications for Provincial and deposition of demonstration area, and there are two 600 9,600 organization sample every 3 months in Environmental Air Quality county PMOs the atmosphere points in total. entrusted a year. Monitoring ( No. 4 Announcement of State Environmental Protection Administration in 2007 ) Qualified Provincial and Fertilizer Use the detection data of fertilizers / / / / organization county PMOs entrusted Monitoring of the by-product vinasse of Qualified Cd, As, Pb, Hg, Collect three samples for each batch of Monitor once for each Hygienic Standard for Feeds Provincial and wine-making 500 1,773 organization Cr vinasse. batch (GB 13078-2001) county PMOs by rice with entrusted over-standard Cadmium 127300 Sub-total Yuan 31800 Sampling expense and others Yuan 159100 Total monitoring expense Yuan 245 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 9-21 Environmental Monitoring Plan of Qiyang County Unit price Monitoring Monitoring Arrangement of monitoring point Executive standards and Expense Monitoring Supervision Monitoring frequency (Yuan per item parameters positions (quantity) specifications (Yuan) organization organization sample) Agricultural land irrigation water Monitoring year: source detection points are set up in Monitoring should be river sections around main irrigation carried out in the first and pH、Cd、Pb、 water inlet of cultivated land in third year of project Technical Specification for the As、Hg、Cr6+、 demonstration area, main irrigation implementation. Environment Quality Qualified Surface water Provincial and CODCr、 water inlets of main canals/branch Frequency: The Monitoring of Water for 520 31,660 organization for irrigation county PMOs NH3-N、TP canals and small reservoir in each key monitoring frequency in a Agricultural Use entrusted (one time only) reservoir level by level. Irrigation year should be 4 times (NY/T396-2000) water drainage sampling is carried out (double cropping rice: at ground drain of demonstration area March, May, July and and irrigation water recession outlet. September). Set the sediment monitoring point at each detection point of the irrigation Two times, one in the first pH, total Cd, water sources on the agricultural lands, year, and one at the final Sediment of Pb, As, Hg, Cr, Technical Specification for Soil Qualified and make sure they are corresponded to stage of project Provincial and irrigation water and Environmental Monitoring 432 8,800 organization the monitoring sampling points of implementation (for the county PMOs source water-soluble (HJ/T 166-2004) entrusted irrigation surface water. Collect one evaluation of the Cd. sample at each sediment monitoring implementation effect). point. Sediment in pH, Cd, Pb, As, Collect one sample in each Technical Specification for Soil Qualified Provincial and sedimentation Hg, Cr, sedimentation basin by method of Once a year Environmental Monitoring 432 4,018 organization county PMOs basin available Cd quartering (HJ/T 166-2004) entrusted pH, available The monitoring points for soil and Once a year 100 21,480 Cd agricultural products shall be in accordance with the data requirements Two times, one in the first of 5+ mu for each governance unit, and year, and one at the final Technical Specification for Soil Qualified Total Cd, Pb, no less than 5 samples for each stage of project Provincial and Soil Environmental Monitoring 300 21480 organization As, Hg and Cr demonstration area. Grid method implementation (for the county PMOs (HJ/T 166-2004) entrusted should be used for points setting, and evaluation of the typical plots with good natural implementation effect). Organic matter conditions, flat ground, relatively Monitored in the first 100 3580 and cation stable factors, and an area greater than year, only once. 246 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report exchange 1300 ㎡ should be selected as capacity (CEC) monitoring and sampling sites. Choose two blocks, 1,000 mu is pH, total Cd, appropriate for each block, and select Samples should be taken Soil of Technical Specification for Soil Qualified As, Pb, Hg, Cr the the high-risk area as far as possible at harvest season, twice a Provincial and demonstration Environmental Monitoring 418.5 23600 organization and available and set a point every 30-50 mu in the year for double cropping county PMOs field (HJ/T 166-2004) entrusted Cd mountainous area, and every 50-100 rice. mu in contiguous area. National Standards for Food Safety: Determination of Cadmium in Foods (GB 5009.15-2014); National Standards for Food Safety: Determination of Lead in Foods (GB 5009.12-2010); The product sampling point should Samples should be taken National Standards for Food correspond to the monitoring sampling at harvest season, once Safety: Determination of Total Qualified Agricultural Cd, Pb, As, Hg, point of soil heavy metals as much as Provincial and per harvest season in a Mercury and Organic Mercury 352 151220 organization products Cr possible, and more than five mixed county PMOs year and twice a year for in Foods (GB 5009.17-2014); entrusted samples should be collected for each double cropping rice. National Standards for Food sample. Safety: Determination of Chromium in Foods (GB 5009.123-2014); National Standards for Food Safety: Determination of Total Arsenic and Inorganic Arsenic in Foods (GB 5009.11-2014) Detection of Qualified compound and Cd, Pb, As, Hg, Provincial and Collect three samples Only once in the first year / 500 210 organization phosphate Cr county PMOs entrusted fertilizers The cadmium content of the organic fertilizer should be Organic Qualified Cd, Pb, As, Hg, Collect three samples for each batch of controlled below 1mg/kg, and Provincial and fertilizer Twice a year 500 2540 organization Cr fertilizers. the proportion of county PMOs detection entrusted easily-oxidized organic carbon content in total carbon content 247 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report should be no more than 15%. Other contents refer to the standards for organic fertilizers formulated by the Ministry of Agriculture -Organic Fertilizers (NY 525-2012). Other agricultural Qualified inputs such as Cd, Pb, As, Hg, Collect three samples for each batch of Monitoring for once per Provincial and / 500 2540 organization lime, Cr passivating agents. purchase batch. county PMOs entrusted passivating agents, etc. The type, frequency and amount to be The type, frequency and used of amount to be used of pesticides; pesticides; incidence rate incidence rate Monitoring in each demonstration area of pests and diseases, of pests and should be focused on agricultural number of pests and their National Standards for Food Monitoring of diseases, Qualified products, and more than five samples natural enemies should be Safety: Maximum Residue Provincial and plant diseases number of pests / 8460 organization of each agricultural product should be monitored once a year. Limit of Pesticide in Foods county PMOs and insect pests and their entrusted collect for detection of pesticide The amount of pesticide (GB2763-2014) natural residues in agricultural products. residues in agricultural enemies; products should be agricultural monitored once per product output harvest season every year. and pesticide residues 2 representative demonstration areas One basic sample is Technical Specification for Soil Qualified Soil: Cd, As, Provincial and and select 3 typical fields in each collected for each typical Environmental Monitoring 300 1520 organization Pb, Hg and Cr county PMOs demonstration area. field, once a year. (HJ/T 166-2004) entrusted Balance Collect the above-ground part of rice in 3 to 5 samples, once a Qualified Plants: Cd, As, Provincial and monitoring mature stage, with 5 to 7 pieces for year for single cropping / 352 1490 organization Pb, Hg and Cr county PMOs each sample. rice entrusted Irrigation Collect one mixed sample of each Collect 8 samples each Technical Specification for the Qualified Provincial and 472 3190 water: pH、Cd、 irrigation water intake year Environment Quality organization county PMOs 248 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Pb、As、Hg、 Monitoring of Water for entrusted Cr6+、CODCr、 Agricultural Use NH3-N、TP (NY/T396-2000) Technical Specification for Automatic Monitoring of Environmental Air Quality Continuous monitoring (HJ/T 193-2005) Dry and wet Set one point in each representative Qualified for 2 years, collecting one Specifications for Provincial and deposition of demonstration area, and there are two 600 1350 organization sample every 3 months in Environmental Air Quality county PMOs the atmosphere points in total. entrusted a year. Monitoring (No. 4 Announcement of State Environmental Protection Administration in 2007) Qualified Provincial and Fertilizer Use the detection data of fertilizers / / organization county PMOs entrusted Monitoring of the by-product vinasse of Qualified Cd, As, Pb, Hg Collect three samples for each batch of Monitor once for each Provincial and wine-making / 500 2540 organization and Cr vinasse. batch county PMOs by rice with entrusted over-standard Cadmium 289700 Sub-total Yuan 57900 Sampling expense and others Yuan 347600 Total monitoring expense Yuan 249 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 8.6.4 Monitoring Report System The monitoring unit shall submit a formal monitoring report after end of each monitoring task and submit it to relevant departments level by level as per procedure. Quarterly report and annual report shall be provided during operation period. Upon occurrence of sudden accidents, they must be immediately reported. The monitoring report procedure of this Project is shown in Figure 8-3 below. Figure 8-3 Diagram of Monitoring Report Procedure 8.7 Environmental Management Expenditure Estimation The total investment for environmental protection and social risk prevention that can be counted in this project is 20.8875 million Yuan, as shown in Table 8-22. Table 8-22 The Environmental Management Expenditure of the Project Estimated Serial Environmental Measure content investment (10,000 No. elements Yuan) Acoustic Shock absorption of the construction equipment 1 40 environment foundation or setting damping seats, etc. Surface covering and water spraying for dust Atmospheric 2 suppression on the the surface of the powdered 40 environment materials during the construction period, etc. 1 Setting up sedimentation basins and temporary dry 3 Water environment toilets within the construction site, and taking water 360 and soil conservation measures, etc. Transportation of the muck to construction site for 4 Solid waste balanced disposal; transportation of the domestic 200 waste to the landfill after collection Monitoring of surface water for irrigation, sediments Monitoring of irrigation water, sediments of sedimentation expenditures during 5 basins, soil, agricultural products, fertilizers and 755.02 project agricultural inputs, pests and diseases, balance of implementation heavy metals, by-product vinasse of wine-making by 250 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report rice with over-standard Cadmium, etc. Control of Compensation for the price of agricultural products 6 standard-exceeding that is lower than the government purchase price due 440 rice to substandard rice Cropping system Subsidy for cropping system change of heavily 7 253.73 change polluted areas Total 2088.75 8.8 Information Management of EMP 8.8.1 Information communication The environmental management requests necessary information communication among different departments and posts of PMO, Project construction unit and Project implementation organization within the organization. Meanwhile, relevant information shall be notified to outside (related parties, social public, etc.). Internal information communication can be carried out by various means such as meeting and internal briefing. However, a formal meeting shall be convened once every month. All communicated information shall be recorded and archived. External information communication shall be conducted once every half a year or every year. Information communication with collaborative units shall form minutes and shall be archived. 8.8.2 Recording Mechanism In order to realize effective operation of environmental management system, the organization must establish a complete recording system and preserves the records involving the following aspects: (1) Statutory and regulatory requirements; (2) Permission; (3) Environmental factors and related environmental impacts; (4) Training; (5) Inspection, checking and maintenance activities; (6) Monitoring data; (7) Effectiveness of corrective and preventive measures; (8) Information of related parties; (9) Audit; 251 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report (10) Review Besides, it is also required to conduct necessary control over various records mentioned above, including identification, collection, cataloguing, filing, storage, management, maintenance, query, preservation term and disposal of records, etc.. 8.8.3 Reporting Mechanism During Project implementation, Project construction unit, Project implementation organization, monitoring unit and PMO shall record Project progress, ESIA execution conditions and environmental monitoring results and timely report to relevant departments. Contents of the following six parts are mainly included: (1) The project implementation organization and Project construction unit shall record Project progress and ESIA execution conditions in detail on a quarterly basis, timely submit the quarterly report to each PMO, and meanwhile copy the quarterly report to Environmental Protection Bureau of Counties. (2) After completing entrusted monitoring tasks, the monitoring unit shall timely submit the monitoring report to PMO and meanwhile copy it to Environmental Protection Bureau of Counties. (3) PMO of Project Counties shall timely submit Project progress report to provincial PMO and meanwhile copy to Environmental Protection Department of Hunan Province. The project progress report (e.g. monthly report, quarterly report and annual report) must include contents of ESIA progress, e.g. execution progress and effect of ESIA and especially environmental monitoring results. (4) The annual ESIA execution report of the project must be completed and submitted to the World Bank before March 31 next year. ESIA execution report may include the following main contents: a. Implementation conditions of training plan; b. Condition of Project progress; c. Execution conditions of environmental protection measures of the project, launching conditions of environmental monitoring and main monitoring results; 252 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report d. Check if there are public complaints. If a complaint occurs, the main contents of the complaint, solution and degree of satisfaction of the public shall be recorded; e. ESIA execution plan in next year 8.8.4 Document management During implementation of the project, the World Bank, leading committee of the project and provincial PMO as well as county Project leading team, county PMO, environmental impact assessment unit and construction unit shall manage relevant documents. The details are shown in Table 8-23 below. 253 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Table 8-23 Document Management Requirements of Each Organization Name of organization Document management 1. Record and file specific implementation conditions of construction every week and submit to county PMO; 2. Record and file specific implementation conditions of construction and submit to county PMO upon emergency ①Construction unit and sudden condition; 3. Complete rectification within 3 working days (within 10 working days if coordination of management organization is needed) and file documents after receiving notice of rectification. ②Unit with construction Project environmental impact assessment qualification certificate 1. Prepare contents of ESIA and file first draft, draft for ③Unit with construction Project review and approved draft. social impact assessment qualification certificate 1. Properly record, sort and file complained contents during Project construction and operation; 2. Record conditions reported by construction unit every quarter and submit relevant report (statement) to provincial ④County (district) PMO PMO; 3. Sign for site checklist of construction unit and verify and file environmental sensitive problems; 4. Manage and file notice of rectification reported. 1. Prepare and supervise the implementation and filing of ESIA 2. Record conditions reported by leading team and PMO in ⑤Project leading committee and each Project point every half a year and submit relevant provincial PMO report to the World Bank for filing; 3. Coordinate with other relevant departments to solve major environmental problems and record and file specific measure conditions. 1. Record and file conditions reported by provincial Project ⑥World Bank leading team and PMO every half a year. 254 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Chapter 9 Conclusion 9.1 Project Brief Introduction The project is Hunan Integrated Management of Agricultural Land Pollution Project in newly-added demonstration areas of 11 sub-project Counties with World Bank Loan. Its objectives are to analyze risk factors of heavy-metal-polluted farmlands in Newly-added Demonstration Areas, borrow and introduce heavy-metal-polluted farmland management experience at home and abroad, establish risk-based integrated management mechanism for polluted farmland, demonstrate and popularize the integrated management mode within the final selected demonstration farmland scope, and then realize safe agricultural production. The project construction content mainly includes contents in four plates of risk-based agricultural land management demonstration, agricultural environment monitoring and management strengthening, project capability construction, and project management and evaluation. 9.2 Current Environmental Status (1) Investigation and evaluation results of current environmental status for surface water In order to investigate and understand the irrigation water quality situation of each newly-added demonstration area, each project county entrust the monitoring unit to monitor irrigation water source in each newly-added demonstration area. It can be known from monitoring result that monitoring factors of water quality, namely pH, CODCr, As, Pb, Cd, Cr6+ and Hg, of irrigation water source in each demonstration area all meet requirements in Standards for Irrigation Water Quality (GB5084-2021); total phosphorus and ammonia nitrogen meet requirements in Type-III in Environmental Quality Standards for Surface Water (GB3838-2002). (2) Soil quality investigation and evaluation result As per the monitoring results and refer to the screening value standard in Table 1 of ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural 253 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report Land (Trial)’ (GB 15618—2018), cadmium generally exceeded the standard in the farmland soil of newly-added demonstration areas in each project county. (3) Investigation and assessment of of current status of irrigation canal sediments As per the monitoring results and refer to ‘Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial)’ (GB 15618—2018), the sediment of irrigation canal in newly-added demonstration area of each project county meets the requirements of control value standard. (4) Investigation and assessment of current rice As per the monitoring results, rice in the newly-added demonstration area of each project county generally exceeds the standard, and the main factor is cadmium. (5) Pollution sources investigation Through on-site survey, public consultation and material collection and analysis, the agricultural land pollution of newly-added demonstration areas of each project county is mainly historical pollutant sources such as factories and mines. These historical pollutant sources are closed and left ore residues are cleared when they are closed; now, there is no tailings reservoir or residue piling as well as left issues of mining and mineral processing, which won’t result in new heavy metal pollution to downstream agricultural land. 9.3 Environmental Impact Analysis and Mitigation Measures of Project The civil engineering construction activities of the integrated management Project of agricultural land pollution in this project can be divided into two categories: ①Small-scale civil engineering construction including the front sedimentation basin, electric pumping station construction, impounding reservoir, motor-pumped well and small-scale field road maintenance (Reinforce the pavement level off only, and no increase the width and length of road); ②The field irrigation facility construction including the drainage canal and irrigation canal renovation and the ecological intercepting ditch construction. The project civil engineering activities have impact on water environment, atmospheric environment, acoustic environment and ecological environment during construction. 254 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report The civil construction activities are small-scale civil construction activities. The project is located around agricultural lands and there is no environmentally sensitive area inside or around the demonstration area. The scale of the project is very small. The number of construction workers for the project is not more than 5 – 10. There is no need to build construction camps, and land acquisition, demolition and ethnic minorities are not involved. Dust, noise, waste water, solid waste, etc. may be produced during the construction process, but these effects are temporary and little. They are limited to a very small area of the construction area, and the impact disappears immediately after the construction is finished. In the agricultural activities, the following have an impact to the environment: waterflooding irrigation, lime application (adjust the pH value by soil acidification), manure fertilizer application, soil passivator application, growing structure adjustment, etc. Waterflooding irrigation during the grain-filling and heading period can reduce the heavy metal absorption by rice. Lime application can regulate the pH value of soil so as to reduce heavy metal absorption by crops. However, the excessive lime application may result in soil hardening. If protection measures are not adopted, lime application may result in poor influence on health of lime application personnel. The application of organic fertilizer can improve physicochemical property of soil, while the application of unqualified organic fertilizer may result in secondary pollution of soil in agricultural land. The application of soil passivator can reduce activity of heavy metal in soil. By removing straws out of the agricultural lands, heavy metal in straws can be removed out of the agricultural lands, which facilitates to reduce heavy metal in agricultural land soil. Therefore, although the construction scheme of the project may cause a certain environmental impact, such impact can be avoided and reduced by taking corresponding environmental measures and the impact during the construction period is less and it is temporary, while the implementation of such project can increase grain safety and improve the living quality of people. So, it is a project facilitating people’s livelihood, and the brought social and environmental benefits are long-term. 255 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report 9.4 Public Consultation and Information Disclosure Conduct at two rounds of public consultation and information disclosure during assessment. The first round is after screening the environmental problems and before the final determination of the environmental assessment outline; the second round is in the completion stage of first draft of environmental impact report. Approaches such as convening of symposium, interview, granting of questionnaires and site announcement are adopted to get to know the opinions and suggestions of the public. Information collected through various methods allows residents in demonstration areas to have a common understanding of the project and the public surveyed all supported the implementation of the project. The EIA summarizes the opinions of public participation and gives corresponding feedback, optimizes the design and construction of the project, and does a good job in environmental protection, so as to bring the social, environmental and economic benefits of the project into full play as soon as possible. At the same time, the project has established an effective information release mechanism, which enables the affected people to get information quickly during the implementation of the project, and ensure that the interests of the affected groups can be fully considered in the process of construction and operation of the project. 9.5 Overall Conclusion The newly-added demonstration areas of the second batch of project counties of Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan involve 11 project counties. The project construction content includes risk-based agricultural land management demonstration, agricultural environment monitoring and management strengthening, project capability construction, and project management and evaluation; in the project, carry out the risk-based assessment on selected agricultural lands in the demonstration area, select applicable integrated technical management measures to demonstrate, strengthen management and control of agricultural land pollution sources and agricultural land pollution risks, and increase the safe utilization level of agricultural sources, so as to achieve the target of producing safe grains. 256 Hunan Research Institute for Nonferrous Metals Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan (The Third Batch of Subprojects) Environmental Impact Report The implementation of the project can increase grain safety and improve the living quality of people. It is a project facilitating people’s livelihood, and has significant environmental and social benefits, and the beneficial effect is the main aspect. Its unfavorable impact mainly lies in the aspects of atmospheric environment, water environment, acoustic environment, etc., and it mainly occurs in the construction process of the project, the impact degree is small, and after taking the corresponding environmental protection measures, various unfavorable impacts are effectively controlled. Therefore, from the view of environmental protection, the overall evaluation thinks that the second batch of project counties in the Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan does not have restrictive environmental and social impact factors, and the project construction is feasible. 257 Hunan Research Institute for Nonferrous Metals Appendix 1 Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan Small Civil Engineering Works Environmental Protection Procedure Foreign Economic and Technical Cooperation Center, Agriculture Commission of Hunan Province Hunan Research Institute for Nonferrous Metals July 2018 Environmental Protection Procedure of Small Civil Engineering Works 1. Bid Invitation and Bidding (1) The bidding documents shall make clear of environmental protection objectives of each sub-project as well as Project contractor’s responsibilities and obligations for environmental protection objectives in Demonstration areas. Each environmental protection measure and suggestion put forward in environmental impact report already approved by environmental protection department shall be clearly specified in contract terms. (2) The contractor shall undertake the obligations for environmental protection in bid documents. Contractors contracting each sub-project shall promise to perform the obligation of environmental protection for environmental protection objectives involved in the demonstration area. The construction organization design and plan conducted shall contain contents involving implementation of environmental protection measures. (3) The ratio of amount of deposit annually budgeted and preserved by the contractor in Project contract funds involving completion of environmental management shall take up approximately 3% of budgeted fund. If the measures adopted by the construction unit for environmental protection are ineffective, relevant environmental protection managers shall order the construction unit to rectify, and the environmental protection measures are still not implemented after rectification, the county PMO may impose a penalty on the construction unit and detain Project funds as overdue fine for environmental protection as well as entrusts other unit to adopt environmental protection measures. 2. General Provisions (1) The project owner shall assign specific personnel to take charge of handling environmental protection problems taking place during construction and operation period as well as handle environmental problems taking place between contractor and environmental protection objectives and supervise the implementation of various environmental protection measures during construction period. Besides, the contractor is required to assign at least one main administrative leader to take charge of environmental protection work so as to coordinate with the owner to jointly implement each environmental protection measure. (2) The contractor shall optimize construction scheme and adopt the most advanced construction processes and implement scientific management as much as possible so as to improve construction progress under the precondition that the construction quality is 1 ensured. Meanwhile, the contractor shall strengthen management and maintenance of construction equipment and avoid leakage of substances such as petroleum and building materials transported so as to reduce the possibility of pollution of surface water pollution in Demonstration areas. (3) The owner shall take charge of compiling and printing materials publicizing environmental protection and distributing such materials to each contractor. Also, the owner shall carry out education of environmental protection of all construction personnel to improve environmental protection awareness of construction personnel. (4) It is strictly forbidden to stack or place muck at excavation or dump it to nearby rivers during construction period. The staff is strictly forbidden to discharge domestic sewage and household garbage to river. (5) During the construction process, advanced equipment shall be adopted as much as possible to reduce the disturbance of construction noise on normal lives and rest of residents around. The construction time shall be strictly controlled within 8:00~20:00. Construction shall be stopped during lunch break (12:00~14:00) to ensure normal rest of residents at night. Besides adoption of necessary prevention and control measures to mitigate disturbance, the contractor shall also post announcements in housing estates. The residents are requested to understand and support so as to reduce incompatibility resulting from construction and benefit smooth progress of Project. (6) Construction personnel will rent local villager’s residences for lease. Field construction camp shall not be set up separately. (7) According to the weather conditions, watering must be timely conducted on the construction site to reduce dust. As for building materials thrown and scattered on the nearby roads, contractor in charge of construction in each bid section shall assign special personnel to timely clean so as to reduce pollution caused by raising dust to environmental air quality. 3. Environmental Protection Provisions on Construction Site Preparation The project does not involve land acquisition, and temporary sites such as construction material stockyards, mixing yards, etc. are set in the waste land or the dry beach land with few vegetation. For the problems involved in ecological issues including vegetation destruction, water and soil loss landscape influence, etc. and pollution to water environment, acoustic environment and air environmental pollution during the setting and use of temporary sites, they shall be carefully treated. 2 (1) Common environmental requirements for selection of temporary construction sites ① Temporary sites shall be kept far away from rivers. It is usually prohibited to set up temporary sites within a range of 200m away from river bank; ② Types of land occupation. Temporary land shall be selected in wasteland or dry bottomland with sparse vegetation as much as possible; (2) Special environmental requirements for site selection of various temporary sites Since different temporary sites have different environmental impacts, the environmental requirements for site selection of different sites also differ: ① Aggregate yard: It shall be set up far away from residential area. It shall be selected along the downwind direction of perennial prevailing wind direction of environmental sensitive point. The distance shall be beyond 300m; ②Cement and concrete mixing yard: Cement and concrete mixing yard shall be set up 300m away from the downwind direction of perennial prevailing wind direction of environmental sensitive point. (3) Site survey shall be carried out ahead of time before entry into construction site. Specific position of construction site shall be reasonably arranged according to status quo of environment of the construction site. 4. Environmental Protection Provisions on Society (1) Management of temporary land The drainage channels and the irrigation channels in the project are reconstructed from the original channels; the pre-sedimentation tank is built in the depressed land or the waste land, and the project does not involve in land acquisition. (2) Management measures against influence on agricultural land and water conservancy along the line ① Parallel operation shall be adopted during earth borrowing in construction. Excavation, leveling and protection shall be conducted simultaneously. Landscape reconstruction shall be timely carried out. ② Works involving relocation of agricultural land water channels shall be constructed in non-irrigation period as much as possible in order to ensure unimpeded agricultural land water channels and prevent water and soil loss. Solid wastes in river channels shall be timely cleared after completion to ensure unimpeded river channels during irrigation period. 3 (3) Management measures against influence on infrastructure including existing transportation ①As for all public facilities and structures influenced by the proposed Project, the contractor shall take all proper measures to protect such facilities and structures during construction period of the proposed Project. ②Protective measures shall be properly adopted to protect infrastructure within scope of roadbed including existing road, communication, electric power, and pipeline network facilities to prevent damages. ③The transport of raw and auxiliary materials or use of large machinery may damage local roads.Therefore, such roads shall be timely repaired during and after construction, or compensation fee shall be paid to local road administrative department for repair. ④The development organization shall properly make a transport plan. Road materials shall be transported beyond peak traffic hours of local roads in order to avoid causing traffic blockage and reduce traffic accidents. ⑤As for excavation work close to public facilities, the contractor shall inform relevant department and invite representative from such department to be present during construction. (4) Environmental protection provisions on traffic ①Project construction in sections shall be adopted as much as possible and excavation and backfill work shall be completed within a period as short as possible. ②Construction methods shall be determined section by section based on Project contents and scale.It is required to not only reduce investment but also ensure Project quality. Construction method combining advancing and excavation shall be implemented to avoid traffic interruption and blockage. ③Signboards around construction points shall be properly set up in consideration of influence of construction on access of targeted groups.Special personnel are set up at the intersection to take charge of traffic dredging and assurance of pedestrians’ safety. ④The construction unit shall post relevant announcement in Project construction area one week before Project implementation to inform the residents of influence of Project construction ahead of time and obtain their understanding. 4 5. Protection Management Provisions on Cultural Relics and Historic Sites If cultural relics and historic sites are discovered or suspected during construction period, the construction unit shall immediately protect the scene and report to local cultural relics bureau to handle the matter according to Cultural Relics Protection Law of the People’s Republic of China (December 29, 2007) and requirements of material cultural resource policies of World Bank. The construction may be resumed after treatment of cultural relics bureau. The reporting procedures of cultural heritage are shown in Figure 5-1. If cultural relics and historic sites are discovered or suspected during construction process, the construction unit shall implement the followings: (1) Construction in the construction position where cultural relics are discovered shall be immediately stopped and site protection shall be strengthened; (2) The contractor shall timely report to competent policy affairs and cultural relics department for authentication and handling; (3) Once the objects discovered are determined by experts as cultural relics, the scope of protection shall be immediately divided; (4) Cultural relics shall be rescued and excavated indeed due to demanding construction period or in case of danger of natural destruction; (5) Rescue and digging of cultural relics must be carried out by professionals using special equipment. The contractor shall not dig without authorization; (6) Once the objects are judged as major cultural relics findings, demonstration as whether the project shall be constructed in other place shall be carried out. 5 Figure 5-1 Procedure Diagram for Handling of Cultural Relics Discovered during Construction Period 6. Environmental Protection Provisions on Noise Pollution Prevention and Control The noise sources during construction period mainly includes mechanical noise generated by construction equipment such as excavator and blender as well as transport vehicles with sound level above 85dB(A). Influence of construction noise to different extents will be imposed within scope of 30m, 80m and 150m around construction site with or without shielding. The following measures are adopted to improve the acoustic environment quality of main protection objectives mentioned above. 6 (1) Strengthen environmental quality on construction site and strictly execute stipulations set out in Noise Limits for Construction Site. In order to reduce the influence of construction on residents around, the construction time is stipulated as from 8:00 in the morning to 20:00 at night. During lunch break from 12:00 at noon to 14:00 in the afternoon, construction is prohibited. (2) Post construction announcements in housing estates around construction site and meanwhile clearly mark the construction team, which cannot only comfort the people and obtain their understanding but also supervise the construction party to benefit the completion of the project as scheduled. (3) In sensitive points such as school, the operation of high-noise equipment shall be implemented beyond school time; high-noise equipment shall not be operated during lunch break. During construction in areas around sensitive points such as schools, the operation time of high-noise equipment shall be shortened as much as possible. Low-noise machinery shall be adopted during selection of construction equipment and methods as much as possible. (4) Method of “centralization of force and construction section by section” shall be adopted to shorten construction period and lighten the influence of construction noise on acoustic environment in local sections. (5) In order to ensure the health of construction personnel, the construction unit is recommended to reasonably arrange personnel’s working times according to Hygienic Standards of Noise of Industrial Enterprises to let the personnel operate construction machinery with high radiation and noise in turn so as to reduce the duration exposed to high noise. Meanwhile, the construction unit shall pay attention to machine maintenance and correct operation so as to maintain the noise of road building machine at the lowest sound level. Operators and relevant personnel are recommended to adopt individual protective measures such as wearing of earplugs and helmets. 7. Environmental Protection Provisions on Atmospheric Pollution Prevention and Control The main polluting factors of the proposed Project influencing the environmental air during construction period include construction waste gases and raising dust. Waste gases mainly refer to tail gas exhausted by various kinds of construction machinery and transport vehicles; raising dust generated during construction period is mainly generated from site excavation and backfill, transport and handling of materials such as stone and cement, as 7 well as road raising dust generated during construction work. Meanwhile, leveling of the site also generates a little quantity of raising dust. The main pollutant is TSP. (1) Raising dust pollution prevention and control measures During the period from foundation excavation to backfill and covering during construction period, the construction site shall be enclosed in order to prevent generation of raising dust from construction. Under the condition that it is continuously sunny and windy during construction, watering or green covering net shall be adopted at the temporary stacking and storage place of excavated earthwork for covering so as to prevent generation of raising dust. The construction unit shall timely dispose spoil as planned and use canvass to cover the carriage of trucks used to transport residual earth during loading (keep enclosed transport of vehicles) as well as carry out watering on transport route without earth pavement. Meanwhile, it is required to avoid excavation of earthwork and handling of materials in windy days. The loading vehicles shall not be overloaded. Certain measures shall be adopted to ensure that the residual earth transport vehicles do not scatter materials along the journey. Before driving of vehicles, mud on the wheels shall be cleaned using sweeper to prevent falling of spoil along the journey to influence environmental tidiness. Meanwhile, clean-keeping system shall be implemented on construction road and spoil shall be timely cleaned if any. The construction unit shall strictly strengthen management and adopt proper measures to strictly control raising dust generated during construction period. In order to minimize the influence of construction Project on surrounding environment during construction period, it is recommended to adopt the following prevention and control measures: ①Special personnel shall be allocated in construction work area to take charge of scientific management and civilized construction; measures shall be adopted during construction period to accelerate Project progress as much as possible. Also, stonework and earthwork shall be timely transported to designated places to shorten the hazard period of stacking. ②The terrace on construction site must be hardened and concrete terrace shall be adopted if the condition allows. ③Watering keeps the work under certain humidity during excavation; loose and dry surface soil within construction site shall also be constantly watered to prevent dust; during backfill of earthwork, watering shall be properly conducted when the soil texture in the surface layer is dry to prevent raising dust. 8 ④Strengthen the management of backfill earthwork stacking yard and formulate measures for earthwork surface compaction and regular water spraying and covering; mud and waste slag of building materials not needed shall be timely transported away and shall not be stacked for a long term. ⑤Earth transport trucks and building material transport trucks shall be equipped with spraying prevention devices as stipulated. The materials shall not be overloaded to ensure that they are not scattered during transport process; also operation routes and time of transport vehicles shall be properly planned to avoid driving in sensitive areas such as traffic centralization area and residents’ residences. ⑥Over-canopy is added on transport vehicles. The loading and unloading place shall be flushed first to reduce spreading of mud carried by wheels and chassis on the pavement. ⑦Mud spread on the pavement during transport shall be timely cleaned to reduce raising dust during operation. ⑧Materials easily generating raising dust such as sand and cement stacked in the open air shall be covered with canvas and plastic cloth to prevent diffusion of raising dust. ⑨Road and vegetation on the site occupied by construction shall be timely recovered upon end of construction. ⑩Construction transport work shall be reasonably arranged. Transport of large components during construction work as well as abundant materials and spoils shall be transported beyond peak traffic hours so as to lighten traffic pressure. (2) Transport vehicle tail gas pollution prevention and control measures ①Construction machinery and vehicles under favorable operation conditions shall be selected and used. ②Fuel oil consuming construction machinery and vehicles shall be used under normal status to ensure standard emission of waste gases. ③Reasonably use equipment and strengthen maintenance and repair of equipment. 8. Environmental Protection Provisions on Water Environment Influence (1) Materials such as cement and gravel shall be covered with tarpaulin during stacking and such materials shall not be stacked alongside river. Fence shall be set up when necessary to prevent flushing of such materials from flowing into the river together with rainfall runoff and causing pollution during rainy season or rainstorm. (2) The waste slag during construction is prohibited to be dumped to river. Instead, it shall be 9 transported to stipulated fill point or stipulated place for unified treatment. (3) Intercepting ditches shall be set up around machinery stacking yard in maintenance work area to prevent machinery oil dirt from flowing into surrounding environment with rainwater and causing pollution during rainy days. Also, the sewage collected in intercepting ditches shall go through oil separation and sedimentation treatment before natural evaporation. Household garbage generated shall be properly managed, collected on a regular basis and transported to designated place for treatment. Meanwhile, maintenance work of machinery in maintenance work area shall be properly conducted to prevent pollution of machinery oil dirt. (4) Serious oil leakage of construction machinery shall be prevented. It is prohibited to discharge oily water generated by machinery during operation to nearby water bodies, or discharge oily water generated during repair of construction machinery to water body. (5) All Demonstration areas are located in rural area. Therefore, local villagers’ residences can be rented as construction camps. The domestic sewage of construction personnel during construction period will be collected through septic tanks in villagers’ residences and then used for fertilization to reduce environmental pollution. (6) The contractor shall not disturb natural flow of river channel, water channel or existing irrigation or drainage system without written consent of supervision engineer ahead of time in order to avoid the occurrence of scouring and sedimentation no matter what the demand is. 9. Environmental Protection Provisions on Disposal of Solid Wastes Solid wastes generated during Project construction period mainly include building garbage and household garbage. The main building garbage generated during construction period is inorganic wastes, mainly including leftovers during construction such as abandoned stacked earth and concrete blocks. Also, a little quantity of organic wastes is included, mainly including various packing materials, abandoned old plastics and foams. These wastes are not easy to rot or dissolve and therefore the surrounding landscape and environmental quality may be influenced if they are not properly treated. In order to avoid the occurrence of such 10 problems, the construction unit is required to classify and treat wastes generated from construction, demolition and site clearing. Materials that can be directly reutilized or recycled shall be classified, recycled and reutilized. The remaining materials may be timely cleared by relevant entrusted clearing and transport unit. Local digestion measures are adopted to return the earthwork and stonework excavated during construction to nature (they shall be properly filled and compacted). Household garbage generated during construction period is mainly organic wastes including leftovers and excrements. Such solid wastes will rot, become smelly and give birth to mosquitoes if they are stacked in construction area at will and not timely and effectively treated. If the situation is serious, it can induce various infectious diseases to affect construction personnel’s physical health. The household garbage generated during construction period of the proposed Project will be centrally collected and then cleared and transported to refuse landfill. Leftovers will be collected and then used by farmer households to feed pigs, and excrements will be used for fertilization. 10. Environmental Protection Provisions on Ecological Environment Protection (1) Vegetation protection measures ①Existing agricultural land and trees shall be properly protected.It is recommended to carry out relevant training of construction personnel before use of temporary land. Civilized work shall be emphasized during construction and damages beyond the work shall not be caused. Management shall be strengthened and trees and vegetation within temporary land shall be strictly and properly protected to reduce damages of surrounding ecological environment in Demonstration areas. ②Construction, greening, slope protection and construction of drainage ditch shall be simultaneously implemented. It is strongly recommended to realize simultaneous use, leveling, greening and secondary ploughing. However, in consideration of feasibility, leveling and greening shall be emphasized after end of Project. ③As for temporary land occupation, it shall be timely leveled and reclaimed or greening and land construction shall be conducted after end of Project. 11 ④Green vegetation beyond the scope of land shall be protected as much as possible.If the existing green vegetation is damaged due to construction of temporary works, it shall be recovered during demolition of temporary works. ⑤Area of vegetation damaged during Project construction shall be strictly controlled. Besides unavoidable Project land occupation and felling, no other form of man-made damage shall take place. ⑥Strengthen education of protection of natural resources and wild animals for construction personnel and stipulate in the employment contract that it is strictly prohibited to fell trees at will. (2) Cultivated land protection measures ①Unnecessary land occupation shall be reduced or avoided during construction as much as possible. Operation shall be carried out according to greening design requirements within scope of Project land. ②Earth borrow and abandoning shall be combined with agricultural development planning and design and basic construction of agricultural land so as to provide conveniences for development of local economy and solving of local actual difficulties. ③Project greening shall carefully implement requirements of relevant policies. If it is cultivated land around the project, width of greenbelts shall be strictly controlled. (3) Greening measures ①Plant protection measures in directly affected areas: There are several land types in directly affected areas, namely, cultivated land, waste slope (wasteland) and grassland. The greening principle in the directly affected areas is that the original land utilization types shall be recovered after completion of main works. Therefore, after completion of Project, land remediation of cultivated land shall be carried out to reclaim the land to agricultural land; after completion of Project, land remediation of waste slope and grassland shall be carried out to create forests mixing trees and shrubs or plant high-quality grass. ②Other greening measures for land occupation: It is mainly to recover vegetation damaged by place with earth borrowed. 12 11. Environmental Protection Provisions on Construction Site During site selection of the project, the following requirements shall be observed according to site selection requirements of construction site and based on actual circumstances of Project: ① Rent villagers’ residences around Demonstration areas and set up household garbage collection points or garbage collecting cans. ② Construction personnel shall abide by local village regulations and nongovernmental agreements, implement civilized construction, and properly handle relationship with local residents. ③ Wastewater sedimentation basin is set up for setting of production site. After sedimentation, production wastewater is reused for construction work and is not discharged out. The domestic sewage is collected and treated in toilets of villagers’ residences and then used by local farmers for agricultural land fertilization. 12. Environmental Protection Provisions on Construction Safety The construction unit is responsible to abide by all national and local safety requirements as well as other measures capable of avoiding accidents to ensure safety and health of construction personnel. (1) Occupational health and safety training shall be carried out to all construction personnel, and basic work rules and personal protection rules in construction place shall be introduced to them as well as that how to prevent injuries of other employees shall be noticed; (2) Fire-extinguishing equipment shall be equipped in construction place. Enough fire-extinguishing equipment shall be provided and maintained at any time to keep them under good working status. Besides, such equipment shall be put in places easy to get; (3) The construction unit shall ensure to provide eligible emergency rescue and allocate emergency rescue tools in construction place; written emergency handling procedure shall be formulated in remote places to facilitate the transfer of patients to proper medical organizations; (4) Correct signboard shall be suspended on devices, materials, safety measures and 13 emergency exits of dangerous areas (distribution room, etc.); (5) If workers’ hands and arms are subject to vibration due to use of tools on their hands and power-driven tools, or the whole bodies of workers are subject to vibration due to standing or sitting on vibrating surfaces, damping cushion or device shall be installed through equipment selection to implement control over restriction of exposure time; (6) Place warning plates on all power-on electric devices and electric wires; check all electric wires, cables and power-driven tools on the hands, check if there is damaged or exposed electric wire, and determine maximum allowable working voltage of such tools according to the suggestions of manufacturers; carry out double insulation/grounding treatment of all power-drive equipment used in moist (or possibly moist) environment; (7) Provide all workers participating in or assisting welding work with proper eye protection tools (e.g. welding goggles and/or masks); (8) Guardrails (one middle bar and surrounding baffles) shall be installed at the edge of vulnerable areas. Meanwhile, the construction personnel shall adopt fall preventive devices (including safety belt and distance restriction lacing wire); (9) The construction unit determines and offers proper individual protection equipment to construction personnel so as to fully protect workers themselves, other workers and occasional visitors. Besides, such equipment shall not bring unnecessary inconveniences to users; (10) The construction unit shall establish procedures and systems to report and record occupational accidents and diseases as well as dangerous conditions; (11) Carry out health education of construction, enhance face-to-face consulting work and encourage individuals to take protective measures; besides, the construction personnel are encouraged to use blocking methods such as mosquito repellent, clothes and mosquito net to avoid mosquito bites spreading diseases. 14 Appendix 2 Hunan Integrated Management of Agricultural Land Pollution Project World Bank Loan Field Irrigation Facility Construction Environmental Protection Procedure Foreign Economic and Technical Cooperation Center, Agriculture Commission of Hunan Province Hunan Research Institute for Nonferrous Metals July 2018 1 Environmental Protection Procedure of Field Irrigation Facility Construction Hunan Integrated Management of Agricultural Land Pollution Project is a Project implemented in order to improve quality and safety of agricultural products and safeguard people’s life health in consideration of the severe situation of heavy metal contamination of cultivated land in Hunan Province. In order to maintain normal implementation of the project, realize use of clean and standard-reaching irrigation water sources during implementation of the project, and provide guarantee for smooth implementation of the project and obtaining of expected effect, the field irrigation facilities in the demonstration areas are hereby reconstructed and perfected. The construction contents of field irrigation facilities include reconstruction of drainage channels and irrigation channels and construction of ecological intercepting ditches. 1. Bid Invitation and Bidding (1) The bidding documents shall make clear of environmental protection objectives of each sub-project as well as Project contractor’s responsibilities and obligations for environmental protection objectives in Demonstration areas. Each environmental protection measure and suggestion put forward in environmental impact report already approved by environmental protection department shall be clearly specified in contract terms. (2) The contractor shall undertake the obligations for environmental protection in bid documents. Contractors contracting each sub-project shall promise to perform the obligation of environmental protection for environmental protection objectives involved in the demonstration area. The construction organization design and plan conducted shall contain contents involving implementation of environmental protection measures. (3) The ratio of amount of deposit annually budgeted and preserved by the contractor in Project contract funds involving completion of environmental management shall take up approximately 3% of budgeted fund. If the measures adopted by the construction unit for environmental protection are ineffective, relevant environmental protection managers shall order the construction unit to rectify, and the environmental protection measures are still not implemented after rectification, the county PMO may impose a penalty on the construction unit and detain Project funds as overdue fine for environmental protection as 1 Hunan Research Institute for Nonferrous Metals well as entrusts other unit to adopt environmental protection measures. 2. General Provisions (1) The project owner shall assign specific personnel to take charge of handling environmental protection problems taking place during construction and operation period as well as handle environmental problems taking place between contractor and environmental protection objectives and supervise the implementation of various environmental protection measures during construction period. Besides, the contractor is required to assign at least one main administrative leader to take charge of environmental protection work so as to coordinate with the owner to jointly implement each environmental protection measure. (2) The construction unit is required to entrust a qualified unit to conduct construction supervision and supervise and urge construction unit to implement each environmental protection measure. (3) The contractor shall optimize construction scheme and adopt the most advanced construction processes and implement scientific management as much as possible so as to improve construction progress under the precondition that the construction quality is ensured. Meanwhile, the contractor shall strengthen management and maintenance of construction equipment and avoid leakage of substances such as petroleum and building materials transported so as to reduce the possibility of pollution of surface water pollution in Demonstration areas. (4) The owner shall take charge of compiling and printing materials publicizing environmental protection and distributing such materials to each contractor. Also, the owner shall carry out education of environmental protection of all construction personnel to improve environmental protection awareness of construction personnel. (5) It is strictly forbidden to stack or place muck at excavation or dump it to nearby rivers during construction period. The staff is strictly forbidden to discharge domestic sewage and household garbage to river. (6) During the construction process, advanced equipment shall be adopted as much as possible to reduce the disturbance of construction noise on normal lives and rest of residents around. Besides adoption of necessary prevention and control measures to mitigate disturbance, the contractor shall also post announcements in housing estates. The residents are requested to understand and support so as to reduce incompatibility resulting from construction and benefit smooth progress of Project. 2 Hunan Research Institute for Nonferrous Metals (7) Construction personnel will rent local villager’s residences for lease. Field construction camp shall not be set up separately. (8) During work on construction site and construction of canal embankments, watering shall be timely conducted to reduce dust based on weather conditions. As for building materials thrown and scattered on the nearby roads, contractor in charge of construction in each bid section shall assign special personnel to timely clean so as to reduce pollution caused by raising dust to environmental air quality. (9) Formulate construction plan and carry out construction of channel works. The influence of construction period on use of irrigation water in agricultural land along the river bank shall be considered. Construction shall be better implemented in non-irrigation period. Temporary water passage shall be built when necessary to ensure irrigation water of agricultural land. 3. Construction Site Management Measures The project construction unit must abide by the following management measures to minimize adverse environmental influence caused from the construction site. (1) Working hours The construction time is within 8:00~20:00. During lunch break from 12:00 at noon to 14:00 in the afternoon, construction is prohibited. Besides, when it is unavoidable to construct at night, surrounding residents shall be notified and relevant formalities shall be handled. Moreover, measures shall be adopted to reduce influence on such residents. Access of construction transport vehicles shall comply with requirements of local government; (2) Borrow area and spoil (slag) ground It is not required to borrow earth during construction according to engineering features of irrigation facilities involved in this Project. Therefore, no borrow area is set up. During construction, “zero balancing” of earthwork and stonework is realized through reasonable allocation and transport of excavation. No spoil ground is set up. (3) Wastewater sedimentation basin is set up on construction site. The construction wastewater is reused for construction work after sedimentation and it is not discharged outside. Instead, the domestic sewage is collected and treated in the toilets of villager’s 3 Hunan Research Institute for Nonferrous Metals residence and then used by local farmers for agricultural land fertilization. (4) Public information platform ①Set up construction nameplate in eye-catching position to make clear of name of Project, scope of construction site, names of development organization, construction organization, supervision unit and regulatory body, name of Project leader, date of completion and supervision and complaint hotline, specific environmental protection measures, etc.; ②The construction unit shall post letter of notification of commencement around the site 7 days before planned commencement of the project. The letter of notification shall contain information such as Project overview, construction plan, names of units responsible for construction, name of Project leader, complaint hotline, etc.; ③Construction at night is restricted. The influence of construction at night on surrounding environment shall be controlled and residents shall be informed ahead of time under special circumstances in order to obtain their understanding; ④The construction unit shall post notice to inform the public in Project points and around affected residents and enterprises 5 days before service interruption (including water, electricity, communication, traffic, etc.). (5) Accident risk prevention The construction unit shall formulate accident prevention plan ahead of time and set up person in charge of emergency accident. Once an accident occurs, the construction unit may seek help from relevant department; (6) People’s safety and health Construction site shall be isolated and enclosed and traffic signs and guard bars shall be set up to ensure pedestrians’ safety; safety training shall be carried out for construction personnel before construction and personal protection facilities shall be provided and required for mandatory use; ensure that materials containing asbestos or other toxic substances are disassembled and handled by specially trained workers; all work shall be stopped in case of rainstorm or any emergency. (7) Prohibited matters 4 Hunan Research Institute for Nonferrous Metals It is prohibited to fell trees at will beyond the approved construction area; it is prohibited to use unapproved toxic substances, such as lead paint and asbestos; it is prohibited to use open fire or let workers to use alcohol. 4. Construction Site Construction and Facility Management Measures 4.1 Management of Construction Building Materials Building materials used in the construction of irrigation facility works mainly include sand, stone, cement, quick lime, raw wood, steel and brick. If these building materials are not properly handled during transport, storage and use, different degrees of influence will be imposed on the environment. Therefore, relevant environmental protection prevention and control measures shall be adopted to minimize such influence. The proposed management measures during transport, storage and use of construction building materials during construction of irrigation facility works are shown as follows: (1) Low-noise vehicles shall be used. The daytime transport shift system shall be strictly executed and management shall be strengthened to reduce number of times of transport at night under abnormal conditions; (2) Speed restriction control measure is adopted for transport vehicles. When passing through environmental protection objectives (e.g. hospitals, residential areas, schools, etc.), the vehicles shall slow down; (3) Vehicle access signboard shall be set up. Vehicle drivers shall drive the vehicles in a civilized way to ensure safe transport; (4) Powdery materials such as cement and lime shall be canned or bagged. Bulk transport is prohibited; vehicles transporting aggregates and construction materials shall be provided with anti-scattering equipment. Excessive loading shall be avoided to prevent materials from being blown up by big wind. It is strictly forbidden to let such materials raise dust and scattered during journey of transport. Felt cloth must be covered; transport route and time shall be properly planned to reduce the influence on environmental sensitive points (areas) as much as possible; (5) Place for stacking of powdery building materials shall be selected 300m along the downwind direction of environmental sensitive point. Stocking volume shall be reduced 5 Hunan Research Institute for Nonferrous Metals and the building materials shall be timely utilized. Measures preventing wind and rain shall be adopted during stacking. Fences shall be set up and watering shall be conducted in fixed timing to prevent raising dust when necessary. Felt cloth shall be added under severe weather conditions; (6) Construction vehicles must be checked on a regular basis and damaged carriages shall be timely repaired to reduce scattering of building materials and wastes of vehicles during driving; (7) Management of transmission and use of powdery materials shall be strengthened during construction period. Watering and cleaning shall be conducted for working faces easily generating secondary raising dust. 4.2 Management of Construction Equipment Construction equipment used for construction of irrigation facility works mainly includes excavator, blender, vibratory unit and tamping machine. Noise and tail gas generated by such construction equipment during construction as well as possible deflation, water emission, liquid dripping and liquid leakage would have an influence on environmental elements in the demonstration areas. In order to minimize such adverse influence, it is planned to adopt the following management measures: (1) Construction equipment shall be stored according to construction area divided. It is not allowed to park construction equipment at will beyond the construction site in order to avoid increase of area of temporary land occupation and destruction of vegetation and soil; (2) Low-noise equipment shall be adopted as construction equipment as much as possible; (3) Silencer shall be installed at equipment noise source to eliminate sound. To be specific, silencers shall be set up in proper positions where various exhaust and venting devices pass through air pipes; meanwhile, foundation damping or damping support may be adopted; (4) Fuel oil consuming construction machinery and machinery must be used under normal status to ensure standard emission of waste gases; 6 Hunan Research Institute for Nonferrous Metals (5) Equipment shall be reasonably used and equipment maintenance and repair of equipment shall be strengthened to prevent the occurrence of deflation, water emission, liquid dripping and liquid leakage and avoid causing influence on surface water environment, soil environment, etc. in the demonstration areas. 5. Environmental Protection Provisions on Construction Stockyards 5.1 Quarry Gravel materials used for Project construction are usually adopted from the existing qualified quarry. Aggregates needed for construction of irrigation facility works shall be purchased from aggregate factory with formal business license in Demonstration areas. However, noise and raising dust generated during handling and vehicle transport of aggregates as well as stacking and storage of aggregates in construction place shall be strictly managed and controlled. 5.2 Prefabrication and Mixing Yard Sand gravel cushion paving + Concrete precast block + Channel lining + Pointing construction procedure shall be adopted for irrigation and drainage channel of irrigation facility construction. Prefabrication and mixing yard shall be arranged around construction point according to environmental features along irrigation channel and based on direction of irrigation channel planned and designed. Noise and maintenance wastewater generated during machinery mixing, vibration of vibratory unit and watering maintenance will have an influence on surrounding acoustic environment and surface water environment. (1) Prefabrication and mixing yard shall be selected 300m beyond downwind direction of environmental sensitive points. Fence shall be set up when necessary; (2) Silencer shall be installed at noise sources of blender and vibratory unit to eliminate sound. Meanwhile, foundation damping or damping support may be adopted; (3) Maintenance wastewater is comprehensively utilized after being treated in temporary sedimentation basin set up. (4) The construction unit is recommended to reasonably arrange construction personnel and reduce the operation time of operators of high-noise machinery. Earmuffs can be equipped for construction personnel to reduce the influence of noise on construction personnel. 7 Hunan Research Institute for Nonferrous Metals 6. Environmental Protection Provisions On Society The reconstruction of field irrigation facilities mainly has an influence on agricultural land water conservancy along the line. The management measures are shown as follows: (1) Parallel operation shall be adopted during construction excavation. Excavation, leveling and protection shall be conducted simultaneously. Landscape reconstruction shall be timely carried out. (2) In order to ensure unimpeded water channels in agricultural land and prevent water and soil loss, reconstruction of drainage and irrigation channels and construction shall be arranged in non-irrigation period as much as possible. Solid wastes in river channels shall be timely cleared after completion to ensure unimpeded river channels during irrigation period. 7. Protection Management Provisions on Cultural Relics and Historic Sites If cultural relics and historic sites are discovered or suspected during construction period, the construction unit shall immediately protect the scene and report to local cultural relics bureau to handle the matter according to Cultural Relics Protection Law of the People’s Republic of China (December 29, 2007) and requirements of material cultural resource policies of World Bank. The construction may be resumed after treatment of cultural relics bureau. The reporting procedures of cultural heritage are shown in Figure 7-1. If cultural relics and historic sites are discovered or suspected during construction process, the construction unit shall implement the followings: (1) Construction in the construction position where cultural relics are discovered shall be immediately stopped and site protection shall be strengthened; (2) The contractor shall timely report to competent policy affairs and cultural relics department for authentication and handling; (3) Once the objects discovered are determined by experts as cultural relics, the scope of protection shall be immediately divided; (4) Cultural relics shall be rescued and excavated indeed due to demanding construction period or in case of danger of natural destruction; (5) Rescue and digging of cultural relics must be carried out by professionals using special equipment. The contractor shall not dig without authorization; (6) Once the objects are judged as major cultural relics findings, demonstration as 8 Hunan Research Institute for Nonferrous Metals whether the project shall be constructed in other place shall be carried out. Figure 7-1 Procedure Diagram for Handling of Cultural Relics Discovered during Construction Period 8. Environmental Protection Provisions on Noise Pollution Prevention and Control The noise sources during construction period mainly includes mechanical noise generated by construction equipment such as excavator and blender as well as transport vehicles with sound level above 85dB(A). Influence of construction noise to different extents will be imposed within scope of 30m, 80m and 150m around construction site with or without shielding. The following measures are adopted to improve the acoustic environment quality of main protection objectives mentioned above. 9 Hunan Research Institute for Nonferrous Metals (1) Strengthen environmental quality on construction site and strictly execute stipulations set out in Noise Limits for Construction Site. In order to reduce the influence of construction on residents around, the construction time is stipulated as from 8:00 in the morning to 20:00 at night. During lunch break from 12:00 at noon to 14:00 in the afternoon, construction is prohibited. (2) Post construction announcements in housing estates around construction site and meanwhile clearly mark the construction team, which cannot only comfort the people and obtain their understanding but also supervise the construction party to benefit the completion of the project as scheduled. (3) In sensitive points such as school, the operation of high-noise equipment shall be implemented beyond school time; high-noise equipment shall not be operated during lunch break. During construction in areas around sensitive points such as schools, the operation time of high-noise equipment shall be shortened as much as possible. Low-noise machinery shall be adopted during selection of construction equipment and methods as much as possible. (4) Method of “centralization of force and construction section by section” shall be adopted to shorten construction period and lighten the influence of construction noise on acoustic environment in local sections. (5) In order to ensure the health of construction personnel, the construction unit is recommended to reasonably arrange personnel’s working times according to Hygienic Standards of Noise of Industrial Enterprises to let the personnel operate construction machinery with high radiation and noise in turn so as to reduce the duration exposed to high noise. Meanwhile, the construction unit shall pay attention to machine maintenance and correct operation so as to maintain the noise of road building machine at the lowest sound level. Operators and relevant personnel are recommended to adopt individual protective measures such as wearing of earplugs and helmets. 9. Environmental Protection Provisions on Atmospheric Pollution Prevention and Control The main polluting factors of the proposed Project influencing the environmental air during construction period include construction waste gases and raising dust. Waste gases mainly refer to tail gas exhausted by various kinds of construction machinery and transport vehicles; raising dust generated during construction period is mainly generated from site excavation and backfill, transport and handling of materials such as stone and cement, as 10 Hunan Research Institute for Nonferrous Metals well as road raising dust generated during construction work. Meanwhile, leveling of the site also generates a little quantity of raising dust. The main pollutant is TSP. (1) Raising dust pollution prevention and control measures The construction unit shall strictly strengthen management and adopt proper measures to strictly control raising dust generated during construction period. In order to minimize the influence of construction Project on surrounding environment during construction period, it is recommended to adopt the following prevention and control measures: ①Special personnel shall be allocated in construction work area to take charge of scientific management and civilized construction; measures shall be adopted during construction period to accelerate Project progress as much as possible. Also, stonework and earthwork shall be timely transported to designated places to shorten the hazard period of stacking. ②The terrace on construction site must be hardened and concrete terrace shall be adopted if the condition allows. ③Watering keeps the work under certain humidity during excavation; loose and dry surface soil within construction site shall also be constantly watered to prevent dust; during backfill of earthwork, watering shall be properly conducted when the soil texture in the surface layer is dry to prevent raising dust. ④Strengthen the management of backfill earthwork stacking yard and formulate measures for earthwork surface compaction and regular water spraying and covering; mud and waste slag of building materials not needed shall be timely transported away and shall not be stacked for a long term. ⑤Earth transport trucks and building material transport trucks shall be equipped with spraying prevention devices as stipulated. The materials shall not be overloaded to ensure that they are not scattered during transport process; also operation routes and time of transport vehicles shall be properly planned to avoid driving in sensitive areas such as traffic centralization area and residents’ residences. ⑥Over-canopy is added on transport vehicles. The loading and unloading place shall be flushed first to reduce spreading of mud carried by wheels and chassis on the pavement. ⑦Mud spread on the pavement during transport shall be timely cleaned to reduce raising dust during operation. ⑧Materials easily generating raising dust such as sand and cement stacked in the open air shall be covered with canvas and plastic cloth to prevent diffusion of raising dust. 11 Hunan Research Institute for Nonferrous Metals ⑨Road and vegetation on the site occupied by construction shall be timely recovered upon end of construction. ⑩Construction transport work shall be reasonably arranged. Transport of large components during construction work as well as abundant materials and spoils shall be transported beyond peak traffic hours so as to lighten traffic pressure. (2) Transport vehicle tail gas pollution prevention and control measures ①Construction machinery and vehicles under favorable operation conditions shall be selected and used. ②Fuel oil consuming construction machinery and vehicles shall be used under normal status to ensure standard emission of waste gases. ③Reasonably use equipment and strengthen maintenance and repair of equipment. 10. Environmental Protection Provisions on Water Environment Influence (1) Materials such as cement and gravel shall be covered with tarpaulin during stacking and such materials shall not be stacked alongside river. Fence shall be set up when necessary to prevent such materials from flowing into river together with rainfall runoff and causing pollution during rainy season or rainstorm. (2) The waste slag during construction is prohibited to be dumped to river. Instead, it shall be transported to stipulated fill point or stipulated place for unified treatment. (3) Intercepting ditches shall be set up around machinery stacking yard in maintenance work area to prevent machinery oil dirt from flowing into surrounding environment with rainwater and causing pollution during rainy days. Also, the sewage collected in intercepting ditches shall go through oil separation and sedimentation treatment before natural evaporation. Household garbage generated shall be properly managed, collected on a regular basis and transported to designated place for treatment. Meanwhile, maintenance work of machinery in maintenance work area shall be properly conducted to prevent pollution of machinery oil dirt. (4) Serious oil leakage of construction machinery shall be prevented. It is prohibited to discharge oily water generated by machinery during operation to nearby water bodies, or discharge oily water generated during repair of construction machinery to water body. 12 Hunan Research Institute for Nonferrous Metals (5) All Demonstration areas are located in rural area. Therefore, local villagers’ residences can be rented as construction camps. The domestic sewage of construction personnel during construction period will be collected through septic tanks in villagers’ residences and then used for fertilization to reduce environmental pollution. (6) The contractor shall not disturb natural flow of river channel, water channel or existing irrigation or drainage system without written consent of supervision engineer ahead of time in order to avoid the occurrence of scouring and sedimentation no matter what the demand is. 11. Environmental Protection Provisions on Disposal of Solid Wastes Solid wastes generated during Project construction period mainly include building garbage and household garbage. The main building garbage generated during construction period is inorganic wastes, mainly including leftovers during construction such as abandoned stacked earth and concrete blocks. Also, a little quantity of organic wastes is included, mainly including various packing materials, abandoned old plastics and foams. These wastes are not easy to rot or dissolve and therefore the surrounding landscape and environmental quality may be influenced if they are not properly treated. In order to avoid the occurrence of such problems, the construction unit is required to classify and treat wastes generated from construction, demolition and site clearing. Materials that can be directly reutilized or recycled shall be classified, recycled and reutilized. The remaining materials may be timely cleared by relevant entrusted clearing and transport unit. Local digestion measures are adopted to return the earthwork and stonework excavated during construction to nature (they shall be properly filled and compacted). Household garbage generated during construction period is mainly organic wastes including leftovers and excrements. Such solid wastes will rot, become smelly and give birth to mosquitoes if they are stacked in construction area at will and not timely and effectively treated. If the situation is serious, it can induce various infectious diseases to affect construction personnel’s physical health. The household garbage generated during construction period of the proposed Project will be centrally collected and then cleared and 13 Hunan Research Institute for Nonferrous Metals transported to refuse landfill. Leftovers will be collected and then used by farmer households to feed pigs, and excrements will be used for fertilization. 12. Environmental Protection Provisions On Ecological Environment 12.1 Ecological Resource Protection and Management Measures (1) Reasonably optimize layout of construction site, reduce scope of construction activities and reduce the degree of damage caused by Project implementation to vegetation; (2) Building materials that shall be purchased during construction such as stone, sand and cement; they shall be transported when needed. Land occupation and vegetation damage shall be reduced; after completion of Project, construction site shall be timely cleared and construction site shall be greened to recover the damaged vegetation as much as possible; (3) Temporary protective fences shall be established around trees not felled or transplanted within construction site before construction according to checking results of construction site; (4) It is not allowed to add other signs besides identification label on the trees or stack or store building materials and park mechanical equipment around tree protection areas; (5) Temporary intercepting ditch shall be built on construction site, and flood guiding channel shall be constructed for surface runoff channel damaged for the project so as to lead the flood formed in rainy season away and avoid scouring of surface runoff to the project; (6) The construction unit shall shorten time of temporary land occupation, control construction time of earthwork, maintain stable excavation and filling of side slope and reduce the influence beyond Project construction under the precondition that construction quality is ensured. 12.2 Water and Soil Conservancy Measures (1) Temporary measures During stacking of sand gravel materials needed for excavation and backfill of earthwork of buildings and structures as well as construction Project, in order to avoid wind erosion and water erosion. Temporary covering measure shall be adopted for 14 Hunan Research Institute for Nonferrous Metals protection. Temporary protective measures adopted mainly include temporary straw bag pressing, covering and watering. ①Covering In order to prevent wind erosion and water erosion, temporary covering measure is adopted for exposed parts of slag body in this temporary mound yard. Dense-mesh dustproof net is selected and used as covering material. Demolition of dustproof covering shall be carried out upon start of earthwork backfill. The dustproof net shall be gradually rolled up backward from a place close to foundation pit. The dustproof net will be recycled after earthwork is fully back filled. ②Temporary pressing measure using earth loading straw bag Dustproof net around temporary mound yard shall be pressed by earth loading in straw bag. Requirements for removal of straw bags: When backfill is conducted after completion of casting of building foundations of main works, the straw bags around shall be manually removed from two sides from the opening and the earth in the straw bags is continuously filled into foundation pit. Straw bags can be recycled for reutilization. ③Watering Watering shall be conducted for 1-2 times after land remediation of construction site. Surface crust with thickness enough to effectively resist wind erosion can be formed if the degree of infiltration of soil reaches approximately 2cm, which benefits recovery of water and soil conservation functions. (2) Engineering measures ①Concave-convex leveling and backfill: Including determination of backfill area and depth, unit weight of backfill object and unit weight of grinding as well as backfill grinding method as well as determination of possible sinking and its hazard prediction and protective measures; ②Plan transport routes of backfill object and earth covering; ③Pit backfill and utilization: During pit backfill, abandoned earth and stone slag shall be fully utilized to strive to realize leveling of pit and full consumption of slag after backfill.The backfill method is determined according to factors such as terrain, 15 Hunan Research Institute for Nonferrous Metals construction conditions and area. Manpower and machinery combined method is usually adopted. When area remediated is relatively big, bulldozer is adopted to conduct trip-type remediation. The lap width between strips is 0.5m; as for corners with relatively area in which mechanical operation is unavailable or applicable, manpower will be employed to remediate dead angles. Shovels are adopted for manpower remediation to carry out pit backfill within depth of 0.3m in remediation area; ④During rough remediation, key parts requiring backfill shall be determined according to features of landform and terrain in Demonstration area. Then, construction machinery such as bulldozer shall be adopted to transport the earthwork to filling area of pit place. During pit backfill, relatively fine sand gravel shall be used and compressed below, while macadam with relatively big grain size shall be paved above and then flatly grinded. After end of rough remediation, tools such as shovel shall be manually used to shovel parts such as edges and dead angles of construction area disturbed and small pits left over by machinery remediation flatly. The landfill treatment shall finally meet the design requirements of leveling. (3) Vegetation measure During vegetation recovery in construction area after end of Project, local species shall be adopted and introduction of external species shall be avoided. 13. Environmental Protection Provisions on Construction Safety The construction unit is responsible to abide by all national and local safety requirements as well as other measures capable of avoiding accidents to ensure safety and health of construction personnel. (1) Occupational health and safety training shall be carried out to all construction personnel, and basic work rules and personal protection rules in construction place shall be introduced to them as well as that how to prevent injuries of other employees shall be noticed; (2) Fire-extinguishing equipment shall be equipped in construction place. Enough fire-extinguishing equipment shall be provided and maintained at any time to keep them under good working status. Besides, such equipment shall be put in places easy to get; 16 Hunan Research Institute for Nonferrous Metals (3) The construction unit shall ensure to provide eligible emergency rescue and allocate emergency rescue tools in construction place; written emergency handling procedure shall be formulated in remote places to facilitate the transfer of patients to proper medical organizations; (4) Correct signboard shall be suspended on devices, materials, safety measures and emergency exits of dangerous areas (distribution room, etc.); (5) If workers’ hands and arms are subject to vibration due to use of tools on their hands and power-driven tools, or the whole bodies of workers are subject to vibration due to standing or sitting on vibrating surfaces, damping cushion or device shall be installed through equipment selection to implement control over restriction of exposure time; (6) Place warning plates on all power-on electric devices and electric wires; check all electric wires, cables and power-driven tools on the hands, check if there is damaged or exposed electric wire, and determine maximum allowable working voltage of such tools according to the suggestions of manufacturers; carry out double insulation/grounding treatment of all power-drive equipment used in moist (or possibly moist) environment; (7) Provide all workers participating in or assisting welding work with proper eye protection tools (e.g. welding goggles and/or masks); (8) Guardrails (one middle bar and surrounding baffles) shall be installed at the edge of vulnerable areas. Meanwhile, the construction personnel shall adopt fall preventive devices (including safety belt and distance restriction lacing wire); (9) The construction unit determines and offers proper individual protection equipment to construction personnel so as to fully protect workers themselves, other workers and occasional visitors. Besides, such equipment shall not bring unnecessary inconveniences to users; (10) The construction unit shall establish procedures and systems to report and record occupational accidents and diseases as well as dangerous conditions; (11) Carry out health education of construction, enhance face-to-face consulting work and encourage individuals to take protective measures; besides, the construction personnel are encouraged to use blocking methods such as mosquito repellent, clothes and mosquito 17 Hunan Research Institute for Nonferrous Metals net to avoid mosquito bites spreading diseases. 18 Hunan Research Institute for Nonferrous Metals Appendix 3 Hunan Integrated Management of Agricultural Land Pollution Project World Bank Loan Agricultural Activities Environmental Protection Procedure Foreign Economic and Technical Cooperation Center, Agriculture Commission of Hunan Province Hunan Research Institute for Nonferrous Metals July 2018 Environmental Protection Procedure of Agricultural Activities 1 Environmental Protection Measures for Lime Application 1.1 Lime Quality Requirements Lime material selected in this Project: It is a composite product comprising quick lime (CaO content>70%), dolomite (CaO+MgO content>45%) and limestone (CaCO3 content >45%) with ratio of 1:3:6. The quality indexes are required as follows: Fineness: Passing of 1mm standard sieve ≥80%; The content of As is ≤ 10.0 mg/kg; cadmium (CD) content ≤ 1.0 mg/kg; lead (Pb) content ≤ 50 mg/kg; chromium (Cr) content ≤ 50 mg/kg; mercury (Hg) content ≤ 2.0 mg/kg; water ≤ 5.0; pH ≥ 9.5. 1.2 Lime transport (1) Bid invitation is adopted to ensure timely application. Public purchasing by invitation to bid is adopted for late rice according to normal procedure. After determination of bid winner, the bid inviter will sign quick lime powder product supply service contract with the bid winner and the bid winner shall transport the product to village groups where the project is conducted as scheduled with required quantity. (2) Waterproof cloth shall be adopted during transport to cover the lime and prevent spreading and overflow of lime during transport. 1.3 Protective measures for lime application (1) When using lime, the lime application personnel shall pay special attention to their safety protection. They shall wear masks, eyeshades (or goggles) and work clothes. After completion of lime application, they shall timely take showers and change cloths. (2) During process of lime application, even application shall be realized to prevent excessive local concentration. (3) During storage of lime, weather and moisture prevention shall be noticed. Lime shall not be stored for a long term. It shall be better used when received. Besides, lime shall not be simultaneously used with chemical fertilizers and pesticide. 1 Hunan Research Institute for Nonferrous Metals 1.4 Determination of application period In order to make it convenient for farmers to use, lime application shall be better carried out beyond busy season and high-temperature season. Period of lime application once every year shall be flexibly determined according to different planting systems. (1) Double cropping rice-slack winter season area. Lime is evenly applied in paddy field about 1 month before winter or transplanting of early season rice. Then, the paddy field shall be ploughed immediately or before transplanting of early season rice. (2) Double cropping rice oilseed rape/green manure area. Lime is evenly applied in paddy field 2-3 days before oilseed rape straws or green manure is ploughed. Then, the paddy field shall be ploughed immediately to transplant early season rice. (3) Oilseed rape-single cropping rice area. Lime is evenly applied in paddy field about 15 days before transplanting of middle-season rice after harvesting of oilseed rape. Then, the paddy field shall be ploughed immediately or before transplanting of middle-season rice. (4) Tobacco-late-season rice area. Lime is evenly applied in paddy field in winter or about 1 month before transplanting of flue-cured tobacco. Then, the paddy field shall be immediately ploughed. Other attentions (1) During top dressing of lime, there shall be no water on the standing grain leaves. In other words, lime shall not be applied in the morning when there is dew or after rain, or under the weather condition of big wind. (2) During application of lime, organic fertilizer shall be applied as coordination. (3) Lime shall not be mixed with chemical fertilizers especially ammonium nitrogen and thoroughly decomposed excrements and urines of people and livestock during application to avoid loss of nitrogen fertilizer. (4) Lime shall not be mixed with trace elements such as boric fertilizer so as to prevent the reduction of effectiveness of lime. 2 Hunan Research Institute for Nonferrous Metals 2 Environmental Protection Measures for Application of Soil Passivator 2.1 Soil Passivator Quality Index The harmful heavy metal indicators of Hg, As, Cd, Pb, Cr. etc. in soil passivator are shown as below: Mercury (Hg) content ≤2.0 mg/kg (on the dry basis); Arsenic (As) content ≤5.0 mg/kg (on the dry basis); Cadmium (Cd) content ≤1.0 mg/kg (on the dry basis); Lead (Pb) content ≤50 mg/kg (on the dry basis); Chromium (Cr) content ≤50 mg/kg (on the dry basis); 2.2 Selection of Soil Passivator (1) The product of soil conditioner must be registered in the agricultural department. (2) The Cd passivator of soil must be the product in the Recommended Product List of Exhibited New Products in 2015-2017 of the “Trial of restoration of agricultural land contaminated by heavy metal and the growing structure adjustment of crops in Hunan”. Meanwhile, it is required that when the soil pH is lower than 5.5, the Cd reduction effect in rice for the applied product reaches above 50%, when pH is 5.5 to 6.5, the application effect reaches over 40%, and when pH is greater than 6.5, the application effect reaches over 30%. (3) The As passivator as well as the Cd-As synchronous passivator of soil must be subjected to the test demonstration by the scientific research and teaching unit which has the capability of working on relevant professional research and study and which is above the provincial level to prove its effect. After applying the As passivator and the Cd-As synchronous passivator, if As and Cd-As in rice is synchronously reduced by over 30%, it is required to supply the product for free to carry out a demonstration in a small area in the demonstration area, and the demonstration area can be enlarged after proving the effect. 2.3 Temporary Storage Requirements A specific indoor warehouse is set up to temporarily store and soil passivator. The temporary storage warehouse shall resist rain, wind and seepage. 3 Environmental Protection Measures for Application of Organic Fertilizers 3.1 Selection and Use of Commercial Organic Fertilizers The specific indexes of commercial organic fertilizers are as follows: 3 Hunan Research Institute for Nonferrous Metals (1) Technical indexes: Organic matter (calculated on dry basis) ≥45%; Total nutrient (nitrogen + phosphorus pentoxide + potassium oxide) (calculated as per dried basis): ≥5.0; Moisture (fresh sample): ≤15%; Potential of hydrogen (PH): 5.5-8.5. (2) Metal indexes: Total Cadmium (Cd) (calculated as per dried basis) ≤1.5 mg/kg; Total Arsenic (As) (calculated as per dried basis)≤15 mg/kg; Total Mercury (Hg) (calculated as per dried basis)≤2.0 mg/kg; Total Lead (Pb) (calculated as per dried basis)≤50 mg/kg; Total Chromium (Cr) (calculated as per dried basis)≤150 mg/kg; Total copper (Cu) (calculated as per dried basis)≤50 mg/kg; Total zinc (Zn) (calculated as per dried basis) ≤200 mg/kg. (3) Bacterial indexes Number of fecal coliforms ≤100 pcs/g; Death rate of ova of roundworm ≥95%. 3.2 Attentions during Application of Organic Fertilizers (1) Use of commercial organic fertilizers is promoted. Commercial organic fertilizers already passing field test, confirmed as safe through secondary pollution evaluation, and certified and registered by relevant certification organization shall be selected. (2) The element content of Cd, As, Hg, Pb, Cr, etc. in the applied manure fertilizer must be lower than relevant index. (3) If manure of livestock and poultry is used as organic fertilizer, the feeds used to feed livestock and poultry must comply with requirements of Hygienic Standard for Feeds (GB 13078-2001). (4) As for livestock’s excrements generated by surrounding farmer households in breeding industry, PMO shall strengthen supervision. Excrements generated by breeding industry without detection or exceeding standard during monitoring shall not be delivered to agricultural land in order to prevent bringing new heavy metal contamination. 4 Hunan Research Institute for Nonferrous Metals (5) Attentions to use of bio-organic fertilizers ①The bio-organic fertilizers shall not be applied to a very deep earth layer. It is suitable to apply the bio-organic fertilizers at a place of 10-15cm below the surface. ②During application, bio-organic fertilizers shall be not mixed with single chemical fertilizer.Since single chemical fertilizer has singular ingredients and the pH value differs, if it is abundantly applied, the biological activity of bio-organic fertilizers will be inevitably compromised.Therefore, bio-organic fertilizers shall be better separately applied. ③The proportioning of bio-organic fertilizer, farm manure and DAP compound fertilizer shall be reasonable.When they are selected and used, they shall be calculated first and then scientific proportioning shall be carried out before application. 4. Environmental Protection Measures against Agricultural Material Package Wastes (1) Strengthening publicity and enhance farmers’ environmental protection awareness Since farmers are the subjects using agricultural material and producing agricultural material package wastes, it is required to strengthen technical training of scientific use of pesticide and other agricultural products for the farmers and enable them to get to know the hazards of agricultural material package wastes to agricultural production and environment and enhance their environmental protection awareness. Also, the farmers shall be educated not to abandon agricultural films at will and to collect and take away agricultural material package wastes. (2) Implementing centralized collection and avoiding storage at will Agricultural material package waste collection points are set in each Demonstration area. Farmers are required to waste agricultural films, pesticide and agricultural material packages already used up in collection points.Meanwhile, they shall contact with agricultural material package recycling station of Counties and transport agricultural material package wastes in the collection points to the recycling station on a regular basis. (3) Strengthening management and ensuring transfer treatment PMO shall strengthen management and supervise the collection and transfer work of 5 Hunan Research Institute for Nonferrous Metals agricultural package wastes to ensure that all such package wastes in Demonstration areas are transported to agricultural package recycling station of Counties that shall recycle such wastes or entrust a qualified unit to treat such wastes. 5. Environmental Protection Measures for Removing Straw from Agricultural Land (1) PPP mode is adopted as operation mechanism to motivate and subsidize farmland operators or professional harvesting cooperatives to change harvesting model (semi-feeding harvesting to ensure overall straw relocation and utilization) and increase crushed grass bundling method (bundling machine can be purchased for harvesting) to realize relocation of crop straws from agricultural land in Demonstration areas. (2) The PMO arranges a part of fund, the forestry company or the cooperative purchases in a unified manner to dispose in a centralized manner, so that it can obtain profit from it to maintain normal operation of the project. (3) By adopting the principle of proximity in the demonstration area, transport the straws into the nearby forest land or the orchard planting base to be used as fertilizer in the forest land or be used for covering and sheltering the orchard base. (4) PMO shall strengthen supervision to ensure that straws are smoothly transported out of the agricultural land and properly disposed. 6. Environmental Protection Measures for Management and Control of Standard-Exceeding Rice in the Husk (1) PMO shall strengthen supervision and entrust relevant unit with relevant detection qualification to detect the rice in the husk in demonstration areas on a regular basis and avoid entry of contaminated rice rice in the husk in demonstration areas to grain ratio market. (2) As for rice with cadmium content ＞0.2mg/kg, it will be purchased by a special enterprise to be used as raw material for liquor making after the project county cooperates with relevant wine companies. (3). The vinasse, a by-product during wine brewing, shall be dried and then transported to refuse landfill for sanitary landfill. 6 Hunan Research Institute for Nonferrous Metals Appendix 4 Technical Plan to be Adopted by Newly-added Demonstration Area of Each Project County Table 4-1 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Yongding District Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at low risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; Touxi Village 67.33 milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Cd content of rice straw is relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply cadmium and arsenic synchronous passivator and apply 3.0 t/ha per year during extremely high (The enrichment coefficient 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at low risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Shiyanping arsenic pollution has no risk; Yuanguping 32.00 milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Village Cd content of rice straw is relatively high. Demonstration area from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply cadmium and arsenic synchronous passivator and apply 3.0 t/ha per year during extremely high (The enrichment coefficient 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at medium risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Hongxing arsenic pollution has no risk; milk stage and keeping moist from the milk stage to the ripening stage with no irrigation 65.07 Village Cd content of rice straw is relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply cadmium and arsenic synchronous passivator and apply 4.5 t/ha per year during extremely high (The enrichment coefficient 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 7 Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, Rice cadmium pollution is at low risk and fertilizer and pesticide shall be strengthened; rice arsenic pollution is at low risk; 2. Popularize the rice species with low cadmium and arsenic absorption; Soil cadmium pollution is at low risk and soil 3. Optimization of water management: controlling moisture before the tillering stage, drying arsenic pollution has no risk; the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Hongtuping 30.13 Cd content and As content of rice straw are milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Village relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply cadmium and arsenic synchronous passivator and apply 4.5 t/ha per year during extremely high (The enrichment coefficient 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at medium risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Changtan arsenic pollution has no risk; 25.67 milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Village Cd content of rice straw is relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply cadmium and arsenic synchronous passivator and apply 4.5 t/ha per year during extremely high (The enrichment coefficient 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at low risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Gaoping arsenic pollution has no risk; 32.73 milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Village Cd content of rice straw is relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply cadmium and arsenic synchronous passivator and apply 3.0 t/ha per year during extremely high (The enrichment coefficient 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. Rice cadmium pollution is at low risk and 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, rice arsenic pollution is at low risk; fertilizer and pesticide shall be strengthened; Yinjiaxi Demonstration Xinglong Soil cadmium pollution is at low risk and soil 2. Popularize the rice species with low cadmium and arsenic absorption; 44.73 area Village arsenic pollution has no risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Cd content and As content of rice straw are the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the relatively high. milk stage and keeping moist from the milk stage to the ripening stage with no irrigation 8 Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) The risk of cultivation management for rice is from about the 10th day of the ripening stage; extremely high (The enrichment coefficient 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha of arsenic is relatively high) respectively per year during 2020-2023. 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, Rice cadmium pollution is at low risk and fertilizer and pesticide shall be strengthened; rice arsenic pollution is at low risk; 2. Popularize the rice species with low cadmium and arsenic absorption; Soil cadmium pollution is at low risk and soil 3. Optimization of water management: controlling moisture before the tillering stage, drying arsenic pollution has no risk; the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Qijiaping Cd content and As content of rice straw are 41.40 milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Village relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha extremely high (The enrichment coefficient respectively per year during 2020-2023. of arsenic is relatively high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, Rice cadmium pollution is at low risk and fertilizer and pesticide shall be strengthened; rice arsenic pollution is at medium risk; 2. Popularize the rice species with low cadmium and arsenic absorption; Soil cadmium pollution is at low risk and soil 3. Optimization of water management: controlling moisture before the tillering stage, drying arsenic pollution has no risk; the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Gaofeng 43.33 Cd content and As content of rice straw are milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Village relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply cadmium and arsenic synchronous passivator and apply 3.0 t/ha per year during extremely high (The enrichment coefficient 2020-2023. of arsenic is relatively high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at high risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is has no risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; Mojiagang milk stage and keeping moist from the milk stage to the ripening stage with no irrigation 32.93 Cd content and As content of rice straw are Village from about the 10th day of the ripening stage; relatively high. 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha The risk of cultivation management for rice is respectively per year during 2020-2023. extremely high (The enrichment coefficient 5. To apply cadmium and arsenic synchronous passivator and apply 3.0 t/ha per year during of arsenic is relatively high) 2020-2023. 6. To apply compound fertilizer in a unified way and the fertilizer access shall be managed 9 Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, Rice cadmium pollution is at low risk and fertilizer and pesticide shall be strengthened; rice arsenic pollution is at low risk; 2. Popularize the rice species with low cadmium and arsenic absorption; Soil cadmium pollution is has no risk and soil 3. Optimization of water management: controlling moisture before the tillering stage, drying arsenic pollution has no risk; the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the Taiji Village 53.47 Cd content and As content of rice straw are milk stage and keeping moist from the milk stage to the ripening stage with no irrigation relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha extremely high (The enrichment coefficient respectively per year during 2020-2023. of arsenic is relatively high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at low risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; Xinglong milk stage and keeping moist from the milk stage to the ripening stage with no irrigation 44.73 Cd content and As content of rice straw are Village from about the 10th day of the ripening stage; relatively high. 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha The risk of cultivation management for rice is respectively per year during 2020-2023. extremely high (The enrichment coefficient 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed of arsenic is relatively high) and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at low risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Yuanda Village 80.00 Yanghuping Cd content of rice straw is relatively high. from about the 10th day of the ripening stage; Demonstration Area The risk of cultivation management for rice is 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha extremely high (The enrichment coefficient respectively per year during 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. Dingjiazhuang Rice cadmium pollution is at low risk and 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, 73.20 Village rice arsenic pollution is at low risk; fertilizer and pesticide shall be strengthened; 10 Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) Soil cadmium pollution is at low risk and soil 2. Popularize the rice species with low cadmium and arsenic absorption; arsenic pollution has no risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Cd content of rice straw is relatively high. the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the The risk of cultivation management for rice is milk stage and keeping moist from the milk stage to the ripening stage with no irrigation extremely high (The enrichment coefficient from about the 10th day of the ripening stage; of arsenic is extremely high) 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha respectively per year during 2020-2023. 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at low risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil Xinqiao the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; Neighborhood 53.80 milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Cd content of rice straw is relatively high. Committee from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha extremely high (The enrichment coefficient respectively per year during 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution has no risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is has no risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Heitan Village 56.60 Cd content of rice straw is relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha extremely high (The enrichment coefficient respectively per year during 2020-2023. Wentang Demonstration of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed Area and controlled strictly, and the organic fertilizer shall be applied appropriately to improve soil quality and capacity. Rice cadmium pollution is at low risk and 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, rice arsenic pollution is at low risk; fertilizer and pesticide shall be strengthened; Soil cadmium pollution is at low risk and soil 2. Popularize the rice species with low cadmium and arsenic absorption; Guanzhuang 51.53 arsenic pollution has no risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Village Cd content and As content of rice straw are the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the relatively high. milk stage and keeping moist from the milk stage to the ripening stage with no irrigation The risk of cultivation management for rice is from about the 10th day of the ripening stage; 11 Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) extremely high (The enrichment coefficient 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha of arsenic is extremely high) respectively per year during 2020-2023. 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly, and the organic fertilizer shall be applied appropriately to improve soil quality and capacity. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution has no risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Baiyun Village 61.67 Cd content of rice straw is relatively high. from about the 10th day of the ripening stage; The risk of cultivation management for rice is 4. To apply lime composite material and apply 4.5 t/ha, 4.5 t/ha, 3.0 t/ha and 3.0 t/ha extremely high (The enrichment coefficient respectively per year during 2020-2023. of arsenic is extremely high) 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed and controlled strictly, and the organic fertilizer shall be applied appropriately to improve soil quality and capacity. 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; Rice cadmium pollution is at low risk and 2. Popularize the rice species with low cadmium and arsenic absorption; rice arsenic pollution is at low risk; 3. Optimization of water management: controlling moisture before the tillering stage, drying Soil cadmium pollution is at low risk and soil the field in the peak tillering stage, flooding by 3-5cm from the peak tillering stage to the arsenic pollution has no risk; milk stage and keeping moist from the milk stage to the ripening stage with no irrigation Bajiao Village 75.13 Cd content and As content of rice straw are from about the 10th day of the ripening stage; relatively high. 4. To apply cadmium and arsenic synchronous passivator: to apply 4.5 t/ha per year during The risk of cultivation management for rice is 2020-2021 and 3.0 t/ha per year during 2022-2023; extremely high (The enrichment coefficient 5. To apply compound fertilizer in a unified way and the fertilizer access shall be managed of arsenic is extremely high) and controlled strictly, and the organic fertilizer shall be applied appropriately to improve soil quality and capacity. 12 Table 4-2 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Jishou City Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectares) 1. Optimize field water management and irrigate with a suitable amount of water; 1. There is no risk of rice cadmium pollution and rice arsenic pollution is at Qianghu 2. Apply the commercial organic fertilizer of 3000kg/ ha/year; 3. Apply the soil low risk; 2. Soil cadmium pollution is at low risk and there is no risk of soil Village, passivator (soil conditioner, 3000kg/ha/season in the first year, and 1500kg/ 10.16 arsenic pollution; 3. The rice enrichment coefficient is at low risk, and the Sanchaping ha/season in the second, third, fourth and fifth year) for the farmland with rice risk (excluding soil) may include the sedimentation, species or Village cadmium and arsenic compound pollution; 5. Measure of removing straws from management risk; 4. Cadmium in rice straws does not exceed the standards. the field; 1. Apply the commercial organic fertilizer of 1500kg/ ha/year; 1. Rice cadmium pollution is at low risk and rice arsenic pollution is also at Hangtuo 2. Apply the soil passivator (soil conditioner, 3000kg/ha/season in the first year, Qianzhou low risk; 2. Soil cadmium pollution is at low risk and there is no risk of soil Village, and 1500kg/ ha/season in the second, third, fourth and fifth year) for the farmland Demonstration Area 14.2 arsenic pollution; 3. The rice enrichment coefficient has no risk, and rice Jilve with cadmium and arsenic compound pollution; risks may include the exogenous (sedimentation), species or management Village 3. Control of standard-exceeding rice; risk; 4.Cadmium in rice straws does not exceed the standards. 4. Measure of removing straws from the field; 1. Rice cadmium pollution is at low risk and there is no risk of rice arsenic 1. Optimize field water management and conduct waterflooding irrigation; pollution; 2. Soil cadmium pollution is at low risk and there is no risk of soil 2. Conduct soil acidification conditioning and apply the lime of 2250kg/ha; Hongping 15.15 arsenic pollution; 3. The rice enrichment coefficient is at low risk, and the 3. Apply the commercial organic fertilizer of 1500kg/ha/year; Village rice risk (excluding soil) may include the sedimentation, species or 4. Control of standard-exceeding rice 5. Measure of removing straws from the management risk; 4. Cadmium in rice straws does not exceed the standards. field; 1. Rice cadmium pollution is at low risk and there is no risk of rice arsenic 1. Optimize field water management and conduct waterflooding irrigation; pollution; 2. Soil cadmium pollution is at medium risk and there is no risk of 2. Conduct soil acidification conditioning and apply the lime of 2250kg/ha; Aizhai 22.1 soil arsenic pollution; 3. The rice enrichment coefficient has no risk, and the 3. Apply the commercial organic fertilizer of 1500kg/ha/year; Community rice risk (excluding soil) may include the species and production 4. Control of s standard-exceeding rice; management risks; 4.Cadmium in rice straws does not exceed the standards. 5. Measure of removing straws from the field; 1. Optimize field water management and irrigate with a suitable amount of water; 1. There is no risk of rice cadmium pollution and rice arsenic pollution is at 2. Apply the commercial organic fertilizer of 1500kg/ ha/year; 3. Apply the soil low risk; 2. Soil cadmium pollution is at low risk and there is no risk of soil Aizhai Demonstration Jiating passivator (soil conditioner, 3000kg/ha/season in the first year, and 1500kg/ 48.5 arsenic pollution; 3. The rice enrichment coefficient has no risk, and the rice Area Village ha/season in the second, third, fourth and fifth year) for the farmland with risk may include the sedimentation, species or management risk; 4. cadmium and arsenic compound pollution; 4. Control of standard-exceeding rice; Cadmium in rice straws does not exceed the standards. 5. Measure of removing straws from the field; 1. Rice cadmium pollution is at low risk and rice arsenic pollution is also at 1. Apply the commercial organic fertilizer of 3000kg/ ha/year; low risk; 2. Soil cadmium pollution is at low risk; 3. The rice enrichment 2. Apply the soil passivator (soil conditioner, 3000kg/ha/season in the first year, Pinglang 18.5 coefficient has no risk, and the rice risk may include the sedimentation, and 1500kg/ ha/season in the second, third, fourth and fifth year) for the farmland Village species or management risk; 4. Cadmium in rice straws does not exceed the with cadmium and arsenic compound pollution; 3. Control of standard-exceeding standards. rice. 4. Measure of removing straws from the field; 13 Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectares) 1. Optimize field water management and irrigate with a suitable amount of water; 1. Rice cadmium pollution is at low risk and rice arsenic pollution is also at 2. Apply the commercial organic fertilizer of 1500kg/ ha/year; low risk; 2. Soil cadmium pollution risk is high and there is no risk of soil 3. Apply the soil passivator (soil conditioner, 3000kg/ha/season in the first year, Liantuan 28 arsenic pollution; 3. The rice enrichment coefficient has no risk, and the rice and 1500kg/ ha/season in the second, third, fourth and fifth year) for the farmland Village risk may include the sedimentation, species or management risk; 4. with cadmium and arsenic compound pollution; Cadmium in rice straws does not exceed the standards. 4. Control of standard-exceeding rice; 5. Measure of removing straws from the field; 1. Optimize field water management and irrigate with a suitable amount of water; 1. There is no risk of rice cadmium pollution and rice arsenic pollution is at 2. Apply the commercial organic fertilizer of 1500kg/ ha/year; low risk; 2. Soil cadmium pollution is at extremely high risk and there is no 3. Apply the soil passivator (soil conditioner, 3000kg/ha/season in the first year, Shu’er 27.2 risk of soil arsenic pollution; 3. The rice enrichment coefficient has no risk, and 1500kg/ ha/season in the second, third, fourth and fifth year) for the farmland Village and the rice risk may include the sedimentation, species or management risk; with cadmium and arsenic compound pollution; 4. Cadmium in rice straws does not exceed the standards. 4. Control of standard-exceeding rice 5. Measure of removing straws from the field; 14 Table 4-3 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Yongshun County Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectare) 1. Rice cadmium pollution is at medium risk and there is no risk of 1. Popularize plantation of rice species with low accumulation; rice arsenic pollution & Pb pollution; 2. Optimize field water management and conduct waterflooding irrigation; 2. Soil cadmium pollution is at medium risk and there is no risk of 3. Conduct soil acidification conditioning: applying 4.5t/ha of lime in 2021, 3.0t/ha Xishaba soil arsenic pollution & Pb pollution; in the second year and 1.5t/ha in the third year; Village, 3. The cadmium enrichment coefficient of rice species is at medium 4. Apply the soil cadmium passivator: applying 4.5t/ha of soil cadmium passivator 26.23 Taozixi risk and the risk of arsenic enrichment coefficient is extremely high; in 2021, 3.0t/ha in the second year and 1.5t/ha in the third year; Village 4. Rice straw cadmium pollution is at medium risk and there is no 5. Adopt leaf inhibitor and control agent; risk of rice straw arsenic pollution & Pb pollution; 6. Apply organic fertilizer: applying 3.0t/ha of organic fertilizer per year during 5. Rice cadmium risk (excluding soil) may include the agriculturally 2021-2023; exogenous, other inputs or management risk. 7. Remove the straws. 1. There is no risk of rice cadmium pollution & arsenic pollution 1. Popularize plantation of rice species with low accumulation; and the rice Pb pollution is at low risk; 2. Optimize field water management and conduct waterflooding irrigation. 2. Soil cadmium pollution is at medium risk and there is no risk of 3. Conduct soil acidification conditioning: applying 4.5t/ha of lime in 2021, 3.0t/ha Shaba Demonstration soil arsenic pollution & Pb pollution; in the second year and 1.5t/ha in the third year; Area Xishaba 3. The cadmium enrichment coefficient of rice species has no risk 42.33 4. Apply the soil passivator: applying 3.0t/ha of soil (cadmium and Pb) passivator Village and the risk of arsenic enrichment coefficient is extremely high; in 2021, 1.5t/ha in the second and the third year; 4. There is no risk of rice straw cadmium pollution and arsenic 5. Adopt leaf inhibitor and control agent; pollution. 6. Apply organic fertilizer: applying 3.0t/ha of organic fertilizer per year during 5. Rice Pb risk (excluding soil) may include the agriculturally 2021-2023; exogenous, other inputs or species and management risk. 1. There is no risk of rice cadmium pollution, arsenic pollution and Pb pollution; 1. Popularize plantation of rice species with low accumulation; 2. There is no risk of soil cadmium pollution, arsenic pollution and 2. Apply the soil passivator: applying 1.5t/ha of soil cadmium and arsenic Taozixi Pb pollution; synchronous passivator in 2021; 60.93 Village 3. The cadmium enrichment coefficient of rice species has no risk 3. Adopt leaf inhibitor and control agent; and the risk of arsenic enrichment coefficient is extremely high; 4. Apply organic fertilizer: applying 3.0t/ha of organic fertilizer per year during 4. There is no risk of rice straw cadmium pollution and arsenic 2021-2023; pollution. 1. There is no risk of rice cadmium pollution & inorganic arsenic 1. Control rice species with high accumulation of heavy metals and popularization Hexin pollution; of rice species with low accumulation; Village, Xiqi Demonstration 2. Soil cadmium pollution is at low risk and there is no risk of 2. Optimization of field water management: changing the waterflooding irrigation Liulangxi 63.00 Area arsenic pollution; in the whole-plant growth stage into a water management mode where seeds are Village, 3. The cadmium enrichment coefficient of rice species has no risk soaked in water, tillers are produced in shallow water, fields are dried when a Xiqi Village and the risk of arsenic enrichment coefficient is extremely high; desired tiller number is reached, booting happens under the wet condition in 15 Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectare) 4. There is no risk of rice straw cadmium pollution and arsenic shallow water and water remains in the field from the heading stage to the filling pollution. stage and is drained after the yellow-ripe stage; 5. Heavy metal pollution risk in agricultural land (excluding soil) 3. Apply the soil passivator: applying 1.5t/ha of soil cadmium and arsenic may include the agriculturally exogenous, other inputs or species synchronous passivator in 2021, and the amount shall be decided as per the and management risk. situation for the second and the third year; 4. Adopt heavy metal leaf inhibitor and control agent; 5. Apply organic fertilizer: applying 3.0t/ha of organic fertilizer per year during 2021-2023; 6. Strengthen the monitoring of heavy metal balance and agricultural inputs in farmland; 16 Table 4-4 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Cili County Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectares) 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 2. Conduct irrigation with a small amount of water, and ensure the cleanness of irrigation water source; Fuxing 1. Rice cadmium pollution is at low 3. Apply the commercial organic fertilizer of 600kg/ha; Village, risk; 2. Rice arsenic pollution is at low 4. Apply cadmium and arsenic synchronous passivator: as per ‘Hunan Integrated Management of Yangliupu Township Xinpu 93.33 risk; 3. Soil cadmium pollution is at Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Cadmium Demonstration Area Village and extremely high risk; 4. Rice straws Reduction by Soil Passivator’ (apply cadmium and arsenic synchronous passivator of 3t/ha/season in the Yangliupu exceeds the standard. first and second year of the project implementation); Community 5.Strengthen the control of rice species with high accumulation; 6. Remove straws from the field; 7. Manage and control the standard-exceeding rice. 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 1. Rice cadmium pollution is at low 2. Conduct soil acidification conditioning by applying lime as per ‘Hunan Integrated Manage ment of risk; 2. Soil cadmium pollution is at low Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Acid Control and Sihuping risk; 3. Rice straws exceeds the Cadmium Reduction by Lime Composite Material’: apply lime of 2.25t/ha/season in the first and second Tongjinpu Town Village, 46.67 standard; 4. The enrichment coefficient year of the project implementation; Demonstration Area Yanzi Village of rice species is low-risk, and there 3. Apply commercial organic fertilizer of 750 kg / ha; may be risks in species and production 4. Conduct waterflooding irrigation and ensure the cleanness of irrigation water source. management. 5. Strengthen the popularization of rice species with low accumulation; 6. Manage and control the standard-exceeding rice. 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 2. Conduct irrigation with a small amount of water, and ensure the cleanness of irrigation water source; 1. Rice cadmium pollution is at low 3. Apply the commercial organic fertilizer of 600kg/ha; Baiyang risk; 2. Rice arsenic pollution is at low 4. Apply cadmium and arsenic synchronous passivator: as per ‘Hunan Integrated Management of Xiangshi Town Village, 5.33 risk; 3. Soil cadmium pollution is at low Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Cadmium Demonstration Area Xurita risk; 4. Rice straws exceeds the Reduction by Soil Passivator’ (apply cadmium and arsenic synchronous passivat or of 3t/ha/season in the Village standard. first and second year of the project implementation); 5.Strengthen the control of rice species with high accumulation; 6. Remove straws from the field; 7. Manage and control the standard-exceeding rice. 1. Rice cadmium pollution is at medium 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; Guangdong risk; 2. Rice arsenic pollution is at low 2. Conduct irrigation with a small amount of water, and ensure the cleanness of irrigation water source; Village, risk; 3. There is no risk of soil cadmium 3. Apply the commercial organic fertilizer of 750kg/ha; Dongyueguan Town 50.67 Xinhua pollution; 4. Rice straws exceeds 4. Apply cadmium and arsenic synchronous passivator: as per ‘Hunan Integrated Management of Village standard; 5. The enrichment coefficient Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Cadmium of rice species is medium-risk, and Reduction by Soil Passivator’ (apply cadmium and arsenic synchronous passivator of 3t/ha/season in the 17 Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectares) there may be risks in species and first and second year of the project implementation); production management. 5. Strengthen the control of rice species with high accumulation; 6. Remove straws from the field; 7. Manage and control the standard-exceeding rice. 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 1. Rice cadmium pollution is at medium 2. Conduct irrigation with a small amount of water, and ensure the cleanness of irrigation water source; risk; 2. Rice arsenic pollution is at 3. Apply the commercial organic fertilizer of 600kg/ha; medium risk. 3. Soil cadmium pollution 4. Apply cadmium and arsenic synchronous passivator: as per ‘Hunan Integrated Management of Zhuangta is at low risk; 4. Heavy metal content in Sanhe Town 4 Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Cadmium Village rice straws exceeds standard; 5. The Reduction by Soil Passivator’ (apply cadmium and arsenic synchronous pass ivator of 3t/ha/season in the enrichment coefficient of rice species is first and second year of the project implementation); medium-risk, and there may be risks in 5. Strengthen the control of rice species with high accumulation; species and production management. 6. Remove straws from the field; 7. Manage and control the standard-exceeding rice. 18 Table 4-5 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Huayuan County Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectare) 1. Strengthen monitoring of heavy metal pollution in farmland and balance control of cadmium and arsenic in 1. Rice cadmium pollution is at low risk farmland; and arsenic pollution is at low risk. Huayuan Town Gaohe 2. Optimize field water management (waterflooding irrigation); 61 2. Soil cadmium pollution is at extremely Demonstration Area Village 3. Conduct alternative fertilization measures for soil acidification conditioning and control the potential risks in rice high risk and there is no risk of arsenic and soil; pollution. 4. Apply commercial organic fertilizer in an amount of 540 kg / ha per year. 19 Table 4-6 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Anhua County Name of Scale Name Risk Analysis Countermeasures Demonstration Area (hectare) 1. Rice cadmium pollution is at 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; Gurong Village 35 medium risk; 2. There is no risk of soil 2. Apply 600 kg / ha of commercial organic fertilizer. cadmium pollution. 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 2. Conduct irrigation with a small amount of water, and ensure the cleanness of irrigation water source; 1. Rice cadmium pollution is at 3. Apply the commercial organic fertilizer of 600kg/ha; medium risk; 2. Rice arsenic pollution 4. Apply cadmium and arsenic synchronous passivator: as per ‘Hunan Integrated Management of is at low risk; 3. Soil cadmium Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Cadmium Wenshi Village 39 pollution is at extremely high risk; 4. Reduction by Soil Passivator’ (apply cadmium and arsenic synchronous passivator of 3t/ha/season in the Heavy metal content in rice straws first and second year of the project implementation, and the amount shall be reduced by half in the third exceeds the standard. and fourth year and stop applying in the fifth and sixth year); 5.Strengthen the control of rice species with high accumulation; 6. Remove straws from the field; 7. Manage and control the standard-exceeding rice. 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 1. Rice cadmium pollution is at low 2. Conduct irrigation with a small amount of water, and ensure the cleanness of irrigation water source; Le’an Town risk; 2. Rice arsenic pollution is at low 3. Apply the commercial organic fertilizer of 600kg/ha; Demonstration Area risk; 3. Soil cadmium pollution risk is 4. Apply cadmium and arsenic synchronous passivator: as per ‘Hunan Integrated Management of extremely high; 4. Rice straws exceeds Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Cadmium Hengshi Village 40 standard; 5. The enrichment coefficient Reduction by Soil Passivator’ (apply cadmium and arsenic synchronous passivator of 3t/ha/season in the of rice species is low-risk, and there first and second year of the project implementation, and the amount shall be reduced by half in the third may be risks in species and production and fourth year and stop applying in the fifth and sixth year); 5.Strengthen the control of rice species management. with high accumulation; 6. Manage and control the standard-exceeding rice. 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 2. Conduct soil acidification conditioning by applying lime as per ‘Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Acid Control and 1. Rice arsenic pollution is at medium Cadmium Reduction by Lime Composite Material’: apply lime of 2.25t/ha/season in the first and second Yizhong Village 39.33 risk; 2. Soil cadmium pollution is at year of the project implementation, and the amount shall be reduced by half in the third year and stop high risk. applying in the fourth, fifth and sixth year; 3. Apply commercial organic fertilizer of 600kg/ha; 4. Conduct waterflooding irrigation and ensure the cleanness of irrigation water source. Dafu Town Muxi Village, 73.33 1. Rice cadmium pollution is at high 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 20 Name of Scale Name Risk Analysis Countermeasures Demonstration Area (hectare) Demonstration Area Mengjia Village risk; 2. Rice arsenic pollution is at low 2. Conduct irrigation with a small amount of water, and ensure the cleanness of irrigation water source; risk; 3. The enrichment coefficient of 3. Apply the commercial organic fertilizer of 600kg/ha; rice species is low-risk, and there may 4. Apply cadmium and arsenic synchronous passivator: as per ‘Hunan Integrated Management of be risks in species and production Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Cadmium management. Reduction by Soil Passivator’ (apply cadmium and arsenic synchronous passivator of 3t/ha/season in the first and second year of the project implementation, and the amount shall be reduced by half in the third year); 5. Strengthen the control of rice species with high accumulation; 6. Remove straws from the field; 7. Manage and control the standard-exceeding rice. 1. Strengthen monitoring of heavy metal pollution in farmland and focus on monitoring of rice and soil; 2. Conduct soil acidification conditioning by applying lime as per ‘Hunan Integrated Management of Agricultural Land Pollution Project with World Bank Loan: Technical Specification for Acid Control and Cadmium Reduction by Lime Composite Material’: apply lime of 2.25t/ha/season in the first and second Qingtang Town Dongtian 1. Rice cadmium pollution is at low 106.67 year of the project implementation, and the amount shall be reduced by half in the third year and stop Demonstration Area Village risk. applying in the fourth, fifth and sixth year; 3. Apply commercial organic fertilizer of 750kg/ha; 4. Conduct waterflooding irrigation and ensure the cleanness of irrigation water source; 5. Manage and control the standard-exceeding rice. 21 Table 4-7 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Hengyang County Name of Village Scale (hectare) Risk Analysis Countermeasures Demonstration Area name 1. Rice cadmium pollution is at medium risk and 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer there is no risk of arsenic pollution; and pesticide shall be strengthened. 2. Soil cadmium pollution is at medium risk and 2. Popularize the rice species with low cadmium absorption. there is no risk of arsenic pollution; 3. Conduct soil acidification conditioning: apply lime of 3.0t/ha/season in the first year of the project 3. Rice straw cadmium pollution is at low risk and implementation, and the amount shall be reduced by half in the second and third year. Qingli Demonstration Qingli 116 there is no risk of arsenic pollution; 4. Water management: flooding reasonably in the early stage, drying properly in the peak tillering Area of Xidu Town Village 4. The rice cadmium enrichment coefficient is at stage and flooding properly after the peak tillering stage but with less flooding intensity and duration. medium risk and there is no risk of rice arsenic 5. Apply soil passivator: apply passivator of 3.0t/ha/season in the first year of the project enrichment coefficient and the rice may include implementation, and the amount shall be reduced by half in the second and third year. pollution risks brought by species, exogenous 6. Apply leaf inhibitor and control agent: 250ml/mu. (sedimentation) or management methods. 7. Apply commercial organic fertilizer: applying 3.0t/ha of commercial organic fertilizer per year; 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer 1. Rice cadmium pollution is at medium risk and and pesticide shall be strengthened. there is no risk of arsenic pollution; 2. Popularize the rice species with low cadmium absorption. 2. There is no risk of soil cadmium pollution and 3. Conduct soil acidification conditioning: apply lime of 3.0t/ha/season in the first year of the project arsenic pollution; implementation, and the amount shall be reduced by half in the second and third year. 3. Rice straw cadmium pollution is at low risk and Fuxing 4. Water management: flooding reasonably in the early stage, drying properly in the peak tillering 140.67 there is no risk of arsenic pollution; Village stage and flooding properly after the peak tillering stage but with less flooding intensity and duration. 4. The rice cadmium enrichment coefficient is at 5. Apply soil passivator: apply passivator of 3.0t/ha/season in the first year of the project medium risk and there is no risk of rice arsenic implementation, and the amount shall be reduced by half in the second and third year. enrichment coefficient and the rice may include 6. Apply leaf inhibitor and control agent: 250ml/mu. pollution risks brought by species, exogenous Yanglin Demonstration 7. Apply commercial organic fertilizer: applying 3.0t/ha of commercial organic fertilizer per year; (sedimentation) or management methods. Area of Fuxing Village 8. Remove the straws (orchard coverage) of Sanhu Town 1. Rice cadmium pollution is at medium risk and 1. The monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer there is no risk of arsenic pollution; and pesticide shall be strengthened. 2. Soil cadmium pollution is at low risk and there is 2. Popularize the rice species with low cadmium absorption. no risk of arsenic pollution; 3. Conduct soil acidification conditioning: apply lime of 3.0t/ha/season in the first year of the project 3. Rice straw cadmium pollution is at low risk and implementation, and the amount shall be reduced by half in the second and third year. Yanglin 60 there is no risk of arsenic pollution; 4. Water management: flooding reasonably in the early stage, drying properly in the peak tillering Village 4. The rice cadmium enrichment coefficient is at stage and flooding properly after the peak tillering stage but with less flooding intensity and duration. medium risk and the rice arsenic enrichment 5. Apply soil passivator: apply passivator of 3.0t/ha/season in the first year of the project coefficient is at low risk and the rice may include implementation, and the amount shall be reduced by half in the second and third year. pollution risks brought by species, exogenous 6. Apply leaf inhibitor and control agent: 250ml/mu. (sedimentation) or management methods. 7. Apply commercial organic fertilizer: applying 3.0t/ha of commercial organic fertilizer per year; 22 Table 4-8 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Hengnan County Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) 1. Monitor the atmospheric sedimentation of heavy metal; 2. Popularize rice species with low accumulation； 3. Apply soil cadmium and arsenic synchronous passivator; Chaoyang 1. Cadmium pollution is at extremely high risk and 4. Remove rice straws out of the farmlands; 73.33 Village arsenic pollution is at medium risk. 5. Control of standard-exceeding rice; 6. Waterflooding irrigation in mature stage； 7. Apply commercial organic fertilizer; 8. Conduct soil acidification conditioning 1. Monitor the atmospheric sedimentation of heavy metal; 2. Popularize rice variety with low accumulation； Xiangyang No. 1 governance unit Cadmium and arsenic 3. Apply soil cadmium and arsenic synchronous passivator; Community compound pollution is at extremely high risk 4. Remove rice straws out of the farmlands; Demonstration Area (cadmium is at extremely high risk and arsenic is at 5. Apply waterflooding irrigation for rice in mature stage; low risk) 6. Control of standard-exceeding rice; Huanghe 7. Apply commercial organic fertilizer; 66.67 8. Conduct soil acidification conditioning Village 1. Monitor the atmospheric sedimentation of heavy metal; 2.Replanting Crops of high threshold values are recommended such as sorghum, corn, etc.; No. 2 governance unit There is no risk of cadmium 3. Apply soil cadmium and arsenic synchronous passivator; pollution and the arsenic pollution is at low risk. 4. Remove rice straws out of the farmlands; 5. Apply commercial organic fertilizer; 6. Conduct soil acidification conditioning 1. Monitor the atmospheric sedimentation of heavy metal; 2. Popularize rice species with low accumulation; 3. Conduct soil acidification conditioning; Cadmium pollution is at risk and the arsenic Quanxi Quanchang 4. Apply soil cadmium and arsenic compound passivator; 80 pollution is at low risk. Demonstration Area Village 5. Remove rice straws out of the farmlands; 6. Apply commercial organic fertilizer; 7. Control of standard-exceeding rice; 8. Waterflooding irrigation in mature stage. 23 Table 4-9 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Lengshuitan District Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectares) 1. There may be exogenous and cultivation management risks, and the monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; 2. Popularize the rice species with low cadmium & arsenic accumulation. 3. A long-term flood irrigation management is used, particularly in the key stage of heavy metal 1. Rice cadmium pollution is at low risk, but the rice cadmium content standard-exceeding rate is absorption and accumulation (booting stage to filling stage) to ensure a control of flooding during the high. beginning and closing 3 weeks for the purpose of reducing the activity of heavy metal cadmium in the Chunguang 2. Soil cadmium pollution is at medium risk. 80 soil to bring down the absorption and accumulation into rice; Village 3. Fertilizer arsenic pollution is at low risk. 4. Rice straw cadmium pollution is at low risk. 4. Apply the soil cadmium passivator: applying 3.75t/ha of soil cadmium passivator in 2021-2022, 5. The enrichment coefficient of rice species is at 1.875t/ha in 2023; medium risk. 5. Apply 2.25t/ha of organic fertilizer in 2021-2022, 15kg/ha of zinc fertilizer and stop applying in 2023. The fertilizer access shall be managed and controlled strictly; 6. Remove standard-exceeding rice straw; Xianghuaba village 7. Control of standard-exceeding rice. Demonstration Area 1. There may be exogenous and cultivation management risks, and the monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; 2. Popularize the rice species with low cadmium & arsenic accumulation. 1. There is no risk of rice cadmium & arsenic 3. A long-term flood irrigation management is used, particularly in the key stage of heavy metal pollution, but the rice cadmium & arsenic absorption and accumulation (booting stage to filling stage) to ensure a control of flooding during the content standard-exceeding rate is high. beginning and closing 3 weeks for the purpose of reducing the activity of heavy metal cadmium in the Datangqian 80 2. Soil cadmium pollution is at low risk; Village soil to bring down the absorption and accumulation into rice; 3. Fertilizer arsenic pollution is at low risk. 4. The enrichment coefficient of rice species is at 4. Apply the soil cadmium passivator: applying 3.75t/ha of soil cadmium passivator in 2021-2022, medium risk. 1.875t/ha in 2023; 5. Apply 2.25t/ha of organic fertilizer in 2021-2022, 15kg/ha of zinc fertilizer and stop applying in 2023. The fertilizer access shall be managed and controlled strictly; 6. Control of standard-exceeding rice. 24 Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectares) 1. There may be exogenous and cultivation management risks, and the monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; 2. Popularize the rice species with low cadmium & arsenic accumulation. 1. Rice cadmium pollution is at low risk, but the 3. A long-term flood irrigation management is used, particularly in the key stage of heavy metal rice cadmium content standard-exceeding rate is absorption and accumulation (booting stage to filling stage) to ensure a control of flooding during the high, reaching 33.3%; beginning and closing 3 weeks for the purpose of reducing the activity of heavy metal cadmium in the Xiangjiang 13.33 2. Fertilizer arsenic pollution is at low risk. Village soil to bring down the absorption and accumulation into rice; 3. The cadmium enrichment coefficient of rice species is at low risk and the risk of arsenic 4. Apply the soil cadmium passivator: applying 3.75t/ha of soil cadmium passivator in 2021-2022, enrichment coefficient is extremely high; 1.875t/ha in 2023; 5. Apply 2.25t/ha of organic fertilizer in 2021-2022, 15kg/ha of zinc fertilizer and stop applying in 2023. The fertilizer access shall be managed and controlled strictly;; 6. Control of standard-exceeding rice. 1. There may be exogenous and cultivation management risks, and the monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; 2. Popularize the rice species with low cadmium & arsenic accumulation. 3. A long-term flood irrigation management is used, particularly in the key stage of heavy metal 1. There is no risk of rice cadmium & arsenic absorption and accumulation (booting stage to filling stage) to ensure a control of flooding during the pollution but the rice cadmium & arsenic content beginning and closing 3 weeks for the purpose of reducing the activity of heavy metal cadmium in the standard-exceeding rate is high. Shixijiang Village Zhuxi 2. Soil cadmium pollution is at low risk; soil to bring down the absorption and accumulation into rice; 80 Demonstration Area Village 3. Fertilizer arsenic pollution is at low risk. 4. Apply the soil cadmium passivator: applying 3.75t/ha of soil cadmium passivator in 2021, 1.875t/ha 4. The cadmium enrichment coefficient of rice in 2022- 2023; species is at low risk and the risk of arsenic enrichment coefficient is extremely high; 5. Apply 2.25t/ha of organic fertilizer in a unified manner, 15kg/ha of zinc fertilizer simultaneously. The fertilizer access shall be managed and controlled strictly; 6. Adopt leaf inhibitor and control agent once respectively in the rice peak tillering stage and the early filling stage; 7. Control of standard-exceeding rice. 25 Name of Village Scale Risk Analysis Countermeasures Demonstration Area name (hectares) 1. There may be exogenous and cultivation management risks, and the monitoring of agricultural inputs such as atmospheric sedimentation, irrigation water, fertilizer and pesticide shall be strengthened; 2. Popularize the rice variety with low cadmium & arsenic accumulation. 3. A long-term flood irrigation management is used, particularly in the key stage of heavy metal 1. There is no risk of rice cadmium & arsenic absorption and accumulation (booting stage to filling stage) to ensure a control of flooding during the pollution but the cadmium content beginning and closing 3 weeks for the purpose of reducing the activity of heavy metal cadmium in the standard-exceeding rate exceeds 40%. soil to bring down the absorption and accumulation into rice; Niujiaoba Xiangshanj 40 2. The soil cadmium activity is high; Demonstration Area ie Village 4. Apply lime: apply 1.5t/ha of lime in 2021-2022 to improve pH of soil; 3. The fertilizer arsenic pollution is at low risk; The cadmium enrichment coefficient of rice 5. Apply the soil cadmium passivator: applying 3.75t/ha of soil cadmium passivator in 2021-2022, species is at low risk and arsenic is at low risk. 1.875t/ha in 2023; 6. Apply 2.25t/ha of organic fertilizer in 2021-2022, 15kg/ha of zinc fertilizer and stop applying in 2023. The fertilizer access shall be managed and controlled strictly; 7. Adopt leaf inhibitor and control agent once respectively in the rice peak tillering stage and the early filling stage; 8. Control of standard-exceeding rice. 26 Table 4-10 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Linwu County Small Name of Scale Village name demonstration Risk Analysis Countermeasures Demonstration Area (hectares) area Zhenshang Village 1 24 1. Rice cadmium pollution is at medium risk and arsenic pollution is at medium risk. 1. Optimize field water management; 2. The soil cadmium pollution and arsenic pollution are at extremely high risk and 2. Apply the soil cadmium and arsenic Wushui Town high risk respectively, with cadmium and arsenic compound pollution. Yaofeng Village 2 39.31 synchronous passivator of 3000kg/ha; 3. The enrichment coefficient of rice species has no risk. 3. Remove straws from the field. 4. Cadmium pollution of rice straw is at extremely low risk. 1. Rice cadmium pollution has no risk and arsenic pollution is at low risk; 2. Soil cadmium pollution and arsenic pollution are at extremely high risk and high 1. Optimize the field water management; Dongjiang Village 3 6.67 risk respectively; 2. Apply the soil cadmium and arsenic 3. The enrichment coefficient of rice has no risk; synchronous passivator of 3000kg/ha. 4. Arsenic pollution of rice straws is at low risk. Shuidong Town 1. Rice cadmium pollution and arsenic pollution are at low risk; 1. Optimize field water management; 2. Soil cadmium pollution and arsenic pollution are at medium risk and high risk 2. Apply the soil cadmium and arsenic Xinhua Village 7 23.33 respectively; synchronous passivator of 3000kg/ha; 3. The enrichment coefficient of rice species has no risk; 3. Remove straws from the field. 4. Arsenic pollution of rice straws is at low risk. Xiangtang Village 4 14 1. There is no risk of rice cadmium pollution and arsenic pollution. 2. Soil cadmium pollution and arsenic pollution are at medium risk and high risk Zhaijiang Village 5 25.33 1. Optimize the field water management; Nanqiang Town respectively. 2. Apply the arsenic passivator of 3000kg/ha. Liantang Village 6 23.26 3. The enrichment coefficient of rice species has no risk. Arsenic pollution in rice straws is at low risk. 27 Table 4-11 Technical Summary of Newly-added Demonstration Areas for Integrated Management of Agricultural Land Pollution Project in Qiyang County Name of Scale Village name Risk Analysis Countermeasures Demonstration Area (hectares) Tongzi Village 1. Popularize plantation of rice species with low accumulation; 1. Rice cadmium pollution is at medium and low risk, while 2.Conduct soil acidification conditioning by applying lime as per ‘Hunan Integrated there is no risk of arsenic pollution; Management of Agricultural Land Pollution Project with World Bank Loan: 2. Soil cadmium pollution is at medium and low risk and Technical Specification for Acid Control and Cadmium Reduction by Lime Xiaojia Demonstration there is no risk of arsenic pollution; 73.33 Composite Material’: apply lime of 3.75t/ha/season in the first and second year of the Area 3. Cadmium in rice straws exceeds the standard. project implementation, and the amount shall be reduced by half in the third and 1. The rice species enrichment coefficient is relatively high fourth year and stop applying in the fifth year; and the rice may include pollution risks brought by species Jiuniba Village 3.Waterflooding irrigation; or management methods. 4.Measure of removing straws from the field; 5. Control of standard-exceeding rice. 28 Appendix 5 Monitoring and Evaluation Result of Surface Water in Newly-added Demonstration Areas of Each Project County 1. Yongding District Table 5-1 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Yongding District (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Name Monitoring Point Position Total Ammonia pH CODcr As Pb Cd Cr6+ Hg phosphorus nitrogen Maoxi River in Taiji Village 8.19 <4 0.098 0.05 0.00088 ＜0.00009 ＜0.00005 <0.004 <0.00004 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Maoxi River in Jiagang Village 8.19 <4 0.105 0.04 0.00083 ＜0.00009 ＜0.00005 <0.004 <0.00004 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Xinglong Brook in Xinglong Village 8.20 <4 0.113 0.029 0.00096 ＜0.00009 ＜0.00005 <0.004 0.000063 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results Jiaoziya The maximum over-standard time 0 0 0 0 0 0 0 0 0 Demonstration Area Xinglong Brook in Qijiaping Village 8.21 <4 0.137 <0.025 0.00085 ＜0.00009 ＜0.00005 <0.004 <0.00004 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Qiaotou Brook in Gaofeng Village 8.20 <4 0.106 0.063 0.00090 ＜0.00009 ＜0.00005 <0.004 <0.00004 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Spring water in Heitan Village 8.21 <4 0.136 0.05 0.00095 ＜0.00009 ＜0.00005 <0.004 <0.00004 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 29 The upstream Baiyun Section of Baiyun-Guanzhuang-Bajiao Luoshui Brook in 8.21 <4 0.097 0.154 0.00089 ＜0.00009 ＜0.00005 <0.004 <0.00004 Luoshui Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results Wentang The maximum over-standard time 0 0 0 0 0 0 0 0 0 Demonstration The downstream Bajiao Section of Area Baiyun-Guanzhuang-Bajiao Luoshui Brook in 8.23 <4 0.141 0.15 0.00092 ＜0.00009 ＜0.00005 <0.004 <0.00004 Luoshui Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 The upstream Dingjiazhuang Section of Dingjiazhuang-Xinqiao Dasha Brook in Xinqiao 7.85 <4 0.048 0.89 0.00212 ＜0.00009 ＜0.00005 <0.004 0.000070 Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 The downstream Xinqiao Section of Dingjiazhuang-Xinqiao Dasha Brook in Xinqiao 7.79 4.76 0.069 0.92 0.00211 ＜0.00009 ＜0.00005 <0.004 0.000040 Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Yanghuping Results Demonstration The maximum over-standard time 0 0 0 0 0 0 0 0 0 Area The upstream Dayu Section of Xiaosha Brook in 7.82 5.71 0.106 1.01 0.00194 ＜0.00009 ＜0.00005 <0.004 <0.00004 Yuanda Village of Xinqiao Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 The downstream Yuanjing Section of Xiaosha 7.79 4.76 0.093 0.97 0.00207 ＜0.00009 ＜0.00005 <0.004 <0.00004 Brook in Yuanda Village of Xinqiao Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 The upstream Matouxi Section of Matou Brook 7.80 <4 0.122 0.90 0.00206 ＜0.00009 ＜0.00005 <0.004 0.000334 Yuanguping in Matouxi Village of Wangjiaping Town Demonstration area Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 30 The downstream Lianghekou Section of Matou 7.80 <4 0.114 1.03 0.00215 ＜0.00009 ＜0.00005 <0.004 0.000094 Brook in Matouxi Village of Wangjiaping Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Mountain spring water in Shiyanping Village of 7.77 <4 0.097 0.87 0.00218 ＜0.00009 ＜0.00005 <0.004 <0.00004 Wangjiaping Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Mountain spring water in Hongxing Village of 7.84 4.76 0.075 0.80 0.00211 ＜0.00009 ＜0.00005 <0.004 <0.00004 Yuanguping Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Mountain spring water in Hongtuping Village of 7.82 <4 0.082 1.07 0.00209 ＜0.00009 ＜0.00005 <0.004 0.000134 Yuanguping Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Mountain spring water in Gaoping Village of 7.82 <4 0.099 1.23 0.00216 ＜0.00009 ＜0.00005 <0.004 0.000900 Xiejiaya Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Mountain spring water in Changtan Village of 7.76 <4 0.099 0.55 0.00228 ＜0.00009 ＜0.00005 <0.004 0.000158 Yuanguping Town (Shuijingya) Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard time 0 0 0 0 0 0 0 0 0 Quality Standards for Farmland Irrigation Water (GB5084-2021) 5.5～8.5 150 / / 0.05 0.2 0.01 0.1 0.001 Type-III stated in Environmental Quality Standards for Surface Water 6～9 20 0.2 1.0 0.05 0.05 0.005 0.05 0.0001 (GB3838-2002) 31 2. Jishou City Table 5-2 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Jishou City (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Name Monitoring Point Position Ammonia Total Cd Pb Hg Cr6+ As pH CODcr nitrogen phosphorus Group 1 of Liantian Village ND 0.00011 ND ND 0.00033 8.28 5.19 0.048 ND Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Group 3 of Xiaoxing Village ND ND ND ND 0.00043 8.25 3.61 0.081 ND Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 Aizhai Demonstration time Area Group 2 of Pinglang Village ND ND ND ND 0.00026 8.22 5.51 0.049 ND Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Group 2 of Shu’er Village ND ND ND ND 0.00059 8.23 5.94 0.025 ND Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Qianghu Village ND ND ND ND 0.00026 8.26 4.72 0.055 ND Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Qianzhou Results The maximum over-standard Demonstration Area 0 0 0 0 0 0 0 0 0 time Group 2 of Sanchaping Village ND ND ND ND 0.00032 8.28 4.12 0.08 ND 32 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Quality Standards for Farmland Irrigation Water (GB5084-2021) 0.01 0.2 0.001 0.1 0.05 5.5～8.5 150 / / Type-III stated in Environmental Quality Standards for Surface Water 0.005 0.05 0.0001 0.05 0.05 6～9 20 1 0.2 (GB3838-2002) 33 3. Yongshun County Table 5-3 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Yongshun County (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Name Monitoring Point Position Chemical Ammonia Pb Cd As Hg Oxygen pH P Cr6+ nitrogen Demand Longtangou River of Xiqi Village <0.00009 <0.00005 0.00040 0.00007 <4 6.68 <0.04 <0.004 <0.02 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Xiangluxi River of Hexin Village <0.00009 <0.00005 0.00040 0.00006 5.40 7.05 <0.04 <0.004 <0.02 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 Xiqi Demonstration time Area Zhangjiawan Reservoir 0.00036 <0.00005 0.0013 0.00005 7.70 6.66 <0.04 <0.004 0.040 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Zhangjiawan river 0.00014 <0.00005 0.00050 0.00005 4.60 7.04 <0.04 <0.004 <0.02 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Brook in Taozixi Village <0.00009 <0.00005 0.00050 0.00005 <4 6.64 <0.04 <0.004 <0.02 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Yashixi Reservoir <0.00009 <0.00005 0.00050 0.00004 5.40 6.2 <0.04 <0.004 0.21 Shaba Demonstration Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Area Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time 34 Huanghuaxi River in Xishaba Village <0.00009 <0.00005 0.00050 0.00007 <4 6.23 <0.04 <0.004 <0.02 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Sanjiawan River in Xihu Community <0.00009 <0.00005 0.00040 0.00004 8.40 6.14 <0.04 <0.004 0.15 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Longdongwan River in Xihu Community <0.00009 <0.00005 0.00065 0.00005 <4 7.23 <0.04 <0.004 <0.02 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Quality Standards for Farmland Irrigation Water (GB5084-2021) 0.2 0.01 0.05 0.001 150 5.5～8.5 / 0.1 / Type-III stated in Environmental Quality Standards for Surface Water 0.05 0.005 0.05 0.0001 20 6～9 0.2 0.05 1 (GB3838-2002) 35 4. Cili County Table 5-4 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Cili County (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Name Monitoring Point Position Ammonia Total Cd Pb Hg Cr6+ As pH CODcr nitrogen phosphorus Zhaojialou Group of Xuri Village ND ND ND ND ND 8.15 7.59 0.053 ND Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 Xiangshi Town time Demonstration Area Baiyang Village ND ND ND ND 0.00068 8.12 19.7 ND 0.01 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Yuquan Group of Xinpu Village ND ND ND ND 0.00051 7.93 6.94 0.041 0.01 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Yangliuwu Village ND ND ND ND 0.00072 7.82 16 0.05 0.04 Yangliupu Town Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Demonstration Area Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Zhangshu Village ND ND ND ND 0.00067 7.87 11.7 0.09 0.03 Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Jianshetang Group of Zhuangta Village ND ND ND ND 0.00065 6.96 27.4 0.036 0.06 Sanhe Township Assessment Over-standard Rate (%) 0 0 0 0 0 0 0 0 0 Demonstration Area Results The maximum over-standard 0 0 0 0 0 0 0 0 0 time Quality Standards for Farmland Irrigation Water (GB5084-2021) 0.01 0.2 0.001 0.1 0.05 5.5～8.5 150 / / 36 5. Huayuan County Table 5-5 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Huayuan County (unit: mg/L, pH being dimensionless) Monitoring and Evaluation Factor Time of Name Monitoring Point Position Ammonia Total Monitoring pH COD Cd Pb As Hg Cr6+ nitrogen phosphorus 1# Upstream irrigation canal of 7.52 13 0.267 0.014 5×10-5L 9×10-5L 1.2×10-4L 4×10-5L 4×10-3L Gaohe Village Over-standard Rate 10/20/2020 Assessment 0 0 0 0 0 0 0 0 0 (%) Results The maximum 0 0 0 0 0 0 0 0 0 over-standard time 2# Upstream irrigation ditch of 7.48 8 0.084 0.230 5×10-5L 9×10-5L 1.2×10-4L 4×10-5L 4×10-3L Biancheng Gaohe Village Town Over-standard Rate 10/20/2020 Assessment 0 0 0 0 0 0 0 0 0 Demonstration (%) Results Area The maximum 0 0 0 0 0 0 0 0 0 over-standard time 3# Upstream irrigation ditch of 7.26 14 0.171 0.018 5×10-5L 9×10-5L 1.2×10-4L 4×10-5L 4×10-3L Gaohe Village Over-standard Rate 10/20/2020 Assessment 0 0 0 0 0 0 0 0 0 (%) Results The maximum 0 0 0 0 0 0 0 0 0 over-standard time Quality Standards for Farmland Irrigation Water (GB5084-2021) 5.5～8.5 150 / / 0.01 0.2 0.05 0.001 0.1 Type-III stated in Environmental Quality Standards for Surface Water 6～9 20 1.0 0.2 0.005 0.05 0.05 0.0001 0.05 (GB3838-2002) L means not detected, whose value is the detection limit. 37 6. Anhua County Table 5-6 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Anhua County (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Time of Name Monitoring Point Position Ammonia Total Monitoring pH COD Cd Pb As Hg Cr nitrogen phosphorus Irrigation canal of Gurong Village 7.8 5-8 0.711-0.76 0.01-0.02 5×10-5L 0.00034-0.00041 0.00050-0.00052 4×10-5L 0.00025-0.00031 Over-standard Rate 12/17/2020 Assessment 0 0 0 0 0 0 0 0 0 (%) Results The maximum 0 0 0 0 0 0 0 0 0 over-standard time Zhangwangchong irrigation canal 8.1-8.2 4L-4 0.050-0.331 0.01-0.06 5×10-5L 9×10-5L 0.00020-0.00051 4×10-5L 1.1×10-4L of Wenshi Village Over-standard Rate 12/17/2020 Assessment 0 0 0 0 0 0 0 0 0 (%) Results The maximum Le’an Town 0 0 0 0 0 0 0 0 0 over-standard time Demonstration Non-irrigation canal of Hengshi Area 7.7-8.0 4-8 0.025-0.061 0.01L-0.01 5×10-5L 9×10-5L 0.00022-0.00025 4×10-5L 1.1×10-4L Village Over-standard Rate 12/17/2020 Assessment 0 0 0 0 0 0 0 0 0 (%) Results The maximum 0 0 0 0 0 0 0 0 0 over-standard time Yishui River irrigation canal of 7.6-7.8 4-8 0.025-0.086 0.02-0.03 5×10-5L 9×10-5L 0.00039-0.00043 4×10-5L 0.00021-0.00022 Yizhong Village Over-standard Rate 12/17/2020 Assessment 0 0 0 0 0 0 0 0 0 (%) Results The maximum 0 0 0 0 0 0 0 0 0 over-standard time Irrigation canal of Muxi Village, 7.3-7.6 4-9 0.031-0.131 0.03-0.14 0.00005-0.000088 9×10-5L 0.00064-0.00182 4×10-5L 1.1×10-4L-1.2×10-4L Mengjia Village Dafu Town Over-standard Rate Demonstration 12/17/2020 Assessment 0 0 0 0 0 0 0 0 0 (%) Area Results The maximum 0 0 0 0 0 0 0 0 0 over-standard time Qingtang Irrigation canal of Dongtian River 12/17/2020 8.3-8.5 4-7 0.258-0.517 0.01 5×10-5L 9×10-5L 0.00025-0.00079 4×10-5L 0.00025-0.00079 Town of DongtianVillage 38 Demonstration Over-standard Rate Assessment 0 0 0 0 0 0 0 0 0 Area (%) Results The maximum 0 0 0 0 0 0 0 0 0 over-standard time Quality Standards for Farmland Irrigation Water (GB5084-2021) 5.5～8.5 150 / / 0.01 0.2 0.05 0.001 0.1 Type-III stated in Environmental Quality Standards for Surface Water 6～9 20 1.0 0.2 0.005 0.05 0.05 0.0001 0.05 (GB3838-2002) L means not detected, whose value is the detection limit. 39 7. Hengyang County Table 5-7 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Hengyang County (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Monitored Water Body Time of Name of Point Position Total Ammonia Monitoring pH CODcr As Pb Cd Cr6+ Hg phosphorus nitrogen Fuxing water conservancy supporting 2,020.12 7.63 17.2 <0.04 0.041 0.0041 <0.00009 <0.00005 <0.004 0.0004 facilities (upstream Zhengshui River) Over-standard Rate / 0 0 0 0 0 0 0 0 0 (%) Assessment Results The over-standard / 0 0 0 0 0 0 0 0 0 time Brookside of Fuxing (Downstream Zhengshui River of Sanhu 2,020.12 7.62 16.3 <0.04 0.041 0.0017 <0.00009 <0.00005 <0.004 0.0004 Zhengshui River Demonstration Area) (Sanhu Demonstration Over-standard Rate Area) / 0 0 0 0 0 0 0 0 0 (%) Assessment Results The over-standard / 0 0 0 0 0 0 0 0 0 time Yanglin (waster in the Shizhu Reservoir) 2020.12 6.89 13.1 <0.04 0.040 0.0012 <0.00009 <0.00005 <0.004 0.0004 Over-standard Rate / 0 0 0 0 0 0 0 0 0 (%) Assessment Results The over-standard / 0 0 0 0.0014 0 0 0 0 time Qingli Demonstration Area (upstream 2020.12 7.03 18.8 0.087 0.2 0.0014 <0.00009 <0.00005 <0.004 0.0004 Zhengshui River) Zhengshui River Over-standard Rate (Qingli Demonstration / 0 0 0 0 0 0 0 0 0 (%) Area) Assessment Results The over-standard / 0 0 0 0 0 0 0 0 0 time 40 Qingli Demonstration Area (downstream 2,020.12 6.93 17.2 <0.04 0.058 0.0011 <0.00009 <0.00005 <0.004 0.0004 Zhengshui River) Over-standard Rate / 0 0 0 0 0 0 0 0 0 Assessment Results (%) The over-standard / 0 0 0 0 0 0 0 0 0 time 5.5 Quality Standards for Farmland Irrigation Water (GB5084-2021) ～ 150 / / 0.05 0.2 0.01 0.1 0.001 8.5 6～ Type-III stated in Environmental Quality Standards for Surface Water (GB3838-2002) 20 0.2 1.0 0.05 0.05 0.005 0.05 0.0001 9 41 8. Hengnan County Table 5-8 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Hengnan County (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Location of Detection Name Ammonia Monitoring Time pH CODcr Total phosphorus As Pb Cd Cr6+ Hg nitrogen Xiangyang Sub-district Canal beside the Yantou Wellhead at the 2020.12 7.01 32.6 0.04 0.16 0.0026 0.00014 <0.00005 <0.004 0.00004 doorway of Lvziping, Hongni Group, Chaoyang Village Over-standard 0 0 0 0 0 0 0 0 0 Rate (%) Assessment Results The over-standard 0 0 0 0 0 0 0 0 0 time Xiangyang Sub-district Ditch beside Yejiaodaqiu, Ouyangzhijia, 2,020.12 7.08 26 <0.04 0.16 0.0009 <0.00009 <0.00005 <0.004 0.00002 Dashuidong, Yangjia Group, Chaoyang Village Over-standard 0 0 0 0 0 0 0 0 0 Xiangyang Rate (%) Assessment Results The Demonstration over-standard 0 0 0 0 0 0 0 0 0 Area time Shangshengtang of Xini Group of Huanghe 2,020.12 6.71 17.3 <0.04 0.31 0.002 <0.00009 <0.00005 <0.004 0.00003 Village Over-standard 0 0 0 0 0 0 0 0 0 Rate (%) Assessment Results The over-standard 0 0 0 0 0 0 0 0 0 time Wantang of Liping Group of Huanghe 2020.12 6.75 32.1 0.04 0.62 0.0028 0.00011 <0.00005 <0.004 0.00002 Village Over-standard 0 0 0 0 0 0 0 0 0 Rate (%) Assessment Results The over-standard 0 0 0 0 0 0 0 0 0 time 42 Canal under Luolaowu high voltage line, 2,020.12 6.78 9.62 0.21 0.14 0.0018 <0.00009 <0.00005 <0.004 0.00002 Quanshuiwan Group, Quanchang Village Quanxi Over-standard 0 0 0 0 0 0 0 0 0 Demonstration Rate (%) Area Assessment Results The over-standard 0 0 0 0 0 0 0 0 0 time 5.5～ Quality Standards for Farmland Irrigation Water (GB5084-2021) 150 / / 0.05 0.2 0.01 0.1 0.001 8.5 Type-III stated in Environmental Quality Standards for Surface Water 6～9 20 0.2 1.0 0.05 0.05 0.005 0.05 0.0001 (GB3838-2002) 43 9. Lengshuitan District Table 5-9 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Lengshuitan District (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Location of Monitoring Time of Name Total Ammonia Monitoring pH CODcr As Pb Cd Cr6+ Hg phosphorus nitrogen Dengjiachong Reservoir 2017.3 7.48 7.6 0.02 ND 0.00158 0.00049 0.00006 0.0004 ND Over-standard Rate Xianghuaba village / / 0 0 0 0 0 0 0 0 Assessment (%) Demonstration Area Results The over-standard / / 0 0 0 0 0 0 0 0 time LanjiangRiver 2017.3 7.41 12.1 0.03 0.191 0.004 0.00001 0.00005 0.0004 ND Over-standard Rate Assessment / / 0 0 0 0 0 0 0 0 Shixi Village Demonstration Area (%) Results The over-standard / / 0 0 0 0 0 0 0 0 time 5.5～ Quality Standards for Farmland Irrigation Water (GB5084-2021) 150 / / 0.05 0.2 0.01 0.1 0.001 8.5 Type-III stated in Environmental Quality Standards for Surface Water (GB3838-2002) 6～9 20 0.2 1.0 0.05 0.05 0.005 0.05 0.0001 44 10. Linwu County Table 5-10 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Linwu County (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Location of Monitoring Name of Point Position Total Ammonia pH CODcr As Pb Cd Cr6+ Hg phosphorus nitrogen Intake canal of Linwandong Bridge 7.5 7 0.21 0.571 3.2×10-3 ND ND ND ND Assessment Results The over-standard time 0 0 0.05 0 0 0 0 0 0 Wushui Town Xiejiang Bridge 8.96 5 0.09 0.125 0.152 ND ND ND ND Assessment Results The over-standard time 0 0 0 0 0 0 0 0 0 Wenxi Xiangtangdong 7.98 8 0.12 0.499 0.0164 ND ND ND ND Assessment Results The over-standard time 0 0 0 0 0 0 0 0 0 Wenxi Bridge 8.06 5 0.06 0.168 1.5×10-3 ND ND ND ND Nanqiang Town Assessment Results The over-standard time 0 0 0 0 0 0 0 0 0 Water source of Liantangjing 7.33 6 0.01 0.09 ND ND ND ND ND Assessment Results The over-standard time 0 0 0 0 0 0 0 0 0 Guanyinge Section of Jinjiang River 7.65 11 0.03 0.197 3.3×10-3 ND ND ND ND Shuidong Town Assessment Results The over-standard time 0 0 0 0 0 0 0 0 0 45 Dongjiang Water Plant 7.95 5 0.02 0.176 1.3×10-3 ND ND ND ND Assessment Results The over-standard time 0 0 0 0 0 0 0 0 0 Shuidong Xinping Substation 8.04 6 0.01 1.73 8×10-4 ND 8×10-4 ND ND Assessment Results The over-standard time 0 0 0 0.73 0 0 0 0 0 5.5～ Quality Standards for Farmland Irrigation Water (GB5084-2021) 150 / / 0.05 0.2 0.01 0.1 0.001 8.5 Type-III stated in Environmental Quality Standards for Surface Water 6～9 20 0.2 1.0 0.05 0.05 0.005 0.05 0.0001 (GB3838-2002) 46 11. Qiyang County Table 5-11 Monitoring and Evaluation Result of Water Quality of Surface Water in Newly-added Demonstration Areas of Qiyang County (unit: mg/L, pH being dimensionless, ND means not detected) Monitoring and Evaluation Factor Time of Monitored Water Body Name of Point Position Ammonia Total Monitoring pH CODcr Cd Pb As Hg Cr6+ nitrogen phosphorus Tongzi Village of Xiaojia Town (Downstream Dajiangbian reservoir, irrigation 7/19/2017 7.42 8 0.222 0.11 ND ND 0.0008 ND ND water intake of demonstration area) Over-standard Rate (%) / 0 0 0 0 0 0 0 0 0 Assessment Results The over-standard time / 0 0 0 0 0 0 0 0 0 Dajiangbian Reservoir Irrigation water intake of Jiuniba Village and irrigation canal 7/19/2017 7.32 10 0.345 0.03 ND ND 0.0006 ND ND Demonstration Area of Xiaojia Town (Xiaojia Assessment Results Over-standard Rate (%) / 0 0 0 0 0 0 0 0 0 Demonstration Area) The over-standard time / 0 0 0 0 0 0 0 0 0 Irrigation water intake of Jiuniba Village 7/19/2017 7.07 18 1.09 0.24 ND ND 0.0024 ND ND Demonstration Area of Xiaojia Town Over-standard Rate (%) / 0 0 0 0 0 0 0 0 0 Assessment Results The over-standard time / 0 0 0.09 0.2 0 0 0 0 0 5.5～ Quality Standards for Farmland Irrigation Water (GB5084-2021) 150 / / 0.01 0.2 0.05 0.001 0.1 8.5 Type-III stated in Environmental Quality Standards for Surface Water (GB3838-2002) 6～9 20 1.0 0.2 0.005 0.05 0.05 0.0001 0.05 47 Appendix 6 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Demonstration Areas in each Project County 1. Sediment of Irrigation Canal in Yongding District Table 6-1 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Yongding District Name of Monitoring factors (unit: mg/kg and pH being dimensionless ) Demonstration Specific Location Area pH Cd Pb Cr As Huchongyu Monitored Value 5.34 0.46 34.5 52.5 7.29 Group, Heitan Village, The over-standard time 0 0 0 0 0 Maoyanhe Town Jigongyu Group, Monitored Value 5.28 0.42 32.9 54.0 7.62 Heitan Village, Maoyanhe Town The over-standard time 0 0 0 0 0 Dayuan Group, Monitored Value 5.21 0.54 34.1 54.4 7.84 Baiyun Village, Luoshui The over-standard time 0 0 0 0 0 Township Qingquanta Monitored Value 5.39 0.48 36.4 50.1 11.3 Wentang Group, Baiyun Demonstration Village, Luoshui The over-standard time 0 0 0 0 0 Area Township Gushubao Group, Monitored Value 5.27 0.49 39.5 53.3 10.8 Guanzhuang Village, Luoshui The over-standard time 0 0 0 0 / Township Wenchangge Monitored Value 5.31 0.52 37.7 48.9 10.5 Group, Guanzhuang Village, Luoshui The over-standard time 0 0 0 0 / Township Bajiaoyu Group, Monitored Value 6.31 0.48 37.8 48.9 9.92 Bajiao Village, Luoshui The over-standard time 0 0 0 0 / Township 48 Bajiaowan Monitored Value 6.18 0.49 37.2 49.7 10.0 Group, Bajiao Village, Luoshui The over-standard time 0 0 0 0 / Township Fengxiangping Monitored Value 6.31 0.40 32.2 43.1 11.1 Group, Gaofeng Village, Qiaotou The over-standard time 0 0 0 0 / Township Dujiayu Group, Monitored Value 6.24 0.48 38.2 49.4 11.7 Gaofeng Village, Qiaotou The over-standard time 0 0 0 / Township Yin’erwan Monitored Value 5.53 0.45 33.6 51.3 6.72 Group, Xinglong Village, Jiaoziya The over-standard time 0 0 0 0 / Town Bajiawan Group, Monitored Value 5.47 0.45 36.0 53.4 6.75 Xinglong Village, Jiaoziya The over-standard time 0 0 0 0 / Town Yinjiaxi Heyingwan Monitored Value 5.63 0.54 33.9 54.0 7.65 Demonstration Group, Qijiaping area Village, Jiaoziya The over-standard time 0 0 0 0 / Town Tayan Group, Monitored Value 5.49 0.53 31.0 50.7 7.92 Qijiaping Village, Jiaoziya The over-standard time 0 0 0 0 / Town Group 9, Taiji Monitored Value 5.42 0.48 34.3 51.6 6.25 Village, Yinjiaxi Town The over-standard time 0 0 0 0 / Group 10, Taiji Monitored Value 6.15 0.32 27.4 61.8 3.93 Village, Yinjiaxi Town The over-standard time 0 0 0 0 / Group 13, Monitored Value 5.83 0.60 34.9 54.3 8.15 Mojiagang Village, Yinjiaxi The over-standard time 0 0 0 0 / Town 49 Group 11, Monitored Value 5.72 0.47 35.0 53.6 7.88 Mojiagang Village, Yinjiaxi The over-standard time 0 0 0 0 / Town Group 5, Yuanda Monitored Value 5.42 0.53 34.4 54.9 6.76 Village, Xinqiao Town The over-standard time 0 0 0 0 / Group 8, Yuanda Monitored Value 5.17 0.46 37.2 48.7 11.8 Village, Xinqiao Town The over-standard time 0 0 0 0 / Dingjiazhuang Monitored Value 5.36 0.51 36.3 48.3 7.99 Group, Dingjiazhuang Village, Xinqiao The over-standard time 0 0 0 0 / Yanghuping Town Demonstration Songjialuo Monitored Value 5.24 0.53 33.8 53.3 7.98 Area Group, Dingjiazhuang Village, Xinqiao The over-standard time 0 0 0 0 / Town Xiejiawan Monitored Value 5.61 0.50 33.2 55.0 7.30 Group, Xinqiao Neighborhood Committee, The over-standard time 0 0 0 0 / Xinqiao Town Tianjiaping Monitored Value 5.73 0.56 35.3 63.7 8.07 Group, Xinqiao Neighborhood Committee, The over-standard time 0 0 0 0 / Xinqiao Town Guanshuiping Monitored Value 6.89 0.61 44.0 53.3 7.74 Group, Matouxi Village, Yuanguping Wangjiaping The over-standard time 0 0 0 0 / Demonstration Town area Zhoujiaping Monitored Value 7.15 0.57 44.5 53.7 7.31 Group, Matouxi Village, The over-standard time 0 0 0 0 / Wangjiaping 50 Town Shiyanping Monitored Value 8.41 0.43 34.0 55.6 9.53 Group, Shiyanping Village, The over-standard time 0 0 0 0 / Wangjiaping Town Tuangonggang Monitored Value 8.15 0.64 45.5 55.1 7.49 Group, Shiyanping Village, Wangjiaping The over-standard time 0 0 0 0 / Town Hongqi Group, Monitored Value 6.21 0.53 36.9 52.0 6.98 Hongxing Village, Yuanguping The over-standard time 0 0 0 0 / Town Changwan Monitored Value 6.75 0.65 44.2 54.6 7.61 Group, Hongxing Village, Yuanguping The over-standard time 0 0 0 0 / Town Zhuyuanjiao Monitored Value 6.47 0.65 46.0 55.2 6.79 Group, Yuanguping Hongtuping Demonstration Village, area The over-standard time 0 0 0 0 / Yuanguping Town Wangjiayu Monitored Value 6.58 0.55 34.0 54.4 8.83 Group, Hongtuping Village, The over-standard time 0 0 0 0 / Yuanguping Town Shuijingya Monitored Value 6.43 0.44 38.9 52.1 10.2 Group, Changtan Village, The over-standard time 0 0 0 0 / Yuanguping 51 Town Shuijingya Monitored Value 6.18 0.57 41.6 53.8 6.87 Group, Changtan Village, Yuanguping The over-standard time 0 0 0 0 / Town Wannei Group, Monitored Value 6.34 0.62 106.0 48.0 10.7 Gaoping Village, Xiejiaya The over-standard time 0 0 0 0 / Township Gaoping Group, Monitored Value 6.28 0.55 34.3 53.5 7.88 Gaoping Village, Xiejiaya The over-standard time 0 0 0 0 / Township When pH≤5.5 ≤1.5 ≤400 ≤800 ≤200 Standard for Risk Control of When 5.5＜pH≤ 6.5 ≤2.0 ≤500 ≤850 ≤150 Soil Pollution of Agricultural Control Value Land (Trial) (GB When 6.5＜pH≤ 7.5 ≤3.0 ≤700 ≤1,000 ≤120 15618—2018) When pH＞7.5 ≤4.0 ≤1,000 ≤1,300 ≤100 52 2. Sediment of Irrigation Canal in Jishou City Table 6-2 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Jishou City Name of Monitoring factors (unit: mg/kg and pH being dimensionless ) Demonstration Specific Location Area Total Cr Cd Pb As pH Monitored Value 62.9 0.598 38.1 9.53 8.14 Group 1 of Liantian Village The over-standard time 0 0 0 0 0 Monitored Value 50.4 0.606 34.5 9.10 7.93 Group 3 of Xiaoxing Village Aizhai The over-standard time 0 0 0 0 0 Demonstration Area Monitored Value 103.0 0.398 27.8 6.50 7.98 Group 2 of Pinglang Village The over-standard time 0 0 0 0 0 Monitored Value 52.2 0.852 43.3 9.9 7.78 Group 2 of Shu’er Village The over-standard time 0 0 0 0 0 Monitored Value 58.7 0.664 33.2 14.1 7.83 Qianghu Village Qianzhou The over-standard time 0 0 0 0 / Demonstration Area Group 2 of Monitored Value 71.6 0.479 40.3 11.9 7.77 Sanchaping Village The over-standard time 0 0 0 0 / ≤800 ≤1.5 ≤400 ≤200 When pH≤5.5 Standard for Risk Control of When 5.5＜pH≤ ≤850 ≤2.0 ≤500 ≤150 Soil Pollution of Agricultural 6.5 Control Value Land (Trial) (GB When 6.5＜pH≤ 15618—2018) ≤1,000 ≤3.0 ≤700 ≤120 7.5 ≤1,300 ≤4.0 ≤1,000 ≤100 When pH＞7.5 53 3. Sediment of Irrigation Canal in Yongshun County Appendix 6-3 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Yongshun County Name of Monitoring factors (unit: mg/kg and pH being dimensionless ) Demonstration Specific Location Area Total Cr Cd Pb As pH Sediment of Monitored Value 75.4 0.17 31.2 10.6 6.6 Guanyuan Canal of Liulangxi The over-standard time 0 0 0 0 0 Village Sediment of Monitored Value 79.7 0.18 34.0 9.86 7.3 Longtan Canal of Xiqi Village The over-standard time 0 0 0 0 0 Xiqi Sediment of Monitored Value 73.6 0.22 35.1 9.55 7.7 Demonstration Xiangluxi River Area The over-standard time 0 0 0 0 0 of Hexin Village Sediment of Monitored Value 96.8 0.24 72.4 5.10 6.2 Zhangjiawan Reservoir The over-standard time 0 0 0 0 0 Sediment of Monitored Value 71.4 0.17 28.2 6.10 7.9 Xiache River of Hexin Village The over-standard time 0 0 0 0 / Sediment of Monitored Value 23.8 0.17 10.0 1.16 7.1 Wugui Spring of Taozixi Village The over-standard time 0 0 0 0 / Sediment of Monitored Value 44.2 0.32 30.3 4.91 6.9 Taozi Brook The over-standard time 0 0 0 0 / Shaba Demonstration Sediment of Monitored Value 53.8 0.27 25.5 2.34 8.3 Area Yashixi Reservoir The over-standard time 0 0 0 0 / Sediment of Monitored Value 49.2 0.61 21.7 5.85 7.2 Huanghuaxi River in Xishaba The over-standard time 0 0 0 0 / Village ≤800 ≤1.5 ≤400 ≤200 When pH≤5.5 Standard for Risk Control of Soil ≤850 ≤2.0 ≤500 ≤150 When 5.5＜pH≤ 6.5 Pollution of Agricultural Land Control Value (Trial) (GB 15618—2018) ≤1,000 ≤3.0 ≤700 ≤120 When 6.5＜pH≤ 7.5 ≤1,300 ≤4.0 ≤1,000 ≤100 When pH＞7.5 54 4. Sediment of Irrigation Canal in Cili County Appendix 6-4 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Cili County Name of Monitoring factors (unit: mg/kg and pH being dimensionless ) Demonstration Monitoring Results Area Total Cr Cd Pb As pH Sanhekou Town Monitored Value 76.3 0.282 26.1 6.59 4.96 Demonstration Zhuangta Village Area The over-standard time 0 0 0 0 / Monitored Value 75.5 0.924 28.8 7.07 6.39 Xuri Village The over-standard time 0 0 0 0 / Xiangshi Town Monitored Value 78.4 0.630 30.3 5.54 6.59 Baiyang Village Demonstration Heping Village Area The over-standard time 0 0 0 0 / Monitored Value 68.7 0.870 67.0 6.2 7.23 Zhaojialou of Xuri Village The over-standard time 0 0 0 0 / ≤800 ≤1.5 ≤400 ≤200 When pH≤5.5 Standard for Risk Control of When 5.5＜pH≤ ≤850 ≤2.0 ≤500 ≤150 Soil Pollution of Agricultural 6.5 Control Value Land (Trial) (GB When 6.5＜pH≤ 15618—2018) ≤1,000 ≤3.0 ≤700 ≤120 7.5 ≤1,300 ≤4.0 ≤1,000 ≤100 When pH＞7.5 55 5. Sediment of Irrigation Canal in Huayuan County Appendix 6-5 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in each Huayuan County Name of Monitoring Factor Demonstration Specific Location Area Total Cr (mg/kg) Cd (mg/kg) Pb (mg/kg) As (mg/kg) pH 1# irrigation Monitored Value 46 1.06 65 19.4 6.80 canal of Gaohe Village The over-standard time 0 0 0 0 0 Biancheng Town 2# irrigation Monitored Value 31 0.98 41 8.9 6.66 Demonstration canal of Gaohe Area Village The over-standard time 0 0 0 0 0 3# irrigation Monitored Value 110 2.57 67 12.9 7.49 canal of Gaohe Village The over-standard time 0 0 0 0 0 ≤800 ≤1.5 ≤400 ≤200 When pH≤5.5 Standard for Risk Control of Soil ≤850 ≤2.0 ≤500 ≤150 When 5.5＜pH≤ 6.5 Pollution of Agricultural Land Control Value (Trial) (GB 15618—2018) ≤1,000 ≤3.0 ≤700 ≤120 When 6.5＜pH≤ 7.5 ≤1,300 ≤4.0 ≤1,000 ≤100 When pH＞7.5 56 6. Sediment of Irrigation Canal in Anhua County Appendix 6-6 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Anhua County Name of Monitoring Factor Demonstration Specific Location Area Total Cr (mg/kg) Cd (mg/kg) Pb (mg/kg) As (mg/kg) Monitored Value 73 0.51 26 16.1 Gurong Village The over-standard time 0 0 0 0 Monitored Value 43 0.20 17 4.47 Zhangwangchong of Wenshi Village Le’an Town The over-standard time 0 0 0 0 Demonstration Area Monitored Value 60 0.27 21 4.75 Hengshi Village The over-standard time 0 0 0 0 Monitored Value 69 0.71 32 8.02 Yishui River of Yizhong Village The over-standard time 0 0 0 0 Dafu Town Monitored Value 68 0.55 23 6.88 Muxi Village, Demonstration Mengjia Village Area The over-standard time 0 0 0 0 Qingtang Town Dongtian River Monitored Value 93 0.72 36 12.0 Demonstration of Area DongtianVillage The over-standard time 0 0 0 0 When pH≤5.5 ≤800 ≤1.5 ≤400 ≤200 Standard for Risk Control of Soil When 5.5＜pH≤ 6.5 ≤850 ≤2.0 ≤500 ≤150 Pollution of Agricultural Land (Trial) (GB 15618—2018) Control When 6.5＜pH≤ 7.5 ≤1,000 ≤3.0 ≤700 ≤120 Value When pH＞7.5 ≤1,300 ≤4.0 ≤1,000 ≤100 57 7. Sediment of Irrigation Canal in Hengyang County Appendix 6-7 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Hengyang County Name of Monitoring Factor Demonstration Specific Location Pb (mg/kg) Total Cr (mg/kg) Cd (mg/kg) As (mg/kg) pH (dimensionless) Area Fuxing water Monitored Value 56.4 65 0.64 11.8 6.4 conservancy supporting The over-standard time 0 0 0 0 / facilities Monitored Value 61.3 55.4 0.71 11.8 7.6 Fuxing Sanhu The over-standard time 0 0 0 0 / Fuxing Yanglin Monitored Value 63.2 84.8 0.74 13.8 7.9 Demonstration Fuxing Maqiao The over-standard time 0 0 0 0 / Area Monitored Value 58.7 64 0.63 12.9 7.0 Fuxing Datang The over-standard time 0 0 0 0 / Monitored Value 65.8 65.3 0.47 14.4 6.0 Fuxing The over-standard time 0 0 0 0 / Monitored Value 75.2 73.9 0.65 24.2 8.4 Yanglin Wangjia The over-standard time 0 0 0 0 / Yunli water Monitored Value 87.4 51.5 1.47 13.1 7.9 conservancy supporting The over-standard time 0 0 0 0 / facilities in Qingli Xidu Town Shaping water Monitored Value 53.8 59.4 0.43 8.96 5.0 Qingli conservancy Demonstration supporting The over-standard time 0 0 0 0 / Area facilities in Qingli Shangde water Monitored Value 62 47.2 0.60 13.4 7.2 conservancy supporting The over-standard time 0 0 0 0 / facilities in Qingli 58 400 800 1.5 200 pH ＜5.5 Soil Environmental Quality Standard for Risk Control of Soil 500 850 2.0 150 5.5≤pH≤ 6.5 Pollution of Agricultural Land (Trial) (GB 15618—2018) Control Value 700 1,000 3.0 120 6.5≤pH≤ 7.5 1,000 1,000 4.0 100 pH＞7.5 59 8. Sediment in Hengnan County Appendix 6-8 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Hengnan County Name of Monitoring Factor Demonstration Specific Location Area Pb (mg/kg) Total Cr (mg/kg) Cd (mg/kg) As (mg/kg) pH (dimensionless) Canal beside the Monitored Value 63.9 36.9 1.14 9.24 6.6 Yantou Wellhead at the doorway of Lvziping, Hongni The over-standard time 0 0 0 0 / Group, Chaoyang Village Xiangyang Ditch beside Monitored Value 76.8 41.8 1.91 8.85 6.0 Demonstration Yejiaodaqiu, Area Ouyangzhijia, Dashuidong, Yangjia Group, The over-standard time 0 0 0 0 / Chaoyang Village Huanghe Village Monitored Value 166 45.5 1.37 42.9 6.4 Shangshengtang of Xini Group The over-standard time 0 0 0 0 / 400 800 1.5 200 pH ＜5.5 Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural Land (Trial) (GB 15618—2018) 500 850 2.0 150 5.5≤pH≤ 6.5 Control Value 700 1,000 3.0 120 6.5≤pH≤ 7.5 1,000 1,000 4.0 100 pH＞7.5 60 9. Sediment of irrigation canal in Lengshuitan Table 6-9 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Lengshuitan Monitoring Factor Name of Demonstration Area Specific location of sample (village/group) Pb Cr (mg/kg) Cd (mg/kg) As (mg/kg) pH (dimensionless) (mg/kg) Irrigation canal 39.6 66.8 0.715 12.5 6.94 Dengjiachong Xianghuaba Demonstration Area The over-standard Reservoir 0 0 0 0 / time Irrigation canal 31.1 45.3 0.534 9.6 7.12 Shixijiang Demonstration Area Lanjiang River The over-standard 0 0 0 0 / time 400 800 1.5 200 pH ＜5.5 Soil Environmental Quality Standard for Risk Control of Soil Pollution of Agricultural 500 850 2.0 150 5.5≤pH≤ 6.5 Land (Trial) (GB 15618—2018) Control Value 700 1,000 3.0 120 6.5≤pH≤ 7.5 1,000 1,000 4.0 100 pH＞7.5 61 10. Sediment of irrigation canal in Linwu County Table 6-10 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Linwu County Monitoring Factor Name of Name of Point Demonstration Monitoring Results Position Available pH Area Total Cr (mg/kg) Cd (mg/kg) Pb (mg/kg) Hg (mg/kg) As (mg/kg) Cd (mg/kg) (dimensionless) Monitored Value 28.7 0.42 24.5 0.058 28.6 0.12 7.68 Wushui Town Zhenshang Village The over-standard time 0 0 0 0 0 / / Monitored Value 39.2 0.37 231 0.075 33.8 0.072 7.83 Nanqiang Town Xiangtang Village The over-standard time 0 0 0 0 0 / / 800 1.5 400 2.0 200 / ≤5.5 Soil Environmental Quality Standard for Risk Control of Soil Pollution 850 2.0 500 2.5 150 / 5.5-6.5 of Agricultural Land (Trial) (GB 15618—2018) Control Value 1,000 3.0 700 4.0 120 / 6.5~7.5 1,300 4.0 1,000 6.0 100 / ＞7.5 62 11. Sediment of irrigation canal in Qiyang County Appendix 6-11 Monitoring and Evaluation Result of Sediment of Irrigation Canal of Newly-added Demonstration Areas in Qiyang County Name of Monitoring Factor Demonstrati Specific Location pH on Area Total Cr (mg/kg) Cd (mg/kg) Pb (mg/kg) Hg (mg/kg) As (mg/kg) (dimensionless) Tongzi Village of Monitored Value 61.3 0.81 31.8 0.184 11.2 6.66 Xiaojia Town (irrigation water intake of The over-standard Demonstration Area) 0 0 0 0 0 / time Xiaojia Irrigation water intake Monitored Value 40.4 0.51 21.8 0.111 4.94 6.16 Demonstrati of Jiuniba Village on Area Demonstration Area of The over-standard 0 0 0 0 0 / Xiaojia Town time Irrigation water intake Monitored Value 61.3 0.30 21.4 0.334 14.9 7.79 of Jiuniba Village Demonstration Area of The over-standard 0 0 0 0 0 / Xiaojia Town time 800 1.5 400 2.0 200 ≤5.5 Soil Environmental Quality Standard for Risk Control of Soil 850 2.0 500 2.5 150 5.5-6.5 Pollution of Agricultural Land (Trial) (GB 15618—2018) Control Value 1,000 3.0 700 4.0 120 6.5~7.5 1,300 4.0 1,000 6.0 100 ＞7.5 63 Appendix 7 Selection Sheet of Project Towns of Each Project County Table 7-1 Selection Sheet of Project Towns in Yongding District Paddy Field Indicator Grain Indicator Attention paid by Pollution local government Serial Proportion Standard-exceeding Analysis of Pollution Pollution Source Town Name Area Proportion Factor and public No. Yield in the rice Source Management Status (hectares) in the whole participation (ton) whole area willingness area (%) (%) Three Wastes were discharged in the past by Since 2008, improvement illegal industrial and mining and treatment as well as businesses and sporadic closedown have been Both the attention mining operations of iron, conducted. paid by the coal, nickel-molybdenum Industrial and mining government and the deposits, etc. into the Lishui Chongwen businesses were closed, participation 1 30.8 0.11% 623.2 0.43% Yes Cd River to cause pollution. Office illegal mining prohibited, willingness of the Farmlands were flooded by solid waste left over from public in the area are the Lishui River in the the past treated, water just average. rainstorm period and quality of the Lishui irrigated by wastewater from River cleaned and flood the Lishui River in the controlled by reservoirs. drought period, which resulted in soil pollution. Both the attention paid by the The nickel-molybdenum government and the Industrial and mining “three mines have been shut participation 2 Daping Town 461.33 1.63% 3,974.13 2.71% Yes Cd wastes” pollution down, with slags piled on willingness of the site. public in the area are just average. The Lishui River was Both the attention Wastewater irrigation by the Dayongqiao tested to be of clean water paid by the 3 70 0.25% 658.57 0.45% Yes Cd Lishui River and flood Office quality, and flood government and the sediments causing pollution prevention and reservoir participation 64 Paddy Field Indicator Grain Indicator Attention paid by Pollution local government Serial Proportion Standard-exceeding Analysis of Pollution Pollution Source Town Name Area Proportion Factor and public No. Yield in the rice Source Management Status (hectares) in the whole participation (ton) whole area willingness area (%) (%) regulation are willingness of the controllable. public in the area are just average. The Lishui River was High attention is paid tested to be of clean water by the government Wastewater irrigation by the Fengxianggang quality, and flood and the participation 4 775.73 2.74% 5,766.39 3.93% Yes Cd Lishui River and flood Township prevention and reservoir willingness of the sediments causing pollution regulation are public in the area is controllable. strong. Both the attention paid by the Three Wastes discharged by Tanmuxi State-owned government and the Guanliping the chemical and mining Coal Mine and Damijie 5 287.13 1.01% 3,376.94 2.30% Yes Cd participation Office businesses and wastewater Iron Mine have been shut willingness of the irrigation by the Lishui River down and slags treated. public in the area are just average. Both the attention paid by the No industrial and mining government and the Hezuoqiao business exists in the Rural cleaning projects participation 6 742.2 2.62% 5,382.83 3.67% Yes Cd Township vicinity. Pollution is caused have been implemented. willingness of the by agricultural inputs. public in the area are just average. The Lishui River was High attention is paid tested to be of clean water by the government Wastewater irrigation by the quality, and flood and the participation 7 Houping Town 1,085.8 3.83% 9,897.95 6.75% Yes Cd Lishui River and flood prevention and reservoir willingness of the sediments causing pollution regulation are public in the area is controllable. strong. 65 Paddy Field Indicator Grain Indicator Attention paid by Pollution local government Serial Proportion Standard-exceeding Analysis of Pollution Pollution Source Town Name Area Proportion Factor and public No. Yield in the rice Source Management Status (hectares) in the whole participation (ton) whole area willingness area (%) (%) High attention is paid No industrial and mining by the government business exists in the Rural cleaning projects and the participation 8 Jiaoziya Town 1,133.33 4.00% 10,504.77 7.17% None Cd vicinity. Pollution is caused have been implemented. willingness of the by agricultural inputs. public in the area is strong. Both the attention paid by the No industrial and mining government and the Luoshui business exists in the Rural cleaning projects participation 9 526.67 1.86% 5,018.53 3.42% Yes Cd Township vicinity. Pollution is caused have been implemented. willingness of the by agricultural inputs. public in the area are just average. Taiping Village is situated High attention is paid southeast of Qingyan Village, by the government The iron mire has been Luotaping where liquid and solid wastes and the participation 10 544.67 1.92% 5,363.21 3.66% Yes Cd shut down and slags County from industrial and mining willingness of the treated. businesses and wastewater public in the area is irrigation happen strong. Both the attention The Lishui River was paid by the tested to be of clean water government and the Wastewater irrigation by the Nanzhuangping quality, and flood participation 11 141.67 0.50% 770.99 0.53% Yes Cd Lishui River and flood Office prevention and reservoir willingness of the sediments causing pollution regulation are public in the area are controllable. just average. Both the attention Qiaotou Industrial and mining “three No measures have been paid by the 12 685.4 2.42% 5,896.16 4.02% None Cd Township wastes” pollution taken yet government and the participation 66 Paddy Field Indicator Grain Indicator Attention paid by Pollution local government Serial Proportion Standard-exceeding Analysis of Pollution Pollution Source Town Name Area Proportion Factor and public No. Yield in the rice Source Management Status (hectares) in the whole participation (ton) whole area willingness area (%) (%) willingness of the public in the area are just average. Both the attention paid by the Tanmuxi State-owned government and the Coal Mine and Damijie Qing’anping Industrial and mining “three participation 13 409.93 1.45% 6,182.39 4.22% Yes Cd Iron Mine have been shut Township wastes” pollution willingness of the down and slags piled on public in the area are site. just average. Both the attention paid by the The nickel-molybdenum government and the Sancha Industrial and mining “three mines have been shut participation 14 437 1.54% 4,483.61 3.06% Yes Cd Township wastes” pollution down, with slags piled on willingness of the site. public in the area are just average. Both the attention paid by the No industrial and mining government and the Sanjiaguan business exists in the Rural cleaning projects participation 15 720 2.54% 8,891.8 6.07% Yes Cd Township vicinity. Pollution is caused have been implemented. willingness of the by agricultural inputs. public in the area are just average. No industrial and mining Both the attention Shadi business exists in the Rural cleaning projects paid by the 16 780.67 2.76% 3,777.86 2.58% Yes Cd Township vicinity. Pollution is caused have been implemented. government and the by agricultural inputs. participation 67 Paddy Field Indicator Grain Indicator Attention paid by Pollution local government Serial Proportion Standard-exceeding Analysis of Pollution Pollution Source Town Name Area Proportion Factor and public No. Yield in the rice Source Management Status (hectares) in the whole participation (ton) whole area willingness area (%) (%) willingness of the public in the area are just average. Both the attention paid by the No industrial and mining government and the Shuangxiqiao business exists in the Rural cleaning projects participation 17 376.93 1.33% 2,953.53 2.02% Yes Cd Township vicinity. Pollution is caused have been implemented. willingness of the by agricultural inputs. public in the area are just average. Both the attention paid by the The nickel-molybdenum government and the Siduping Industrial and mining “three mines have been shut participation 18 699.87 2.47% 5,097.56 3.48% Yes Cd Township wastes” pollution down, with slags piled on willingness of the site. public in the area are just average. Both the attention paid by the No industrial and mining government and the Wangjiaping business exists in the Rural cleaning projects participation 19 1,179.27 4.16% 7,856.07 5.36% Yes Cd Town vicinity. Pollution is caused have been implemented. willingness of the by agricultural inputs. public in the area are just average. The Lishui River was High attention is paid Wastewater irrigation by the tested to be of clear water by the government 20 Wentang Town 245 0.86% 3,161.07 2.16% Yes Cd Lishui River and flood quality, river sediments and the participation sediments causing pollution have been removed and willingness of the 68 Paddy Field Indicator Grain Indicator Attention paid by Pollution local government Serial Proportion Standard-exceeding Analysis of Pollution Pollution Source Town Name Area Proportion Factor and public No. Yield in the rice Source Management Status (hectares) in the whole participation (ton) whole area willingness area (%) (%) flood prevention and public in the area is reservoir regulation are strong. controllable. Mining by any individual has been prohibited by the government. Part of High attention is paid slags has been treated and by the government Xixiping Industrial and mining “three the remaining will be and the participation 21 Sub-district 816.87 2.88% 7,141.31 4.87% Yes Cd wastes” pollution used as raw materials for willingness of the Office cement plants and such public in the area is treatment will be strong. accomplished year by year. Both the attention paid by the government and the Xiejiaya Controllable pollution participation 22 711.67 2.51% 6,661.85 4.55% Yes Cd Unclear pollution Township source willingness of the public in the area are just average. Both the attention paid by the government and the No measures have been 23 Xinqiao Town 661.47 2.34% 6,099.03 4.16% Yes Cd Unclear pollution source participation taken yet willingness of the public in the area are just average. The Lishui River was High attention is paid Wastewater irrigation by the Yanghuping tested to be of clean water by the government 24 885.6 3.13% 6,264.31 4.27% Yes Cd Lishui River and flood Town quality, and flood and the participation sediments causing pollution prevention and reservoir willingness of the 69 Paddy Field Indicator Grain Indicator Attention paid by Pollution local government Serial Proportion Standard-exceeding Analysis of Pollution Pollution Source Town Name Area Proportion Factor and public No. Yield in the rice Source Management Status (hectares) in the whole participation (ton) whole area willingness area (%) (%) regulation are public in the area is controllable. strong. Both the attention paid by the government and the Controllable pollution participation 25 Yinjiaxi Town 1,333.13 4.71% 12,256.51 8.36% None Clear pollution source source willingness of the public in the area are just average. The Lishui River was Both the attention tested to be of clear water paid by the Wastewater irrigation by the quality, river sediments government and the Yongding 26 0.67 0.00% 0.29 0.000% Yes Cd Lishui River and flood have been removed and participation Office sediments causing pollution flood prevention and willingness of the reservoir regulation are public in the area are controllable. just average High attention is paid by the government Yuanguping Controllable pollution and the participation 27 1,077.8 3.80%16964 8,492.14 5.79% Yes Cd Clear pollution source Town source willingness of the public in the area is strong. In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the local government to participate. Through the evaluation and selection, Jiaoziya Town, Wentang Town, Yanghuping Town and Yuanguping Town are selected as the newly-added project towns. 70 Table 7-2 Selection Sheet of Project Towns in Jishou City Indicator of farmland area Indicator of rice output Paddy Proportion of Ranking in Rice Rice Ranking of Attention paid by local Selected Serial Pollution sources and Pollution source management Town Name field cultivated land the cultivated output in output % of rice output government and public project No. pollution paths status area area in the land area of 2015 the total in in the total participation willingness towns (ha) whole city (%) the city (ton) the city in the city Average attention is paid by the government at the town and Jilue Scattered small area of There is no relevant 1 359 3.24 10 807.75 3.14 10 township level and the Township mining land management measure. participation willingness of the public in the area is not strong. During the “Twelfth Five-Year Plan” period, all enterprises High attention is paid by the Larger areas are required involving in heavy metal governments at the town and 2 Aizhai Town 978 8.84 7 2,200.5 8.55 8 for mining with a pollution in the area had taken township level and the √ centralized mapping. effective treatment measures as participation willingness of the required by the environmental public in the area is strong. protection authorities. Average attention is paid by the government at the town and Majing’ao Scattered small area of There is no relevant 3 2,016 18.22 1 4,536 17.63 1 township level and the Town mining land management measure. participation willingness of the public in the area is not strong. Average attention is paid by the government at the town and Shijiachong Scattered small area of There is no relevant 4 1,029 9.30 5 2,315.25 9.00 5 township level and the Sub-district mining land management measure. participation willingness of the public in the area is not strong. Average attention is paid by the government at the town and Danqing Scattered small area of There is no relevant township level and the 5 1,427 12.89 3 3,210.75 12.48 3 Town mining land management measure. participation willingness of the public in the area is not strong. Average attention is paid by the government at the town and Taiping Scattered small area of There is no relevant 6 1,246 11.26 4 2,803.5 10.89 4 township level and the Town mining land management measure. participation willingness of the public in the area is not strong. 71 Average attention is paid by the government at the town and Scattered small area of There is no relevant 7 Hexi Town 995 8.99 6 2,238.75 8.70 6 township level and the mining land management measure. participation willingness of the public in the area is not strong. Average attention is paid by the government at the town and Donghe Scattered small area of There is no relevant 8 480 4.34 9 1,080 4.20 9 township level and the Sub-district mining land management measure. participation willingness of the public in the area is not strong. During the “Twelfth Five-Year Plan” period, all enterprises High attention is paid by the Larger areas are required involving in heavy metal governments at the town and Qianzhou 9 1,436 12.98 2 3,877.2 15.07 2 for mining with a pollution in the area had taken township level and the √ Sub-district centralized mapping. effective treatment measures as participation willingness of the required by the environmental public in the area is strong. protection authorities. During the “Twelfth Five-Year Plan” period, all enterprises High attention is paid by the Larger areas are required involving in heavy metal governments at the town and Shuangtang 10 844 7.63 8 2,278.8 8.86 7 for mining with a pollution in the area had taken township level and the √ Sub-district centralized mapping. effective treatment measures as participation willingness of the required by the environmental public in the area is strong. protection authorities. Average attention is paid by the government at the town and Jifeng Scattered small area of There is no relevant 11 126 1.14 12 189 0.73 12 township level and the Sub-district mining land management measure. participation willingness of the public in the area is not strong. Average attention is paid by the government at the town and Zhenxi Scattered small area of There is no relevant 12 131 1.18 11 196.5 0.76 11 township level and the Sub-district mining land management measure. participation willingness of the public in the area is not strong. Total of the whole 11,067 100 25,734 100.00 city In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through the evaluation and selection, Aizhai Town and Qianzhou Sub-district are selected as the project towns. 72 Table 7-3 Selection Sheet of Project Towns in Yongshun County Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county A total of 4 point High attention locations were set up, is paid by the including 1 point Illegal mining Illegal mining governments at location with operations exited in the operations have the town and cadmium content of Cd town and township area been cracked Shouche No data township level 1 1,036.1 2.62 2,752.4 2.24 0.6-0.9mg/kg, pollution in the past and Three down on and Town yet and the accounting for 25%; 3 risk Wastes from these now are all shut participation point locations with operations were the down and willingness of cadmium content of source of pollution. banned. the public in the 0.3-0.6mg/kg, area is strong. accounting for 75%. High attention is paid by the A total of 7 point Small-size governments at locations were set up, metallurgical There is no the town and including 7 point Cd enterprises exited in the Kesha No data relevant township level 2 1,411.2 3.56 4,505.0 3.66 locations with pollution town and township area Township yet management and the cadmium content of risk and Three Wastes from measure. participation 0.3-0.6mg/kg, these businesses were willingness of accounting for 100%. the source of pollution. the public in the area is strong. A total of 17 point There is No enterprise involving There is no Average Furong No data 3 2,020.5 5.10 5,299.5 4.31 locations were set up, no risk of heavy metal pollution relevant attention is paid Town yet including 17 point cadmium existed in the town. management by the 73 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county locations with & arsenic Pollution may source measure. government at cadmium content of pollution. from the high the town and 0.3-0.6mg/kg, background values of township level accounting for 100%. heavy metals in the soil and the 2 point locations with and agricultural inputs. participation arsenic content of willingness of 20-30mg/kg and 5 the public in the point locations with area is not arsenic content of strong. 15-20mg/kg A total of 18 point locations were set up, Average including 3 point There once were some Enterprises attention is paid locations with nickel-molybdenum involving in by the cadmium content of enterprises involving in heavy metal government at ≥0.9mg/kg, There is heavy metal pollution pollution are all the town and accounting for no risk of Yongmao No data in the town and shut down and township level 4 463.8 1.17 1,586.1 1.29 16.67%; 7 point cadmium Town yet township area in the the tailing dams and the locations with & arsenic past and Three Wastes treated and participation cadmium content of pollution. from these businesses hence no new willingness of 0.6-0.9mg/kg, were the source of pollution will the public in the accounting for pollution. be caused. area is not 38.89%; 8 point strong. locations with cadmium content of 74 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county 0.3-0.6mg/kg, accounting for 44.44%; 8 point locations with arsenic content of 20-30mg/kg and 5 point locations with arsenic content of 15-20mg/kg A total of 6 point locations were set up, High attention including 6 point is paid by the locations with Illegal mining Illegal mining governments at cadmium content of There is operations exited in the operations have the town and 0.3-0.6mg/kg, no risk of town and township area been cracked Daba No data township level 5 889.2 2.24 3,844.2 3.12 accounting for 100%. cadmium in the past and Three down on and Township yet and the 1 point location with & arsenic Wastes from these now are all shut participation arsenic content of pollution. operations were the down and willingness of 15-20mg/kg and 5 source of pollution. banned. the public in the point locations with area is strong. arsenic content of ＜ 15mg/kg. A total of 6 point Cd No enterprise involving There is no High attention Diaojing No data 6 1,072.8 2.71 2,978.2 2.42 locations were set up, pollution heavy metal pollution relevant is paid by the Township yet including 6 point risk existed in the town. management governments at 75 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county locations with Pollution may source measure. the town and cadmium content of from the high township level 0.3-0.6mg/kg, background values of and the accounting for 100%. heavy metals in the soil participation 1 point location with and agricultural inputs. willingness of arsenic content of the public in the 20-30mg/kg and 5 area is strong. point locations with arsenic content of ＜ 15mg/kg. A total of 14 point locations were set up, High attention including 14 point No enterprise involving is paid by the locations with heavy metal pollution governments at cadmium content of existed in the town. There is no the town and 0.3-0.6mg/kg, Cd Fuzhi No data Pollution may source relevant township level 7 1,073.9 2.71 2,823.3 2.29 accounting for 100%. pollution Township yet from the high management and the 1 point location with risk background values of measure. participation arsenic content of heavy metals in the soil willingness of 15-20mg/kg and 13 and agricultural inputs. the public in the point locations with area is strong. arsenic content of ＜ 15mg/kg. Changguan A total of 11 point There is No data No enterprise involving There is no Average 8 353.8 0.89 1,204.2 0.98 Town locations were set up, no risk of yet heavy metal pollution relevant attention is paid 76 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county including 2 point cadmium existed in the town. management by the locations with & arsenic Pollution may source measure. government at cadmium content of pollution. from the high the town and ≥0.9mg/kg, background values of township level accounting for heavy metals in the soil and the 18.18%; 1 point and agricultural inputs. participation location with willingness of cadmium content of the public in the 0.6-0.9mg/kg, area is not accounting for 9.10%; strong. 8 point locations with cadmium content of 0.3-0.6mg/kg, accounting for 72.72%; 3 point locations with arsenic content of 15-20mg/kg. A total of 25 point Small-size Average locations were set up, There is metallurgical attention is paid There is no including 4 point no risk of enterprises exited in the by the Qingping No data relevant 9 1,157.9 2.92 2,318.5 1.88 locations with cadmium town and township area government at Town yet management cadmium content of & arsenic and Three Wastes from the town and measure. ≥0.9mg/kg, pollution. these businesses were township level accounting for 16%; 3 the source of pollution. and the 77 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county point location with participation cadmium content of willingness of 0.6-0.9mg/kg, the public in the accounting for 12%; area is not 18 point locations strong. with cadmium content of 0.3-0.6mg/kg, accounting for 72%; 3 point locations with arsenic content of 20-30mg/kg, 6 point locations with arsenic content of 15-20mg/kg and 12 point locations with arsenic content of ＜ 15mg/kg. There once were some Enterprises High attention A total of 5 point lead-zinc mining involving in is paid by the locations were set up, enterprises involving in heavy metal governments at including 5 point Cd Yanjing No data heavy metal pollution pollution are all the town and 10 745.5 1.88 1,418.4 1.15 locations with pollution Township yet in the town and shut down and township level cadmium content of risk township area in the the tailing dams and the 0.3-0.6mg/kg, past and Three Wastes treated and participation accounting for 100%. from these businesses hence no new willingness of 78 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county were the source of pollution will the public in the pollution. be caused. area is strong. A total of 14 point locations were set up, including 6 point locations with cadmium content of ≥0.9mg/kg, accounting for High attention 42.86%; 2 point No enterprise involving is paid by the location with heavy metal pollution governments at cadmium content of There is existed in the town. There is no the town and 0.6-0.9mg/kg, no risk of No data Pollution may source relevant township level 11 Zejia Town 1,633.3 4.12 4,042.0 3.28 accounting for cadmium yet from the high management and the 14.28%; 6 point & arsenic background values of measure. participation locations with pollution. heavy metals in the soil willingness of cadmium content of and agricultural inputs. the public in the 0.3-0.6mg/kg, area is strong. accounting for 42.86%; 1 point location with arsenic content of 15-20mg/kg and 13 point locations with arsenic content of ＜ 79 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county 15mg/kg. A total of 30 point locations were set up, including 2 point locations with cadmium content of Average ≥0.9mg/kg, attention is paid accounting for 6.67%; No enterprise involving by the 1 point location with heavy metal pollution government at cadmium content of There is existed in the town. There is no the town and 0.6-0.9mg/kg, no risk of No data Pollution may source relevant township level 12 Shidi Town 4,646.4 11.73 12,424.0 10.1 accounting for 3.33%; cadmium yet from the high management and the 27 point locations & arsenic background values of measure. participation with cadmium content pollution. heavy metals in the soil willingness of of 0.3-0.6mg/kg, and agricultural inputs. the public in the accounting for 90.0%; area is not 6 point locations with strong. arsenic content of 20-30mg/kg and 7 point locations with arsenic content of 15-20mg/kg A total of 15 point Cd Metallurgical There is no High attention Wanping No data 13 2,118.9 5.35 7,233.3 5.88 locations were set up, pollution enterprises and relevant is paid by the √ Town yet including 1 point risk fertilizer plants existed management governments at 80 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county location with in the town and measure. the town and cadmium content of township area in the township level 0.6-0.9mg/kg, past and Three Wastes and the accounting for 6.67%; from them were the participation 14 point locations source of pollution. willingness of with cadmium content the public in the of 0.3-0.6mg/kg, area is strong. accounting for 93.33%. Average attention is paid by the A total of 2 point Illegal mining Illegal mining government at locations were set up, operations exited in the operations have the town and including 2 point Cd town and township area been cracked Tawo No data township level 14 2,492.1 6.29 7,683.0 6.24 locations with pollution in the past and Three down on and Town yet and the cadmium content of risk Wastes from these now are all shut participation 0.3-0.6mg/kg, operations were the down and willingness of accounting for 100%. source of pollution. banned. the public in the area is not strong. A total of 7 point Guanping Iron Mine in Enterprises High attention Cd Shaba locations were set up, No data the Taozixi Mine Area involving in is paid by the 15 2,621.6 6.62 9,422.0 7.66 pollution Town including 1 point yet in the town and heavy metal governments at risk location with township area in the pollution are all the town and 81 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county cadmium content of past discharged Three shut down and township level 0.6-0.9mg/kg, Wastes, which was the the mine pits and the accounting for source of pollution. closed and participation 14.29%; 6 point hence no new willingness of locations with pollution will the public in the cadmium content of be caused. area is strong. 0.3-0.6mg/kg, accounting for 85.71%. A total of 9 point locations were set up, including 9 point Average locations with There was no attention is paid cadmium content of enterprise in the town by the 0.3-0.6mg/kg, and township involving government at There is accounting for 100%. in heavy metal There is no the town and no risk of Lingxi 1 point locations with No data pollution. Pollution relevant township level 16 1,512.5 3.82 5,603.5 4.55 cadmium Town arsenic content of yet may source from the management and the & arsenic 20-30mg/kg, 5 point high background measure. participation pollution. locations with arsenic values of heavy metals willingness of content of in the soil and the public in the 15-20mg/kg and 3 agricultural inputs. area is not point locations with strong. arsenic content of ＜ 15mg/kg. 82 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county A total of 8 point locations were set up, including 5 point locations with High attention cadmium content of ≥ is paid by the 0.9mg/kg, accounting Illegal mining Illegal mining governments at for 62.5%; 3 point There is operations exited in the operations have the town and locations with no risk of town and township area been cracked Liangcha No data township level 17 796.2 2.01 2,223.9 1.81 cadmium content of cadmium in the past and Three down on and Township yet and the 0.3-0.6mg/kg, & arsenic Wastes from these now are all shut participation accounting for 37.5%. pollution. operations were the down and willingness of 1 point location with source of pollution. banned. the public in the arsenic content of area is strong. 20-30mg/kg and 7 point locations with arsenic content of ＜ 15mg/kg. There was no Average A total of 3 point enterprise in the town attention is paid locations were set up, and township involving There is no by the including 3 point Cd Shaoha No data in heavy metal relevant government at 18 766.5 1.94 3,688.9 3 locations with pollution Township yet pollution. Pollution management the town and cadmium content of risk may source from the measure. township level 0.3-0.6mg/kg, high background and the accounting for 100%. values of heavy metals participation 83 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county in the soil and willingness of agricultural inputs. the public in the area is not strong. High attention is paid by the A total of 20 point governments at locations were set up, There was no There is no the town and including 20 point enterprise in the town Xiqi No data relevant township level 19 722.4 1.82 2,207.6 1.79 locations with No risk and township involving Township yet management and the cadmium content of≤ in heavy metal measure. participation 0.3mg/kg, accounting pollution. willingness of for 100%. the public in the area is strong. A total of 19 point High attention locations were set up, is paid by the including 8 point Illegal mining Illegal mining governments at locations with There is operations exited in the operations have the town and cadmium content of no risk of town and township area been cracked Duishan No data township level 20 559.3 1.41 1,774.2 1.44 ≥0.9mg/kg, cadmium in the past and Three down on and Township yet and the accounting for & arsenic Wastes from these now are all shut participation 42.11%; 1 point pollution. operations were the down and willingness of location with source of pollution. banned. the public in the cadmium content of area is strong. 0.6-0.9mg/kg, 84 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county accounting for 5.26%; 10 point locations with cadmium content of 0.3-0.6mg/kg, accounting for 52.63%; 2 point locations with arsenic content of 15-20mg/kg and 17 point locations with arsenic content of ＜ 15mg/kg. A total of 12 point locations were set up, Enterprises High attention including 1 point involving in is paid by the location with Small-size heavy metal governments at cadmium content of ≥ There is metallurgical pollution are all the town and 0.9mg/kg, accounting no risk of enterprises exited in the Liexi No data shut down and township level 21 863.5 2.18 2,230.2 1.81 for 8.33%; 11 point cadmium town and township area Township yet the tailing dams and the locations with & arsenic and Three Wastes from treated and participation cadmium content of pollution. these businesses were hence no new willingness of 0.3-0.6mg/kg, the source of pollution. pollution will the public in the accounting for be caused. area is strong. 91.67%. 2 point locations with arsenic 85 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county content of 20-30mg/kg, 2 point locations with arsenic content of 15-20mg/kg and 8 point locations with arsenic content of ＜ 15mg/kg. A total of 42 point locations were set up, including 1 point location with There was no High attention cadmium content of enterprise in the town is paid by the 0.6-0.9mg/kg, and township involving governments at accounting for 2.38%; There is in heavy metal There is no the town and 41 point locations no risk of Songbai No data pollution. Pollution relevant township level 22 2,619.4 6.61 10,985.1 8.93 with cadmium content cadmium Town yet may source from the management and the of 0.3-0.6mg/kg, & arsenic high background measure. participation accounting for pollution. values of heavy metals willingness of 97.62%. 3 point in the soil and the public in the locations with arsenic agricultural inputs. area is strong. content of 20-30mg/kg, 14 point locations with arsenic content of 86 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county 15-20mg/kg and 25 point locations with arsenic content of ＜ 15mg/kg. A total of 21 point locations were set up, including 19 point locations with cadmium content of Average 0.3- 0.6mg/kg, Enterprises attention is paid accounting for involving in by the 90.48%; 2 point Small-size heavy metal government at locations with There is metallurgical pollution are all the town and cadmium content of ≤ no risk of enterprises exited in the Gaoping No data shut down and township level 23 1,787.8 4.51 5,390.0 4.38 0.3mg/kg, accounting cadmium town and township area Township yet the tailing dams and the for 9.52%. 3 point & arsenic and Three Wastes from treated and participation locations with arsenic pollution. these businesses were hence no new willingness of content of the source of pollution. pollution will the public in the 20-30mg/kg, 6 point be caused. area is not locations with arsenic strong. content of 15-20mg/kg and 12 point locations with arsenic content of ＜ 15mg/kg. 87 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county A total of 16 point locations were set up, including 1 point location with cadmium content of ≥0.9mg/kg, accounting for 6.25%; Average 6 point locations with Enterprises attention is paid cadmium content of involving in by the 0.6-0.9mg/kg, Small-size heavy metal government at accounting for 37.5%; There is metallurgical pollution are all the town and 8 point locations with no risk of enterprises exited in the Huilong No data shut down and township level 24 379.9 0.96 1,693.0 1.38 cadmium content of cadmium town and township area Township yet the tailing dams and the 0.3-0.6mg/kg, & arsenic and Three Wastes from treated and participation accounting for 50%; 1 pollution. these businesses were hence no new willingness of point location with the source of pollution. pollution will the public in the cadmium content of be caused. area is not ≤0.3mg/kg, strong. accounting for 6.25% 5 point locations with arsenic content of 20-30mg/kg and 2 point locations with arsenic content of 15-20mg/kg 88 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county A total of 6 point locations were set up, including 1 point location with There was no High attention cadmium content of enterprise in the town is paid by the ≥0.9mg/kg, and township involving governments at accounting for in heavy metal There is no the town and Cd Xiaoxi 16.67%; 3 point No data pollution. Pollution relevant township level 25 805.2 2.03 2,409.4 1.96 pollution Township locations with yet may source from the management and the risk cadmium content of high background measure. participation 0.3-0.6mg/kg, values of heavy metals willingness of accounting for 50%; 2 in the soil and the public in the point locations with agricultural inputs. area is strong. cadmium content of ≤ 0.3mg/kg, accounting for 33.33%; A total of 19 point There was no High attention locations were set up, enterprise in the town is paid by the including 9 point There is and township involving governments at There is no locations with no risk of in heavy metal the town and Langxi No data relevant 26 419.8 1.06 1,574.7 1.28 cadmium content of cadmium pollution. Pollution township level Township yet management ≥0.9mg/kg, & arsenic may source from the and the measure. accounting for pollution. high background participation 47.37%; 2 point values of heavy metals willingness of locations with in the soil and the public in the 89 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county cadmium content of agricultural inputs. area is strong. 0.6-0.9mg/kg, accounting for 10.53%; 7 point locations with cadmium content of 0.3-0.6mg/kg, accounting for 36.84%; 1 point location with cadmium content of ≤0.3mg/kg, accounting for 5.26%. 1 point location with arsenic content of 20-30mg/kg, 2 point locations with arsenic content of 15-20mg/kg and 16 point locations with arsenic content of ＜ 15mg/kg. A total of 4 point Cd There was no There is no High attention Runya No data 27 841.6 2.12 2,636.3 2.14 locations were set up, pollution enterprise in the town relevant is paid by the Township yet including 1 point risk and township involving management governments at 90 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county location with in heavy metal measure. the town and cadmium content of pollution. Pollution township level 0.3- 0.6mg/kg, may source from the and the accounting for 25%; 3 high background participation point locations with values of heavy metals willingness of cadmium content of ≤ in the soil and the public in the 0.3mg/kg, accounting agricultural inputs. area is strong. for 75%. A total of 3 point locations were set up, High attention including 2 point is paid by the Illegal mining Illegal mining locations with governments at operations exited in the operations have cadmium content of the town and Cd town and township area been cracked Cheping 0.3- 0.6mg/kg, No data township level 28 982.2 2.48 4,089.9 3.32 pollution in the past and Three down on and Township accounting for yet and the risk Wastes from these now are all shut 66.67%; 1 point participation operations were the down and location with willingness of source of pollution. banned. cadmium content of ≤ the public in the 0.3mg/kg, accounting area is strong. for 33.33%. A total of 14 point There is There was no Average There is no locations were set up, no risk of enterprise in the town attention is paid Maoba No data relevant 29 1,786.7 4.51 4,241.3 3.45 including 14 point cadmium and township involving by the Township yet management locations with & arsenic in heavy metal government at measure. cadmium content of pollution. pollution. Pollution the town and 91 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county 0.3-0.6mg/kg, may source from the township level accounting for 100%. high background and the 2 point locations with values of heavy metals participation arsenic content of in the soil and willingness of 15-20mg/kg and 12 agricultural inputs. the public in the point locations with area is not arsenic content of ＜ strong. 15mg/kg. A total of 17 point locations were set up, including 2 point locations with There once were some Enterprises High attention cadmium content of lead-zinc mining involving in is paid by the 0.6-0.9mg/kg, enterprises involving in heavy metal governments at accounting for There is heavy metal pollution pollution are all the town and 11.76%; 15 point no risk of Wanmin No data in the town and shut down and township level 30 1,030.9 2.60 2,780.2 2.26 locations with cadmium Township yet township area in the the tailing dams and the cadmium content of & arsenic past and Three Wastes treated and participation 0.3-0.6mg/kg, pollution. from these enterprises hence no new willingness of accounting for were the source of pollution will the public in the 88.24%. 1 point pollution. be caused. area is strong. location with arsenic content of 20-30mg/kg and 16 point locations with 92 Whether Attention paid the Pollution by local farmland Rice Selected Heavy metal content source government Indicator of farmland Indicator of rice is at risk Cd Main pollution source project of soil management and public and the content towns status participation Towns and type of Serial willingness townships risk No. Name Rice Proportion Paddy output % of Rice field of the cultivated output area total in land in the (ton) (ha) the county (%) county arsenic content of ＜ 15mg/kg. Total 39,610.6 100.00 123,062.3 100.00 In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through the evaluation and selection, Xiqi Township and Shaba Town are selected as the project towns. 93 Table 7-4 Selection Sheet of Project Towns in Cili County Standard-exceeding Standard-exceeding Pollution Selected Indicator of Indicator of rice rice soil factor Main pollution source Pollution source management status project farmland towns Towns and Serial Rice townships Paddy Proportion of No. Rice output % Name field cultivated output of the total area land in the (ton) in the (ha) county (%) county Sewage effluent treatment plants are The Industrial Park of the built in the Industrial Park. Three County and mining of coal Lingyang Wastes are collected through the 1 1,387 5.60% 8,716.8 5.60% Yes Yes Cd and calcareous shale cause Town pipeline network. Coal and calcareous agricultural non-point source shale mines are shut down while pollution, etc. tailings need to be treated. There are no mines, Use of agricultural inputs was reduced Yanbodu atmospheric sedimentation, 2 1,671 6.75% 10,501.6 6.75% Yes Yes Cd and ‘cleaning projects’ are developed Town agricultural non-point source and ‘beautiful villages’ built. pollution, etc. There were no mines, Environmental governance will be Nanshanping 3 746 3.01% 4,688.4 3.01% Yes Yes Cd atmospheric sedimentation, developed, ‘beautiful villages’ built Town soil parent materials, etc. and use of agricultural inputs reduced. Nickel-molybdenum ore Ganyan The enterprise was shut down in 2008 4 1,807 7.30% 11,356.2 7.30% Yes Yes Cd processing enterprises cause Township while three wastes need to be treated. Three Wastes pollution, etc. Environmental protection projects and Atmospheric sedimentation, measures are developed including Yanghe “three wastes” from daily life 5 1,268 5.12% 7,968.8 5.12% No ‘cleaning projects’, ‘beautiful Township and agricultural non-point villages’, ‘urban-rural co-governance’, source pollution, etc. etc. Environmental protection projects and Atmospheric sedimentation, measures are developed including Xujiafang “three wastes” from daily life 6 1,061 4.29% 6,667.9 4.29% No ‘cleaning projects’, ‘beautiful Township and agricultural non-point villages’, ‘urban-rural co-governance’, source pollution, etc. etc. 3 nickel-molybdenum The enterprise was shut down in 2008 7 Xikou Town 655 2.65% 4,116.4 2.65% Yes Yes Cd processing enterprises causing and Three Wastes treatment Three Wastes pollution, commenced but the source of pollution 94 Standard-exceeding Standard-exceeding Pollution Selected Indicator of Indicator of rice rice soil factor Main pollution source Pollution source management status project farmland towns Towns and Serial Rice townships Paddy Proportion of No. Rice output % Name field cultivated output of the total area land in the (ton) in the (ha) county (%) county atmospheric sedimentation, is not cut off yet. etc. Three Wastes pollution, Mines were closed and mining stopped Jinyan atmospheric sedimentation, 8 812 3.28% 5,103.1 3.28% Yes Yes Cd in 2008 while tailings and slags Township etc. in the nickel-molybdenum treatment has not been finished yet. mining area. Mines were closed and mining stopped in 2008, eco-environmental restoration and protection developed and tailing Atmospheric sedimentation, Dongxi dams treated. A total of RMB100 9 622 2.51% 3,909 2.51% Yes Yes Cd, As etc. in the nickel-molybdenum Township million has been invested. Stage 1 and mining area Stage 2 have been accepted and Stage 3 of treatment is being inspected for acceptance. The mine was shut down in 2008 and Nickel molybdenum mining eco-environmental restoration and area, metallurgical plants, protection developed. Baizhuyu and 10 Gaoqiao Town 1,087 4.39% 6,831.3 4.39% Yes Yes Cd, As Yes atmospheric sedimentation, Huanglinyu tailing dams are treated, etc. slags buried and wastewater treatment reaching the standard. Marble mining and processing causing atmospheric ‘Beautiful villages’ have been being Longtanhe 11 1,469 5.94% 9,232 5.94% Yes Yes Cd sedimentation, agricultural built while tailings and Three Wastes Town non-point source pollution, from enterprises need to be treated. etc. Environmental protection projects and Atmospheric sedimentation, measures are developed including Erfangping domestic three wastes, 12 1,179 4.76% 7,409.5 4.76% Yes Yes ‘cleaning projects’, ‘beautiful Township agricultural non-point source villages’, ‘urban-rural co-governance’, pollution, etc. etc. 95 Standard-exceeding Standard-exceeding Pollution Selected Indicator of Indicator of rice rice soil factor Main pollution source Pollution source management status project farmland towns Towns and Serial Rice townships Paddy Proportion of No. Rice output % Name field cultivated output of the total area land in the (ton) in the (ha) county (%) county Environmental protection projects and Atmospheric sedimentation, measures are developed including domestic three wastes, 13 Lingxi Town 2,110 8.53% 13,260.4 8.53% No No ‘cleaning projects’, ‘beautiful agricultural non-point source villages’, ‘urban-rural co-governance’, pollution, etc. etc. Shut down already. A wastewater Exploitation of Bailong Coal treatment project was launched in the 14 Miaoshi Town 419 1.69% 2,633.2 1.69% No No Mine, atmospheric county in 2016 and treatment is sedimentation, etc ongoing. Three wastes pollution from Guangfuqiao Guangfuqiao Coal Mine, The mine was shut down in 2008 15 786 3.18% 4,939.7 3.18% No No Town atmospheric sedimentation, while three wastes need to be treated.. etc. Zhuangta Reservoir is polluted Zhuangta Coal Mine has been shut Yangliupu by Zhuangta Coal Mine, down and the source of irrigation 16 845 3.41% 5,310.4 3.41% Yes Yes Cd, As Yes Township resulting in wastewater water has been tested to be irrigation. satisfactory. Zhuangta Reservoir is polluted Zhuangta Coal Mine has been shut Dongyueguan by Zhuangta Coal Mine, down and the source of irrigation 17 940 3.80% 5,907.5 3.80% Yes Yes Cd, As Yes Town resulting in wastewater water has been tested to be irrigation. satisfactory. Zhuangta Reservoir is polluted Zhuangta Coal Mine has been shut Tonfjinpu by Zhuangta Coal Mine, down and the source of irrigation 18 995 4.02% 6,253.1 4.02% Yes Yes Cd, As Yes Town resulting in wastewater water has been tested to be irrigation. satisfactory. Zhuangta Reservoir is polluted Zhuangta Coal Mine has been shut by Zhuangta Coal Mine, Shanmuqiao down and the source of irrigation 19 864 3.49% 5,429.9 3.49% Yes Yes Cd where it is situated in the Town water has been tested to be Irrigated Area of West Major satisfactory. Canal, causing wastewater 96 Standard-exceeding Standard-exceeding Pollution Selected Indicator of Indicator of rice rice soil factor Main pollution source Pollution source management status project farmland towns Towns and Serial Rice townships Paddy Proportion of No. Rice output % Name field cultivated output of the total area land in the (ton) in the (ha) county (%) county irrigation. Environmental protection projects and Atmospheric sedimentation, measures are developed including Xiangshi “three wastes” from daily life 20 530 2.14% 3,330.8 2.14% No No ‘cleaning projects’, ‘beautiful Yes Town and agricultural non-point villages’, ‘urban-rural co-governance’, source pollution, etc. etc. Three wastes pollution from The Realgar Plant was closed in 2002 21 Sanhe Town 727 2.94% 4,568.9 2.94% Yes Yes Cd, As the Realgar Plant and and the coal mine is now closed, and Yes Zhuangta Coal Mine solid waste has been almost treated. Environmental protection projects and Atmospheric sedimentation, measures are developed including “three wastes” from daily life 22 Jiangya Town 1,048 4.23% 6,586.2 4.23% No No ‘cleaning projects’, ‘beautiful and agricultural non-point villages’, ‘urban-rural co-governance’, source pollution, etc. etc. Environmental protection projects and Atmospheric sedimentation, measures are developed including Zhaojiagang “three wastes” from daily life 23 589 2.38% 3,701.6 2.38% No No ‘cleaning projects’, ‘beautiful Township and agricultural non-point villages’, ‘urban-rural co-governance’, source pollution, etc. etc. Environmental protection projects and Atmospheric sedimentation, measures are developed including Sanguansi “three wastes” from daily life 24 871 3.52% 5,473.8 3.52% No No ‘cleaning projects’, ‘beautiful Township and agricultural non-point villages’, ‘urban-rural co-governance’, source pollution, etc. etc. Environmental protection projects and Atmospheric sedimentation, measures are developed including Gaofeng “three wastes” from daily life 25 262 1.06% 1,646.6 1.06% No No ‘cleaning projects’, ‘beautiful Township and agricultural non-point villages’, ‘urban-rural co-governance’, source pollution, etc. etc. 97 98 Table 7-5 Selection Sheet of Project Towns in Huayuan County Indicator of farmland area Indicator of rice output Proportion of Ranking of In 2014 Rice Ranking of Pollution sources Attention paid by local Selected Serial Town Paddy Pollution source management cultivated land the cultivated Rice output % of rice output and pollution government and public project No. Name field area status in the county land area in output the total in in the total in paths participation willingness towns (ha) (%) the county (ton) the county the county During the “Twelfth Five-Year Plan” High attention is paid by the Larger areas are period, all enterprises involving in governments at the town and required for Longtan heavy metal pollution in the area had township level and the 1 1,047 4.24 13 2,230.0 3.88 14 mining with a √ Town taken effective treatment measures participation willingness of centralized as required by the environmental the public in the area is mapping. protection authorities. strong. Average attention is paid by the government at the town Scattered small There is no relevant management and township level and the 2 Minle Town 885 3.58 18 2,522.0 4.39 12 area of mining measure. participation willingness of land the public in the area is not strong. Average attention is paid by Larger areas are the government at the town required for Tuanjie There is no relevant management and township level and the 3 1,240 5.02 9 2,378.0 4.14 13 mining with a Town measure. participation willingness of centralized the public in the area is not mapping. strong. Average attention is paid by Scattered small There is no relevant management the government at the town 4 Jiwei Town 2,424.6 9.81 1 5,833.0 10.16 1 area of mining measure. and township level and the land participation willingness of 99 Indicator of farmland area Indicator of rice output Proportion of Ranking of In 2014 Rice Ranking of Pollution sources Attention paid by local Selected Serial Town Paddy Pollution source management cultivated land the cultivated Rice output % of rice output and pollution government and public project No. Name field area status in the county land area in output the total in in the total in paths participation willingness towns (ha) (%) the county (ton) the county the county the public in the area is not strong. During the “Twelfth Five-Year Plan” High attention is paid by the period, all enterprises involving in governments at the town and Scattered small Malichang heavy metal pollution in the area had township level and the 5 1,493 6.04 7 4,231.0 7.37 4 area of mining √ Town taken effective treatment measures participation willingness of land as required by the environmental the public in the area is protection authorities. strong. Average attention is paid by the government at the town Scattered small Yayou There is no relevant management and township level and the 6 1,054 4.27 12 2,091.0 3.64 15 area of mining Town measure. participation willingness of land the public in the area is not strong. High attention is paid by the government at the town and Scattered small Biancheng There is no relevant management township level and the 7 1,214 4.91 10 3,182.0 5.54 8 area of mining Town measure. participation willingness of land the public in the area is strong. Scattered small During the “Twelfth Five-Year Plan” High attention is paid by the Huayuan 8 2,080 8.42 3 5,255.0 9.15 2 area of mining period, all enterprises involving in governments at the town and √ Town land heavy metal pollution in the area had township level and the 100 Indicator of farmland area Indicator of rice output Proportion of Ranking of In 2014 Rice Ranking of Pollution sources Attention paid by local Selected Serial Town Paddy Pollution source management cultivated land the cultivated Rice output % of rice output and pollution government and public project No. Name field area status in the county land area in output the total in in the total in paths participation willingness towns (ha) (%) the county (ton) the county the county taken effective treatment measures participation willingness of as required by the environmental the public in the area is protection authorities. strong. Average attention is paid by the government at the town Scattered small Changle There is no relevant management and township level and the 9 1,573 6.37 5 3,162.0 5.51 9 area of mining Township measure. participation willingness of land the public in the area is not strong. Average attention is paid by The government at the town Scattered small Lianghe There is no relevant management and township level and the 10 1,002 4.05 15 2,017.0 3.51 16 area of mining Township measure. participation willingness of land the public in the area is not strong. Average attention is paid by the government at the town Scattered small Paibi There is no relevant management and township level and the 11 1,266 5.12 8 2,910.0 5.07 10 area of mining Township measure. participation willingness of land the public in the area is not strong. Dongmaku Scattered small There is no relevant management Average attention is paid by 12 1,638 6.63 4 3,617.0 6.30 7 Township area of mining measure. the government at the town 101 Indicator of farmland area Indicator of rice output Proportion of Ranking of In 2014 Rice Ranking of Pollution sources Attention paid by local Selected Serial Town Paddy Pollution source management cultivated land the cultivated Rice output % of rice output and pollution government and public project No. Name field area status in the county land area in output the total in in the total in paths participation willingness towns (ha) (%) the county (ton) the county the county land and township level and the participation willingness of the public in the area is not strong. During the “Twelfth Five-Year Plan” High attention is paid by the Larger areas are period, all enterprises involving in governments at the town and required for Mao'er heavy metal pollution in the area had township level and the 13 1,499 6.07 6 4,376.0 7.62 3 mining with a √ Township taken effective treatment measures participation willingness of centralized as required by the environmental the public in the area is mapping. protection authorities. strong. During the “Twelfth Five-Year Plan” High attention is paid by the period, all enterprises involving in governments at the town and Scattered small Dao’er heavy metal pollution in the area had township level and the 14 950 3.84 16 1,365.0 2.38 18 area of mining √ Township taken effective treatment measures participation willingness of land as required by the environmental the public in the area is protection authorities. strong. Average attention is paid by the government at the town Scattered small Paiwu There is no relevant management and township level and the 15 1,074 4.35 11 1,913.0 3.33 17 area of mining Township measure. participation willingness of land the public in the area is not strong. 16 Pailiao 908 3.67 17 2,595.0 4.52 11 Scattered small There is no relevant management Average attention is paid by 102 Indicator of farmland area Indicator of rice output Proportion of Ranking of In 2014 Rice Ranking of Pollution sources Attention paid by local Selected Serial Town Paddy Pollution source management cultivated land the cultivated Rice output % of rice output and pollution government and public project No. Name field area status in the county land area in output the total in in the total in paths participation willingness towns (ha) (%) the county (ton) the county the county Township area of mining measure. the government at the town land and township level and the participation willingness of the public in the area is not strong. Average attention is paid by the government at the town Scattered small Yaqiao There is no relevant management and township level and the 17 1,011 4.09 14 3,626.0 6.31 6 area of mining Township measure. participation willingness of land the public in the area is not strong. Average attention is paid by the government at the town Scattered small Buchou There is no relevant management and township level and the 18 2,199 8.90 2 4,130.0 7.19 5 area of mining Township measure. participation willingness of land the public in the area is not strong. Average attention is paid by the government at the town Scattered small There is no relevant management and township level and the Total of the county 24,712.21 100.00 57,433.0 100.00 area of mining measure. participation willingness of land the public in the area is not strong. 103 Indicator of farmland area Indicator of rice output Proportion of Ranking of In 2014 Rice Ranking of Pollution sources Attention paid by local Selected Serial Town Paddy Pollution source management cultivated land the cultivated Rice output % of rice output and pollution government and public project No. Name field area status in the county land area in output the total in in the total in paths participation willingness towns (ha) (%) the county (ton) the county the county In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through the evaluation and selection, Biancheng Town is selected as the newly-added project town. 104 Table 7-6 Selection Sheet of Project Towns in Anhua County Indicator of Indicator of rice output Whether farmland area Attention paid the In 2016 Rice Ranking Pollution by local Area of Proportion farmland Pollution Selected Serial Paddy output % of rice Heavy metal content of source government Town Name the of area of is at risk Rice Cd content sources and project No. soil management and public territory field the Rice of the output in and the pollution paths towns area total in the total status participation territory output type of willingness (ha) (ton) the in the risk (%) county county A total of 20 point locations were set up, including 5 point locations with cadmium content of ≥0.9mg/kg, accounting for 25%; 2 Three Wastes point locations with High attention is discharged by cadmium content of paid by the the enterprises 0.6-0.9mg/kg, governments at There is involving heavy accounting for 10%; 5 the town and risk of metal pollution Gaoming point locations with township level 1 9,750 412 4.23% 3,087 1.68% 19 cadmium No data yet pollute the Township cadmium content of and the & arsenic farmlands by 0.3-0.6mg/kg, participation pollution. atmospheric accounting for 25%; 8 willingness of sedimentation point locations with the public in the and wastewater cadmium content of area is strong. irrigation. ≤0.3mg/kg, accounting for 40%. 1 point location of cadmium and arsenic compound pollution A total of 36 point A total of 21 point Three Wastes High attention is locations were set up, locations were set up in discharged by paid by the including 15 point the town, including 15 the enterprises governments at There is locations with cadmium point locations with involving heavy the town and risk of Qingtangpu content of ≥0.9mg/kg, cadmium content of metal pollution Has been township level 2 23,400 1,408 6.02% 10,558 5.76% 7 cadmium √ Town accounting for 41.67%; <0.2mg/kg, accounting pollute the treated and the & arsenic 8 point locations with for 71.43%; 1 point farmlands by participation pollution. cadmium content of location with cadmium atmospheric willingness of 0.6-0.9mg/kg, content of sedimentation the public in the accounting for 22.22%; 0.2-0.4mg/kg, and wastewater area is strong. 105 7 point locations with accounting for 4.76%; 3 irrigation. cadmium content of point locations with 0.3-0.6mg/kg, cadmium content of accounting for 19.44%; 0.4-0.6mg/kg, 6 point locations with accounting for 14.29%; cadmium content of 2 point locations with ≤0.3mg/kg, accounting cadmium content of ＞ for 16.67%. 3 point 0.6mg/kg, accounting locations of cadmium for 9.52%. 2 point and arsenic compound locations of cadmium pollution and arsenic compound pollution Three Wastes A total of 5 point High attention is discharged by locations were set up, paid by the the enterprises including 2 point government at involving heavy locations with cadmium the town and Cd metal pollution content of 0.3- township level 3 Le’an Town 19,190 2,400 12.51% 18,003 9.81% 2 pollution No data yet pollute the 0.6mg/kg, accounting and the risk farmlands by for 40%; 3 point participation atmospheric locations with cadmium willingness of sedimentation content of ≤ 0.3mg/kg, the public in the and wastewater accounting for 60%. area is strong. irrigation. A total of 8 point Average locations were set up, Three Wastes attention is paid including 2 point discharged by by the locations with cadmium the enterprises government at content of 0.3- involving heavy the town and 0.6mg/kg, accounting Cd & Hg metal pollution Meicheng township level 4 18,620 2,316 12.44% 17,367 9.47% 4 for 25%; 6 point pollution No data yet pollute the Town and the locations with cadmium risk farmlands by participation content of ≤ 0.3mg/kg, atmospheric willingness of accounting for 75%. 2 sedimentation the public in the point locations with Hg and wastewater area is not exceeding the standard irrigation. strong. value. A total of 8 point Three Wastes Average locations were set up, Cd discharged by attention is paid 5 Xianxi Town 28,140 1,355 4.82% 10,161 5.54% 8 including 1 point pollution No data yet the enterprises by the location with cadmium risk involving heavy government at content of 0.6-0.9mg/kg, metal pollution the town and 106 accounting for 12.5%; 4 pollute the township level point locations with farmlands by and the cadmium content of atmospheric participation 0.3-0.6mg/kg, sedimentation willingness of accounting for 50%; 3 and wastewater the public in the point locations with irrigation. area is not cadmium content of ≤ strong. 0.3mg/kg, accounting for 37.5%. A total of 25 point locations were set up, A total of 20 point including 19 point locations were set up in locations with cadmium the town, including 1 content of ≥0.9mg/kg, point location with accounting for 76%; 4 cadmium content of point locations with <0.2mg/kg, accounting Three Wastes High attention is cadmium content of for 5%; 1 point location discharged by paid by the 0.6-0.9mg/kg, with cadmium content the enterprises governments at accounting for 16%; 2 of 0.2-0.4mg/kg, involving heavy Cd, As & the town and point locations with accounting for 5%; 1 metal pollution Changtang Hg township level 6 17,700 1,525 8.62% 11,438 6.23% 6 cadmium content of point location with pollute the √ Town pollution and the 0.3-0.6mg/kg, cadmium content of farmlands by risk participation accounting for 8%; 4 0.4-0.6mg/kg, atmospheric willingness of point locations with accounting for 5%; 17 sedimentation the public in the cadmium and arsenic point locations with and wastewater area is strong. compound pollution, 1 cadmium content of ＞ irrigation. point location with 0.6mg/kg, accounting cadmium and Hg for 85%. 2 point compound pollution and locations of cadmium 1 point location of and arsenic compound cadmium, arsenic and pollution Hg compound pollution. A total of 10 point Three Wastes High attention is locations were set up, discharged by paid by the including 4 point There is the enterprises government at locations with cadmium risk of involving heavy the town and 7 Dafu Town 22,600 2,537 11.23% 19,025 10.37% 1 content of ≥0.9mg/kg, cadmium No data yet metal pollution township level accounting for 40%; 1 & arsenic pollute the and the point location with pollution. farmlands by participation cadmium content of atmospheric willingness of 0.6-0.9mg/kg, sedimentation the public in the 107 accounting for 10%; 1 and wastewater area is strong. point location with irrigation. cadmium content of 0.3-0.6mg/kg, accounting for 10%; 3 point locations with cadmium content of ≤0.3mg/kg, accounting for 30%. 1 point location of cadmium and arsenic compound pollution Three Wastes A total of 5 point High attention is discharged by locations were set up, paid by the the enterprises including 3 point governments at involving heavy locations with cadmium the town and Cd metal pollution content of 0.6-0.9mg/kg, township level 8 Taoxi Town 15,420 624 4.05% 4,683 2.55% 16 pollution No data yet pollute the accounting for 60%; 2 and the risk farmlands by point locations with participation atmospheric cadmium content of willingness of sedimentation 0.3-0.6mg/kg, the public in the and wastewater accounting for 40%. area is strong. irrigation. Average Three Wastes A total of 5 point attention is paid discharged by locations were set up, by the the enterprises including 1 point government at involving heavy location with cadmium the town and Cd metal pollution Xiaoyan content of≥ 0.9mg/kg, township level 9 17,705 753 4.25% 5,650 3.08% 13 pollution No data yet pollute the Town accounting for 20%; 4 and the risk farmlands by point locations with participation atmospheric cadmium content of ≤ willingness of sedimentation 0.3mg/kg, accounting the public in the and wastewater for 80%. area is not irrigation. strong. A total of 25 point A total of 20 point Three Wastes High attention is locations were set up, locations were set up in discharged by paid by the Cd Jiangnan including 8 point the town, including 6 the enterprises Has been governments at 10 13,140 1,285 9.78% 9,636 5.25% 9 pollution √ Town locations with cadmium point locations with involving heavy treated the town and risk content of ≥0.9mg/kg, cadmium content of metal pollution township level accounting for 32%; 3 <0.2mg/kg, accounting pollute the and the 108 point locations with for 30%; 1 point farmlands by participation cadmium content of location with cadmium atmospheric willingness of 0.6-0.9mg/kg, content of sedimentation the public in the accounting for 12%; 11 0.2-0.4mg/kg, and wastewater area is strong. point locations with accounting for 5%; 5 irrigation. cadmium content of point locations with 0.3-0.6mg/kg, cadmium content of accounting for 44%; 3 0.4-0.6mg/kg, point locations with accounting for 25%; 8 cadmium content of point locations with ≤0.3mg/kg, accounting cadmium content of ＞ for 12%. 0.6mg/kg, accounting for 40%. 8 point locations of cadmium and arsenic compound pollution Three Wastes A total of 5 point High attention is discharged by locations were set up, paid by the the enterprises including 2 point governments at involving heavy locations with cadmium the town and Cd metal pollution Tianzhuang content of 0.3- township level 11 20,770 734 3.53% 5,505 3.00% 14 pollution No data yet pollute the Township 0.6mg/kg, accounting and the risk farmlands by for 40%; 3 point participation atmospheric locations with cadmium willingness of sedimentation content of ≤ 0.3mg/kg, the public in the and wastewater accounting for 60%. area is strong. irrigation. Average Three Wastes A total of 10 point attention is paid discharged by locations were set up, by the the enterprises including 7 point government at involving heavy locations with cadmium the town and Cd metal pollution Yangjiaotang content of 0.3- township level 12 24,680 1,930 7.82% 14,475 7.89% 5 pollution No data yet pollute the Township 0.6mg/kg, accounting and the risk farmlands by for 70%; 3 point participation atmospheric locations with cadmium willingness of sedimentation content of ≤ 0.3mg/kg, the public in the and wastewater accounting for 30%. area is not irrigation. strong. Lengshi A total of 10 point Cd & Hg Three Wastes High attention is 13 18,304 779 4.26% 5,843 3.19% 12 No data yet Town locations were set up, pollution discharged by paid by the 109 including 8 point risk the enterprises governments at locations with cadmium involving heavy the town and content of 0.3- metal pollution township level 0.6mg/kg, accounting pollute the and the for 80%; 2 point farmlands by participation locations with cadmium atmospheric willingness of content of ≤ 0.3mg/kg, sedimentation the public in the accounting for 20%. 1 and wastewater area is strong. point location of irrigation. cadmium and arsenic compound pollution Three Wastes High attention is discharged by paid by the the enterprises A total of 5 point governments at involving heavy locations were set up, the town and Cd metal pollution Longtang including 5 point township level 14 14,200 656 4.62% 4,920 2.68% 15 pollution No data yet pollute the Township locations with cadmium and the risk farmlands by content of 0.3-0.6mg/kg, participation atmospheric accounting for 100%. willingness of sedimentation the public in the and wastewater area is strong. irrigation. A total of 46 point locations were set up, including 12 point locations with cadmium content of ≥0.9mg/kg, Three Wastes High attention is accounting for 26.09%; discharged by paid by the 8 point locations with the enterprises A total of 21 point governments at cadmium content of There is involving heavy locations were set up, the town and 0.6-0.9mg/kg, risk of metal pollution Dongping including 21 point Has been township level 15 19,750 2,336 11.83% 17,518 9.55% 3 accounting for 17.39%; cadmium pollute the √ Town locations with cadmium treated and the 23 point locations with & arsenic farmlands by content of ＞0.6mg/kg, participation cadmium content of pollution. atmospheric accounting for 100%. willingness of 0.3-0.6mg/kg, sedimentation the public in the accounting for 50%; 3 and wastewater area is strong. point locations with irrigation. cadmium content of ≤0.3mg/kg, accounting for 6.52%. 3 point locations of cadmium 110 and arsenic compound pollution A total of 12 point locations were set up, Three Wastes including 1 point High attention is discharged by location with cadmium paid by the the enterprises content of 0.6-0.9mg/kg, governments at involving heavy accounting for 8.33%; 4 the town and Cd metal pollution point locations with township level 16 Zhexi Town 14,250 167 1.17% 1,250 0.68% 24 pollution No data yet pollute the cadmium content of and the risk farmlands by 0.3-0.6mg/kg, participation atmospheric accounting for 33.33%; willingness of sedimentation 7 point locations with the public in the and wastewater cadmium content of ≤ area is strong. irrigation. 0.3mg/kg, accounting for 58.33%. A total of 14 point locations were set up, A total of 86 point including 3 point locations were set up in locations with cadmium the town, including 43 High attention is content of ≥0.9mg/kg, point locations with paid by the accounting for 21.43%; cadmium content of Three Wastes government at 1 point location with <0.2mg/kg, accounting discharged by the town and cadmium content of for 50%; 13 point the enterprises township level 0.6-0.9mg/kg, There is locations with cadmium involving heavy and the accounting for 7.14%; 6 risk of content of metal pollution participation 17 Malu Town 28,492 912 3.20% 6,838 3.73% 10 point locations with cadmium 0.2-0.4mg/kg, pollute the willingness of cadmium content of & arsenic accounting for 15.12%; farmlands by the public in the 0.3-0.6mg/kg, pollution. 6 point locations with atmospheric area is strong. accounting for 42.86%; cadmium content of sedimentation VIP pilot 4 point locations with 0.4-0.6mg/kg, and wastewater treatment has cadmium content of accounting for 6.98%; irrigation. been carried out ≤0.3mg/kg, accounting 24 point locations with for heavy metal for 28.57%. 1 point cadmium content of ＞ pollution. locations of cadmium 0.6mg/kg, accounting and arsenic compound for 27.90%. pollution A total of 57 point Cd, As & A total of 46 point Three Wastes High attention is locations were set up, Hg locations were set up in discharged by Has been paid by the 18 Kuixi Town 24,224 820 3.39% 6,150 3.35% 11 √ including 16 point pollution the town, including 1 the enterprises treated governments at locations with cadmium risk point location with involving heavy the town and 111 content of ≥0.9mg/kg, cadmium content of metal pollution township level accounting for 28.07%; <0.2mg/kg, accounting pollute the and the 19 point locations with for 2.17%; 9 point farmlands by participation cadmium content of locations with cadmium atmospheric willingness of 0.6-0.9mg/kg, content of sedimentation the public in the accounting for 33.33%; 0.2-0.4mg/kg, and wastewater area is strong. 19 point locations with accounting for 19.57%; irrigation. cadmium content of 5 point locations with 0.3-0.6mg/kg, cadmium content of accounting for 33.33%; 0.4-0.6mg/kg, 3 point locations with accounting for 10.87%; cadmium content of 31 point locations with ≤0.3mg/kg, accounting cadmium content of ＞ for 5.26%. 8 point 0.6mg/kg, accounting locations with cadmium for 67.39%. 3 point and arsenic compound locations with cadmium pollution and 2 point and arsenic compound locations of cadmium pollution, 3 point and Hg compound locations with cadmium pollution. and Hg compound pollution and 2 point locations with cadmium, arsenic and Hg compound pollution. Three Wastes A total 10 point High attention is discharged by locations were set up, paid by the the enterprises including 1 point governments at involving heavy location with cadmium the town and Cd metal pollution content of≥ 0.9mg/kg, township level 19 Yanxi Town 19,600 432 2.20% 3,242 1.77% 18 pollution No data yet pollute the accounting for 10%; 9 and the risk farmlands by point locations with participation atmospheric cadmium content of ≤ willingness of sedimentation 0.3mg/kg, accounting the public in the and wastewater for 90%. area is strong. irrigation. A total of 5 point Three Wastes High attention is locations were set up, discharged by paid by the Cd Qujiang including 1 point the enterprises governments at 20 8,623 174 2.02% 1,305 0.71% 23 pollution No data yet Town locations with cadmium involving heavy the town and risk content of 0.3- metal pollution township level 0.6mg/kg, accounting pollute the and the 112 for 20%; 3 point farmlands by participation locations with cadmium atmospheric willingness of content of ≤ 0.3mg/kg, sedimentation the public in the accounting for 80%. and wastewater area is strong. irrigation. High attention is paid by the A total of 5 point governments at locations were set up, the town and Pingkou including 5 point township level 21 10,340 332 3.21% 2,488 1.36% 20 No risk No data yet Town locations with cadmium and the content of≤ 0.3mg/kg, participation accounting for 100%. willingness of the public in the area is strong. Three Wastes A total of 5 point High attention is discharged by locations were set up, paid by the the enterprises including 3 point governments at involving heavy locations with cadmium the town and Cd metal pollution Nanjin content of 0.3- township level 22 19,484 253 1.30% 1,894 1.03% 22 pollution No data yet pollute the Township 0.6mg/kg, accounting and the risk farmlands by for 60%; 2 point participation atmospheric locations with cadmium willingness of sedimentation content of ≤ 0.3mg/kg, the public in the and wastewater accounting for 40%. area is strong. irrigation. Three Wastes A total of 5 point High attention is discharged by locations were set up, paid by the the enterprises including 2 point governments at involving heavy locations with cadmium the town and Cd metal pollution Gulou content of 0.3- township level 23 17,183 322 1.87% 2,415 1.32% 21 pollution No data yet pollute the Township 0.6mg/kg, accounting and the risk farmlands by for 40%; 3 point participation atmospheric locations with cadmium willingness of sedimentation content of ≤ 0.3mg/kg, the public in the and wastewater accounting for 60%. area is strong. irrigation. Total 425,565 24,462 183,451 In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township go vernment to participate. Through the evaluation and selection, Le’an Town, Dafu Town and Qingtang Town 113 are selected as the project towns. 114 Table 7-7 Selection Sheet of Project Towns in Hengyang County Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River Private mining of alum and gold at the upper Zhengshui River before 2010 Illegal High attention together with enterprises in is paid by the small-size the reach of the government at workshops along Zhengshui the town level, the Zhengshui River River have now with VIP pilot discharged liquid been shut down treatment Cd and solid wastes and the present carried out for Xidu Town 15,273.86 Yes/Yes 5,315.33 34.80 5,180.85 97.47 pollution 55,932 8.94 polluting the situation heavy metal √ risk Zhengshui River. monitoring data pollution, and Water from the show that the the Zhengshui River water quality of participation was used as the the Zhengshui willingness of source of irrigation River reaches the public in to pollute the the standard. the area is farmlands on the fairly strong. both sides of the River in this town/township. High attention Taiyuan Nonferrous is paid by the Metal Products Co., government at Ltd. of Hengyang the town level Cd County and several It’s all closed and the Jibing Town 6,862.98 No/No 2,177.18 31.72 1,335.92 61.36 pollution 17,215 2.75 small-size ceramic now. participation risk factories discharge willingness of liquid and solid the public in wastes. the area is strong. Average Several small-size attention is Shanqiao Cd ceramic factories in It’s all closed paid by the Town 7,100.67 No/No 1,527.17 21.51 763.59 50 pollution 14,020 2.24 the region discharge now. government at risk liquid and solid the town level wastes. and the 115 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River participation willingness of the public in the area is strong. Average attention is paid by the Unauthorized Some of them government at Cd mining of iron ore have been the town level Jingtou 15,518.44 No/No 3,478.37 22.41 948.55 27.27 pollution 22,234 3.55 and granite in the closed and have and the Town risk past in the region met the participation caused pollution. discharge willingness of standards. the public in the area is strong. Average attention is paid by the government at Cd Unauthorized gold the town level Yanpi Town 8,746.58 No/No 3,025.94 34.60 1,815.56 60 pollution 25,841 4.13 mining in the past It’s partly and the risk in the region caused closed now. participation pollution. willingness of the public in the area is average. Average attention is Some of them paid by the Unauthorized gold have been government at Cd mining in the past closed and have the town level Jinlan Town 16,483.65 No/No 4,082.94 24.77 2,895.21 70.91 pollution 38,034 6.08 in the region caused met the and the risk pollution. discharge participation standards. willingness of the public in the area is average. 116 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River High attention is paid by the Small-size illegal Operations of government at operations of indigenous the town level, indigenous method method with VIP pilot vanadium refining vanadium treatment Cd in the past caused refining have carried out for Hongshi 11,299.46 Yes/Yes 2,924.74 25.88 2,638.99 90.23 pollution 27,303 4.36 liquid and solid now been shut heavy metal √ Town risk waste pollution and down and the pollution, and hence pollution by water quality of the wastewater the Zhengshui participation irrigation from the River reaches willingness of Zhengshui River. the standard. the public in the area is fairly strong. Private mining of alum and gold at the upper Zhengshui River before 2010 together with Illegal small-size enterprises in Average workshops along the reach of the attention is the Zhengshui River Zhengshui paid by the discharged liquid River have now government at Cd and solid wastes been shut down the town level Qulan Town 11,789.71 Yes/Yes 2,835.75 24.05 1,531.31 54 pollution 24,876 3.98 polluting the and the present and the risk Zhengshui River. situation participation Water from the monitoring data willingness of Zhengshui River show that the the public in was used as the water quality of the area is source of irrigation the Zhengshui average. to pollute the River reaches farmlands on the the standard. both sides of the River in this town/township. There is no Clean Average Cd enterprise involving production attention is Jinxi Town 11,243.08 No/No 1,793.1 15.95 757.05 42.22 pollution 13,466 2.15 heavy metal projects in rural paid by the risk pollution in the areas have been government at 117 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River region and implemented. the town level agricultural inputs and the are the source of participation pollution. willingness of the public in the area is average. Average attention is Farmland pollution paid by the relates to the open government at Cd mining of porcelain the town level Jiepai Town 9,894.43 No/No 1,328.64 13.43 569.46 42.86 pollution 11,122 1.78 clay at the local. It’s all closed and the risk Dust due to wind now participation and rain and willingness of leachate pollute the the public in farmland. the area is average. Private mining of alum and gold at the upper Zhengshui River before 2010 together with Illegal small-size enterprises in workshops along the reach of the Average the Zhengshui River Zhengshui attention is discharged liquid River have now paid by the and solid wastes been shut down government at Zhajiang Cd polluting the and the present the town level Town 14,044.12 Yes/Yes 4,856.25 34.58 4,912.86 89.53 pollution 42,266 6.76 Zhengshui River. situation and the risk Water from the monitoring data participation Zhengshui River show that the willingness of was used as the water quality of the public in source of irrigation the Zhengshui the area is to pollute the River reaches average. farmlands on the the standard. both sides of the River in this town/township. All of them have been 118 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River closed or have met the discharge standards. Private mining of alum and gold at the upper Zhengshui River before 2010 together with small-size workshops along Illegal the Zhengshui River enterprises in discharged liquid the reach of the High attention and solid wastes Zhengshui is paid by the polluting the River have now government at Cd Zhengshui River. been shut down the town level Sanhu Town 11,255.88 Yes/Yes 3,210.9 28.53 1,261.88 39.30 pollution 29,607 4.73 Water from the and the present and the risk Zhengshui River situation participation was used as the monitoring data willingness of source of irrigation show that the the public in to pollute the water quality of the area is farmlands on the the Zhengshui strong. both sides of the River reaches River in this the standard. town/township. All of them have been closed or have met the discharge standards. Private mining of Illegal High attention alum and gold at the enterprises in is paid by the upper Zhengshui the reach of the government at River before 2010 Zhengshui the town level, together with River have now with VIP pilot Taiyuan Cd small-size been shut down treatment Town 11,894.59 Yes/Yes 4,836.01 40.66% 3,143.41 65 pollution 40,762 6.51 workshops along and the present carried out for √ risk the Zhengshui River situation heavy metal discharged liquid monitoring data pollution, and and solid wastes show that the the polluting the water quality of participation Zhengshui River. the Zhengshui willingness of 119 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River Water from the River reaches the public in Zhengshui River the standard. the area is was used as the fairly strong. source of irrigation to pollute the farmlands on the both sides of the River in this town/township. All of them have been closed or have met the discharge standards. Average attention is There are several paid by the small iron mines in Some of them government at Cd the town, and the have been the town level Guanshi 9,074.32 No/No 2,622.08 28.90 932.41 35.56 pollution 19,627 3.14 pollution source is closed and have and the Town risk the discharge of met the participation three wastes from discharge willingness of iron mines. standards. the public in the area is average. Average attention is There is no paid by the enterprise involving Clean government at Cd heavy metal production the town level Kuzongqiao 9,973.21 No/No 2,633.7 26.41 1,580.22 60 pollution 23,281 3.72 pollution in the projects in rural and the Town risk region and areas have been participation agricultural inputs implemented. willingness of are the source of the public in pollution. the area is average. There are several Average Xianshan Cd small iron mines in attention is Town 15,661.39 No/No 5,099.49 32.56 4,686.43 91.90 pollution 45,651 7.30 the town, and the Closed now paid by the risk pollution source is government at the discharge of the town level 120 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River three wastes from and the iron mines. participation willingness of the public in the area is average. Average attention is There is no paid by the enterprise involving Clean government at Cd heavy metal production the town level Shishi Town 14,516.32 No/No 3,504.78 24.14 2,453.35 70 pollution 29,729 4.75 pollution in the projects in rural and the risk region and areas have been participation agricultural inputs implemented. willingness of are the source of the public in pollution. the area is average. Average attention is There is no paid by the enterprise involving Clean government at Cd heavy metal production the town level Zhangmu 9,903.29 No/No 1,922.34 19.41 1,537.87 80 pollution 16,568 2.65 pollution in the projects in rural and the Township risk region and areas have been participation agricultural inputs implemented. willingness of are the source of the public in pollution. the area is average. Average There is no attention is enterprise involving paid by the heavy metal Clean government at Goulou Cd pollution in the production the town level Township 12,024.14 No/No 1,588.38 13.21 857.73 54 pollution 11,835 1.89 region and projects in rural and the risk agricultural inputs areas have been participation are the source of implemented. willingness of pollution. the public in the area is average. 121 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River Average attention is There is no paid by the enterprise involving Clean government at Cd heavy metal production the town level Lanlong 5,134.68 No/No 1,729.29 33.68 1,296.97 75 pollution 15,038 2.40 pollution in the projects in rural and the Township risk region and areas have been participation agricultural inputs implemented. willingness of are the source of the public in pollution. the area is average. Private mining of alum and gold at the upper Zhengshui River before 2010 together with small-size workshops along Illegal the Zhengshui River enterprises in Average discharged liquid the reach of the attention is and solid wastes Zhengshui paid by the polluting the River have now government at Cd Zhengshui River. been shut down the town level Da’an 7,905.54 Yes/Yes 2,452.15 31.02 1,554.91 63.41 pollution 21,282 3.40 Water from the and the present and the Township risk Zhengshui River situation participation was used as the monitoring data willingness of source of irrigation show that the the public in to pollute the water quality of the area is farmlands on the the Zhengshui average. both sides of the River reaches River in this the standard. town/township. All of them have been closed or have met the discharge standards. There is no Clean Average Xijiang Cd enterprise involving production attention is Township 8,422.07 No/No 2,485.51 29.51 1,188.07 47.80 pollution 17,650 2.82 heavy metal projects in rural paid by the risk pollution in the areas have been government at 122 Area of the Location Indicator of polluted Indicator of farmland area Grain Indicator territory (whether it farmland range is located Whether Attention paid along the the by local Zhengshui farmland Proportion Pollution source Selected Proportion Main pollution source government and Town Name River) / Area of is at risk Rice of rice management project Area of area of and pollution path public (hectares) whether it polluted Proportion and the output output in status towns (hectares) the participation is irrigated farmland type of (ton) the whole territory willingness by the risk county (%) Zhengshui River region and the town level implemented. agricultural inputs and the are the source of participation pollution. willingness of the public in the area is average. Average attention is There is no paid by the enterprise involving Clean government at Risk of heavy metal production the town level Chang’an 3,894.51 Yes/No 1,505.74 38.66 1,204.59 80 Cd 12,352 1.97 pollution in the projects in rural and the Township pollution vicinity, and areas have been participation agricultural inputs implemented. willingness of are the source of the public in pollution. the area is average. Average attention is Farmland pollution paid by the relates to the open government at Cd mining of porcelain the town level Banshi 2,749 No/No 1,097.88 39.94 953.4 86.84 pollution 10,871 1.74 clay at the local. Closed now and the Township risk Dust due to wind participation and rain and willingness of leachate pollute the the public in farmland. the area is average. In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through the evaluation and selection, Sanhu Town and Xidu Town in Hengyang are selected as the newly-added project towns. Table 7-8 Selection Sheet of Project Towns in Hengnan County Area of Indicator of farmland Whether Pollution sources and pollution Pollution source Attention paid Selected Town Name Grain Indicator Heavy metal content of soil the area the paths management status by local project 123 territory Proportion farmland government and towns (ha) of area of is at risk public Area Output Proportion the and the participation (hectares) (ton) (%) territory type of willingness (%) risk A total of 22 point locations were set up, including 3 point locations with cadmium content of ≦0.3, accounting for 13.64%; 9 point locations with cadmium content of 0.3-0.6mg/kg, accounting High attention is for 40.9%; 7 point locations paid by the with cadmium content of governments at There is 0.6-0.9mg/kg, accounting the town and risk of The farmland is mainly polluted by for 31.82%; 3 point There is no relevant township level Yunji Town 10,180 2,491.3 24.47% 21,868 3.46% cadmium liquid and solid wastes generated by locations with cadmium management measures and the & arsenic smelters and dust discharge content of ≥0.9mg/kg, participation pollution. accounting for 13.64%. 7 willingness of the point locations with arsenic public in the area content of ≦15mg/kg, is strong. accounting for 31.82%; 8 point locations with arsenic content of 15-20mg/kg, accounting for 36.36%; 7 point locations with arsenic content of ≥20mg/kg, accounting for 31.82%. A total of 30 point locations were set up, including 0 High attention is point location with cadmium Severe pollution in the demonstration paid by the content of ≦0.3, accounting area was caused by Three Wastes governments at for 0%; 14 point locations directly discharged from the Those factories and pig the town and with cadmium content of Cd Xiangyang once-existing plants in the upper farms have all been township level 12,840 2,400.9 18.70% 33,253 5.26% 0.3-0.6mg/kg, accounting pollution √ Town reach including the electrical closed or moved out in and the for 46.67%; 13 point risk machinery plant, the nitrogen recent years. participation locations with cadmium fertilizer plant, the bearing plant and willingness of the content of 0.6-0.9mg/kg, the pig farm. public in the area accounting for 43.33%; 3 is strong. point locations with cadmium content of 124 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk ≥0.9mg/kg, accounting for 10%. A total of 20 point locations were set up, including 0 point location with cadmium High attention is content of ≦0.3, accounting paid by the for 0%; 6 point locations The irrigation water was polluted by governments at with cadmium content of indiscriminate discharge of “three the town and Cd Liaotian 0.3-0.6mg/kg, accounting wastes” by enterprises beside the There is no relevant township level 11,600 2,271.9 19.59% 25,298 4.00% pollution Town for 30%; 9 point locations Xiangjiang River; excessive input of management measure. and the risk with cadmium content of agricultural fertilizer pollutes participation 0.6-0.9mg/kg, accounting farmland. willingness of the for 45%; 5 point locations public in the area with cadmium content of is strong. ≥0.9mg/kg, accounting for 25%. A total of 33 point locations were set up, including 3 point locations with cadmium content of ≦0.3, accounting for 9.1%; 19 High attention is point locations with Pig farms have been paid by the cadmium content of renovated. Leishui governments at 0.3-0.6mg/kg, accounting There is Pollution sources are mainly upstream River is no longer used the town and for 57.58%; 5 point risk of industrial and mining enterprises for irrigation. Therefore, township level Chashi Town 7,010 2,386.5 34.04% 19,314 3.06% locations with cadmium cadmium pollution brought by irrigation water √ the pollution sources are and the content of 0.6-0.9mg/kg, & arsenic source Leishui River and two local basically controlled and participation accounting for 15.15%; 6 pollution. pig farms. no new pollution will be willingness of the point locations with caused. public in the area cadmium content of is strong. ≥0.9mg/kg, accounting for 18.18%. 9 point locations with arsenic content of ≦15mg/kg, accounting for 27.27%; 9 point locations 125 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk with arsenic content of 15-20mg/kg, accounting for 27.27%; 15 point locations with arsenic content of ≥20mg/kg, accounting for 45.46%. A total of 29 point locations were set up, including 7 point locations with High attention is cadmium content of ≦0.3, paid by the accounting for 24.13%; 19 The source of pollution is unclear yet. governments at point locations with It might be the excessive heavy metal the town and cadmium content of Cd Guanshi content in the fish feed that causes the There is no relevant township level 8,400 3,385.2 40.30% 34,400 5.44% 0.3-0.6mg/kg, accounting pollution Town pollution of irrigation water or management measure. and the for 65.52%; 1 point location risk perhaps the excessive use of participation with cadmium content of agricultural fertilizers. willingness of the 0.6-0.9mg/kg, accounting public in the area for 3.45%; 2 point locations is strong. with cadmium content of ≥0.9mg/kg, accounting for 6.9%. A total of 23 point locations By 2015, all quarries were set up, including 7 have been shut down, point locations with Pollution in the Demonstration Area High attention is and now there is almost cadmium content of ≦0.3, and the vicinity was carried over from paid by the no residue left and new accounting for 30.43%; 12 the past due to three basalt quarries in governments at pollution will be caused point locations with the Fangyuan Pit that discharged the town and Cd in the Demonstration Jiangkou cadmium content of liquid and solid wastes. Major township level 10,000 3,178.4 31.78% 32,930 5.21% pollution Area. Mud, pollutants √ Town 0.3-0.6mg/kg, accounting flooding consecutively in 2006 and and the risk and introduced for 52.17%; 2 point 2007 caused the Leishui River to flow participation organisms caused by locations with cadmium backward, resulting in a great deal of willingness of the major flooding have content of 0.6-0.9mg/kg, mud and pollutants that contaminated public in the area been almost cleared accounting for 8.7%; 2 point the plowing layer. is strong. away and will not cause locations with cadmium any new pollution. content of ≥0.9mg/kg, 126 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk accounting for 8.7%. A total of 32 point locations were set up, including 20 point locations with cadmium content of ≦0.3, accounting for 62.5%; 12 point locations with cadmium content of 0.3-0.6mg/kg, accounting High attention is for 37.5%; 0 point location paid by the with cadmium content of The source of pollution is unclear yet. governments at There is 0.6-0.9mg/kg, accounting It might be the irrational discharge of the town and risk of for 0%; 0 point location with domestic sewage that causes the There is no relevant township level Baogai Town 17,650 3,593.5 20.36% 32,100 5.08% cadmium cadmium content of pollution of irrigation water or management measure. and the & arsenic ≥0.9mg/kg, accounting for perhaps the excessive use of participation pollution. 0%. 2 point locations with agricultural fertilizers. willingness of the arsenic content of public in the area ≦15mg/kg, accounting for is strong. 6.25%; 2 point locations with arsenic content of 15-20mg/kg, accounting for 6.25%; 28 point locations with arsenic content of ≥20mg/kg, accounting for 87.5%. Huaqiao A total of 19 point locations The iron ore High attention is Town, were set up, including 10 There were two iron ore and tungsten metallurgical plant and paid by the Jiangkou point locations with There is ore smelters in the in the 1940s. tungsten ore governments at Town, Chashi cadmium content of ≦0.3, risk of Pollution in the Demonstration Area metallurgical plant were the town and Town, 14,500 2,582.3 17.81% 30,982 4.90% accounting for 52.64%; 7 cadmium and the vicinity was carried over from shut down as early as 50 township level √ Xiangyang point locations with & arsenic the past due to the liquid and solid years ago and now there and the Town, Qishan cadmium content of pollution. wastes from it containing iron, is almost neither residue participation Sub-district 0.3-0.6mg/kg, accounting tungsten, lead, etc. left nor any new willingness of the Office for 36.84%; 1 point location pollution to be caused in public in the area 127 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk with cadmium content of the Demonstration Area. is strong. 0.6-0.9mg/kg, accounting for 5.26%; 1 point location with cadmium content of ≥0.9mg/kg, accounting for 5.26%. 1 point location with arsenic content of ≤15mg/kg, accounting for 5.26%; 2 point locations with arsenic content of 15-20mg/kg, accounting for 10.53%; 16 point locations with arsenic content of ≥20mg/kg, accounting for 84.21%. A total of 12 point locations were set up, including 1 point location with cadmium content of ≦0.3, accounting for 8.33%; 10 point locations with cadmium High attention is content of 0.3-0.6mg/kg, paid by the accounting for 83.33%; 1 government at There is point location with cadmium Pollution mainly sources from the the town and risk of Tiesitang content of 0.6-0.9mg/kg, local fluorite mine. Farmlands are The mine was closed in township level 7,340 1,632.8 22.25% 20,160 3.19% cadmium Town accounting for 8.33%; 0 polluted by excessive use of 2010 but the & arsenic point location with cadmium agricultural fertilizers. participation pollution. content of ≥0.9mg/kg, willingness of the accounting for 0%. 1 point public in the area location with arsenic content is average. of ≤15mg/kg, accounting for 8.33%; 3 point locations with arsenic content of 15-20mg/kg, accounting for 25%; 8 point locations with 128 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk arsenic content of ≥20mg/kg, accounting for 66.67%. A total of 15 point locations were set up, including 0 point locations with cadmium content of ≦0.3, accounting for 0%; 11 point locations with cadmium content of 0.3-0.6mg/kg, accounting for 73.34%; 2 High attention is point locations with paid by the Major flooding consecutively in 2006 cadmium content of governments at There is and 2007 caused the Leishui River to 0.6-0.9mg/kg, accounting the town and risk of flow backward, resulting in a great for 13.33%; 2 point There is no relevant township level Quanxi Town 5,500 1,779.1 32.35% 14,980 2.37% cadmium deal of mud and pollutants that locations with cadmium management measure. and the & arsenic contaminated the irrigation water. content of ≥0.9mg/kg, participation pollution. Farmlands are polluted by excessive accounting for 13.33%. 0 willingness of the use of agricultural fertilizers. point location with arsenic public in the area content of ≤15mg/kg, is strong. accounting for 0%; 0 point location with arsenic content of 15-20mg/kg, accounting for 0%; 5 point locations with arsenic content of ≥20mg/kg, accounting for 100%. A total of 23 point locations High attention is Major flooding consecutively in 2006 were set up, including 5 paid by the There is and 2007 caused the Leishui River to point locations with governments at risk of flow backward, resulting in a great Hongshan cadmium content of ≦0.3, There is no relevant the town and 11,163 3,086.4 27.65% 39,911 6.31% cadmium deal of mud and pollutants that Town accounting for 21.73%; 16 management measure. township level & arsenic contaminated the irrigation water. point locations with and the pollution. Farmlands are polluted by excessive cadmium content of participation use of agricultural fertilizers. 0.3-0.6mg/kg, accounting willingness of the 129 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk for 69.57%; 1 point location public in the area with cadmium content of is strong. 0.6-0.9mg/kg, accounting for 4.35%; 1 point location with cadmium content of ≥0.9mg/kg, accounting for 4.35%. 14 point locations with arsenic content of ≤15mg/kg, accounting for 60.87%; 7 point locations with arsenic content of 15-20mg/kg, accounting for 30.43%; 2 point locations with arsenic content of ≥20mg/kg, accounting for 8.7%. A total of 27 point locations were set up, including 2 point locations with cadmium content of ≦0.3, High attention is accounting for 7.41%; 14 paid by the point locations with Farmlands are polluted by waste government at cadmium content of water, residue and dust discharged the town and Cd The cement plant and 0.3-0.6mg/kg, accounting from the cement plant and the township level Santang Town 6,780 2,168.1 31.98% 23,240 3.68% pollution metallurgical plant were for 51.85%; 8 point metallurgical plant in the vicinity. but the risk closed in 2012. locations with cadmium Domestic sewage enters into the participation content of 0.6-0.9mg/kg, irrigation water to cause pollution. willingness of the accounting for 29.63%; 3 public in the area point locations with is average. cadmium content of ≥0.9mg/kg, accounting for 11.11%. A total of 34 point locations Cd The source of irrigation water is The mine was shut High attention is Tanzishan 11,058 2,998.1 27.11% 28,152 4.45% were set up, including 0 pollution polluted by Three Wastes from barite down in 2008 but the paid by the Town point location with cadmium risk ore. Metal-containing liquid from the residue has not been government at 130 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk content of ≦0.3, accounting piled slags flows into the farmlands cleaned up yet. the town and for 0%; 26 point locations with rain water to cause pollution. township level with cadmium content of Farmlands are polluted by excessive but the 0.3-0.6mg/kg, accounting use of agricultural fertilizers. participation for 76.47%; 7 point willingness of the locations with cadmium public in the area content of 0.6-0.9mg/kg, is average. accounting for 20.59%; 1 point location with cadmium content of ≥0.9mg/kg, accounting for 2.94%. A total of 19 point locations were set up, including 1 point location with cadmium High attention is content of ≦0.3, accounting paid by the for 5.26%; 6 point locations The source of pollution is unclear yet. governments at with cadmium content of It might be the irrational discharge of the town and 0.3-0.6mg/kg, accounting Cd domestic sewage that causes the There is no relevant township level Jilong Town 10,800 2,092.7 19.38% 14,720 2.33% for 31.58%; 6 point pollution pollution of irrigation water or management measure. and the locations with cadmium risk perhaps the excessive use of participation content of 0.6-0.9mg/kg, agricultural fertilizers. willingness of the accounting for 31.58%; 6 public in the area point locations with is strong. cadmium content of ≥0.9mg/kg, accounting for 31.58%. A total of 28 point locations High attention is were set up, including 2 There was once an arsenic The arsenic paid by the point locations with metallurgical plant discharging waste metallurgical plant was governments at cadmium content of ≦0.3, Cd water and residue, which caused shut down in 2007. the town and Quanhu Town 9,045 2,404.2 26.58% 26,965 4.27% accounting for 7.14%; 20 pollution arsenic pollution in the vicinity. Control and prevention township level √ point locations with risk Farmlands were polluted to a certain of agricultural non-point and the cadmium content of extent by excessive use of agricultural source pollution has participation 0.3-0.6mg/kg, accounting fertilizers. been enhanced. willingness of the for 71.43%; 4 point public in the area 131 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk locations with cadmium is strong. content of 0.6-0.9mg/kg, accounting for 14.29%; 2 point locations with cadmium content of ≥0.9mg/kg, accounting for 7.14%. A total of 15 point locations were set up, including 0 point location with cadmium High attention is content of ≦0.3, accounting paid by the for 0%; 12 point locations The source of pollution is unclear yet. governments at with cadmium content of It might be the excessive heavy metal the town and Cd 0.3-0.6mg/kg, accounting content in the fish feed that causes the There is no relevant township level Zhashi Town 7,960 1,780.8 22.37% 20,201 3.20% pollution for 80%; 2 point locations pollution of irrigation water or management measure. and the risk with cadmium content of perhaps the excessive use of participation 0.6-0.9mg/kg, accounting agricultural fertilizers. willingness of the for 13.33%; 1 point location public in the area with cadmium content of is strong. ≥0.9mg/kg, accounting for 6.67%. A total of 8 point locations were set up, including 0 point location with cadmium High attention is content of ≦0.3, accounting paid by the for 0%; 6 point locations The source of pollution is unclear yet. governments at with cadmium content of It might be the excessive heavy metal the town and Cd 0.3-0.6mg/kg, accounting content in the fish feed that causes the There is no relevant township level Maoshi Town 15,600 3,175.1 20.35% 28,603 4.53% pollution for 75%; 2 point locations pollution of irrigation water or management measure. and the risk with cadmium content of perhaps the excessive use of participation 0.6-0.9mg/kg, accounting agricultural fertilizers. willingness of the for 25%; 0 point location public in the area with cadmium content of is strong. ≥0.9mg/kg, accounting for 0%. 132 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk A total of 50 point locations were set up, including 4 point location with cadmium High attention is content of ≦0.3, accounting paid by the for 8%; 9 point locations governments at Change of the irrigation with cadmium content of The pollution source is mainly from the town and Cd water source has been 0.3-0.6mg/kg, accounting industrial and mining enterprises township level Lijiang Town 13,100 3,682.9 28.11% 34,861 5.52% pollution gradually ongoing √ for 18%; 20 point locations pollution brought by contaminated and the risk without any new with cadmium content of Xiangjiang River. participation pollution to be caused. 0.6-0.9mg/kg, accounting willingness of the for 40%; 17 point locations public in the area with cadmium content of is strong. ≥0.9mg/kg, accounting for 34%. A total of 24 point locations were set up, including 0 point location with cadmium content of ≦0.3, accounting for 0%; 11 point locations with cadmium content of High attention is 0.3-0.6mg/kg, accounting paid by the for 45.83%; 11 point The source of pollution is unclear yet. governments at locations with cadmium There is It might be the excessive heavy metal the town and content of 0.6-0.9mg/kg, risk of content in the fish feed that causes the There is no relevant township level Liushi Town 12,000 3,126.6 26.06% 33,534 5.31% accounting for 45.83%; 2 cadmium pollution of irrigation water or management measure. and the point locations with & arsenic perhaps the excessive use of participation cadmium content of pollution. agricultural fertilizers. willingness of the ≥0.9mg/kg, accounting for public in the area 8.34%. 10 point locations is strong. with arsenic content of ≤15mg/kg, accounting for 41.67%; 9 point locations with arsenic content of 15-20mg/kg, accounting for 37.5%; 5 point locations 133 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk with arsenic content of ≥20mg/kg, accounting for 20.83%. A total of 11 point locations were set up, including 0 point location with cadmium High attention is content of ≦0.3, accounting paid by the for 0%; 1 point location with The Xiangjiang River as the source of governments at cadmium content of irrigation water is polluted by the the town and Cd Jinweizhou 0.3-0.6mg/kg, accounting random discharge of Three Wastes There is no relevant township level 12,000 1,627.9 13.57% 18,000 2.85% pollution Town for 9.1%; 10 point locations from the enterprises nearby. management measure. and the risk with cadmium content of Farmlands are polluted by excessive participation 0.6-0.9mg/kg, accounting use of agricultural fertilizers. willingness of the for 90.9%; 0 point location public in the area with cadmium content of is strong. ≥0.9mg/kg, accounting for 0%. A total of 19 point locations were set up, including 1 point location with cadmium High attention is content of ≦0.3, accounting Residues and waste liquid from the paid by the for 5.26%; 4 point locations piled slags of the metallurgical plant government at with cadmium content of flow into the farmlands with rain the town and 0.3-0.6mg/kg, accounting Cd Chejiang water to cause pollution. The The metallurgical plant township level 11,200 2,241.1 20.01% 29,208.3 4.62% for 21.05%; 8 point pollution Town Xiangjiang River as the source of was shut down in 2010. but the locations with cadmium risk irrigation water is polluted. Farmlands participation content of 0.6-0.9mg/kg, are polluted by excessive use of willingness of the accounting for 42.11%; 6 agricultural fertilizers. public in the area point locations with is average. cadmium content of ≥0.9mg/kg, accounting for 31.58%. A total of 13 point locations There is Waste water and residue containing In 2008, Henglong High attention is Xiantang 5,200 1,508.5 29.01% 1,165 0.18% were set up, including 4 risk of calcium sulfate, etc. discharged from Gypsum Mine Co., Ltd. paid by the √ Town point locations with cadmium Henglong Gypsum Mine Co., Ltd. was closed. When the governments at 134 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk cadmium content of ≦0.3, & arsenic produces dust and leachate by wind enterprise was closed, the town and accounting for 30.77%; 7 pollution. and rain to pollute the farmlands. the plant equipment and township level point locations with slag field had been and the cadmium content of cleaned up. There was participation 0.3-0.6mg/kg, accounting no residue left on the willingness of the for 53.85%; 1 point location site, which basically did public in the area with cadmium content of not cause new heavy is strong. 0.6-0.9mg/kg, accounting metal pollution to the for 7.69%; 0 point location surrounding agricultural with cadmium content of land. ≥0.9mg/kg, accounting for 0%. 1 point location with arsenic content of ≤15mg/kg, accounting for 7.69%; 1 point location with arsenic content of 15-20mg/kg, accounting for 7.69%; 11 point locations with arsenic content of ≥20mg/kg, accounting for 84.62%. A total of 19 point locations were set up, including 1 point location with cadmium High attention is content of ≦0.3, accounting paid by the Major flooding consecutively in 2006 for 5.27%; 10 point governments at There is and 2007 caused the Leishui River to locations with cadmium the town and risk of flow backward, resulting in a great Xiangshi content of 0.3-0.6mg/kg, There is no relevant township level 7,680 2,562.4 33.36% 23,925 3.79% cadmium deal of mud and pollutants that Township accounting for 52.63%; 2 management measure. and the & arsenic contaminated the farmland. Farmlands point locations with participation pollution. are polluted by excessive use of cadmium content of willingness of the agricultural fertilizers. 0.6-0.9mg/kg, accounting public in the area for 10.53%; 6 point is strong. locations with cadmium content of ≥0.9mg/kg, 135 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk accounting for 31.57%. 5 point locations with arsenic content of ≤15mg/kg, accounting for 26.32%; 4 point locations with arsenic content of 15-20mg/kg, accounting for 21.05%; 10 point locations with arsenic content of ≥20mg/kg, accounting for 52.63%. A total of 4 point locations were set up, including 0 point location with cadmium High attention is content of ≦0.3, accounting paid by the for 0%; 2 point locations The source of irrigation water was government at with cadmium content of polluted by the coal mine, the the town and Cd Coal ore was closed in Zhoushi 0.3-0.6mg/kg, accounting metallurgical plant and the excessive township level 9,900 2,933.5 29.63% 32,005 5.06% pollution 1998 and smelting plant Township for 50%; 2 point locations heavy metal content in the fish feed. but the risk was closed in 2012. with cadmium content of Farmlands were polluted by excessive participation 0.6-0.9mg/kg, accounting use of agricultural fertilizers. willingness of the for 50%; 0 point location public in the area with cadmium content of is average. ≥0.9mg/kg, accounting for 0%. A total of 2 point locations Three Wastes discharged from High attention is were set up, including 0 Hengnan County Longtai paid by the point location with cadmium Metallurgical Plant, Hengnan County governments at content of ≦0.3, accounting Chunxiang Zinc Industry Co., Ltd., the town and for 0%; 0 point location with Cd Hengnan County Dingli Lead Industry Songjiang Some enterprises were township level 12,900 3,313.6 25.69% 5,218 0.82% cadmium content of pollution Co., Ltd., Hengnan County Honghui Town closed in 2011 and 2016 and the 0.3-0.6mg/kg, accounting risk Zinc Products Co., Ltd., Hengnan participation for 0%; 0 point location with County Zhushun Chemical Industry willingness of the cadmium content of Co., Ltd., Hengyang City Longfeng public in the area 0.6-0.9mg/kg, accounting Metallurgy Co., Ltd.; slag piles and is strong. for 0%; 2 point locations tailing dams produce dust and 136 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk with cadmium content of leachate by wind and rain to pollute ≥0.9mg/kg, accounting for the farmlands. 100%. A total of 3 point locations were set up, including 0 point location with cadmium content of ≦0.3, accounting for 0%; 1 point location with cadmium content of 0.3-0.6mg/kg, accounting High attention is for 33.33%; 2 point The source of irrigation water is paid by the locations with cadmium polluted by Three Wastes from the governments at content of 0.6-0.9mg/kg, There is tungsten mine. the town and accounting for 66.67%; 0 risk of Heavy-metal-containing liquid from Chuankou The tungsten ore was township level 14,000 650.5 4.65% 6,319.5 1.00% point location with cadmium cadmium the piled slags flows into the Office closed in 2011 and the content of ≥0.9mg/kg, & arsenic farmlands with rain water to cause participation accounting for 0%. 1 point pollution. pollution. Farmlands are polluted by willingness of the location with arsenic content excessive use of agricultural public in the area of ≤15mg/kg, accounting for fertilizers. is strong. 33.33%; 0 point location with arsenic content of 15-20mg/kg, accounting for 0%; 2 point locations with arsenic content of ≥20mg/kg, accounting for 66.67%. A total of 11 point locations Local government has High attention is The pollution source may be the high were set up, including 0 vigorously strengthened paid by the background value of heavy metals in point location with cadmium prevention and control governments at the soil caused by the soil parent Qishan content of ≦0.3, accounting Cd of agricultural non-point the town and material. In addition, the unreasonable Sub-district 6,870 112.8 1.64% 718.3 0.11% for 0%; 3 point locations pollution source pollution. township level √ application of cadmium-containing Office with cadmium content of risk Low-toxic and and the phosphate fertilizer for many years 0.3-0.6mg/kg, accounting less-persistent pesticides participation has enriched the heavy metals in the for 27.27%; 3 point shall be promoted and willingness of the soil, causing the pollution in past. locations with cadmium the green control and public in the area 137 Indicator of farmland Whether Grain Indicator Attention paid area the Area of by local Proportion farmland Selected the Pollution sources and pollution Pollution source government and Town Name of area of Heavy metal content of soil is at risk project territory Area Output Proportion paths management status public the and the towns (ha) (hectares) (ton) (%) participation territory type of willingness (%) risk content of 0.6-0.9mg/kg, prevention and is strong. accounting for 27.27%; 5 integrated prevention point locations with and treatment of crop cadmium content of diseases and pests shall ≥0.9mg/kg, accounting for be carried out. 45.46%. In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through the evaluation and selection, Xiangyang Town and Quanxi Town are selected as the newly-added project towns. 138 Table 7-9 Selection Sheet of Project Towns in Lengshuitan District Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) A total of 171 point locations were set up, A total of 122 including 87 point point locations locations with were set up, The enterprises cadmium content including 102 involving heavy metal of≤ 0.3mg/kg, point locations pollution including accounting for with cadmium Huaqiao Metallurgical 50.88%; 83 point content of Plant, Xiyanghong locations with <0.2mg/kg, Three Wastes from Metallurgical Plant, High attention is cadmium content accounting for the enterprises and Wuxing Antimony paid by the of 0.3-0.6mg/kg, 83.61%; 12 point involving heavy Products Factory were governments at accounting for There is locations with metal pollution banned and closed the town and 48.54%; 1 point risk of cadmium content including Huaqiao before 2012. Residue Huaqiaojie township level 1 1,247 3.84 10 16,017 4.58 10 location with cadmium of 0.2-0.4mg/kg, Metallurgical Plant, left over by Town and the cadmium content & arsenic accounting for Xiyanghong Xiyanghong participation of 0.6-0.9mg/kg, pollution. 9.84%; 5 point Metallurgical Plant, Metallurgical Plant, willingness of the accounting for locations with and Wuxing and Wuxing Antimony public in the area 0.58%; 38 point cadmium content Antimony Products Products Factory after is strong. locations with of 0.4-0.6mg/kg, Factory. they were closed was arsenic content of accounting for completed with ＜15mg/kg, 4.1%; 3 point treatment in 2015, accounting for locations with which passed the 22.22%; 67 point cadmium content provincial-level locations with of ＞0.6mg/kg, acceptance. arsenic content of accounting for 15-20mg/kg, 2.45%. accounting for 39.18%; 66 point 139 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) locations with arsenic content of 20-30mg/kg, accounting for 38.6%. A total of 429 A total of 319 point locations point locations were set up, were set up, including 71 point including 290 locations with point locations cadmium content with cadmium High attention is of ≤ 0.3mg/kg, content of paid by the accounting for <0.2mg/kg, government at the 16.55%; 301 point accounting for Slags in the Puliqiao town and locations with 90.9%; 16 point Manganese Ore Puliqiao Manganese township level, cadmium content There is locations with Cluster are piled up Ore Cluster was with VIP pilot of 0.3-0.6mg/kg, risk of cadmium content in the open air in the banned and closed treatment carried 2 Puliqiao Town 3,229 9.95 2 39,813 11.39 2 accounting cadmium of 0.2-0.4mg/kg, slag yard. Pollution √ before 2008 and the out for heavy for70.16%; 52 & arsenic accounting for from the coal mine coal mine and silica metal pollution, point locations pollution. 5.03%; 3 point and silica mine was mine are closed. and the with cadmium locations with carried over from participation content of cadmium content the past. willingness of the 0.6-0.9mg/kg, of 0.4-0.6mg/kg, public in the area accounting for accounting for is fairly strong. 12.12%; 5 point 0.94%; 10 point locations with locations with cadmium content cadmium content of ≥0.9mg/kg, of ＞0.6mg/kg, accounting for accounting for 1.17%; 111 point 3.13%; 306 point 140 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) locations with locations with arsenic content of arsenic content of ＜15mg/kg, ＜0.2mg/kg, accounting for accounting for 25.87%; 116 point 95.92%; 12 point locations with locations with arsenic content of arsenic content of 15-20mg/kg, 0.2-0.4mg/kg, accounting for accounting for 27.04%; 54 point 3.77%; 1 point locations with location with arsenic content of arsenic content of 20-30mg/kg, 0.4-0.6mg/kg, accounting for accounting for 12.59%; 148point 0.31%. locations with arsenic content of ＞30mg/kg, accounting for 34.5%. A total of 269 A total of 207 Slags in the High attention is point locations point locations Niujiaoba paid by the were set up, were set up, Manganese Ore Niujiaoba Manganese government at the including 30 point including 161 Cluster are piled up Ore Cluster was town and There is locations with point locations in the open air in the banned and closed township level, risk of Niujiaoba cadmium content with cadmium slag yard. Pollution before 2008 and with VIP pilot 3 1,876 5.78 7 24,098 6.89 6 cadmium √ Town of ≤ 0.3mg/kg, content of from Huojian Coal Huojian Coal Mine, treatment carried & arsenic accounting for <0.2mg/kg, Mine, Hongqi Coal Hongqi Coal Mine and out for heavy pollution. 11.15%; 199 point accounting for Mine and Lingling Lingling Coal Mine are metal pollution, locations with 77.78%; 36 point Coal Mine was closed. and the cadmium content locations with carried over from participation of 0.3-0.6mg/kg, cadmium content the past. willingness of the 141 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) accounting for of 0.2-0.4mg/kg, public in the area 73.98%; 36 point accounting for is fairly strong. locations with 17.39%; 2 point cadmium content locations with of 0.6-0.9mg/kg, cadmium content accounting for of 0.4-0.6mg/kg, 13.38%; 4 point accounting for locations with 0.97%; 8 point cadmium content locations with of ≥0.9mg/kg, cadmium content accounting for of ＞0.6mg/kg, 1.49%; 98 point accounting for locations with 3.86%; 206 point arsenic content of locations with ＜15mg/kg, arsenic content of accounting for ＜0.2mg/kg, 36.43%; 95 point accounting for locations with 99.52%; 1 point arsenic content of location with 15-20mg/kg, arsenic content of accounting for 0.2-0.4mg/kg, 35.32%; 34 point accounting for locations with 0.48%. arsenic content of 20-30mg/kg, accounting for 12.64%; 42 point locations with arsenic content of ＞30mg/kg, accounting for 15.61%. 142 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) A total of 174 point locations were set up, including 16 point locations with A total of 129 cadmium content point locations of ≤ 0.3mg/kg, were set up, accounting for including 68 point 9.2%; 62 point locations with Three Wastes from locations with cadmium content the enterprises Enterprises involving cadmium content of <0.2mg/kg, involving heavy heavy metal pollution of 0.3-0.6mg/kg, accounting for High attention is metal pollution including Yongzhou accounting for 52.71%; 17 point paid by the including Yongzhou City Dongxing Mining 35.63%; 53 point locations with governments at There is City Dongxing Industry Co., Ltd., locations with cadmium content the town and risk of Mining Industry Yongzhou City Hongye Gaoxishi cadmium content of 0.2-0.4mg/kg, township level 4 1,955 5.78 6 21,173 6.06 8 cadmium Co., Ltd., Yongzhou Metallurgy Co., Ltd., Town of 0.6-0.9mg/kg, accounting for and the & arsenic City Hongye Tangquan accounting for 13.18%; 14 point participation pollution. Metallurgy Co., Metallurgical Plant, 30.46%; 43 point locations with willingness of the Ltd., Tangquan Xiaofeng Metallurgical locations with cadmium content public in the area Metallurgical Plant, Plant, etc. were banned cadmium content of 0.4-0.6mg/kg, is strong. Xiaofeng and closed before of ≥0.9mg/kg, accounting for Metallurgical Plant, September 2017. accounting for 10.85%; 30 point etc. 24.71%; 50 point locations with locations with cadmium content arsenic content of of ＞0.6mg/kg, ＜15mg/kg, accounting for accounting for 23.26%. 28.74%; 33 point locations with arsenic content of 15-20mg/kg, 143 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) accounting for 18.96%; 50 point locations with arsenic content of 20-30mg/kg, accounting for 28.74%; 41 point locations with arsenic content of ＞30mg/kg, accounting for 23.56%. A total of 243 point locations were set up, including 40 point A total of 178 locations with point locations Huangyangsi cadmium content were set up, Slags in the Manganese Ore Cluster High attention is of ≤ 0.3mg/kg, including 163 Huangyangsi was banned and closed paid by the accounting for point location with Manganese Ore before 2008. Residue governments at There is 16.46%; 171 point cadmium content Cluster are piled up left over by Lantian the town and risk of Huangyangsi locations with < 0.2mg/kg, in the open air in the Chemical Plant after it township level 5 3,080 9.49 3 37,976 10.86 3 cadmium Town cadmium content accounting for slag yard and Three was closed was and the & arsenic of 0.3-0.6mg/kg, 91.58%; 15 point Wastes are completed with participation pollution. accounting for locations with discharged from treatment in 2015, willingness of the 70.37%; 25 point cadmium content Lantian Chemical which passed the public in the area locations with of 0.2-0.4mg/kg, Plant. provincial-level is strong. cadmium content accounting for acceptance. of 0.6-0.9mg/kg, 8.42%. accounting for 10.29%; 7 point locations with 144 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) cadmium content of ≥0.9mg/kg, accounting for 2.88%; 93 point locations with arsenic content of ＜15mg/kg, accounting for 38.27%; 88 point locations with arsenic content of 15-20mg/kg, accounting for 36.21%; 37 point locations with arsenic content of 20-30mg/kg, accounting for 15.23%; 25 point locations with arsenic content of ＞30mg/kg, accounting for 10.29%. 145 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) A total of 567 A total of 420 Li Xiangyang Copper point locations point locations Sulfate Plant and were set up, were set up, Yongzhou City including 79 point including 283 Tianyuan Chemical locations with point locations Three Wastes from Co., Ltd. were banned cadmium content with cadmium the enterprises and closed before of ≤ 0.3mg/kg, content of involving heavy September 2017. accounting for <0.2mg/kg, metal pollution Residue left over by Li 13.93%; 130 point accounting for including Li Xiangyang Copper locations with 67.38%; 87 point Xiangyang Copper Sulfate Plant and High attention is cadmium content locations with Sulfate Plant, Yongzhou City paid by the of 0.3-0.6mg/kg, cadmium content Yongzhou City Tianyuan Chemical government at the accounting for of 0.2-0.4mg/kg, Tianyuan Chemical Co., Ltd. after they town and 75.66%; 36 point accounting for Co., Ltd., Yongzhou were closed was township level, There is locations with 20.71%; 16 point City Xiangsheng completed with with VIP pilot risk of Shanglingqiao cadmium content locations with Metallurgy Co., treatment in 2015, treatment carried 6 6,151 18.96 3 75,842 21.69 1 cadmium √ Town of 0.6-0.9mg/kg, cadmium content Ltd., Jinli which passed the out for heavy & arsenic accounting for of 0.4-0.6mg/kg, Metallurgical Plant, provincial-level metal pollution, pollution. 6.35%; 23 point accounting for Jiepai acceptance. Enterprises and the locations with 3.81%; 34 point Manganese-rich involving heavy metal participation cadmium content locations with Slag Metallurgical pollution including willingness of the of ≥0.9mg/kg, cadmium content Plant, Yongzhou City public in the area accounting for of ＞0.6mg/kg, Wangniansheng Xiangsheng Metallurgy is fairly strong. 4.06%; 206 point accounting for Metallurgical Plant, Co., Ltd., Jinli locations with 8.1%. 403 point Yongfa Ferroalloy Metallurgical Plant, arsenic content of locations with Plant, Liudazhao Jiepai Manganese-rich ＜15mg/kg, arsenic content < Metallurgical Plant, Slag Metallurgical accounting for 0.2mg/kg, etc. Plant, Wangniansheng 36.33%; 88 point accounting for Metallurgical Plant, locations with 95.95%; 13 point Yongfa Ferroalloy arsenic content of locations with Plant, Liudazhao 15-20mg/kg, arsenic content of Metallurgical Plant, 146 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) accounting for 0.2-0.4 mg/kg, etc. were banned and 15.52%; 153 point accounting for closed before locations with 3.1%; 4 point September 2017. arsenic content of locations with 20-30mg/kg, arsenic content of accounting for 0.4-0.6mg/kg, 26.99%; 78 point accounting for locations with 0.95%. There is no arsenic content of Pb, Hg and other ＞30mg/kg, heavy metals. accounting for 13.76%. A total of 281 A total of 281 point locations point locations were set up, were set up, including 99 point including 133 locations with point locations No enterprise cadmium content with cadmium High attention is involving heavy of ≤ 0.3mg/kg, content of paid by the metal pollution accounting for <0.2mg/kg, governments at There is existed in the town. 35.23%; 171 point accounting for the town and risk of Pollution may locations with 47.33%; 61 point There is no relevant township level 7 Yitang Town 2,678 8.25 5 34,400 9.84 4 cadmium source from the cadmium content locations with management measure. and the & arsenic high background of 0.3-0.6mg/kg, cadmium content participation pollution. values of heavy accounting for of 0.2-0.4mg/kg, willingness of the metals in the soil 60.85%; 10 point accounting for public in the area and agricultural locations with 21.71%; 28 point is strong. inputs. cadmium content locations with of 0.6-0.9mg/kg, cadmium content accounting for of 0.4-0.6mg/kg, 3.36%; 1 point accounting for location with 9.97%; 59 point 147 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) cadmium content locations with of ≥0.9mg/kg, cadmium content accounting for of ＞0.6mg/kg, 0.36%; 92 point accounting for locations with 20.99%. There is arsenic content of no As, Pb, Hg and ＜15mg/kg, other heavy accounting for metals. 32.74%; 121 point locations with arsenic content of 15-20mg/kg, accounting for 43.06%; 67 point locations with arsenic content of 20-30mg/kg, accounting for 23.84%; 1 point location with arsenic content of ＞30mg/kg, accounting for 0.36%. A total of 141 A total of 105 Three Wastes from Enterprises involving High attention is point locations point locations the enterprises heavy metal pollution paid by the There is were set up, were set up, involving heavy including Guo Baohua governments at risk of including 22 point including 104 metal pollution Metallurgical Plant, the town and 8 Caishi Town 1,583 4.88 9 19,518 5.58 9 cadmium locations with point locations including Guo Lengshuitan District township level & arsenic cadmium content with cadmium Baohua Yongshun and the pollution. of ≤ 0.3mg/kg, content < Metallurgical Plant, Metallurgical Plant, participation accounting for 0.2mg/kg, Lengshuitan District etc. and Qishantou willingness of the 148 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) 15.6%; 105 point accounting for Yongshun Manganese Ore Mine public in the area locations with 99.05%; 1 point Metallurgical Plant, were banned and is strong. cadmium content location with etc.; slags in the closed in 2008. of 0.3-0.6mg/kg, cadmium content Qishantou accounting for of 0.2-0.4mg/kg, Manganese Ore 74.47%; 12 point accounting for Mine are piled up in locations with 0.95%. There is no the open air in the cadmium content As, Pb, Hg and slag yard. of 0.6-0.9mg/kg, other heavy accounting for metals. 8.51%; 2 point locations with cadmium content of ≥0.9mg/kg, accounting for 1.42%; 44 point locations with arsenic content of ＜15mg/kg, accounting for 31.2%; 56 point locations with arsenic content of 15-20mg/kg, accounting for 39.72%; 30 point locations with arsenic content of 20-30mg/kg, accounting for 21.28%; 11 point locations with 149 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) arsenic content of ＞30mg/kg, accounting for 7.8%. A total of 97 point locations were set up, including 5 point locations A total of 71 point with cadmium locations were set content of ≤ up, including 70 0.3mg/kg, point locations No enterprise accounting for Average attention with cadmium involving heavy 5.16%; 87 point is paid by the content < metal pollution locations with government at the There is 0.2mg/kg, existed in the town. cadmium content town and risk of accounting for Pollution may Yangcundian of 0.3-0.6mg/kg, There is no relevant township level 9 1,032 3.18 11 13,256 3.79 11 cadmium 98.59%; 1 point source from the Township accounting for management measure. and the & arsenic location with high background 89.69%; 4 point participation pollution. cadmium content values of heavy locations with willingness of the of 0.2-0.4mg/kg, metals in the soil cadmium content public in the area accounting for and agricultural of 0.6-0.9mg/kg, is not strong. 1.41%. There is no inputs. accounting for As, Pb, Hg and 4.12%; 1 point other heavy location with metals. cadmium content of ≥0.9mg/kg, accounting for 1.03%; 30 point 150 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) locations with arsenic content of ＜15mg/kg, accounting for 30.93%; 46 point locations with arsenic content of 15-20mg/kg, accounting for 47.42%; 20 point locations with arsenic content of 20-30mg/kg, accounting for 20.62%; 1 point location with arsenic content of ＞30mg/kg, accounting for 1.03%. A total of 268 A total of 196 Three Wastes from Enterprises involving point locations point locations the enterprises Average attention heavy metal pollution were set up, were set up, involving heavy is paid by the including Yongzhou including 43 point including 140 metal pollution government at the There is City Xinhai Metallurgy locations with point locations including Yongzhou town and risk of Co., Ltd., Longtao Quhe cadmium content with cadmium City Xinhai township level 10 2,771 8.54 4 34,166 9.77 5 cadmium Metallurgical Plant, Sub-district of ≤ 0.3mg/kg, content of Metallurgy Co., and the & arsenic Longxiaolin accounting for <0.2mg/kg, Ltd., Longtao participation pollution. Metallurgical Plant, 46.04%; 218 point accounting for Metallurgical Plant, willingness of the etc. were banned and locations with 71.43%; 34 point Longxiaolin public in the area closed before cadmium content locations with Metallurgical Plant, is not strong. September 2017. of 0.3-0.6mg/kg, cadmium content etc. 151 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) accounting for of 0.2-0.4mg/kg, 81.35%; 6 point accounting for locations with 17.35%; 12 point cadmium content locations with of 0.6-0.9mg/kg, cadmium content accounting for of 0.4-0.6mg/kg, 2.24%; 1 point accounting for location with 6.12%; 10 point cadmium content locations with of ≥0.9mg/kg, cadmium content accounting for of ＞0.6mg/kg, 0.37%; 111 point accounting for locations with 5.1%. There is no arsenic content of As, Pb, Hg and ＜15mg/kg, other heavy accounting for metals. 41.42%; 111 point locations with arsenic content of 15-20mg/kg, accounting for 41.42%; 43 point locations with arsenic content of 20-30mg/kg, accounting for 16.04%; 3 point locations with arsenic content of ＞30mg/kg, accounting for 1.12%. 152 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) A total of 223 point locations were set up, including 50 point locations with cadmium content of ≤ 0.3mg/kg, accounting for A total of 160 22.42%; 162 point point locations locations with were set up, cadmium content including 149 of 0.3-0.6mg/kg, point locations High attention is accounting for with cadmium paid by the 72.64%; 8 point content < governments at There is Slags in the Renwan locations with 0.2mg/kg, Renwan Town the town and risk of Town Manganese Yangjiaqiao cadmium content accounting for Manganese Ore Cluster township level 11 1,836 5.66 8 22,638 6.47 7 cadmium Ore Cluster are Sub-district of 0.6-0.9mg/kg, 93.12%; 11 point was banned and closed and the & arsenic piled up in the open accounting for locations with before 2008. participation pollution. air in the slag yard. 3.59%; 3 point cadmium content willingness of the locations with of 0.2-0.4mg/kg, public in the area cadmium content accounting for is strong. of ≥0.9mg/kg, 6.88%. There is no accounting for As, Pb, Hg and 1.35%; 85 point other heavy locations with metals. arsenic content of ＜15mg/kg, accounting for 38.12%; 81 point locations with arsenic content of 15-20mg/kg, 153 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) accounting for 36.32%; 56 point locations with arsenic content of 20-30mg/kg, accounting for 25.11%; 1 point locations with arsenic content of ＞30mg/kg, accounting for 0.45%. A total of 58 point locations were set A total of 42 point up, including 13 locations were set point locations up, including 31 with cadmium point locations content of≤ High attention is with cadmium 0.3mg/kg, paid by the content < accounting for Slags in the Shanhu governments at There is 0.2mg/kg, 22.41%; 43 point Township Shanhu Township the town and risk of accounting for Shanhu locations with Manganese Ore Manganese Ore Cluster township level 12 667 2.06 12 7,223 2.07 12 cadmium 73.81%; 11 point Sub-district cadmium content Cluster are piled up was banned and closed and the & arsenic locations with of 0.3-0.6mg/kg, in the open air in the before 2008. participation pollution. cadmium content accounting for slag yard. willingness of the of 0.2-0.4mg/kg, 74.14%; 2 point public in the area accounting for locations with is strong. 26.19%. There is cadmium content no As, Pb, Hg and of 0.6-0.9mg/kg, other heavy accounting for metals. 3.35%; 20 point locations with 154 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) arsenic content of ＜15mg/kg, accounting for 34.48%; 29 point locations with arsenic content of 15-20mg/kg, accounting for 50%; 9 point locations with arsenic content of 20-30mg/kg, accounting for 15.52%. A total of 34 point A total of 25 point locations were set locations were set up, including 16 up, including 19 point locations point locations with cadmium High attention is with cadmium Small-size content of ≤ paid by the content < metallurgical 0.3mg/kg, governments at Maping There is 0.2mg/kg, enterprises exited in accounting for the town and Agricultural risk of accounting for the town and 22.41%; 18 point There is no relevant township level 13 Economic 288 0.89 13 3,551 1.02 13 cadmium 76%; 6 point township area and locations with management measure. and the Development & arsenic locations with Three Wastes from cadmium content participation Zone pollution. cadmium content these businesses of 0.3-0.6mg/kg, willingness of the of 0.2-0.4mg/kg, were the source of accounting for public in the area accounting for pollution. 74.14%; 29 point is strong. 24%. There is no locations with As, Pb, Hg and arsenic content of other heavy 15-20mg/kg, metals. accounting for 155 Indicator of farmland area Indicator of rice output Proportion Whether In 2016 Ranking Attention paid of Ranking in the of output by local cultivated the Output % farmland Serial Heavy metal Rice heavy metals Pollution sources Pollution source government and Selected Town Name Paddy land area cultivated of the total in the is at risk No. field area total content of soil content and pollution paths management status public project towns in the land area Output in the and the (ha) output in participation whole of the district type of (ton) the willingness district district risk district (%) 3.35%; 9 point locations with arsenic content of 20-30mg/kg, accounting for 15.52%. Total 28,393 349,671 In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through the evaluation and selection, Xianghuaba, Niujiaoba Town and Shixijiang are selected as the project towns. Table 7-10 Selection Sheet of Project Towns in Linwu County Indicator of farmland Attention paid Grain Indicator area by local Selected Serial Town Paddy Proportion Standard-exceeding Standard-exceeding Analysis of Pollution source government and project No. Name field of area of Output rice factors Pollution Source management status public Proportion towns area the (ton) participation (ha) territory willingness Average attention No relevant data and No relevant is paid by the Shunfeng management 1 1,279.06 12.24% 8,433 9.41% No data yet information has government at the Town measures have been been collected yet town and collected yet township level 156 Indicator of farmland Attention paid Grain Indicator area by local Selected Serial Town Paddy Proportion Standard-exceeding Standard-exceeding Analysis of Pollution source government and project No. Name field of area of Output rice factors Pollution Source management status public Proportion towns area the (ton) participation (ha) territory willingness and the participation willingness of the public in the area is not strong. Average attention is paid by the government at the No relevant data and town and No relevant Jinjiang management township level 2 644.83 12.89% 3,358.2 3.75% No data yet information has Town measures have been and the been collected yet collected yet participation willingness of the public in the area is not strong. There was no enterprise in the High attention is town involving in paid by the heavy metal governments at pollution. No relevant data and the town and Wushui Pollution may management township level 3 1,676.87 17.42% 14,736.7 16.44% Yes Cd, As √ Town source from the measures have been and the high background collected yet participation values of heavy willingness of the metals in the soil public in the area and agricultural is strong. inputs. There was no High attention is enterprise in the paid by the town involving in governments at No relevant data and heavy metal the town and Nanqiang management 4 1,705.08 9.79% 13,141.07 14.66% Yes Cd, As pollution. township level √ Town measures have been Pollution may and the collected yet source from the participation high background willingness of the values of heavy public in the area 157 Indicator of farmland Attention paid Grain Indicator area by local Selected Serial Town Paddy Proportion Standard-exceeding Standard-exceeding Analysis of Pollution source government and project No. Name field of area of Output rice factors Pollution Source management status public Proportion towns area the (ton) participation (ha) territory willingness metals in the soil is strong. and agricultural inputs. Iron and manganese ores were closed in Average attention the late 1990s. Slags is paid by the in once-existing iron government at the Exploitation of and manganese town and Fenshi iron ore and mines have been township level 5 1,259.89 11.86% 10,033.23 11.19% Yes Cd, As Town manganese ore in cleaned up and and the 1990s. almost will not participation cause any heavy willingness of the metal pollution to public in the area the farmlands in the is not strong. lower reach. High attention is Manganese mines, paid by the Manganese ores, iron mines, and coal governments at silicon ores, and mines have been the town and tin ores were Shuidong banned and closed, township level 6 749.89 6.83% 4,392 4.90% Yes Cd, As mined in small √ Town with tea-oil and the workshops with Camellia trees participation slags piled in the planted in the willingness of the open air. surrounding area. public in the area is strong. Pollution mainly Average attention sources from the is paid by the waste water, government at the residue and slags No relevant data and town and as well as dust Chujiang management township level 7 1,001.68 13.19% 6,819 7.61% Yes Cd, As from local mining Town measures have been and the workshops of collected yet participation manganese mines, willingness of the iron mines and public in the area coal mines in the is not strong. 1960-1970s. 158 Indicator of farmland Attention paid Grain Indicator area by local Selected Serial Town Paddy Proportion Standard-exceeding Standard-exceeding Analysis of Pollution source government and project No. Name field of area of Output rice factors Pollution Source management status public Proportion towns area the (ton) participation (ha) territory willingness Average attention is paid by the government at the No relevant data and town and No relevant Maishi management township level 8 1,099.33 14.00% 5,131 5.72% No data yet information has Town measures have been and the been collected yet collected yet participation willingness of the public in the area is not strong. Average attention is paid by the government at the No relevant data and town and No relevant Xianghua management township level 9 607.23 7.84% 2,878 3.21% Yes Cd, As information has Town measures have been and the been collected yet collected yet participation willingness of the public in the area is not strong. Average attention is paid by the government at the No relevant data and town and No relevant Huatang management township level 10 854.18 12.48% 7,269 8.11% Yes Cd, As information has Township measures have been and the been collected yet collected yet participation willingness of the public in the area is not strong. Average attention No relevant data and is paid by the No relevant Wanshui management government at the 11 904.32 14.99% 5,571 6.21% Yes Cd, As information has Township measures have been town and been collected yet collected yet township level and the 159 Indicator of farmland Attention paid Grain Indicator area by local Selected Serial Town Paddy Proportion Standard-exceeding Standard-exceeding Analysis of Pollution source government and project No. Name field of area of Output rice factors Pollution Source management status public Proportion towns area the (ton) participation (ha) territory willingness participation willingness of the public in the area is not strong. Average attention is paid by the government at the No relevant data and town and No relevant Zhennan management township level 12 618.25 7.47% 3,018 3.37% Yes Cd information has Township measures have been and the been collected yet collected yet participation willingness of the public in the area is not strong. Average attention is paid by the government at the Xishan No relevant data and town and No relevant Xishan management township level 13 620.86 3.06% 4,375 4.88% No data yet information has Yao measures have been and the been collected yet Township collected yet participation willingness of the public in the area is not strong. Average attention is paid by the government at the No relevant data and town and No relevant management township level 14 Others 492 0.55% No data yet information has measures have been and the been collected yet collected yet participation willingness of the public in the area is not strong. Total 13,021.5 9.47% 89,647.2 100.00% No data yet 160 Indicator of farmland Attention paid Grain Indicator area by local Selected Serial Town Paddy Proportion Standard-exceeding Standard-exceeding Analysis of Pollution source government and project No. Name field of area of Output rice factors Pollution Source management status public Proportion towns area the (ton) participation (ha) territory willingness In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evaluation indicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the township government to participate. Through the evaluation and selection, Wushui Town, Nanqiang Town and Shuidong Town are selected as the project towns. 161 Table 7-11 Selection Sheet of Project Towns in Qiyang County Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory A total of 91 point locations were set up, Qiyang including 3 Guanyintan point locations Paper Mill was “Three with cadmium closed in 2012; wastes” content of< Hunan Qiyang discharge 0.3mg/kg, Huaxiang from accounting for Metallurgical enterprises 3.30%; 57 Group Co., Ltd. like Hunan point locations and Qiyang Qiyang Average with cadmium Licheng Huaxiang attention is content of Smelting Co., Metallurgical paid by the 0.3-0.6mg/kg, Ltd. were closed Cadmium & arsenic Group Co., government at accounting for in 2013, but the pollution. Ltd., Qiyang the town and 62.64%; 31 slag has not Guanyintan Standard-exceeding Cd: 2 Cd: 20.00% Licheng township 81.18 2,069 1,969 3.9% point locations 22,783 4.37 10 Cd, As been completely Town Cd: 89.01% As: 1 As: 10.0.% Smelting Co., level and the with cadmium removed; Standard-exceeding Ltd., Qiyang participation content of> Yongzhou As: 46.15% Guanyintan willingness of 0.6mg/kg, Huaxin Paper Mill, the public in accounting for Magnetic Yongzhou the area is 34.07%. 39 Materials Co., Huaxin strong. point locations Ltd. has been Magnetic with arsenic closed in 2014 Materials content of < and Guanyintan Co., Ltd. and 20mg/kg, Yongda Guanyintan accounting for Company Yongda 42.85%; 42 stopped Company. point locations production for with arsenic treatment in content of 2016. 20-30mg/kg, accounting for 162 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory 46.15%; 2 point locations with arsenic content of > 30mg/kg, accounting for 10.99%. A total of 30 point locations were set up, including 16 Manganese point locations In the mines, iron with cadmium 1960-1970s, mines, and coal content of > manganese mines have 0.6mg/kg, ores, iron been banned accounting for ores, and coal Average and closed, with 53.33%; 14 ores were attention is the surrounding point locations mined in paid by the farmland with cadmium Cadmium & arsenic small government at returned to content of pollution. workshops the town and forest. Maozhu 0.3-0.6mg/kg, Standard-exceeding Cd: 4 Cd: 16.00% with slags township 92.05 1,871 1,698 3.3% 22,669 4.35 25 Cd, As Zhenhong Town accounting for Cd: 93.33%; As: 4 As: 16.00% piled in the level and the Coking Plant of 46.67%. 8 standard-exceeding open air. participation Maozhu Town point locations As: 86% Waste water willingness of stopped with arsenic was the public in production for content of < discharged the area is treatment in 20mg/kg, from strong. 2016. accounting for large-scale Large-scale 26.67%; 20 livestock and livestock and point locations poultry poultry breeding with arsenic breeding. stopped. content of 20-30mg/kg, accounting for 66.67%; 2 163 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory point locations with arsenic content of > 30mg/kg, accounting for 6.67%. A total of 5 point locations were set up, including 3 point locations with cadmium content of > There was no 0.6mg/kg, enterprise in accounting for Average the town 60%; 2 point attention is involving in locations with paid by the heavy metal cadmium Cadmium & arsenic No relevant data government at pollution. content of pollution. and the town and Pollution may Dazhongqiao 0.3-0.6mg/kg, Standard-exceeding management township 138 3,389 3,195 6.3% 27,752 5.32 No data yet source from Town accounting for Cd: 100%; measures have level and the the high 40%. 4 point standard-exceeding been collected participation background locations with As: 20% yet willingness of values of arsenic the public in heavy metals content of < the area is in the soil and 20mg/kg, strong. agricultural accounting for inputs. 80%; 1 point location with arsenic content of > 30mg/kg, accounting for 20%. 164 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory A total of 12 Jinxin Furnace Waste water point locations Charge of was were set up, Sankoutang Average discharged including 3 Town, Qiyang attention is from Jinxin point locations County was paid by the Furnace with cadmium closed in 2014. government at Charge of content of > Cd pollution with Some the town and Sankoutang Sankoutang 0.6mg/kg, 100% enterprises township 61.8 2,408 2,205 4.3% 21,435 4.11 8 Cd Cd: 4 Cd: 50% Town, Town accounting for standard-exceeding reached the level and the Qiyang 25%; 9 point rate discharge participation County. locations with standard after willingness of Pollution cadmium treatment. the public in might source content of Pollution might the area is from 0.3-0.6mg/kg, source from strong. agricultural accounting for agricultural inputs. 75%. inputs. A total of 67 Iron and Iron and point locations manganese manganese ores were set up, ores in the were closed in including 6 Dajiang the late 1990s. point locations Forest Farm Slags in High attention with cadmium were once once-existing is paid by the content of < mined in the iron and government at 0.3mg/kg, Cadmium pollution. 1990s. Waste manganese the town and accounting for Standard-exceeding water was mines have township Cd: 44 Cd: 69.84% iaojia Town 107.78 2,976 2,499 4.9% 8.950%; 47 rate of Cd is 20.16% 35,808 6.87 63 Cd, As discharged been cleaned up level and the √ As: 12 As: 19.05% point locations and that of As is from Xiaojia and almost will participation with cadmium 20.16% Village Paper not cause any willingness of content of Mill of heavy metal the public in 0.3-0.6mg/kg, Qiyang pollution to the the area is accounting for County, farmlands in the strong. 70.14%; 14 Bamiao Paper lower reach. point locations Mill of Xiaojia Village with cadmium Qiyang Paper Mill of content of > County, etc. Qiyang County 165 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory 0.6mg/kg, and Bamiao accounting for Paper Mill of 20.90%. 39 Qiyang County point locations are closed in with arsenic 2011 and passed content of < the 20mg/kg, provincial-level accounting for acceptance. 58.20%; 20 point locations with arsenic content of 20-30mg/kg, accounting for 29.85%; 8 point locations with arsenic content of > 30mg/kg, accounting for 11.94%. A total of 27 point locations Average were set up, Manganese Manganese attention is including 18 ores, silicon mines, iron paid by the point locations Cadmium & arsenic ores, and tin mines, and coal government at with cadmium pollution. ores were mines have the town and content of < Standard-exceeding Cd: 21 Cd: 20.00% mined in been banned township Babao Town 199.2 2,136 1,891 3.7% 20,696 3.97 23 Cd, As 0.3mg/kg, rate of Cd is 33.33% As: 6 As: 11.00% small and closed, with level and the accounting for and that of As is workshops tea-oil Camellia participation 66.67%; 1 11.11% with slags trees planted in willingness of point location piled in the the surrounding the public in with cadmium open air. area. the area is content strong. of >0.6mg/kg, 166 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory accounting for 3.70%; 8 point locations with cadmium content of 0.3-0.6mg/kg, accounting for 29.63%. 3 point locations with arsenic content of > 30mg/kg, accounting for 11.11%. A total of 31 point locations were set up, Pollution including 21 mainly point locations sources from with cadmium There were coal High attention the waste content of mines in the is paid by the water, residue 0.3-0.6mg/kg, upper reach of government at Cadmium & arsenic and slags as accounting for the Baishui the town and pollution. well as dust 67.74%; 8 River, which township Standard-exceeding Cd: 21 Cd: 91.31% from local aishui Town 126.99 4,059 3,590 7.0% point locations 42,431 8.14 23 Cd, As was closed in level and the √ Cd: 67.74%; As: 6 As: 26.09% mining with cadmium 1996 but there participation standard-exceeding workshops of content of are still some willingness of As: 9.68% manganese <0.3mg/kg, slags not the public in mines, iron accounting for completely the area is mines and 25.81%; 2 cleaned up. strong. coal mines in point locations the with cadmium 1960-1970s. content of >0.6mg/kg, accounting for 167 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory 6.45%. 26 point locations with arsenic content of < 20mg/kg, accounting for 83.87%; 3 point locations with arsenic content of 20-30mg/kg, accounting for 9.68%; 2 point locations with arsenic content of > 30mg/kg, accounting for 6.45%. A total of 4 point locations were set up, Average including 2 attention is point locations paid by the with cadmium Cadmium & arsenic No relevant data government at content of 0.3- pollution. No relevant and the town and Huangnitang 0.6mg/kg, Standard-exceeding information management township 70.59 2,081 1,601 3.1% 20,170 3.87 No data yet Town accounting for Cd: 75%; has been measures have level and the 50%; 2 point standard-exceeding collected yet been collected participation locations with As: 50% yet willingness of cadmium the public in content of > the area is 0.6mg/kg, strong. accounting for 50%. 2 point 168 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory locations with arsenic content of < 20mg/kg, accounting for 50%; 1 point location with arsenic content of 20-30mg/kg, accounting for 25%; 1 point location with arsenic content of > 30mg/kg, accounting for 25%. A total of 5 point locations were set up, Average including 4 attention is point locations paid by the with cadmium Cadmium & arsenic No relevant data government at content of 0.3- pollution. No relevant and the town and 0.6mg/kg, Jinbaotang Standard-exceeding information management township 64.72 2,315 2,088 4.1% accounting for 23,555 4.52 No data yet Town rate of Cd is 80% has been measures have level and the 80%; 1 point and that of As is collected yet been collected participation location with 20% yet willingness of cadmium the public in content of > the area is 0.6mg/kg, strong. accounting for 20%. 4 point locations with 169 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory arsenic content of < 20mg/kg, accounting for 80%; 1 point location with arsenic content of 20- 30mg/kg, accounting for 20%. A total of 15 point locations “Three were set up, wastes” Average including 15 discharged by attention is point locations Qiyang paid by the with cadmium Hongfeng government at Qiyang content of 0.3- Chemical the town and Cadmium pollution. Hongfeng 0.6mg/kg, Plant, and township anshi Town 128.34 2,105 1,925 3.8% Standard-exceeding 22,860 4.38 No data yet Chemical Plant accounting for there was level and the rate of Cd is 100% was closed in 100%; 15 wastewater participation 2014 point locations discharge by willingness of with arsenic large-scale the public in content of < aquaculture the area is 20mg/kg, farm near the strong. accounting for water source; 100% A total of 5 Average point locations Cadmium & arsenic No relevant data attention is were set up, pollution. No relevant and paid by the including 3 Standard-exceeding information management government at Meixi Town 63.39 1,704 1,334 2.6% 14,766 2.83 No data yet point locations rate of Cd is 100% has been measures have the town and with cadmium and that of As is collected yet been collected township content of 0.3- 20% yet level and the 0.6mg/kg, participation 170 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory accounting for willingness of 60%; 2 point the public in locations with the area is cadmium strong. content of > 0.6mg/kg, accounting for 40%. 4 point locations with arsenic content of < 20mg/kg, accounting for 80%; 1 point location with arsenic content of 20- 30mg/kg, accounting for 20%. A total of 20 Average attention is The point locations paid by the wastewater Average were set up, government at the discharge attention is including 5 town and township from paid by the point locations level and the Cadmium & arsenic Xinjiang government at with cadmium participation pollution. Paper Mill, the town and content of > willingness of the Several paper Yangjiaotang Standard-exceeding Cd: 5 Xuelihong township 126.89 3,503 3,071 6.0% 0.6mg/kg, 38,740 7.43 9 Cd, As public in the area is mills have been Town rate of Cd is 100% As: 3 Paper Mill level and the accounting for strong. closed down and that of As is and Jixiang participation 25%; 15 point 35% Paper Mill in willingness of locations with Yangjiaotang the public in cadmium Town, the area is content of Qiyang strong. 0.3-0.6mg/kg, County. accounting for 171 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory 75%. 10 point locations with arsenic content of < 20mg/kg, accounting for 50%; 8 point locations with arsenic content of 20-30mg/kg, accounting for 40%; 2 point locations with arsenic content of > 30mg/kg, accounting for 10%. Average A total of 5 attention is point locations paid by the were set up, No relevant data government at including 5 Cd pollution with No relevant and the town and Xiamadu point locations 100% Cd information management township 125.29 2,574 2,497 4.9% 31,085 5.96 No data yet Town with cadmium standard-exceeding has been measures have level and the content of rate collected yet been collected participation 0.3-0.6mg/kg, yet willingness of accounting for the public in 100%. the area is strong. A total of 4 Wastewater Average Cadmium pollution. Qiliqiao Paper Qiliqiao point locations discharge attention is 108.3 2,074 1,847 3.6% Standard-exceeding 21,915 4.2 No data yet Mill was closed Town were set up, from Qiliqiao paid by the rate of Cd is 75% in 2016 including 7 Paper Mill government at 172 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory point locations the town and with cadmium township content of level and the 0.3-0.6mg/kg, participation accounting for willingness of 100%. the public in the area is strong. A total of 4 point locations were set up, Average Wastewater including 1 attention is discharge point location paid by the from with cadmium government at Chongshan content of Cd pollution with the town and Paper Mill in Dacundian <0.3mg/kg, 75% Cd Paper Mill was township 92.73 2,771 2,635 5.2% 29,155 5.59 No data yet Dacundian Town accounting for standard-exceeding closed in 2011. level and the Town; the 25%; 3 point rate participation other locations with willingness of pollution cadmium the public in sources were content of the area is not clear 0.3-0.6mg/kg, strong. accounting for 75%. A total of 102 “Three Qiyang Average point locations wastes” Jiangnan attention is were set up, discharge Trading Co., paid by the including 13 Cd and As pollution; from Qiyang Ltd. was closed government at point locations Standard-exceeding Jiangnan in 2014 and the town and Lijiaping Cd: 4 Cd: 30.77% 83.25 2,482 2,349 4.6% with cadmium rate of Cd is 84.31% 24,234 4.65 13 Cd, As Trading Co., Yongzhou township Town As: 5 As: 38.46% content of and that of As is Ltd., Feixiang level and the <0.3mg/kg, 18.63% Yongzhou Smelting Co., participation accounting for Feixiang Ltd. was closed willingness of 12.75%; 29 Smelting Co., in 2013. But the public in point locations Ltd. and slag some slag has the area is 173 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory with cadmium being piled not been strong. content openly. thoroughly of >0.6mg/kg, cleaned up. accounting for 28.43%; 60 point locations with cadmium content of 0.3-0.6mg/kg, accounting for 58.82%. 83 point locations with arsenic content of < 20mg/kg, accounting for 81.37%; 15 point locations with arsenic content of 20-30mg/kg, accounting for 14.71%; 4 point locations with arsenic content of > 30mg/kg, accounting for 3.92%. A total of 4 Cadmium & arsenic Wastewater Qiyang Average point locations pollution. discharge Wenmingpu attention is Wenfushi were set up, Standard-exceeding from Qiyang Cement Plant paid by the 61.29 1,820 1,715 3.4% 19,406 3.72 No data yet Town including 1 rate of Cd is 100% Wenmingpu was closed in government at point location and that of As is Cement Plant 2011 and no the town and with cadmium 25% and no other other relevant township 174 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory content of > relevant treatment level and the 0.6mg/kg, information measures have participation accounting for has been been collected. willingness of 25%; 3 point collected. the public in locations with the area is cadmium strong. content of 0.3-0.6mg/kg, accounting for 75%. 3 point locations with arsenic content of < 20mg/kg, accounting for 75%; 1 point location with arsenic content of 20- 30mg/kg, accounting for 25%. A total of 4 Average point locations attention is were set up, paid by the including 1 No relevant data government at point location Cd pollution with No relevant and the town and with cadmium Wenmingpu 75% Cd information management township 112.11 4,008 3,705 7.3% content of 35,039 6.72 No data yet Town standard-exceeding has been measures have level and the <0.3mg/kg, rate collected yet been collected participation accounting for yet willingness of 25%; 3 point the public in locations with the area is cadmium strong. content of 175 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory 0.3-0.6mg/kg, accounting for 75%. 4 point locations with arsenic content of < 20mg/kg, accounting for 100%. A total of 4 point locations were set up, including 1 point location with cadmium content of <0.3mg/kg, Average accounting for attention is 25%; 2 point paid by the locations with Cadmium & arsenic No relevant data government at cadmium pollution. No relevant and the town and Gongjiaping content of Standard-exceeding information management township 79.98 2,586 2,353 4.6% 26,325 5.05 No data yet Town 0.3-0.6mg/kg, rate of Cd is 75% has been measures have level and the accounting for and that of As is collected yet been collected participation 50%; 1 point 25% yet willingness of location with the public in cadmium the area is content strong. of >0.6mg/kg, accounting for 25%. 2 point locations with arsenic content of < 20mg/kg, 176 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory accounting for 50%; 2 point locations with arsenic content of 20- 30mg/kg, accounting for 50%. A total of 12 point locations were set up, including 2 point locations "Three with cadmium wastes" content of discharge <0.3mg/kg, from Hunan Average accounting for Hunan Qiyang Qiyang attention is 16.67%; 2 Huatian Huatian paid by the point locations Metallurgy and Cadmium & arsenic Metallurgy government at with cadmium Chemical pollution. and Chemical the town and content Industry Co., Changhong Standard-exceeding Industry Co., township 36.1 899 794 1.6% of >0.6mg/kg, 9,779 1.88 7 As As: 3 As: 42.86% Ltd., Qiyang Office rate of Cd is 83.33% Ltd., Qiyang level and the accounting for Xiangqi and that of As is Xiangqi participation 16.67%; 8 Economic and 8.33% Economic willingness of point locations Trade Industrial and Trade the public in with cadmium Co., Ltd. were Industrial the area is content of closed in 2016 Co., Ltd. and strong. 0.3-0.6mg/kg, other accounting for ferroalloy 66.67%. 8 plants point locations with arsenic content of < 20mg/kg, accounting for 177 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory 75%; 4 point locations with arsenic content of 20- 30mg/kg, accounting for 25%. A total of 4 point locations were set up, including 3 point locations with cadmium content of > 0.6mg/kg, Qiyang Average accounting for Nitrogen attention is 75%; 1 point "Three Fertilizer Plant paid by the location with wastes" and Qiyang Cadmium & arsenic government at cadmium discharge Smelter were pollution. the town and content of from Qiyang closed, whose Longshan Standard-exceeding township 39.9 617 577 1.1% 0.3-0.6mg/kg, 5,302 1.02 No data yet Nitrogen original sites Office rate of Cd is 100% level and the accounting for Fertilizer have been and that of As is participation 25%. 1 point Plant and developed for 25% willingness of location with Qiyang commercial the public in arsenic Smelter housing and the area is content of 20- non-profitable strong. 30mg/kg, house. accounting for 25%; 3 point locations with arsenic content of< 20mg/kg, accounting for 178 Heavy metal pollution of soil in Attention Area of Indicator of farmland area Grain Indicator Indicator of standard-exceeding rice Main agricultural land Pollution paid by local the pollution Selec source government Town Name territory Proportion source and proj Agricultural Paddy Proportion Sample Pollution management and public (square of area of Pollution Output Standard-exceeding Standard-exceeding pollution tow area field area Pollution type (%) number factor status participation kilometer) the status (ton) number (pcs) proportion path (hectares) (hectares) (pcs) willingness territory 75%. A total of 5 point locations were set up, including 5 point locations with cadmium Average content of attention is 0.3-0.6mg/kg, paid by the accounting for Cadmium & arsenic government at Wastewater 100%. 2 point pollution. the town and discharge of locations with Standard-exceeding Paper Mill was township Wuxi Office 33.2 579 543 1.1% 5,602 1.07 No data yet Qiyang Wuxi arsenic rate of Cd is 100% closed in 2011. level and the Yuanfa Paper content of 20- and that of As is participation Mill 30mg/kg, 40% willingness of accounting for the public in 40%; 3 point the area is locations with strong. arsenic content of < 20mg/kg, accounting for 60%. In the selection of the Demonstration Area, priorities are given to the pollution sources caused by industrial and mining enterprises. Referring to the selection principle of the Demonstration Area, the selection evalua ndicators are set to include the following aspects: paddy field area, grain output, agricultural land pollution, pollution sources and pollution paths, pollution source management status, and the willingness of the towns overnment to participate. Through the evaluation and selection, Xiaojia Town and Baishui Town are selected as the project towns. 179 180 Appendix 8 Comparison and Selection Sheet of Demonstration Area of Each Project County Table 8-1 Comparison and Selection Sheet of Demonstration Area in Yongding District Main factors considered in Name of demonstration area and comment & analysis comparison and selection of demonstration area Yuanguping Demonstration Yanghuping Demonstration Daping Town Demonstration Yinjiaxi Demonstration Area Wentang Demonstration Area Area Area Area Regional Main type of Paddy field Paddy field Paddy field Paddy field Paddy field representation cultivated land Clear: the Lishui River was Clear: the Lishui River was Clear: the Lishui River was Clear: the Lishui River was polluted in the past. polluted in the past. polluted in the past. polluted in the past. Farmlands were flooded by Farmlands were flooded by Farmlands were flooded by Farmlands were flooded by Clear: soil pollution caused Whether the heavy the Lishui River in the the Lishui River in the the Lishui River in the the Lishui River in the by industrial and mining metal pollution rainstorm period and irrigated rainstorm period and irrigated rainstorm period and irrigated rainstorm period and irrigated “three wastes” pollution in cause is clear by wastewater from the Lishui by wastewater from the Lishui by wastewater from the Lishui by wastewater from the Lishui history River in the drought period, River in the drought period, River in the drought period, River in the drought period, which resulted in soil which resulted in soil which resulted in soil which resulted in soil pollution. pollution. pollution. pollution. Industrial and mining Industrial and mining Industrial and mining Industrial and mining Pollution Is the main enterprises were closed down, enterprises were closed down, enterprises were closed down, enterprises were closed down, source is pollution source illegal mining prohibited, illegal mining prohibited, illegal mining prohibited, illegal mining prohibited, clear and controllable or solid wastes left over from the solid wastes left over from the solid wastes left over from the solid wastes left over from the The slag is piled on-site and controllable will it cause new past treated, water quality of past treated, water quality of past treated, water quality of past treated, water quality of the pollution source is not pollution to the the Lishui River cleaned, the Lishui River cleaned, the Lishui River cleaned, the Lishui River cleaned, controllable downstream flood controlled by reservoirs flood controlled by reservoirs flood controlled by reservoirs flood controlled by reservoirs cultivated land and pollution source and pollution source and pollution source and pollution source controlled. controlled. controlled. controlled. Whether or not the tailings pond, if any, is safe and None None None None None free of any leakage. Water quality of Standard irrigation water Standard irrigation water Standard irrigation water Standard irrigation water Standard irrigation water irrigation water Type of Content of main Cd pollution: average 0.49 mg Cd pollution: average 0.39 mg Cd pollution: average 0.34 mg Cd pollution: average 0.36 mg Cd pollution: mainly between heavy metal heavy metal / kg (mainly between 0.3-1.0 / kg (mainly between 0.3-1.0 / kg (mainly between 0.3-1.0 / kg (mainly between 0.3-1.0 0.3-0.6 mg / kg pollution pollution factors in mg / kg) mg / kg) mg / kg) mg / kg) 181 Main factors considered in Name of demonstration area and comment & analysis comparison and selection of demonstration area Yuanguping Demonstration Yanghuping Demonstration Daping Town Demonstration Yinjiaxi Demonstration Area Wentang Demonstration Area Area Area Area soil (mg/kg) Standard-exceeding Cd & As: Standard-exceeding Cd & As: Standard-exceeding Cd & As: Cd average 0.24 mg / kg Cd average 0.25 mg / kg Cd average 0.25 mg / kg Standard-exceeding Cd: Standard-exceeding Cd: Rice heavy metal (mainly between 0.2-0.4 mg / (mainly between 0.2-0.4 mg / (mainly between 0.2-0.4 mg / average 0.24 mg / kg (mainly average 0.24 mg / kg (mainly pollution (mg/kg) kg); As average 0.26 mg / kg kg); As average 0.30 mg / kg kg); As average 0.26 mg / kg between 0.2-0.4 mg / kg) between 0.2-0.4 mg / kg) (mainly between 0.2-0.4 mg / (mainly between 0.2-0.4 mg / (mainly between 0.2-0.4 mg / kg) kg) kg) Whether it is included in local No No No No No relevant planning Whether heavy metal pollution Attention No No No No No treatment has been paid and conducted locally participation Positivity to willingness participate of farmer and Very positive Very positive Very positive Very positive Moderate agriculture professional cooperative Whether included in this batch of Conclusion Yes Yes Yes Yes No demonstration areas 182 Table 8-2 Comparison and Selection Sheet of Demonstration Area in Jishou City Main factors considered in comparison Name of demonstration area and comment & analysis and selection of demonstration area Qianzhou Demonstration Area Aizhai Demonstration Area Majing’ao Demonstration Area Selected towns and townships in the Qianzhou Sub-district and Hexi Town Jilue Township Aizhai Town Majing’ao Town demonstration area Main type of Paddy field Paddy field Paddy field Paddy field cultivated land 1、It is located in the suburban area of 1. It is located in the western region in 1. It is located in the suburban area 1. It is located in the suburban area the county, mainly in the landform of the county, mainly in the landform of of the county, mainly in the of the county, mainly in the hills and plains. hills and downland. landform of hills. landform of hills. 2、The farmland is mainly of paddy 2. The farmland is mainly of paddy rice 2. The farmland is mainly of 2. The farmland is mainly of paddy rice soil type with medium and high soil type with generally higher content paddy rice soil type with high rice soil type with high content of content of organic matters. Sandy loam of organic matters. Sandy loam soil content of organic matters. Sandy organic matters. Sandy loam soil soil dominates in the soil, with weak dominates in the soil, with week loam soil dominates in the soil, dominates in the soil, with week acidity. acidity or alkalinity. with week acidity. acidity. 3、The region provides a good 3. It has been incorporated into the 3. It has been incorporated into the 3. It has not been incorporated into hydrothermal condition and acts as the local heavy metal pollution treatment local heavy metal pollution the local heavy metal pollution main area of supply of agricultural plan and VIP pilot treatment has been treatment plan and VIP treatment plan. products to the urban area and carried out for heavy metal pollution. experimental treatment has been 4. The local people averagely Regional representation surrounding areas. It is highly regarded The local people highly recognize the carried out for heavy metal recognize the farmland pollution by the municipal government. Strong farmland pollution treatment. pollution. The local people highly treatment. Representative 4. The farmland is polluted by the supports of preferential policies are recognize the farmland pollution 5. The farmland is polluted by the analysis heavy metal caused by “three wastes” given in the region where there are a treatment. heavy metal caused by “three variety of agricultural supporting of historical enterprises involving 4. It has been incorporated into the wastes” of historical enterprises projects. heavy metal pollution, the rice and local heavy metal pollution involving heavy metal pollution, 4. It has been incorporated into the sediment test samples exceed the treatment plan and VIP pilot the rice test samples exceed the local heavy metal pollution treatment standards, and the municipal treatment has been carried out for standards, and the pollution plan and VIP pilot treatment has been environmental protection bureau will heavy metal pollution. The local sources have been effectively carried out for heavy metal pollution. further take countermeasures for people highly recognize the controlled. The local people highly recognize the pollution sources in the area. farmland pollution treatment. 6. The main farmland rice farmland pollution treatment. 5. The main cultivated-land pollution 5. The farmland is polluted by the pollution type is cadmium and 5. The farmland is polluted by the type is cadmium and arsenic compound heavy metal caused by “three arsenic compound pollution, the pollution, the cadmium content heavy metal caused by “three wastes” wastes” of historical enterprises cadmium content changes greatly changes greatly and is 0.2-0.4mg/kg, of historical metallurgical enterprises involving heavy metal pollution, and is 0.2-0.4mg/kg; the arsenic the arsenic content changes greatly and involving heavy metal pollution, the is 0.2-0.4mg/kg, both of which are the rice test samples exceed the content changes greatly and is rice test samples exceed the standards, slightly polluted. standards, and the pollution 0.2-0.4mg/kg, both of which are 183 Main factors considered in comparison Name of demonstration area and comment & analysis and selection of demonstration area Qianzhou Demonstration Area Aizhai Demonstration Area Majing’ao Demonstration Area and the pollution sources have been sources have been effectively mildly polluted, and some effectively controlled. controlled. farmlands are pollution-free. 6. The main farmland pollution type is 6. The main farmland rice arsenic pollution, the arsenic content pollution type is cadmium and changes greatly and is 0.2-0.4mg/kg arsenic compound pollution, the (slightly polluted), and there is still a cadmium content changes greatly and is 0.2-0.4mg/kg; the arsenic small amount of unpolluted farmland. content changes greatly and is 0.2-0.4mg/kg, both of which are mildly polluted, and some farmlands are pollution-free. Whether the heavy Clear: in history, industrial and mining Clear: in history, industrial and mining Clear: in history, industrial and Clear: in history, industrial and metal pollution cause enterprises discharged waste water enterprises discharged waste water mining enterprises discharged mining enterprises discharged is clear causing soil pollution causing soil pollution waste water causing soil pollution waste water causing soil pollution During the “Twelfth Five-Year During the “Twelfth Five-Year During the “Twelfth Five-Year Plan” During the “Twelfth Five-Year Plan” Is the main pollution Plan” period, all enterprises Plan” period, all enterprises period, all enterprises involving in period, all enterprises involving in source controllable or involving in heavy metal pollution involving in heavy metal pollution heavy metal pollution had taken heavy metal pollution had taken will it cause new had taken effective treatment had taken effective treatment effective treatment measures as effective treatment measures as pollution to the measures as required by the measures as required by the Pollution source required by the environmental required by the environmental downstream environmental protection environmental protection is clear and protection authorities. The source of protection authorities. The source of cultivated land authorities. The source of pollution authorities. The source of pollution controllable pollution is controllable. pollution is controllable. is controllable. is controllable. Whether or not the tailings pond, if any, is safe and free of None None None None any leakage. Water quality of Standard irrigation water Standard irrigation water Standard irrigation water Standard irrigation water irrigation water Content of main heavy metal pollution Cd pollution: mainly between 0.3-1.0 Cd pollution: mainly between 0.3-1.0 Cd pollution: mainly between Cd pollution: mainly between factors in soil mg / kg mg / kg 0.3-1.0 mg / kg 0.3-1.0 mg / kg Type of heavy (mg/kg) metal pollution Mainly Cd & As compound Mainly Cd & As compound Mainly Cd & As compound pollution, Rice heavy metal Mainly arsenic pollution, with arsenic pollution, with Cd content being pollution, with Cd content being with Cd content being 0.2-0.4mg/kg content (mg/kg) content being 0.2-0.4mg/kg, 0.2-0.4mg/kg and As content being 0.2-0.4mg/kg and As content being and As content being 0.2-0.4mg/kg, 0.2-0.4mg/kg, 0.2-0.4mg/kg, 184 Main factors considered in comparison Name of demonstration area and comment & analysis and selection of demonstration area Qianzhou Demonstration Area Aizhai Demonstration Area Majing’ao Demonstration Area Whether it is included in local Yes Yes Yes No relevant planning Whether heavy metal Attention paid pollution treatment Launched vip pilot Launched vip pilot Launched vip pilot None and has been conducted participation locally willingness Positivity to participate of farmer and agriculture Very positive Very positive Very positive Moderate professional cooperative Whether included in Conclusion this batch of Yes Yes Yes No demonstration areas 185 Table 8-3 Comparison and Selection Sheet of Demonstration Area in Yongshun County Main factors considered in comparison and selection of Name of demonstration area and comment & analysis demonstration area Shaba Demonstration Area Xiqi Demonstration Area Qingping Town Regional Main type of cultivated land Shuitian Village Shuitian Village Shuitian Village representation Clear: small metallurgical enterprises existed in Whether the heavy metal pollution Clear: residues, slags and waste water from Clear: residues, slags and waste water from coal the towns and townships and the pollution cause is clear coal mining polluted the soil. mining polluted the soil. source was the “three wastes” discharge. Industrial and mining enterprises were Industrial and mining enterprises were closed Is the main pollution source closed down, illegal mining prohibited, Pollution source is down, illegal mining prohibited, solid wastes controllable or will it cause new solid wastes left over from the past treated, There are no relevant measures, and the clear and left over from the past treated, water quality of pollution to the downstream water quality of the Lishui River cleaned, pollution source is uncontrollable. controllable the Lishui River cleaned, flood controlled by cultivated land flood controlled by reservoirs and pollution reservoirs and pollution source controlled. source controlled. Whether or not the tailings pond, if None None None any, is safe and free of any leakage. Water quality of irrigation water Standard irrigation water Standard irrigation water Standard irrigation water Content of main heavy metal Cd pollution: average 0.382 mg / kg Cd pollution: average 0.373 mg / kg (mainly Cd pollution: mainly between 0.3-1.0 mg / kg pollution factors in soil (mg/kg) (mainly between 0.3-1.0 mg / kg) between 0.3-1.0 mg / kg) Standard-exceeding Pb, Cd & As: the rice Type of heavy Standard-exceeding Cd & As: the rice Cd Cd content in mainly between metal pollution content in mainly between 0.2~0.4mg/kg; the Standard-exceeding Cd & As: Pb, Cr & Hg Rice heavy metal content (mg/kg) 0.2~0.4mg/kg; the rice As content in mainly rice As content in mainly between meet the standard between 0.2~0.4mg/kg; the rice Pb content 0.2~0.4mg/kg in mainly between 0.2~0.4mg/kg Whether it is included in local No No No relevant planning Whether heavy metal pollution Attention paid and treatment has been conducted No No No participation locally willingness Positivity to participate of farmer and agriculture professional Very positive Very positive Moderate cooperative Whether included in this batch of Conclusion Yes Yes No demonstration areas 186 Table 8-4 Comparison and Selection Sheet of Demonstration Area in Cili County Main factors considered in Name of demonstration area and comment & analysis comparison and selection of Dongyueguan Town Yangliupu Township Tongjinpu Town Xiangshi Town Sanhe Town Ganyan Demonstration demonstration area Demonstration Area Demonstration Area Demonstration Area Demonstration Area Demonstration Area Area Regional Main type of Paddy field Paddy field Paddy field Paddy field Paddy field Paddy field representation cultivated land Clear: the farmland is Clear: the farmland is Clear: the heavy metal Clear: the heavy metal Clear: the heavy metal Clear: the farmland is Whether the affected by cadmium and affected by historical pollution of farmland pollution of farmland pollution of farmland affected by historical heavy metal arsenic pollution caused ni-mo ore processing was caused due to the was caused due to the was caused due to the ni-mo ore mining, pollution cause by historical iron ore enterprises, thereby sewage irrigation from sewage irrigation from sewage irrigation from thereby causing heavy is clear mining and realgar causing heavy metal Zhuangta Reservoir Zhuangta Reservoir Zhuangta Reservoir metal pollution. tailings pollution. Is the main pollution source NO; it has been No; it has been controllable or NO; the source of NO; the source of NO; the source of incorporated into the Uncontrollable, Pollution effectively controlled will it cause pollution, Zhuangta Coal pollution, Zhuangta Coal pollution, Zhuangta Coal local heavy metal enterprise "three wastes" source is and factories and mines new pollution Mine, is closed now Mine, is closed now Mine, is closed now treatment plan and has have not been treated clear and have been closed. to the been effectively treated controllable downstream cultivated land Whether or not the tailings pond, if any, is None None None None None None safe and free of any leakage. Water quality Standard irrigation water Standard irrigation water Standard irrigation water Standard irrigation water Standard irrigation water Standard irrigation water of irrigation water Content of main heavy Cd pollution (cadmium Cd pollution (cadmium Cd pollution (cadmium Cd pollution (cadmium Cd pollution (cadmium Cd pollution (cadmium metal pollution content is mainly content is mainly content is mainly content is mainly content is mainly content is mainly factors in soil between 0.3-1.0 mg / kg) between 0.3-1.0 mg / kg) between 0.3-1.0 mg / kg) between 0.3-1.0 mg / kg) between 0.3-1.0 mg / kg) between 0.3-1.0 mg / kg) Type of (mg/kg) heavy metal Standard-exceeding Cd Standard-exceeding Cd Standard-exceeding Cd Standard-exceeding Cd pollution & As: the rice Cd content & As: the rice Cd & As: the rice Cd content & As: the rice Cd content Rice heavy Standard-exceeding Cd: Standard-exceeding Cd: in mainly between content in mainly in mainly between in mainly between metal content rice Cd content is mainly rice Cd content is mainly 0.2~0.4mg/kg; the rice between 0.2~0.4mg/kg; 0.2~0.4mg/kg; the rice 0.2~0.4mg/kg; the rice (mg/kg) between 0.2-0.4 mg / kg between 0.2-0.4 mg / kg As content in mainly the rice As content in As content in mainly As content in mainly between 0.2~0.4mg/kg mainly between between 0.2~0.4mg/kg between 0.2~0.4mg/kg 187 Main factors considered in Name of demonstration area and comment & analysis comparison and selection of Dongyueguan Town Yangliupu Township Tongjinpu Town Xiangshi Town Sanhe Town Ganyan Demonstration demonstration area Demonstration Area Demonstration Area Demonstration Area Demonstration Area Demonstration Area Area 0.2~0.4mg/kg Whether it is included in No No No No No No local relevant planning Whether heavy metal pollution Attention treatment has No No No No No No paid and been conducted participation locally willingness Positivity to participate of farmer and Very positive Very positive Very positive Very positive Very positive Moderate agriculture professional cooperative Whether included in this Conclusion batch of Yes Yes Yes Yes Yes No demonstration areas Table 8-5 Analysis table of selecting demonstration area in Huayuan County Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Biancheng Town Demonstration Area Yongfeng Demonstration Area Selected villages in the demonstration area Gaohe Village Yongfeng Village Area, hectares 61 52 Regional 47 Centralized and contiguous area, hectares 58 representation Main type of cultivated land Paddy field Paddy field Whether it belongs to the main grain producing area The grain output per mu is 760 kg / year The grain output per mu is 710 kg / year Pollution source is Clear: residues, slags and waste water from lead-zinc mineral Clear: residues, slags and waste water from lead-zinc mineral Whether the heavy metal pollution cause is clear clear and separation polluted the soil. separation polluted the soil. 188 Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Biancheng Town Demonstration Area Yongfeng Demonstration Area controllable The lead-zinc mining and separation enterprises were closed in Is the main pollution source controllable or will it cause new There are lead-zinc mining and separation enterprises in 2015 and residues cleaned up. The source of pollution is pollution to the downstream cultivated land operation and the source of pollution is not controllable. controllable. Whether or not the tailings pond, if any, is safe and free of None None any leakage. The irrigation water body is Gaohe River, whose water source is The irrigation water is mainly spring water and its quality can Irrigation water quality (including irrigation water sediment) mainly spring water and the quality can meet the standard; meet the standard; the upstream sediment of irrigation water The upstream sediment of irrigation water exceeds the standard exceeds the standard Range of pH value 5.64~7.65, most pH is under 6.5 5.25~7.01, most pH is under 6.5 Type of heavy metal Content of main heavy metal pollution factor (mg/kg) As: 0.15 As: 0.15 pollution Standard-exceeding As: Cd , Pb, As, Hg & Cr meet the Standard- exceeding rice heavy metal Standard-exceeding As: Cd , Pb, As, Hg & Cr meet the standard standard Whether it is included in local relevant planning No No Attention paid and Whether heavy metal pollution treatment has been participation Yes Yes conducted locally willingness Positivity to participate of farmer and agriculture Very positive Moderate professional cooperative Infrastructure and No facilities and non-matching ratio of field infrastructure 20% 30% construction Total investment of each demonstration area (RMB 10,000) 200 200 investment of the project Investment per hectare (RMB 10,000) 1.40 1.40 Conclusion Whether included in this batch of demonstration areas Yes No 189 Table 8-6 Analysis table of selecting demonstration area in Anhua County Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Dafu Town Qingtang Town Le’an Town Demonstration Area Meicheng Town Demonstration Area Demonstration Area Selected villages in Muxi Mengjia the demonstration Gurong Village Wenshi Village Hengshi Village Yizhong Village Dongtian Village Zhongtian Village Village area Area, hectares 73.3 87.3 85.3 80 120 80 88 Centralized and Regional contiguous area, 58.6 69.8 66.5 63.2 93.6 64 66 representation hectares Main type of Paddy field Paddy field Paddy field Paddy field Paddy field Paddy field Paddy field cultivated land Whether it belongs The grain output is 549 The grain output is The grain output is The grain output is The grain output is The grain output is The grain output is 600 t / to the main grain t / year 654 t / year 639 t / year 600 t / year 900 t / year 600 t / year year producing area Clear: the farmland Clear: the farmland Clear: the farmland Clear: the farmland Clear: the farmland is is polluted by is polluted by is polluted by is polluted by Clear: the farmland is Relatively clear: the polluted by atmospheric dust fall atmospheric dust fall atmospheric dust fall atmospheric dust fall polluted by farmland is polluted by atmospheric dust fall and wastewater and wastewater and wastewater and wastewater atmospheric dust fall Whether the heavy atmospheric dust fall and and wastewater irrigation from irrigation from irrigation from irrigation from and wastewater metal pollution wastewater irrigation from irrigation from "three "three wastes" "three wastes" "three wastes" "three wastes" irrigation from "three cause is clear "three wastes" discharged wastes" discharged by discharged by discharged by discharged by discharged by wastes" discharged by by enterprises involving enterprises involving enterprises enterprises enterprises involving enterprises enterprises involving heavy metal pollution heavy metal pollution involving heavy involving heavy heavy metal involving heavy heavy metal pollution metal pollution metal pollution pollution metal pollution Industrial and Industrial and Industrial and Industrial and Industrial and mining Industrial and mining mining enterprises mining enterprises mining enterprises mining enterprises Is the main enterprises were Industrial and mining Pollution source enterprises were closed were closed down, were closed down, were closed down, were closed down, pollution source closed down, illegal enterprises will be closed is clear and down, illegal mining illegal mining illegal mining illegal mining illegal mining controllable or will mining prohibited and down and illegal mining controllable prohibited and solid prohibited and solid prohibited and solid prohibited and solid prohibited and solid it cause new solid wastes left over prohibited but solid wastes wastes left over from wastes left over wastes left over wastes left over wastes left over pollution to the from the past treated. left over from the past still the past treated. The from the past from the past from the past from the past downstream The source of exist. The source of source of pollution is treated. The source treated. The source treated. The source treated. The source cultivated land pollution is pollution is uncontrollable. controllable. of pollution is of pollution is of pollution is of pollution is controllable. controllable. controllable. controllable. controllable. Whether or not the tailings pond, if None None None None None None Yes any, is safe and free of any leakage. Irrigation water The water from The water from The irrigation water The irrigation water The water from The water from Kuixi The water from Meidongxi quality (including Shuangxi Reservoir Natural Well and is mountain spring is Chenxi Brook and Kuixi and Zijintang and Zijintang Reservoir is used as irrigation water and Niujiaotang Xiadong’ao water and the the quality can meet Reservoir is used as Reservoir is used as irrigation water, and the 190 Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Dafu Town Qingtang Town Le’an Town Demonstration Area Meicheng Town Demonstration Area Demonstration Area sediment) Reservoir is used as Reservoir is used as quality can meet the the standard; irrigation water, and irrigation water, and quality of irrigation water irrigation water, and irrigation water, and standard; The upstream the quality of the quality of exceeds the standard; the the quality of irrigation the quality of The upstream sediment of irrigation water is up irrigation water is up upstream sediment of water is up to the irrigation water is up sediment of irrigation water to the standard; the to the standard; the irrigation water exceeds the standard; the upstream to the standard; the irrigation water exceeds the standard upstream sediment upstream sediment of standard sediment of irrigation upstream sediment exceeds the standard of irrigation water irrigation water water exceeds the of irrigation water exceeds the standard exceeds the standard standard exceeds the standard Range of pH value 5.66-6.47 5.4-7.93 4.93-7.73 4.42-7.42 4.83-6.94 4.97-7.26 4.96-6.40 Cadmium pollution: Content of main Cadmium pollution: Cadmium pollution: 0.49- 3.09, with a heavy metal 0.33~4.81, with one 0.52~4.86, with one Cadmium pollution: Cadmium pollution: Cadmium pollution: Cadmium pollution: small part being Ca, pollution factor point being Ca & Hg point being Ca & As 0.66-2.43 0.37-3.52 0.43-1.69 0.43-1.69 Hg & As compound Type of heavy (mg/kg) compound pollution compound pollution pollution metal pollution Standard-exceeding Standard-exceeding Standard-exceeding Standard-exceeding Standard-exceeding Standard-exceeding Cd: Cd: 0.29-3.1; Cd: 0.22-0.94; Cd: 0.21-2.5; Standard-exceeding Cd: 0.21-2.6; Cd: 0.29-1.2; 0.29-1.2; Rice heavy metal standard-exceeding As: standard-exceeding standard-exceeding Cd: 0.39-4.4; Pb, As, standard-exceeding standard-exceeding standard-exceeding As: content (mg/kg) 0.207-0.331; Pb, Cr & As: 0.208-0.247; Pb, As: 0.262-0.319; Pb, Cr & Hg did not As: 0.24; Pb, Cr & As: 0.235- 0.506g; Pb, 0.235- 0.506g; Pb, Cr & Hg Hg did not exceed the Cr & Hg did not Cr & Hg did not exceed the standard Hg did not exceed Cr & Hg did not did not exceed the standard standard exceed the standard exceed the standard the standard exceed the standard Whether it is included in local No No No Yes No No No relevant planning Whether heavy metal pollution Yes, launched vip No No No No No No Attention paid treatment has been pilot and participation conducted locally willingness Positivity to participate of farmer and Very positive Very positive Very positive Very positive Very positive Very positive Moderate agriculture professional cooperative No facilities and non-matching ratio Infrastructure 60% 30% 25% 20% 31% 55% 26% of field and construction infrastructure investment of Total investment of the project each demonstration 613.02 728.2 711 669.8 1,673.24 None area (RMB 10,000) 191 Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Dafu Town Qingtang Town Le’an Town Demonstration Area Meicheng Town Demonstration Area Demonstration Area Investment per hectare (RMB 8.36 8.34 8.33 8.37 8.37 None 10,000) Whether included in this batch of Conclusion Yes Yes Yes Yes Yes No demonstration areas 192 Table 8-7 Analysis table of selecting demonstration area in Hengyang County Name of demonstration area and comment & analysis Main factors considered in selecting demonstration area Sanhu Demonstration Area Project villages Fuxing Village Yanglin Zhonghu Area (hectares) (cultivated land area) 190.93 107.14 95.3 Regional Centralized and contiguous area representation 141.2 85.59 92.5 (hectares) Main type of cultivated land Shuitian Village Shuitian Village Shuitian Village Grain output (t/mu) 2,327 2,561 2,300 There were once two small-size recycled paper mills, three illegal Waste water and residues from the pharmaceutical companies indigenous method vanadium refining plants, etc. Incomplete environmental and livestock farms, etc. polluted the Zhengshui River and Pollution source protection measures caused the waste water to pollute the Zhengshui River irrigation using water from the Zhengshui River polluted the and irrigation using water from the Zhengshui River polluted the farmlands farmlands on both sides of the River. on both sides of the River. Is the main pollution source After treatment, the quality of irrigation water from the Pollution After treatment, the quality of irrigation water from the Zhengshui River has controllable or will it cause new Zhengshui River has reached the standard and there is no source is clear reached the standard and there is no enterprise involving heavy metal pollution to the downstream cultivated enterprise involving heavy metal pollution in and around the and pollution in and around the Demonstration Area. land Demonstration Area. controllable Whether or not there are tailings ponds and safety impact assessment No tailings No tailings on such tailings ponds. Irrigation water quality The irrigation water is Zhengshui River, the quality meets the standard and The irrigation water is Zhengshui River, the quality meets the (including upstream sediment) the sediment do not exceeds the standard. standard and the sediment do not exceeds the standard. Soil pH value range 4.8-7.9 5.6-6.9 Type of heavy Content of main heavy metal pollution Cadmium pollution: 0.24- 0.82 mg/kg Cadmium pollution: 0.18- 0.93mg/kg metal factors in soil (mg/kg) pollution Standard-exceeding Cd: 0.23—0.752; Rice heavy metal content (mg/kg) Standard-exceeding Cd: 0.159-0.521; As & Cr did not exceed the standard Pb & As did not exceed the standard Attention paid Whether it is included in local No No and relevant planning participation Whether heavy metal pollution No No willingness treatment has been conducted locally 193 Name of demonstration area and comment & analysis Main factors considered in selecting demonstration area Sanhu Demonstration Area Public positivity High Not high No facilities and non-matching ratio 15% 35% of field infrastructure Field facilities Total investment of each and demonstration area 1,078.25 / infrastructure (10,000 yuan) Unit investment 5.36 / (10,000 yuan/ha) Whether included in this round of Conclusion Yes No project implementation plan 194 Table 8-7 Analysis table of selecting demonstration area in Hengyang County Name of demonstration area and comment & analysis Main factors considered in selecting demonstration area Qingli Demonstration Area of Xidu Town Project villages Yingnan Village Tianxing Village Qingli Village Area (hectares) 160.9 136 174.4 (cultivated land area) Regional Centralized and representation 120.23 122.44 149.47 contiguous area (hectares) Main type of cultivated Paddy field Paddy field Paddy field land Grain output (t/mu) 2,400 2,380 2,450 Above all, waste water and residues from the enterprises of Waste water and residues from the Waste water and residues from the nonferrous metallurgy, plastics, glass, etc. in the Bao’an pharmaceutical companies and livestock pharmaceutical companies and livestock Village in the upper reach and livestock farms in the upper farms, etc. polluted the Zhengshui River farms, etc. polluted the Zhengshui River Pollution source reach polluted the paddy rice field. Secondly, irrigation and irrigation using water from the and irrigation using water from the using water from the Zhengshui River polluted the Zhengshui River polluted the farmlands on Zhengshui River polluted the farmlands on farmlands on both sides of the River. both sides of the River. both sides of the River. After treatment, almost all sources of pollution due to the Is the main pollution discharge of the enterprises have been cut off and the After treatment, the quality of irrigation After treatment, the quality of irrigation source controllable or will quality of irrigation water from the Zhengshui River has water from the Zhengshui River has water from the Zhengshui River has Pollution source it cause new pollution to reached the standard. There is no enterprise involving heavy reached the standard and there is no reached the standard and there is no is clear and the downstream metal pollution around the Village but a small amount of enterprise involving heavy metal pollution enterprise involving heavy metal pollution controllable cultivated land domestic sewage from the County is discharged into the in and around the Demonstration Area. in and around the Demonstration Area. paddy rice field. Whether or not there are tailings ponds and safety No tailings No tailings No tailings impact assessment on such tailings ponds. Irrigation water quality The irrigation water is Zhengshui River, The irrigation water is Zhengshui River, The irrigation water is Zhengshui River, the quality meets (including upstream the quality meets the standard and the the quality meets the standard and the the standard and the sediment do not exceeds the standard. sediment) sediment do not exceeds the standard. sediment do not exceeds the standard. Soil pH value range 5.8-7.5 59-7.3 5.1-7.9 Type of heavy metal pollution Content of main heavy Cadmium pollution: 0.31- 5.62mg/kg, Cadmium pollution: 0.25- 3.62mg/kg, Cadmium pollution: 0.38- 4.40mg/kg, metal pollution factors in Pb pollution: 48- 215mg/kg; Pb pollution: 68- 250mg/kg; Pb pollution: 52.7-288mg/kg; As pollution: soil (mg/kg) As pollution: 25-36mg/ kg As pollution: 23.6-45.3mg/ kg 13.6-47.6mg/kg 195 Name of demonstration area and comment & analysis Main factors considered in selecting demonstration area Qingli Demonstration Area of Xidu Town Standard-exceeding Cd: 0.14- 0.648; As: Rice heavy metal content Standard-exceeding Cd: 0.25- 0.63; As: 0.021- 0.354, Standard-exceeding Cd: 0.17- 0.52; 0.034- 0.289 (mg/kg) Pb: 0.132-0.45 As: 0.031-0.35, Pb: 0.015-0.35 Pb< 0.02-0.351 Whether it is included in No No No local relevant planning Attention paid Whether heavy metal and participation pollution treatment has No No No willingness been conducted locally Public positivity Not high Not high High No facilities and non-matching ratio of 30% 20% 12% field infrastructure Field facilities Total investment of each and infrastructure demonstration area / / 459.96 (10,000 yuan) Unit investment / / 3.97 (10,000 yuan/ha) Whether included in this Conclusion round of project No No Yes implementation plan Table 8-8 Analysis table of selecting demonstration area in Hengnan County Name of demonstration area and comment & analysis Main factors considered in comparison and Songjiang Demonstration selection of demonstration area Xiangyang Demonstration Area Quanxi Demonstration Area Area Selected villages in Chaoyang Village Huanghe Village Songjiang Community Quanchang Village the demonstration area Regional Area, hectares 156.7 220.6 105.7 139. representation Centralized and 94.6 173.3 74.2 114.5 contiguous area, 196 Name of demonstration area and comment & analysis Main factors considered in comparison and Songjiang Demonstration selection of demonstration area Xiangyang Demonstration Area Quanxi Demonstration Area Area hectares Main type of Shuitian Village Shuitian Village Shuitian Village Shuitian Village cultivated land Whether it belongs to The grain output per mu is 1227 t / the main grain The grain output per mu is 815 t / year The grain output per mu is 1004 t / year year producing area Clear: pollution caused by the Clear: major flooding Whether the heavy Clear: the main pollution source of this Clear: the main pollution source of this discharge of chemical plants consecutively in 2006 and 2007 metal pollution cause demonstration area is the historical demonstration area is the historical along the two sides of the caused the Leishui River to flow is clear pollution of Xiangjiang River pollution of Xiangjiang River. Xiangjiang River. backward Environmental rehabilitation has been Environmental rehabilitation has been Is the main pollution conducted to the enterprises in the conducted to the enterprises in the With the clean-up and control in source controllable or Region involving in heavy metal Region involving in heavy metal recent years, silt, pollutants and will it cause new pollution. In the meantime, the source of pollution. In the meantime, the source of Pollution source is not foreign organisms caused by pollution to the pollution can be almost controlled due pollution can be almost controlled due to controllable previous floods have been downstream cultivated to the measures such as the change of the measures such as the change of basically cleaned up and no new Pollution source land source of irrigation, etc. No new source of irrigation, etc. No new pollution will be produced. is clear and pollution will be caused. pollution will be caused. controllable Whether or not the tailings pond, if any, is None None None None safe and free of any leakage. The irrigation water is Shantang, The irrigation water is Leishui Shantang in the village is basically used Irrigation water Ouyanghai irrigation canal and River and the quality can meet the as the irrigation water and the quality quality (including Shuangbanqiao Reservoir and the quality standard; meets the standard. The upstream / irrigation water meets the standard. The upstream The upstream sediment of sediment of irrigation water exceeds the sediment) sediment of irrigation water exceeds the irrigation water exceeds the standard standard standard Soil pH value range 4.68-7.69 5.58-7.32 5.35-6.54 Content of main heavy Cadmium pollution: Cadmium pollution: 0.608-14.60 mg/kg; Pb pollution: 43.1-648 mg/kg; Cadmium pollution: 0.627-3.57 metal pollution factors 0.28-4.53 mg/kg; Pb As pollution: 6.04-147.69 mg/ kg mg/kg; in soil (mg/kg) pollution: 57.2-321 mg/kg; Type of heavy Standard-exceeding Cd: Standard-exceeding Cd: metal pollution 0.028-0.32mg/kg; 0.01-0.514mg/kg; Standard-exceeding Cd: 0.102-2.872mg/kg; standard-exceeding As: 0.106-0.33 Rice heavy metal standard-exceeding As: standard-exceeding As: mg/kg, content (mg/kg) 0.12-0.29 mg/kg; 0.157-0.278 mg/kg; Standard-exceeding Pb: 0.027-0.302 mg/kg standard-exceeding Pb: standard-exceeding Pb: 0.01-0.32 0.01-0.35 mg/kg mg/kg Attention paid Whether it is included and participation in local relevant No No No No willingness planning 197 Name of demonstration area and comment & analysis Main factors considered in comparison and Songjiang Demonstration selection of demonstration area Xiangyang Demonstration Area Quanxi Demonstration Area Area Whether heavy metal pollution treatment has No No No No been conducted locally Positivity to participate of farmer and agriculture Very positive Very positive Moderate Very positive professional cooperative No facilities and non-matching ratio of 25% 18% / 20% field infrastructure Infrastructure and Total investment of construction each demonstration investment of the 283.08 246.42 / 300.88 area project (10,000 yuan) Unit investment (RMB 3.86 3.70 / 3.76 10,000/ha) Whether included in Conclusion this batch of Yes Yes No Yes demonstration areas 198 Table 8-9 Analysis table of selecting demonstration area in Lengshuitan District Main factors considered in comparison and Name of demonstration area and comment & analysis selection of demonstration area Xianghuaba Demonstration Area Shixi Village Demonstration Area Niujiaoba Demonstration Area Quhe Demonstration Area Selected villages in the Xiangshanjie Village, Yangsi Xianghuaba Village Shixijiang Village Quhe Sub-district demonstration area Temple Area, hectares 340 186.66 430 150 Centralized and Regional contiguous area, 296 152.5 322 113 representation hectares Main type of cultivated Paddy field Paddy field Paddy field Paddy field land Whether it belongs to the main grain The grain output is 2133 t/year The grain output is 2389 t/year The grain output is 2219 t/year The grain output is 2120 t/year producing area Clear: Yongzhou Xinhai Smelting Clear: manganese ores, coal cores Whether the heavy Clear: soil pollution caused by Clear: soil pollution caused by Co., Ltd., Longtao Smelter, and silica ores as the source of metal pollution cause is historical pollution sources of historical pollution sources of Longxiaolin Smelter and other pollution carried over from the past clear manganese and coal mines manganese and coal mines enterprises involving heavy metal cause the soil pollution. pollution lead to soil pollution Is the main pollution Industrial and mining enterprises Industrial and mining enterprises Industrial and mining enterprises Enterprises in the Region involving source controllable or were closed down, illegal mining were closed down, illegal mining were closed down, illegal mining heavy metal pollution are closed will it cause new prohibited and solid wastes left over prohibited and solid wastes left prohibited and solid wastes left and knocked out. Residues left over pollution to the from the past treated. The source of over from the past treated. The over from the past treated. The from the past are treated and the Pollution source is downstream cultivated pollution is controllable. source of pollution is controllable. source of pollution is controllable. source of pollution is controllable. clear and land controllable Whether or not the tailings pond, if any, is None None None None safe and free of any leakage. The water from Dengjiachong The irrigation water is Lanjiang Irrigation water quality Reservoir is used as irrigation water River and its quality can meet the The irrigation water is Xiangjiang (including irrigation and the quality of irrigation water is standard; the upstream sediment of The irrigation water is Shixi River River water sediment) up to the standard; the upstream irrigation water can meet the sediment of irrigation water is up to standard 199 Main factors considered in comparison and Name of demonstration area and comment & analysis selection of demonstration area Xianghuaba Demonstration Area Shixi Village Demonstration Area Niujiaoba Demonstration Area Quhe Demonstration Area the standard Range of pH value 5.6-7.7 5.4-7.0 4.6-7.8 6.5-7.8 Content of main heavy Cadmium pollution: 0.26- Cadmium pollution: 0.23- Cadmium pollution: 0.27- 0.46 metal pollution factor Cadmium pollution: 0.1- 0.92 mg/kg 0.69mg/kg, 0.94mg/kg, mg/kg Type of heavy (mg/kg) As pollution 7.22- 21.7mg/kg As pollution 8.96- 31mg/kg metal pollution Standard-exceeding Cd: Standard-exceeding Cd: 0.008- Standard-exceeding Cd: 0.02- 0.007-0.634mg/kg; Standard-exceeding Cd: Rice heavy metal 0.404mg/kg; 0.548mg/kg; standard-exceeding standard-exceeding As: 0.11-0.68mg/kg; As & Pb did not content (mg/kg) Standard-exceeding Cd: 0.105-0.521; As: 0.081-0.217mg/kg; Pb & Cr 0.073-0.326 mg/kg; Pb did not exceed the standard Pb & Cr did not exceed the standard did not exceed the standard exceed the standard Whether it is included in local relevant No No No No planning Whether heavy metal Attention paid and pollution treatment has No No No No participation been conducted locally willingness Positivity to participate of farmer and The willingness of public Very positive Very positive Very positive agriculture professional participation is not strong cooperative No facilities and non-matching ratio of 20% 25% 22% 15% Infrastructure and field infrastructure construction Total investment of investment of the each demonstration 1,028.52 522.28 258.8 / project area (RMB 10,000) Investment per hectare 5.93 6.53 6.47 / (RMB 10,000) Whether included in Conclusion this batch of Yes Yes Yes No demonstration areas 200 201 Table 8-10 Analysis table of selecting demonstration area in Linwu County Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Nanqiang Demonstration Wushui Demonstration Area Shuidong Demonstration Area Area Xiangtang Village, Selected villages in the Zhenshang village, Yaofeng Zhaijiang Village, Liantang Dongjiang Village Litouzui Village Xinhua Village Hongxing Village demonstration area Village Village Area, hectares 37.33 62.59 6.67 5.45 23.33 20.56 Regional Centralized and contiguous 31.73 53.2 5.67 3.26 19.83 16.32 representation area, hectares Main type of cultivated land Paddy field Paddy field Paddy field Paddy field Paddy field Paddy field The grain output The grain output Whether it belongs to the main The grain output per mu is The grain output per mu is The grain output per mu is The grain output per per mu is 700 per mu is 700 grain producing area 700 kg/year 700 kg/year 700 kg/year mu is 700 kg/year kg/year kg/year Whether the heavy metal Clear: historical Clear: historical Clear: historical Clear: historical pollution Clear: historical pollution Clear: historical pollution pollution cause is clear pollution pollution pollution Is the main pollution source controllable or will it cause Controllable pollution Controllable pollution Controllable Controllable Controllable Controllable pollution source new pollution to the source source pollution source pollution source pollution source downstream cultivated land Whether or not the tailings pond, if any, is safe and free of None None None None None None Pollution source is any leakage. clear and controllable The irrigation water The irrigation water is Wushui The irrigation water is The irrigation water is is Shuidong River The irrigation The irrigation River and the indicator of Renmin River and the Shuidong River and the and the quality can water is Shuidong water is Shuidong Irrigation water quality water heavy metal is up to quality can meet the quality can meet the meet the standard; River and the River and the (including irrigation water standard; standard;； standard; The upstream quality can meet quality can meet sediment) The upstream sediment of The upstream sediment of The upstream sediment of sediment of the standard; the standard; irrigation water exceeds the irrigation water exceeds the irrigation water exceeds irrigation water standard standard the standard exceeds the standard Range of pH value 5.14～67.52 7.27～8.12 6.41～7.57 No data yet 5.40～5.65 No data yet Type of heavy Cd Content of main heavy metal Cd 0.344-0.878mg/kg, Hg Cd 0.67-10.0mg/kg, As metal pollution Cd 0.48-0.69mg/kg and As 0.839-1.31mg/kg pollution factors in soil 0.139-0.487mg/kg and As 25.1-65.2mg/kg and Hg No data yet No data yet 15.7-38.6mg/kg and As (mg/kg) 15.6-24.9mg/kg 0.12-1.06mg/kg 21.8-64.0mg/kg 202 Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Nanqiang Demonstration Wushui Demonstration Area Shuidong Demonstration Area Area Cd pollution is at Cd pollution is at low and Cd pollution is at low and Cd pollution is at low risk Rice heavy metal content high risk and As medium risk and As pollution medium risk and As and As pollution is at low No data yet No data yet (mg/kg) pollution is at is at medium risk pollution is at medium risk risk medium risk Whether it is included in local No No No No No No relevant planning Whether heavy metal Attention paid and pollution treatment has been No No No No No No participation conducted locally willingness Positivity to participate of The willingness is The willingness is farmer and agriculture Very positive Very positive Very positive Very positive not strong not strong professional cooperative No facilities and non-matching ratio of field 65% 75% 70% 70% 70% 70% Infrastructure infrastructure construction Total investment of each investment of the demonstration area (RMB 174.41 240.35 26.28 / 91.92 / project 10,000) Investment per hectare (RMB 4.94 3.84 3.94 / 3.94 / 10,000) Whether included in this batch Conclusion Yes Yes Yes No Yes No of demonstration areas 203 Table 8-11 Analysis table of selecting demonstration area in Qiyang County Name of demonstration area and comment & analysis Main factors considered in comparison and selection of demonstration area Xiaojia Demonstration Area Selected villages in the demonstration area Tongzi Village, Jiuniba Village Xiaojia Village Area, hectares 73.33 76.56 Regional Centralized and contiguous area, hectares 71.86 70.28 representation Main type of cultivated land Shuitian Village Shuitian Village Whether it belongs to the main grain producing area Yes Yes Clear: the soil is polluted by waste residue, slag and Clear: the soil is polluted by waste residue, slag and Whether the heavy metal pollution cause is clear waste water from iron and manganese mining waste water from iron and manganese mining The mining time was in the 1990s, which was in small The mining time was in the 1990s, which was in small Is the main pollution source controllable or will it cause new scale. It was closed at the end of 1990s. The slag was scale. It was closed at the end of 1990s. The slag was Pollution source is pollution to the downstream cultivated land cleaned up and the pollution source was controllable cleaned up and the pollution source was controllable clear and Whether or not the tailings pond, if any, is safe and free of any controllable None None leakage. The irrigation water is Dajiangbian Reservoir and the The irrigation water is Dajiangbian Reservoir and the Irrigation water quality (including irrigation water sediment) quality can meet the standard; quality can meet the standard; The sediment of irrigation water exceeds the standard The sediment of irrigation water exceeds the standard Range of pH value 5.15-6.43 No data yet Type of heavy metal Content of main heavy metal pollution factor (mg/kg) Cadmium pollution: 0.31~ 0.67 No data yet pollution Standard-exceeding Cd: 0.028- 0.70mg/kg; Rice heavy metal content (mg/kg) standard-exceeding As: 0.10-0.42mg/kg; Pb, Hg & Cr No data yet did not exceed the standard Whether it is included in local relevant planning No No Attention paid and Whether heavy metal pollution treatment has been conducted participation No No locally willingness Positivity to participate of farmer and agriculture professional Very positive The willingness is not strong cooperative Infrastructure and No facilities and non-matching ratio of field infrastructure 47% 50% construction Total investment of each demonstration area (RMB 10,000) 579.3 / investment of the project Investment per hectare (RMB 10,000) 7.9 / Conclusion Whether included in this batch of demonstration areas Yes No 204 Attached Figure 1-1 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Yongding District 205 Attached Figure 1-2 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Jishou City 206 Attached Figure 1-3 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Yongshun County 207 Attached Figure 1-4 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Cili County 208 Diagrammatic Sketch of Location of Demonstration Area of Integrated Management of Agricultural Land Pollution Project with World Bank Loan in Huayuan County Attached Figure 1-5 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Huayuan County 209 Attached Figure 1-6 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Anhua County 210 Note: The blue area means the implementation scope of the new expansion project village sediment monitoring point monitoring section of surface water Attached Figure 1-7 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Hengyang County 211 Xiangxi Modern Professional Agricultural Cooperative (Lianhua Village, Jinxiangyan Planting and Breading Cooperatives (Maiyuan Chashi Town) Village, Huaqiao Town) Xiangjian Organic Fruit Tree, Livestock, Agriculture and Fishery Production and Marketing Cooperatives (Xiaoxiang Village, Songjiang Town) Agricultural Material Recycling Station of Hengnan County (Baohe Community, Yunji Town) sediment monitoring point monitoring section of surface water Attached Figure 1-8 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Hengnan County 212 Attached Figure 1-9 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Lengshuitan District 213 Attached Figure 1-10 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Linwu County 1 Attached Figure 1-11 Diagrammatic Sketch of Location of Demonstration Area and Distribution of Environmental Sensitive Points and Scope of Evaluation in Qiyang County 2