E-380 VOL. 3 Huai River Water Pollution Control Project Environmental Assessment SCMN" LErC. Summary P4L {. w ZIpnatn .) LfICr GRJTF ESW CdTRg An F- t L _7_ f L_ ! September 2000 -~~~~~~~~~~~~~~~~~~~~;. .cf ~ ~ ~ D = ..- . .--r .~ , - -~~ .. - ., * - ~ '*.. '->~_,o, .e.-' -, -$- ,- ' p9_- .__ - * 7_ 2 Z .'. ~- . '7-~~ ~~~~~ ,-, "i7__ - 'M_ ,S, . , , _, Anhui Provincial PMO Shandong Provincial PMO with assistance from Mott MacDonald/ERM Huai River Water Pollution Control Project Environmental Assessment Summary Table of Contents 1 Overview . 2 Huai River Basinn.I 2.1 General .1 2.2 Anhui Province .2 2.3 Shandong Province .3 3 HRWPCP Project Goals and Objectives ............................3 4 Need for the Project ............................3 5 The Prioritisation of Schemes ..4.........................4 6 Overview of HRWPCP Components ..5 6.1 Anhui Province .5 6.2 Shandong Province .6 6.3 Implementation Schedule .7 6.4 Technical Assistance .7 7 Water and Environmental Objectives ...................................8 8 Project Benefits and Impacts ...................................8 8.1 Project Benefits ...8...............................8 8.2 Social Impacts ...................................9 8.3 Environmental Impacts ...................................9 9 Alternatives Reviewed in Project Development ................................... 10 10 Mitigation and Monitoring ...................................11 10.1 Mitigation and Monitoring Budget .................................. 11 10.2 Annual Environmental Quality Report .................................. 12 11 Public Participation in the Environmental Assessment ..14 12 Overall HRWPCP Project Assessment ..14 12.1 COD Removed, Anhui Province .15 12.2 COD Removed, Shandong Proince .16 13 Conclusions and Recommendations ..18 14 Ongoing Activities ..20 15 Attached Figures ..20 S-i September 2000 Huai River Water Pollution Control Project Environmental' Assessment Summary Currency Equivalents (Exchange Rate Effective October 1999) Currency Name: Renminbi Currency Unit: RMB RMB 8.3 = US$1.00 US$0.12 =RMB 1.0 Abbreviations and Acronyms AC Advisory Consultant NCMEDI North China Mun Eng Design Institute AIC Average Incremental Cost OD Oxygen Demand AP Action Plan for IDP PAD Project Appraisal Document (WB) ATP Ability to Pay PAP Project Affected Person BOD Biochemical Oxygen Demand PIP Project Implementation Plan COD Chemical Oxygen Demand PIU Project Implementation Unit (Municipal) DHV DHV Consult. BV/D&J Eng Consult. Co PMO Project Management Office (Provincial) DO Dissolved Oxygen PPP Project Procurement Plan DRICSI 9h Design & Research Institute for PRC People's Republic of China China Shipbuilding Industry PS Pumping Station DWF Dry Weather Flow (sewage) PV Present Value EA Environmental Assessment RAP Resettlement Action Plan EIRR Economic Internal Rate of Return RMC Resident Mission in China EMP Environmental Management Plan RMDI Rizhao Municipal Design Institute EPB Environmental Protection Bureau SDPC State Development and Planning Commission ERM Environmental Resource Management SEPA State Environmental Planning Agency FIRR Financial Internal Rate of Return SLIDI Shandong Light Industry Design Institute FSR Feasibility Study Report SS Suspended Solids HRBC Huai River Basin Commission SUCDRI Shandong Urban Construction Design HRWPCP Huai River Water Pollution Research Institute Control Project TVE Town and Village Enterprise IDC Interest During Construction WB World Bank (International Bank for IDP Institutional Development Plan Reconstruction and Development) IST Institutional Strengthening and Training WRB Water Resources Bureau JMEDI Jinan Municipal Engineering Design WSC Water Supply Company Institute WTP Willingness to Pay LG Leading Group WTW Water Treatment Works lI/c/d Litres per capita per day WWC Wastewater Enterprise LIBOR London Inter-bank Borrowing Rate WwTW Wastewater Treatment Works MLG Municipal Local Government MoF State Ministry of Finance NB: SI units of measurement have been used throughout this report S-ii September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary 1 OVERVIEW This report provides a brief summary of the major findings in the two Provincial Environmental Assessment (EA) Reports produced for Anhui and Shandong Provinces, under the Huai River Water Pollution Control Project (HRWPCP). The Provincial EA for Anhui Province was conducted by the Hefei Design Institute (HDI), under the Ministry of Coal Industry. The Provincial EA for Shandong Province was conducted by the Shandong Scientific Research and Design Institute of Environmental Protection (SIEP), under the Shandong Provincial Environmental Protection Bureau (EPB) in Jinan. Both of the English versions of these EA reports were prepared with the assistance of the AC (Mott MacDonald and ERM International). The full Provincial EA reports cover the assessment of the environment impacts of the project components to be undertaken under the HRWPCP in each Provinces. The EA reports were prepared as Category B, as directed by the World Bank (WB). Full Resettlement Action Plans (RAPs) were prepared in each Province and the findings incorporated into the EA reports. The EA reports were prepared in both Chinese and English versions. The Chinese versions of these EAs were submitted to the Chinese State Environmental Protection Agency (SEPA) for approval. Both the Anhui Provincial EA and Shandong Provincial EA were approved by SEPA in September 2000. The final English versions of the provincial EAs were submitted to the WB in August 2000. 2 HUAI RIVER BASIN 2.1 General The Huai River Basin lies across four provinces in the centre of China, covering an area of 270,000 km2 between the Yangtze and Yellow Rivers and the Yellow Sea. The Basin is divided into two major systems: (1) The Huai River System (190,000 ki2), originating from Mt.Tongbo in Henan Province and about 1,000 km long with 120 tributaries, flows east through Anhui Province to Hongze Lake, through Jiangsu Province and discharges into the Yangtze River. (2) The Yi-Shu-Si River System (80,000 km2) originates in Shandong, flows south to Jiangsu Province and discharges into the Yellow Sea. The Grand Canal in the east connects the Huai River and Yi-Shu-Si systems as well as the Yangtze and Yellow Rivers. The economic and environmental impacts of water pollution on the Huai River Basin area are widespread and acute. In 1994, severe water pollution caused temporary production stoppage at many factories and drinking water problems for many inhabitants in the Huai River Basin. The 1994 Huai River pollution incident was caused by the discharge of polluted wastewater from many straw pulp factories, paper mills, and tanneries in Henan Province and Anhui Province located in the upstream portion of the Ying He River. These industries discharged a great quantity of polluted wastewater during the dry season when river control gates were often closed; 60-70 % of the annual river flow occurs during May-August time period, the gates are closed during the dry season for storage purposes. During the flood season the river control gates were opened releasing the concentrated stored pollution. This sudden increase in pollution of downstream sections of the Ying He River caused power station malfunction and consequently major impacts on the Hua Dong power network. Furthermore, fishery resources were destroyed and agricultural and industrial damages were widespread. Urban water sources were also affected resulting in significant shortages for the S-1 September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary inhabitants of the downstream cities. Direct economic damages were estimated at over one billion yuan. Consequently the State Council authorised various actions to combat water pollution and prevent future pollution disasters in the Huai River Basin. The central government approved the "Ninth Five- Year Plan (1996-2000) of Water Pollution Control" (WPCP) in June of 1996. The WPCP defined targets for the Huai River Basin as follows: * By 1997, all the wastewater discharges from industrial pollution sources should meet standards for effluent and the total Basin COD should be reduced from 1.5 million tons in 1993 to 0.89 million tons (including 0.207 million tons from Anhui Province and 0.264 million tons from Shandong Province); * By 2000, the total Basin COD should be reduced to 0.368 million tons (including 77,000 tons from Anhui Province and 64,700 tons from Shandong Province); * By 2000, the Huai River mainstream, main tributaries, and rivers that are sources for urban water supplies, should reach the Class m of the National Surface Water Standard. As part of the efforts of the State Council and the four Huai basin provinces (i.e. Henan, Anhui, Jiangsu and Shandong) to meet water pollution control targets, the Huai River Water Pollution Control Project (HRWPCP) is currently being prepared for Anhui and Shandong Provinces. At the request of the PRC, the WB has listed the proposed project in the lending programme for WB fiscal year 2001. Water pollution control in Henan and Jiangsu is being dealt with under separate programmes. As described below, despite significant efforts, including the closure of a large number of polluting industries, the targets listed above are far from being achieved, with provision of municipal wastewater control facilities in particular lagging far behind programme. This project will thus be a significant step towards achieving the proposed pollution reduction targets and, through the associated technical assistance activities, will help to provide the necessary skills and experience to execute further projects within the plan. 2.2 Anhui Province Anhui Province extends over the centre of the Huai River Basin. The Huai River mainstream flows through the centre of Anhui Province with major tributaries located both north and south. See Figure S-1 for the locations of the Huai River mainstream and major tributaries in Anhui and Shandong Provinces. (Note, all figures are located at the end of this Summary). The length of the mainstream of the Huai River in the province is 420 km and the length of the tributaries is 1,580 km. River pollution is mainly organic, with sections in urban reaches being more polluted than rural reaches, and pollution in tributaries being more serious than in the mainstream reaches. Anhui Province is approximately 139,400 krn2, of which 66,940 km2 is located within the Huai River Basin (24.8% of the total basin area). The total 1998 population of Anhui Province was 61.3 million, with 11.2 million in urban areas, of this, 34.7 million were within the Huai River Basin including 4.6 million in urban areas. S-2 September 2000 Huai River Water Pollution Control Project Figure S-1 Location of Project Sub-components , ~~BOHAI SEA NSN' ^\ J N AS ,~~~~S Or*z >_k¢Z >= ' */- > '! 2t <~~~~~ Figure 3.1 ~~~~~~~~~ < a St~~HEE Ozv < S 5} A 5' H 1; 1 ,J} ~~~Figure 2.1 > > t W J ~~~~~~~~~~SHAGH ° CITY WITH SEWERAGE PROJECT * PROVINCIAL CAPITAL PROVINCIAL BOUNDARY * CITY WITH SEWERAGE AND WwTW PROJECT COASTLINE HUAI RIVER BASIN (PLANNING BOUNDARY) A INDUSTRIAL POLLUTION CONTROL PROJECT PRINCIPAL RIVER --HUAI RIVER BASIN (NATURAL DRAINAGE BOUNDARE Huai River Water Pollution Control Project Environmental Assessment Summary 2.3 Shandong Province Shandong Province includes most of the Yi-Shu-Si System of the Huai River Basin. This system is hydrologically connected to the Huai River via the Grand Canal but actually flows directly to the Yellow Sea. Pollution is mainly organic, with sections in urban reaches being more polluted than rural reaches. Shandong Province is approximately 156,700 km2, of which 47,100 km2 is located within the Huai River Basin (17.4% of the total basin area). The total 1998 population of Shandong Province was 86.10 million, with 23 rnillion in urban areas. Of this, about 30 million were within the Huai River Basin including 1.2 million in urban areas. 3 HRWPCP PROJECT GOALS AND OBJECTIVES In order to fully solve the pollution problems in the two provinces, major pollution control schemes will need to be developed for most cities. It is not possible to finance all necessary works in one step. It is therefore foreseen that further phases of the HRWPCP will be needed over the coming years. In accordance with the national WB policies and priorities, the Anhui and Shandong Provincial Governments have requested WB and bi-lateral donor support for the Huai River Water Pollution Control Project. The HRWPCP is also a key element of China's Agenda 21 programme. The sector- related goal for the project is: Improve quality of water for the entire basin by providing environmental infrastructure operated in a sustainable manner The HRWPCP objectives are to: 1. Upgrade water quality in the Huai River (Class El[ target) and its tributaries (Class IV target) within the two provinces. 2. Establish performing and efficient wastewater agencies. 3. Consolidate water quality monitoring systems and procedures. To accomplish this goal and objectives, the outputs for each project component are: 1. Increase in municipal wastewater collection. 2. Increase in quantity of wastewater treated. 3. Implementation of cost-recovery for wastewater operations. 4. Improved water quality monitoring systems and procedures. 4 NEED FOR THE PROJECT According to the draft "3H Basins Action Program Study for Water Resources, Water Pollution Control" prepared in November 1999 for the Ministry of Water Resources and the WB (known as the '3H Study since it covers the Hai, Huai, and Huang rivers), the WPCP goals have not been met in the Huai River basin. This report indicates that significant additional resources are required to meet the Class 11/IV river target standards of the WPCP, and that rural sources such as uncontrolled township and village enterprises (TVEs) and non-point source pollution (mainly polluted agricultural and urban surface water runoff) will remain a problem even after implementation of industrial controls and domestic wastewater treatment facilities. S-3 September 2000 Huai River Wawer Pollution Control Project Environmental Assessment Summary Implementation of industrial and domestic wastewater treatment lags behind the WPCP implementation schedule due to funding problems. The main pollutants are unionised ammonia, BOD, COD and bacteria levels, and the problems are especially acute in the dry seasons when background flows are reduced to at or near zero levels. Environmental resources are minimal and the assimilative capacity of the surface waters during low-flow periods is virtually zero. In summnary, the water quality problems in the Huai River Basin remain severe, the implementation of municipal wastewater treatment facilities has been slow, and the HRWPCP is targeted to support a major need. It is the national goal to have wastewater collection and secondary treatment facilities constructed in all cities within the Huai River Basin. A number of the cities in the basin have completed or are currently building wastewater collection and treatment facilities with international bi-lateral assistance. The HRWPCP is designed to help meet overall basin objectives by supplementing these ongoing efforts in the larger cities of Anhui and Shandong provinces that have not been addressed by other projects. In 1999, the Chinese Research Academy of Environmental Sciences (CRAES) selected 45 major stations to investigate the current water quality of the Huai River Basin. Data from national environmental water quality reports between 1986 and 1993, 1994 for the Huai mainstream, 1995 to 1996 for trans-boundary assessments and some incomplete data from 1997 and 1998 were used by CRAES to determine the existing water quality of the river basin. CRAES (1999) reported that of the 45 sections, only 4 reached their designated beneficial use classification. Pacific Consultants and the Danish Hydraulic Institute in 1999 estimated the total COD loading in Anhui Province as of 1997 at over 363,000 t/a. Data on year 2000 loading is difficult to obtain and verify, but it is likely closer to this 1997 estimate than to the WPCP goal for 2000 in Anhui Province of 77,000 tla. The Anhui HRWPCP treatment facilities (Luan and Guoyang) will remove approximately 7,008 t/a of COD (ultimate WwTW sizing removes 11,498 t/a of COD), while the related bi-lateral treatment facilities will remove an additional 48,618 t/a of COD. This total ultimate COD removal of 60,116 t/a can be seen to be a good start for Anhui Province, but far short of the overall WPCP needs in the province. It is undoubtedly true that the total COD loading in 1997 in Shandong Province also exceeds the WPCP goals, but verifiable data is not readily available. Although municipal and industrial wastewater loads were included in the plan goal for 1997, the WPCP did not account for the "other" sources of COD in the basin. In addition, the progress in achieving municipal and industrial pollution control since 1997 has lagged behind plan goals so that the year 2000 goals of 64,700 tons for Shandong province have not been met. SIEP estimates that the current year 2000 COD loading in Shandong Province is approximately 213,000 t/year, including TVEs and non-point source pollution. The HRWPCP projects will remove approximately 37,145 t/year of COD, leaving the overall Shandong loading well in excess of the target of 67,400 t/year. 5 THE PRIORITISATION OF SCHEMES Provision of municipal wastewater collection and treatment facilities in the cities of the Huai River Basin is a priority action item in the WPCP, and a critical component shown in the 3H Rivers Action S-4 September 2000 Huai River Watwr Pollution Control Project Environentar Assessment Summary Plan. The WPCP anticipated that much of the construction of wastewater collection and treatment facilities would be completed by the year 2000, but the programme is running well behind schedule. Table S-1 provides a listing of the cities and overall municipal treatment needs in the Huai River Basin, as shown in the 3H Action Plan. The project cities supported by the HRWPCP in Anhui and Shandong provinces are highlighted. Table S-1 illustrates the enormous backlog of municipal wastewater treatment needs in the Basin that require additional funding. Thus the HRWPCP is part of a much larger comprehensive effort to control industrial and municipal pollution in the Huai Basin. This project has been designed to complement the activities already underway in order to move more quickly toward WPCP goals. Table S-1: Overall Municipal Treatment Needs in Basin WwTW Capital No. of WwTW Capital No. of WwTW Capital No. of City/Country Cost (RMB WwTWs City/County Cost (RMB WwTWs City/Country Cost (RMB WwTWs million) rnillion) million) Baofeng 45 1 LUnquan 58 I Wugang 90 1 Bengbu* 150 1 _ Linyi 154 1 Xiangcheng 191 2 Bozbou* 60 1 _ I Lingying 45 1 Xiaoxian 16 1 Cangshan I 60 1 _ Luan 5o0 I Y Xinrni 18 I Chang | 65 1 Luohe 114 1 Xinyang 70 1 Chuzhou 80 1 Mengecheng 42 1 Xinyang 44.5 2 Dengfen 63 1 I Mengyin 49 1 Xinyi 7 Peixian 54 1 Mingguang 60 1 Xinzheng 25.5 Fengtai 32 1 Minquan 20 1 Xiping 50 Fengxian 10 1 1I_ | Peizhou 6 1 Xuchany 127 I Feicheng** 50 1 | Pingdingshan 228 1 Xuecheng 50 1 Fuyang* 8 S0 I Q Qufu 11 I Xuzhou 100 2 Gansu 53 1 Rizhao*** 36 1 Yancheng 150 i Guoyang* 50 1 | Shangiu 144 I Yangzhou 160 1 Guanyuanxian 52 1 1= Shanqui 74 2 Yan.zhou 132 1 Guozhenxian 28 1 1 Sihong 8 1 Yinan 50 1 Haian 100 1 _ _ I SIshui 50 1 Yishui 95 1 Huaibel 60 1 Suiping 50 1 Yantai 32 2 Huaiyin | 45 1 | Sugian 53 1 _ Yuzhou 60 1 Huaian* 48 I Suzhou | 50 1 1 = Zaozhuang 105 I Heze** 80 1 1_ | Taihe 34 1 _ Zhengzhou 640 1 Jieshou 70 | __ | Tengzhou 186 I Zhumadian 170 1 Jining 426 I Tainchang 60 1 Zhuokou 100 Ioo Kaifeng 165 Tongshan 3 1 Zoucheng 97 Lianyunggang 136 2 Woyang 60 1 Note: * HRWPCP Project City, Anhui/Shandong Provinces, in 3H Action Plan ** HRWPCP Project City, Anhui/Shandong Provinces, not in 3H Action Plan *** Rizhao Municipality contains Rizhao City and Ju County Project Area 6 OVERVIEW OF HRWPCP COMPONENTS 6.1 Anhui Province The HRWPCP is designed to supplement these ongoing efforts in the mnajor cities of the Anhui Province that have not been addressed by other projects. Table S-2 shows the projects that are proposed for the HRWPCP in Anhui Province: S-5 September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary Table S-2: HRWPCP-Anhui Province Components Sewerage Sewerage Sewerage Total Pump Treatment plant Project Main-pipe Sub-pipe Pumping Mains Length station capacity City (km) (km) (km) (No.) (m3/d) Bozhou 56.3 50.0 106.3 4 . Bi-lateral Huaibei 63.8 35.0 98.8 5 Bi-lateral Guoyang 37.3 35.0 72.3 1 40,000 Suzhou 52 22.0 74.0 3 Bi-lateral Fuyang 817 50.0 3 134.7 4 Bi-lateral Bengbu 78.9 60.0 1.61 140.5 3 Bi-lateral Huainan 48.6 39.0 2.6 90.2 4 Bi-lateral Lu'an 32.5 5 2.4 39.9 3 40,000 Total 451.1 296 9.61 756.7 27 80,000 Figures S-2 to S-9 provide schematics of the proposed Anhui project components. It is proposed to take thickened and dewatered sludge from the WwTW at Guoyang and Lu'an to sanitary landfill sites near the cities. The Anhui Component also includes a sub-component to strengthen the capability of the Anhui Environmental Monitoring Centres operated by the Provincial and municipal EPBs. The sub- component will include rehabilitation of laboratory facilities, water quality sampling and analysis equipment and training. 6.2 Shandong Province Shandong Province is currently proposing four municipal wastewater schemes and one industrial pollution control sub-component for inclusion in the HRWPCP. All the municipal wastewater schemes involve improvement and extension of existing sewerage networks and three include new WwTWs. Most of the sub-components also include operation and maintenance equipment including laboratory equipment and vehicles. The Rizhao City component also includes construction of sea outfalls. One of the cities, Ju County, already has a WwTW under construction using local funding. Hence, this WwTW is outside of this project. The sewerage schemes will involve both the interception of existing municipal sewage and industrial wastewater outfalls and provision of first wastewater collection in more recently developed areas of the cities. Wastewater will be conveyed to WwTWs and will make a major contribution to control of water pollution in the Huai River Basin, and in the case of Rizhao, control pollution in off-shore waters and nearby bathing beaches. Table S-3 shows the project details that are proposed for the HRWPCP in Shandong Province: S-6 September 2000 Huai River Water Pollution Control Project Environmental Assessment Sunmary Table S-3: Proposed Sewerage in Shandong Province Sewerage Sewerage Sewerage Total Pump Treatment plant Project Main-pipe Sub-pipe Pumping Mains Length station capacity City (km) (km) (km) (No.) (m3/d) Feicheng 19.5 19.5 40,000 Heze 26.2 28.4 54.6 4 80,000 Rizhao 31.1 8.5 8.5 3 100,000 Ju County 15.0 15.0 Local funded Chengwu 0 20,000 (WWTP) Paper Mill 1300 (Black liquor) Total 91.8 28A 8.5 128.70 7 220,000 (municipal _ _ _ _ _ _ _ _ _ _ _ ~~~~~~~~~WWTP) Notes: Feicheng also includes 7 km of DN3 15 PVC recycled effluent pressure main. Rizhao also includes 2.8km DN 1600 pressure pipe to header chamber, 2.5km twin DN1200 outfall and 0.5km DN1200 emergency outfall. Figures S-10 to S-14 provide schematics of the proposed Shandong project components. 6.3 Implementation Schedule An overall implementation program for the current phase of the HRWPCP is shown in Table S-4, based on WB appraisal in late 2000. Individual component implementation programmes can be found in the sub-component PIPs and PPPs. Table S-4: HRWPCP Implementation Programme Year 2000 2001 2002 2003 2004 Activity _____ Final design and bid document preparation Pre-qualification (NCB contracts only) _ Bidding and Award process Construction and commissioning - Commence operation (all WwTW) Technical assistance (supervision, studies and training) 6.4 Technical Assistance The WB considers it critical that institutions responsible for implementing and managing HRWPCP sub-projects are equipped with the management and technical knowledge, skills and equipment necessary to carry out their mandates. A technical assistance (TA) programme is scheduled which will provide institutional strengthening and training (including equipment) to the provincial PMO, city PRJs, Provincial and City EPBs, and the new municipal wastewater companies. I S-7 September 2000 Huai River Water Pollution Control Project Environnmental Assessment Summary Of particular relevance to the EA, the project includes an overall environmental strengthening component in the area of environmental monitoring. This strengthening is aimed at improving the Basin wide ability to monitor and report on environmental condition, as well as providing the means to better assess the environmental performance of the project investment package. This component would be implemented under the Huai River Basin Commission. 7 WATER AND ENVIRONMENTAL OBJECTIVES All surface waters in China have been classified according to ambient stream standards. The following is a general translation of the surface water classes: Class Description I used for water sources and state nature reserves II used for class I protection areas for drinking water sources, protection zones for valuable fish, spawning grounds of fish and shrimps III used for class II protection areas for drinking water sources, general protection zones for fish and bathing areas [Huai River mainstream target] IV used for general industrial water areas and water recreation areas where no direct contact with hurans occurs [Major tributary target] V used for agricultural water areas and scenic water areas. A new Environmental Quality Standard for Surface Water, GHZB-1 1999, was issued on July 20, 1999, and became effective on January 1, 2000. This new standard replaced the previous GB3838-88 standard. The parameters of most significance to the HRWPCP wastewater schemes are shown below: Parameter (mg/I) Class III Class IV Non-ionic ammonia 0.02 0.2 D.O. (Min.) 5.0 3.0 CODa 20 30 BOD5 4.0 6.0 8 PROJECT BENEFITS AND IMPACTS 8.1 Project Benefits Public health projects like the HRWPCP carry many general benefits for the citizens of the project cities. The project feasibility and EA reports outline specific benefits including: * Raising the output of agricultural, fish and livestock production; * Increased domestic output due to improved water resources; * Public health improvements; * Increased revenue from tourism; * Increased real estate values; * Improved surface water quality. Other additional potential benefits might include: * Reduced risk of groundwater contamination in the service areas. S-8 September 2000 Huai River Water Pollution Control Project Environmental Assessnient Summary * The impact of making realistic charges for wastewater services should help to encourage waste minimisation at source, and intemalise the costs of pollution control. * Amenity benefits to the population of project cities are likely to accrue as the quality of the adjacent rivers improve. This could include use of the river for recreational purposes and the development of riverside walks and parks for public use. 8.2 Social Impacts Resettlement and compensation plans have been prepared and are covered in separate "Resettlement Action Plans" (RAP) for each province. The final Anhui Province RAP was prepared for the WB at the same time as the EA and the summary is shown in Table S-5. Table S-5: Project Affected Land Statistics, Anhui Province City Perntinent LanI Acquisition (Mu) Temporary Land (u) Irrig. Dry Veg. Fish State- Other Sub- Affected Veg. Fruit Sub- Affected land land land ponds owned land total people land orchard total people ________ ___ ____ _______ landI Huaibei 0.0 3.4 2.9 0.0 0.0 0.0 6.3 31 0 0 0 0 Bengbu 4.1 1.6 3.5 0.0 0.0 0.0 9.2 28 0 0 0 0 Huainan 3.0 0.0 0.0 1.3 9.0 1.1 14.4 7 0 0 0 0 Fuyang 0.0 0.0 0.0 0.0 0.5 1.8 2.3 21 0 0 0 0 Bozhou 0.0 4.3 0.0 0.0 3.9 0.0 8.2 17 0 0 0 0 Lu'an 29.6 16.4 8.2 0.0 1.6 33.6 89.4 131 0 0 0 0 Guoyang 0.0 . 85.0 0.0 0.0 0.5 10.0 95.5 141 0 0 0 0 Total 36.7 110.7 14.6 1.3 15.4 46.5 225.2 376 0 0 0 0 Note 1: Suzhou sub-project dose not require any resettlement, as the land for the sub-projeat is government land which is reserved for landscape works in the city. The government has agreed that this land is used for the project and as such a resettlement action plan for Suzhou is not required as ther are no affected people. Note 2: 15 Mu equal one Hectare The final Shandong Province RAP was also prepared at the same time as the EA and the summary is shown in Table S-6. Table S-6: Project Affected Land Statistics, Shandong Province City Permanent Land Ac uisition (Meu) Teporary Land (Mu) l TiDled Veg. Wood Otbers Sub- State- Affected TiDled | Veg. Others Sub- State- Affected land land total owned people land total owned people ________ ______ _____ ______ ______ _______ land _ _ _ _ _ _ ___ _ _ _ _ __ land _ _ _ _ Rizhao 107.3 54.9 52.4 214.6 214.6 435 68.1 6 125.5 199.6 199.6 255 Ju County - - - - - - - 21 5 - 26 - 26 78 Feichcng 70.95 . 0.75 1.80 73.5 94 19.2 - 1.5 20.7 1.5 52 Heze 91.75 - 28.22 119.97 9.62 129 4.95 r 0.72 230.5 236.1 | 227.7 12 Total 270.0 54.9 | 0.75 82A 408.1 224.2 658 113.25 | 11.72 3575 | 482A . 454.8 397 Note 1: No land acquisiton or resettlement is needed for the Chengwu Paper Mill component as all works will occur on empty land within the existing factory compound. Note 2: 15 Mu equal one Hectare 8.3 Environmental Impacts During the construction period, there are potential impacts on the social environment, natural environment and living quality and these are generally temporary and relatively minor. Construction of wastewater collection and treatment facilities will inevitable cause some disruption to traffic and local communities. The project will also affect noise and air quality of the immediate surrounding areas. Construction will also impact on sidewalk trees, vegetation and rainfall inlets S-9 Septemnber 2000 Huai River Water Pollution Control Project Environmental Assessment Summary Mitigation measures for the construction period have been built into the project and these should enable the unfavourable effects to be minimised or eliminated entirely. These mitigation measures are based on international approaches to similar problems elsewhere. For disruption to local communities involving temporary and permanent land acquisition the RAP include detailed measures for compensation and livelihood restoration in accordance with PRC laws and WB policy. These construction impacts have been sorted according to their geographic location within the overall project. Details of mitigation measures, the monitoring required to ensure that mitigation measures are effectively implemented, and responsibilities are provided in detailed charts within the Consolidated EAs. HRWPCP PMOs will have an ongoing responsibility to track and report the monitoring work of all the identified agencies, in addition to their own direct monitoring activities. The potential operational phase impacts are relatively minor and easily mitigated. Many of the concems have been addressed in the course of the design of the wastewater collection and wastewater treatment facilities. Details of mitigation measures, a programme for monitoring mitigation measures and responsibilities are provided in detailed charts in the Provincial EAs. Potential impacts that were evaluated included: * Raw sewage discharges and intermittent operation of overflows; * Industrial wastewater influent problems (WwTW upsets, sewer corrosion); - Noise problems at pump stations and WwTWs; * Odour problems; - Air Quality impacts; * Treated effluent impacts at outfall locations; * Sludge treatment and disposal; * Improper O&M of WwTWs. The financial analysis for HRWPCP components indicates that they are affordable for the stakeholders (municipal governments, service population and industries). This project is meeting a "backlog" need for environmental infrastructure and should not induce adverse extensive growth or secondary impacts. The present environmental problems are serious and the provision of this environmental infrastructure is necessary for current needs and to mitigate current problems. Future problems without the project would become even more critical. 9 ALTERNATIVES REVIEWED IN PROJECT DEVELOPMENT The evaluation of alternatives for individual project components covered issues such as: * Sewerage system interception ratio; * Pipe materials; * Pipeline construction; * Number of pump stations and pressure mains; * Number of WwTWs; * WwTW site selection; * Wastewater flows and capacity of the WwTWs; The quality of wastewater to be treated; S-10 September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary * The use of septic tanks; * Treated effluent standards; * The degree of treatment; * Wastewater treatment options; * Variants of the oxidation ditch; * Sludge disposal; * Chengwu Paper Mill treatment processes; * "Without Project" altematives. 10 MITIGATION AND MONITORING 10.1 Mitigation and Monitoring Budget The capital budgets prepared for HRWPCP components include allowances for laboratory construction and equipment for use by the wastewater companies. Use of this equipment to perform the necessary testing by the wastewater company is also included in the operations budget for the project. Furthermore, accomplishing the specified monitoring and reporting outlined in this mitigation plan will be greatly enhanced by the TA programme. This TA programme will also allow for improved overall performance assessment of the HRWPCP programme relative to meeting the project objectives. Future phases of the HRWPCP will benefit from such assessments. Despite the above facilities and training the conduct of the mitigation monitoring programme will require additional funding. Cost estimates to cover long-term environmental monitoring have been estimated. "Long-term" is defined as annual monitoring required to verify the environmental performance and other operational mitigation measures previously outlined. These mitigation monitoring costs have been. added to the wastewater company operational cost estimates. Costs for mitigation measures that relate to the management of construction will be included in the tender documents and responsibility passed on to the construction contractors. Table S-7 summarises the monitoring cost estimates for Anhui Province. S-l1 September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary Table S-7: Anhui Environmental Monitoring Costs Environmental Monitoring Cost Estimates (104 Yuan/Year) City World Bank Projects Bi-Lateral Projects Total, WB and Bi-Lateral Short Term Short Term Short Term Long Term (5 years) Long (5 years) L years) Bozhou 7.24 8.10 36.16 5.40 43.40 13.50 Huaibei 7.24 8.10 39.16 5.40 46.40 13.50 Guoyang 27.00 7.50 N/a N/a 27.00 7.50 Suzhou 8.24 8.10 40.16 5.40 48.40 13.50 Fuyang 8.24 8.10 46.16 5.40 54.40 13.50 Bengbu 8.24 8.10 46.16 5.40 54.40 13.50 Huainan 8.24 8.10 46.16 5.40 54.40 13.50 Lu'an 27.00 7.50 N/a N/a 27.00 7.50 Anhui Total 10144 63.6 253.96 32.4 355.4 96 Annual CostI Table S-8 summarises the monitoring cost estimates for Anhui Province. Table S-8: Shandong Environmental Monitoring Costs Monitonng No. Sub-project management fee per year (10000yuan) I Rizhao wastewater treatment plant 30 _ and pipe network 2 Ju County wastewater pipe network 10 (include wastewater plant) 3 Heze wastewater treatment plant 15 and pipe network 4 Chengwu paper mill 20 5 Feicheng wastewater treatment plant 12 and pipe network 6 Total investment for enviromnmental 87 protection 10.2 Annual Environmental Quality Report The recommended environmental monitoring programme is important during both the construction and initial operation phases of the project and involves participants from both the sub-component and provincial levels. The results of this environmental monitoring programme will be summarised in an Annual Environmental Quality Report (AEQR) for each Province, which is distributed to all relevant project offices as well as the World Bank. The charts in the beginning of the mitigation and monitoring chapter of each provincial EA provide convenient checklists for these reports. At the beginning of January every year, each PIU will sort the relative monitoring data and provide it to their provincial PMO. The Provincial PMO will then consolidate the data in an AEQR. The minimum information that should be reported in an AEQR is shown in Table S-9. S- 12 September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary Table S-9: Minimum Monitoring Data in Annual Environmental Quality Report Year ended December 31 Unit 2000 2001 2002 2003 2004 1. Physical Parameters Wastewater generated 1000 m3/y Wastewater collected 1000 m3/y Wastewater treated 1000 m3/y Wastewater billed 1000 m3/y Sewer connections Number Length of combined sewers Km Length of separate sewers Km Length of interceptor sewers Km X Total treatment capacity 1000 m3/d Capacity of treatment plant Nol 1000 m3/d Capacity of treatment plant No 2 1 000 m3/d Biochemical Oxygen Demand outlet (Nol) Mg/litre Chemical Oxygen Demand outlet (No 1) Mg/litre Suspended Solids outlet (No 1) Mg/litre Biochemical Oxygen Demand outlet (No2) Mg/litre Chemical Oxygen Demand outlet (No 2) Mg/litre Suspended Solids outlet (No 2) Mg/litre X X BOD in the recipient downstream a) Mg/litre COD in the recipient downstream Mg/litre SS in the recipient downstream Mg/litre DO in the recipient downstream b) Mg/litre E-Coli (triplicate sampling) c) MPN/l00nml 2. Manaeement of Oreratine Aeencies __ _ _ _ Agency employees d) Number Employees/l 000 connections Number 3. Financial Parameters _ Average sewerage tariff RMB/m3 Days of account receivable Number Receivables over billing % Working ratio i Operating Ratio % Maintenance expenses to total cost of % operations l l Contribution to investment |_%_l Debt service coverage Number _ | Debt equity ratio Number T_=__=_ 4. Institutional DeveloDment Parameters | l Days training accomplished Number | TA days input Number Number of Board meetings Number Staff recruited Number Key Action Plan target dates achieved _ a) approval of business (A) license Date (B) charter Date b) appointment of Board Date c) first Board Meeting Date d) issue of RfP for TA Date e) commence TA IDate f) commence training program Date a) BOD, COD, SS, DO and E-Coli in receiving river would be sampled quarterly and the respective progress report would show lowest and highest results b) Dissolved Oxygen c) Applicable methodology (multiple-tube fermentation technique or membrane filter technique) determined at pre-appraisal. d) Excluding casual labourers. S-13 September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary 11 PUBLIC PARTICIPATION IN THE ENVIRONMENTAL ASSESSMENT During the 12-month project development time leading up to this provincial consolidated EA, there have been many meetings with the city PIUs, utility companies, city EPBs and other affected city organisations to discuss the proposed projects and preparation of the sub-component environmental assessment reports. These meetings have occurred monthly at a minimum and have resulted in full collaboration with local officials and full support of the project and the EA process. It is estimated that in total 3040 meetings have been held with the public and over 50 meetings have been held with local government officials during the development of the projects, in both of the HRWPCP provinces. HDI also prepared a survey form to gauge the public perception of the positive and negative impacts of each of the proposed projects in Anhui Province. The investigation was made with representatives of the local government sectors, People's Congress, political consultative conference, women's federation, communist youth league, trade union and other organisations, as well as urban residents' comrnittee. The survey results showed widespread support for the HRWPCP in all Anhui cities. In Shandong Province, SIEP undertook public participation activities included random opinion sampling questionnaires and holding meetings/conferences in order to inform and obtain suggestions from the public. These activities involved both representatives of local government sectors (similar groups to those used by HDI in Anhui) and also villages, factories and enterprises near the proposed WwTWs. The public included workers, farmers and students etc. of different ages, professions and educational levels. The public participation results showed widespread support for the HRWPCP in all Shandong cities. In addition, each PIU announced project infornation using local newspapers, TV, etc. The public was able to inspect the sub-component and consolidated EA reports or summaries of these reports at local locations arranged by the sub-component PIU, and express their views on the proposed projects. The many meetings with public officials in the province coupled with the surveys of public support show that these projects are considered to have large positive benefits and are well received by the public. Comments received have been addressed, for example, comments that adequate compensation should be assessed for acquired land have been fully addressed in the RAPs. No objections have been received by the city PIU's and there is no indication that there is anyone that is not is support of these projects or would try to stop their completion. Details of the public participation events including time, place, attendees and issues are provided in the consolidated EAs for Shandong and Anhui respectively. 12 OVERALL HRWPCP PROJECT ASSESSMENT The HRWPCP projects have been properly formulated and they will form an important contribution to the achievement of the goals of the WPCP. The construction of WwTWs in the Huai River Basin has lagged behind the planned schedule of the WPCP, making it more important to accelerate WwTW construction. Significant progress has been made in regard to the control of industrial pollution since the WPCP was formulated. However, domestic wastewater collection and treatment remains well behind the WPCP schedule. S- 14 September 2000 Huai River Water Pollution Control Project Environmental Assessment Summary With respect to environmental protection, the general urban plan and the drainage project plan, the design of wastewater facilities and the locations selected for proposed pump stations and treatment works for HRWPCP projects in the Anhui and Shandong project cities has proved to be reasonable. The locations of the WwTWs meet the requirements of the local urban plans and environmental protection. For the Chengwu Paper Mill, project altematives have been comprehensively assessed, and the proposed project is technically superior and cost-effective. 12.1 COD Removed, Anhui Province HDI predicted the reduction in COD discharged to the Huai River Basin for the two HRWPCP WwTWs is shown in Table S-10 and in Table S-11 for all HRWPCP cities, both in the "near future" (with existing World Bank and bi-lateral WwTW) and the "further future" (assuming all municipal WwTW needs have been met in the cities. Table S-10: Estimated COD Reductions for HRWPCP WwTWs Wastewater Amount of Amount of Red Total Controlled Sub-components Quantity Discharge before Discharge after etia) Amount of CODcr (t/d) Treatment(tta) Treatment(tla) Discharge (t/a) (near futur 80,000 10804 3504 7,300 3600 (near future) 50,000 6388 2190 4,198 2190 Note that HDI analyses in the Chinese EA used these higher WwTW capacities for the two WwTWs at Guoyang and Luan based on the SDPC approval documents. The proposed capacities of these HRWPCP WwTWs were reduced 40,000 m3/day, which reduces the COD removal rate to 3,650 t/a at Luan and 3,358 t/a at Guoyang (total reduction for both WwTW therefore 7,008 t/a). Similarly, Table S-11 uses the SDPC proposed WwTW capacities in these cities. Using the actual proposed capacities reduces the short-term COD removal in the Province by about 4,400 t/a. S-15 September 2000 Huai River Water Pollution Control Project Environmental Assessment Sunmary Table S-1l1: Estimated COD Reductions for Projects Cities in the Future Unit: t/a (except items remarked) Project Sub- Discharge Discharge Reduction component Wastewater Quantity (10,OOOtId) Quantity before Quantity after (t/a) Treatment Treament 8 (near future) 9198 3504 5694 12 (further future) 13797 5252 8541 10 (near future) 10950 2190 8760 Bengbu Xi Jia Gou WwTW 20 (further future) 21900 4380 17520 Yang Taizi WwTW 20 (further future) 25550 4380 21170 10 (near future) 10366 2190 8176 20 (further future) 20732 4380 16352 10 (near future) 15184 4380 10804 Fuyang 20 (further future) 30368 8760 21608 Ying Bei WwTW 15 (further future) 22776 6570 16206 8 (near future) 10512 3504 7008 20 (further future) 26280 8760 17520 8 (near future) 11680 3504 8176 Suzhou Cheng Nan WwTW 16 (furnher future) 23360 7008 16352 4 (near future) 10804 3504 7300 Lu'an Cheng Bei WwTW 25 (further future) 33763 10950 22813 Cheng Dong WwTW 8 (near future) 10804 3504 7300 4 (near future) 6388 2190 4198 Guoyang______ Cheng Dong WwTW___ 10 (further future) 12775 4380 8395 12.2 COD Removed, Shandong Province Feicheng, Heze, Rizhao City and Ju County in Shandong Province will benefit from improved urban surface water quality after construction of sewerage and WwTWs. In the case of Rizhao City, the adjacent sea water quality will also be improved with benefits to fisheries and important tourist bathing beaches. The improved wastewater treatment systems at the Chengwu Paper Mill will significantly reduce current levels of pollution discharging to the Dong Yu River benefiting downstream commnunities. After the HRWPCP is implemented the situation with respect to COD, discharges will be as shown in Table S-12. Table S-12: Total COD,r Discharged in Shandong Sub-components Sewage treatment COD Discharged COD Total control Sub-component volume after treatment removed standard for river (m3/d) (t/a) (t/a) (se/a Rizhao 100,000 10220 5110 10220 Ju county 40,000* 1752 5548 1752 Heze 80,000 3504 11096 1000 Feicheng 40,000 1168 5402 1700 Chengwu Paper Mill 01,300 (black liquor) 2380 9989.2 3375 Sewerage is part of HRWPCP - WwTW is being built using local funding and is not part of HRWPCP S-16 September 2000 Huai River Water Pollution Control Project Environmental Assessment Sunmmary Based on the maximum permitted COD discharge for each COD control section in Table S-12, the COD discharged before the HRWPCP is implemented and the distance between the sewage discharge site and the control section, it can be seen that without the HRWPCP, the COD discharged to the control section of the receiving rivers will exceed the COD standard. The construction of the project will have great effect on the realising of total volume control target in Huai River Basin administrated by Shandong. Table S-13 provides the SEEP estimates of COD reductions associated with HRWPCP projects. Table S-13: COD forecast for Zhushui, Kangwang, Dongyu River COD concentration (n before project after project reduction reduction 2000m down stream Zhushui from the WwTW Low flow 94.0 36.0 58.0 61.7 outfall 100m upstream Low flow 137.2 63.7 73.5 53.6 Kangwang from the junction Flood period 63.6 26.0 37.6 59.1 with the Hui River Normal flow 117.4 51.9 65.5 55.8 Low flow 660.9 130.6 530.3 80.2 Dongyu Zhangzhuang Flood period 85.8 46.3 39.5 46.0 _Normal flow 103.4 44.3 59.1 57.1 From Table S-14, it can be seen that the COD concentration in the river near the proposed WwTWs will be greatly reduced by the HRWPCP. During the low flow period the Zhushui River will be able to reach Class V standard and during the flood period the Kangwang River will be able to reach Class IV. However, the Kangwang, Dongyu and Shu (Ju County) rivers will still not be able to attain better than Class V for all flow periods, although they can satisfy the water quality requirement of fannland irrigation. (wet farming: COD<200 mg/I; dry fanning: COD<3WO mg/I; vegetable COD \ WwTW Built by Project interceptor/ < WwTW Others (now/future) main sewer A - - - Project pumping main kt Project PS Lake:. . *o PS Built by Others _ River: ;-e /PS\ (no or fulue) _ . -Sewers built by others; V ~ Note: Only principal sewers shown.- _ l ~~~~~~ - - A (; *_ - _\ X~~~~~~~~~~~~~~~~~~~~~~~~~Ong ZiRver ITX kinterceptor~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~i t ~~~~~~~~~~~~Huai River:-ilhj I ;;¢Faittre, Nrl. S i ping Station osIot~~rcepior ~ - ....~,/\ Proposed Yang Tal Zi WwTW Ba Li Gou Phase I Capasiiy (2005) i0,000 muId Pu/iure Nc 4 Lift Pumping Station Phase 2 Capacity (2015) =200,000 m5/d I / bxi Jl Coc sTW - \\et : - x' 'nis K'S' ' ' 'i. r" p;,'j',' '' : 1 ass flows to future WwTW./ | / thsts I 'Capgci't (2 ol) P p 0,000 Ppsd N c I , Pu p Sta S ,he ,e Proposed , or WrApgbd Fund,nJtl 'piN Li ;': .': . '' /. ( t\ ^~~Phiimpldr 2idiys 17ttitj__/ . 1)138.9km of new PVC and concrete$ w .PropoOitdNt 3Lil 'rmping Stations Nr\ i\,;:':''" :'' I tp oeNIiPu pingstation .PastlICapacitj-ft4201/ls | \\\ >;; J haselICapacity 10001/ls De''DtiB Htid - 10 tn|\\mP.".- ........," .:/.........../S Design Head = 0 m se co:Pitmpr s 82 d.t9i, sndby 'Pumps 2 duty, standby Be // Sanrni> ,-,', > >........... ..........Long Zity tT777 ;/ > > - Sr;iF ' ^'38--77 L ~~~~~~~~~~~~Lake /t Scheme Proposed for WB Futnding .. , >: ;,..,,................ 1) 138.9 km of new PVC and concrete ; e sewers comprises 78.9 km of interceptor and.a main sewers, DN 300 to DN 2000, and 60 Bengbu City km of secondary sewers with diameters of (1998 urban pop. was 540 000. ExIsting combined sewer DN 300 or smaller; system, approx. 163 km long, comprises pipes and A 2) 3 Nr intermediate pumping stations; ditches discharging untreated effluent to Hual River) w. '- uf' 3) 1.61 km of DN 800 pumping main. k _ Huai River Water Pollution Control Project Environmental Assessment Figure S.3 Bozhou Wastewater Project - Schematic N~~~~~~~~~~~~~~~~~~~~ Urban Area Proposed Nr I Lift Pumping Station i - Jv3ing Ju7 Phase I Capacity = 150 I/s Raa (W T Project WwTW \ \ ~~Design Head = 10 m ; Gog River Pumps =2 duty, I standby WwTW Built by PAs WwTW /g\< ;L :;; 7 0 - ;0:; t: : t00 000 :Others (now/future) iPS \AGuo ver A PS - -j- 0 \Project PS Phase t Caps =70 PS Buit by Others Pumps I dut1', I siandby ~ ~ ~ ~ ~ ~ ~ ~ PA (ow r utre Iae I a t 0 \s Project Interceptor/ egn |ead = \n Main Sewer I 1:: .: l / \ _ ~~~~~~~~~~River I I 5: l . : Z i --~~~~~~- -- Stream/Channel l _ _ Z : < 1 - :: :. ; 0 f ;001 i: i;: ~ Bridge 91 . 0 ::;; 0 D; 00 - - | 00 - 0t . 0st : :: 0 f Note: Only principal l ^ $ 4 d S ,;; - ;004S0; 8; -ir; zt t proposed sewers shown i Proposed Nr 2 Lift Pumping Station up uy tnb Phase I Caacjily = 420 I/s / - Design Hcad = 10m mr I WwTW Pumps = I d I standby Pas capacity (2001) = S0,000 m3/d Proposed Nt 3 :Lif- (under construction ia an 'P_e I Capacity -4 W5w TW / S : - ,. Long Feng :- . : PropoSed Nr 4 Lift PvmpIng iChannel r 2 ; I standby PhsIapct 42 l - Song Tang He D-' o Cheng New .000, ~~~~~~~~~~~~~~*River I- ~ - Bozhou City (1998 urban pop. was 241,800. Existing Scheme Proposed for WB Funding' combined sewer system, approx. 154 km long, 1) 106.3 km of new concrete and PVC sewers comprises pipes and ditches discharging C1mprising 56.3 km of interceptor and main sewers untreated effluent to river system) DN 300 to DN1600, and 50 km of secondary sewers with diameters less than DN 300; 2) Four intermediate pumping stations; Huai River Water Pollution Control Project Environmenlal Assessment Figure S-4 Fuyang Wastewater Project Fuyang City N -Schematic (1998 urban pop.428,000. Existing combined sewer system comprises pipes and ditches) Ying River Proposed Nr 4 Pumping Station (Quan He Qiao PS) -Pha I Capacity - 2S0 s, , Design Head - 11 m- Pumps = I duty, I standby Futai Road PS S S Phasel I Cpacilix 15 5 lls,` kimp's,F j4uty;l staudby:ij -~~~~~Proposed 'Kr 3 Pumping Station Phase I Capacity 450 l1s Read \12 in P.mps= Ws dutdy, I standby parto f WwTW \je) \ . WwTW Sii YinS River S 1hem r 2 f r Pu p atidonr , 1)131.7km of new PVC and concrete sewers comprises 81.7 km of interceptor and Project WwTW . Urban Area main sewers, DN 400 to DN 1500, and 50 WT ul yPoetitretr km of secondary sewers with diameters of WwTW Oes lt( byno/ftue)m ins er DN 300 or smaller; Ohr nwftr)mi ee 2) 4 Nr intermediate pumping stations, ; Project PS - . - Project pumping main 3)3.0 km of pumping main, DN600 to P SRiver DN900. PS Built by Others As (now or future) Pro dNote Only principal proposed sewers shown Phase ICapacit =650 Is | | S / Ylg Nn W4T- Huai River Water Pollution Control Project Environmental Assessment Figure S-5 N Guoyang Wastewater Project *Schematic Wu Jia River G Cit \ D 7.:00G.uoyang City ?\ (1998 urban pop. :was 107,940. tExisting1 combined SewerTsystem, approx. 44 km long, comprises pipes and ditches) Guo R iver_ Railway Cuo~~~~~~~ .u .< . . . . .. t i;: :; d V ;:: p: n I 1 ; ~~~~~~~~Proposed Nr 1WvTW WT ) Proj c t wTW Propos Nr i Lflt Pumpin1 Station S || Phase. I Capacity (2003) = 40,000 rnStd L ~~~~~~~~~~~~~Phase I Capacity =740Vs ;[ t NComprises preliminary treatment (fine \WwTW Built by Design Head = tOrmn screens and grit removal), biological WwTW secondary treatment (conventionalto ervemort Others (now/future) Pumps = 2 duty, I standby | eonidatio dtcproaessnwith settlement A ~~~~~~~~~~~~~~~~~~~~~~~~~~~tanks), gravity sludge thickening and Project P'S sludge dewatering using belt presses. /j PS Built by Others _. (now or future) r.Schemne Provosed for WB Futndini' Project Interceptor! Main 1) 72.3 km of new concrete or PVC sewers4 Sewer .comprising 37.3 km of interceptor and main sewers, - -. Existing sewers DN 300 to DN1500, and 35 km of secondary sewers - Rtver with diameters DN 300 or less; - Stream/Channel 2) One intermediate pumping station; '~ Bridge tn3) New 40,000 m31d WwTW (Phase 1). Note: Only principal proposed N I WwT sewers shown . 2 _ Itnb P.--S Buil by Other PAs,,,,, (no or,g future),,,, W _ SceePo_oe o W udn Huai River Water Pollution Control Project Environmental Assessment N Figure S-6 Huaibei Wastewater Project Dai River\ - Schematic / ~~~~~~~~~~~~~~~Dai Ri ver\ /\Railway Huaibei City ~ ~~~~~~~~~~~~Proposed Nr 2 Lift Pumping Station New Sui Rivert (1998 urban pop. was 250,650. Phase I Capacity = 120 I/s /Existing combined sewer system Design Head = 10 m comprises pipes and ditches) Pumps I duty, I standby I , \ \''1'' I\ j Old City \Pa (combined sewerage. I system) \ i Is ' X.- 1 ' I \ \ [Interceptor - j : Se Y . ,,.e. I ' \ Pr> t . . . . . .hoposed Hr I Lift Pumping Station / Phase I Capacity = 500 I/s / :1 - il / * . . . . . ' Pemps 2 duty,. I standby / Proposed Nr 5 Lift Pumping Station Phase I Capacity = 1000 I/ s Long River Proposed Nr 3 <'|:, Design Head = 10 m_ mP s = 2 duty. I standby Lift Pumping Statin | ~ ^ umps=2dt,Itaby> hase I Capacity = 320 I/s '. , , Design Hcad-IOm | - umps =2 duty, 1 stanby / umps = 2 duty, I standby . \ . ' | gWwTW .JtProposed Nr4 Lift Pumping Stationr Old Sui River% Phase I Capacity = 100 I/s KEY Design Head = 10 m I t.. :_ Pumps =1 duty, I standby Urban Area I / 1 \Project WwTW Nr I WwT% (Diag Lou) Al …\WwTW - by Others ,Phase I capacity (2001) = 80,000 m3/d - - - - - -(now/future) (under construction) u A Project PS Scheme Proposed for WB Fundine PS Built by Others 1) 98.8 km of new PVC and concrete sewers LAs (now or future) comprises 63.8 km of interceptor and main Project Interceptor/ sewers, DN 400 to DN 1600, and 35 km of Main Sewer secondary sewers with diameters of DN 300 Sewer not included or smaller; - River 2) 5 Nr intermediate pumping stations - Stream/Channel Note: Only principal _=.x, - ........... ==,> ............... z; proposed sewers shown Huainan City _ ~~~~~~~~(1998 urban pop. 404,900. Existing combined sewer t system, approx. 260 km long, comprises pipes and~ tches, dicharging to HuaiRvr \~~~~~~~~~~~~~~~~~~~~~~~hs I caacity (2001) 10O0r/d 0 . . 0 - K - .; X - und(uner constrUciD Proposed NrlIpLiftpPumping Stalion Nr 3 Lif Pupn Station Phase I Capacily- =240 1/5;nX 1Phase Nr3 Ctpaingtyi 22r ~~~~~~~~~~~~~~~~~D e s ig n Reedd= 1 0 m C a a i y = h i Pumps = 2 duty.,1Istandbyp . . . ; _ 0:-. 0 . 7 i - l: j - Demsig=2 Head = tn mdb Pum"s 2;l duly, I standby p t; ' i -g? L _ . . Pumps=2 duty I standby Proposed Nt 2 Lift Pumping Station t- ¢:;~ 0 0 0 | 0 ; 00 ; SC ;.; f . ;0|ropsedNr4 Lft :mingStaio Phase I Capacity = 260 lli . k N1 . - : . t i . Ps C t. Design "cad = 10 m e 4 j ' § .$> ;:V\ s : . 0 '; :: .: .0 . 0A DegHe:: Pumps n 2 duly, I standby ^/: :: 0 > : v .: 0:; . a 0 ;0 . . . . .t:: tn: KEY Project WwTW Urban Area C Scheme Proposed for WB Fund'n WwTW Built by Project -nterceptor 1) 87.6 km of new PVC and concrete gravity sewers Others (now/future) Sewer comprises 48.6 km of interceptor sewers, DN 400 to - - - Project pumping main DN 1800, and 39 km of secondary sewers with Project PS diameters of DN 300 or smaller; = Rivet Scheme Propesedfor WB Fltnding / WwTWS Built by Others ntrepore 2) 4 Nr intermediate pumping stations; Stram/Channel 3) 2.6 km of DN 400 pumping main. ( . ~~~~~Note: Only principal proposed sewers shown d )b:?ey r: ^; 2 - 77-7~~~~~~~~~~~~- e 0~~~~~~~~~~~~~~a-. To Huai 4 River To Pi River ,\Pi Main N Proposed Nr I WwTW Phase I Capacily (2003) = 40,000 ml/d Lu'an City Comprises preliminary treatment (fine (1998 urban pop. was 217,000. Existing screens and grit removal), biological combined sewer system, approx. 145 km secondary treatment (conventional long, compriseser pesl andpditches.)1 P River 4 I oxidation ditch process with settlement long, comprises pipes and ditches.) 'tIverl r /~ / tanks), mechanical sludge thickening and sludge dewatering. / / / h. ~~/ - N. -_ - Proposed Nr I Lift Pumping Station /_ Phase I Duly Capacity = 208 I/s Design Head = 7.5 m P/ˇ2S I Pumps =2 duty, 2 standby / P rpo Std 1/ 1 , East C ily PS 130uty Ca1cIty ii IOo Il (ftu - cptcity 2 df'/^r i !.4*r;l's2d/l'1 * , - '': 'Sn ' ' .iiot confirmed) IntrceptorWo \ \ Fsiture- t Sewer 2 r S ; 1 ti :: 1st r: rF \ I + bevelopment Zone I Proposed Nr 2 (South City) . Pumping Station A Phasc I Duty Capacity = 224 /l /PS Design Head = 29 m . _ Punmps = 2 duly, I standby Pi Main KEY Canal KEYc~ Canal ~ ~ Ptoject WwTW UbnAe ' Scheme Proposed for WB Funding Urban Area 1) 34.9 km of new gravity sewers comprises 29.9 km <' 3 WwTW Built by - Project interceptor/ of ineteceptor and main sewers, DN 300 to DN Qles(o/uur)mi ee 1800, and 5 km of secondary sewers with diameters Others (now/future) main sewer of DN 300 or smaller; A - - - Project pumping main to Project PS , 2) 2.4 km of pumping main, DN 300 to DN 600; -- River ir -> 3) 3 Nr intermediate pumping stations; PS Built by Others 3 2 4) One wastewater treatment works with capacity of PAs (now or future) ta -; 40,000 m3/d. Note: Only principal proposed sewers shown Huai River Water Pollution Control Project Environmental Assessment N Figure S-9 Suzhou Wastewater Project - Schematic Railway Xian Bian River ---------------- ------ Xiao Hong River Suzhou City Tuo River I (1998 urban pop was 272,670. Existing - f - 0 : 0 \ 00i00 1 $ 00V1 ;; 0 -: combined system, approx. 92 km long, Prpoe :r 2 PS : > 9 'comprises pipes and ditches.) \ s ~~~~~~~~Pro posed Nr 2 PS Phase I Capacity = 200 lis Us Design Head = 10 m Ms tu =I duty. I standby San Ba Canal\ -- 0 - : ; \} I;000 0 ;000 0 t 0 7 0 lt: 00 t- 0 fr ;0;0X\Tuo River . - i,1;:- 1: -T :.S -. I,; ,-I: S., . :;, 1X C : : f. ProposedNr I Lift Pumping Staion ji Phase I Capacity 600 has Design Head = 10 m , j Pumps= 2 duty, I standby Prped Nr 3 Lift Pumping Station ;andby~ 1 f -+0 x; i0 0 ; ; si Phase I Capacity = 425 I/s Design Head = 10 m Pumps = 2 duty, I standby KEY Phase Ne I WwTW - Urban Area Icapacity (2001) = 80,000 in/d Project WwTW | (UDdcr constTuction) \ /IT Yun Liang Canal 1 Ri v er W w T W ) .--.;;:,. .;.:i3 - - - Effluent recycle pipe ZZC Bridge . l- .g*& Note: Only principal proposed sewers shown -,n4f VT:''s+5 .F. r ,. N KEY Scheme Proposed for WB Funding Urban Area F I) New 80,000 m3/d WwTW (Phase 1); /-/ \ i 2) 72.2 km of new HDPE sewer comprising 26.1 km wfi/ / Project WwTW of main sewers, DN 400 or greater and 46.1 km Df secondary sewers, DN 300; WwTW Built by 3) 4 Nr sewage lift pumping stations (PS). /W\ W Others (now/future) oWKC g ,,:;,-,Y'A, ,K,>,, .!:.:$ Zh4Sao Wang River A Project PS 8 PS Built by Others Old City Boundary Dyk PAs (now or future) - Project Interceptor/ /~~~16.6; R i ve .rChnel ,RS ;..,,,, Note: Only principal proposed sewers shown | 9 ' >'' ' > > , _ &til?:ris. g t n - Zhu hui River Proposed Nr 2 Pumpittg Station ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ' PdiingSt'to' Pumps 2 duty, I standby Proponed N~ PUmP~ SuIoft Comprises preliminarytr t (f iettndby: Proposed Nr 2 Pumping Station _c and grit r - b i Phasc I Maximum Capacilj - 41811 ,;-Ip/s.,,i,:;,. -,,,, . ,, Proposed Nr I WwTW Purnps-2duty, I stanldby kieps^rXunilsain>;s>.0;:-', ,l ;Crpicpei(° Phase I Maximum Capacity = 1,255 1/g Proposed Nr 4 Pumping Station icrteens and grit removal)j, biological Design Head = 6.0 m Phase I Maximum Capacily = 339 I/s secondary treatment (conventional , ; He e ~ jt Pumps = 6 duty, 2 standby Design Head = 6.0 m oxidalion ditch process with setilement Heze City Pumps = 2 duty, t standby tanks), gravity sludge thickening and } (1998 urban pop. was 280,000. Existing combined sludge dewatering using belt presses. '; sewer system, approx. 50 km long, comprises c pipes and ditches, discharging untreated effluent to river system) Huai River Water Pollution Control Project Environmental Assessment KEY Figure S-12 Rizhao City Wastewater Project Project WwTW - Schematic WwTW Built by Others (now/future) Project PS A PS Built by Others / /PAS (now or future) i Project Interceptor/ Main r _ - Rizhao City Sewer or Outfall - . . Project pumping main 1(98ubu o.ws5,0.islgeuie Coastlinojet pumping main - j - -and sepirate sewer system, approx. 142fkm loDg, , - - --... Coastline -comprises pipes and ditches, discharging eMuent - - River/Channel I to,river system or direct to the sea) Note: Only project - . sewers shown 4/.;o I 7 r t a i > > P- DN 1200. !ProposedNr3PS. . . . -J .2.1 km w . . Phase laum ON 800, 443 km / DNiOOG, ~~(refWV)Ca_pacity z 600 u/s DN Ps00, 4 DN/.1 km ,DN , Desigp Head- 14 m (ref Wa4) DN 1200, Pumps du,(refW4 I standby I ., J fs AcS/;?2 PS. At' D~~~~~~~~~~N t200,~ .uinn=1ui s5 tanr-d i.b. ; ~~~ 14km~~~~VW .4k lr lC .r \goI. ,;7 7 iretf7Wb" ., 100 -~~~~~~i 100 tD 10 v' 2.c (ref Wb3),,S, - 10km(refWa9) :. (refWI) Proposed Nrl Pumping j ~~:Pbae I M mum , Station at Lmjia |,zlia, i. - '"'^ N ' " ' | Cpacity s 00 ;3 Phase jI Cpacity (i{2003 ,i 100 00 I sf W ,s )r Design Head ~~ J Phase ~Capncaty (2010) ~~ 200 000 m104 P .p .1', , ' creens and grit removatl),primary settlement t:yi-i S! SgI DN 1200 E t '' f tanks), gravit y sludje .thickenintg antd sludge 0 in,T y .f short sea out al1,,' N ~ ~ ~ ~ ~~~.dewaterflng 15WJ blt ichressein;. f ,t .ror emergency us >~~~~~~~~~~~D -1 2. tm -' - fr WN;) ir r, Nrpoe Prrose tle Pmpii tatotat *T N Phase I MaximumCapacity = 2640 1IJ 0 0 e Design Head = 13 m . Single DN 00 Harbour Pus Pumps =2dnty. I standby I 2.B km In t i - - ' ' (to header cha nbet) li ' u Header f e ~~~~~Chamber ., ..*- F Scheme Proosed for WB Furndin,y I) 39.6 km of new RC interceptor, main sewers and pumping mains, ON S00 to ON 2000; Design Htad = 13 m, I wingl DN I1200 .,ou 2) 3 Nr sewage intermediate pumping stations; i2.5 m ong sea 3)1l00,000 m3/d WwTW (Phase 1) providing preliminary outfall. and primary treatment; 4) 1 Nr outlet pumping station to pump flows to outfall f header chamber; 5) 2.8 km of DN 1600 pressure main to head chamber Yellow Sea 6) Header chamber and 2.5 km long sea outfall comprising twin aN 1200 laid in submarine trench; 7) Single DN 1200 short sea outfall pipe for emergency use. \4=S, __ Huai River Water Pollution Control Project Environmental Assessment KEY Figure S.13 Ju County Wastewater Project <= P Project WwTW -- 0 Urban Area Schematic WwTW Built by Project Interceptor / Others (now/future) Sewer Project PS - - - Project pumping main N vPx Project PSN ' - x ~ ~~~~~ Riveer. PS Built by Others _ _ Stream/Channel /PAs (now or future) Note: Only proposed project sewers shown / Youi strzam/ /. ditck - ~v1 / : jf : 5 Shu ; 0 \ 0 : ;0 0 t} / 0 0i. 0 / 0 f 0 . 0 River Iner West / Ring Road Sewer Wei Xe Read Sewer / .2.3 Im of concrete PIPe. / .: kM .f concrete pipe : DN 500 to DN 00 toDNS0 10 Liuqing I River. . ' .| | ;-0/ 0~ ~ ~ ~ ~~19 . ,u7E| w rba pop war. OO: . ; Exitn .5k fcombined 2.1 kinof - and co vered~cbanmels) StMainSeNrl,'<' It0 00'0i'0-l,,$;;000 ;'t 2 tm onf concrett pipe, : : DN1000sa.dDNA100 , Main sewer to be laid in river course to intercept I txisting seweTs on both R sides of the rivers la Zhov Road Sewer 6.5 km of concrete sewer, * R ' DN 500 to DN 900 Main Sewer Nr 2 1.4 km of DN 1200 concrete pipe IWWwTW d - < . Nr I WwTW: :: / Phase I capacity -42003) 40,000 mild g1To Huai River Basin via Shu River Scheme Proposed for WB Fundint 15 km of new interceptor sewers. DN 500 to DN 1200 and associated overflow structures. FIual River Water Pollution Contirol Project Envirminiineiatl Avnsciiicien Raw Water from Boreholes , 6,216 m'/d Alkali Recovery Plant 12,000 m3/d Process water losses 6,000 m3/d (design capacity 1200 t/d) approx 150 mt/d Pulp Production Pulp Washing from Straw 120 t/d 5 Nr drum type vacuum pulp Pulp Pulp Bleaching Bleached pulp Paper Manufacture Kraft proess - litaw cookedwashing machines used in12tdADfrmSawPl Kraft process - straw cooked pulp scrics. 85% or black liquor 4920 mtld - chlorine process from trawyPul with caustic soda to produce extracted, solids concentration washwater 50,000 ton/year brownstock. of black liquor 10% Black Liquor White Wastewater 4 /d 1,296 ON Itldmldcen ac o 10% solids Mid-Section Wastewater 18,s00 m /d lean waterfor Treatment Works Screening and cleaning, Evaporation (design capacity 20,000 m3/d) Storage laundcrs etc (Includes storage, tube and Condensate - wasui water ( plate type evaporation and 940 m3Id condensation) PAM Black Liquor 7.6 kg/d To 80 m chimney } 48% solids . Removal Dust removal using _ A_Sludge wastewater R -claimed Fibre elctrostatic precipitator I \ Dewatering 7. t/d (2,550 t/yr) Fuel _ SugCaIncinerationSlud Fucl Oil l ~~~~~~~~~ ~~ ~~ ~~ ~ ~~144 I/d ' __ 124 kg/d (423 V/y) |Green Liquor (48,960 t/yr) Sludge Flocculation 28Z9-7 Wm'/ 20% ids w/w | Thickening | 20kg/d Lime 24.2 /d (8,231 t Soda Ash Recovery Water, 206 m'/d Ilr ~ l Sedimentation Ae|NuratlAdiion Tan wit Sedimentation Recycled to pulp Soda ash (NaOH) production area 2. recovered 24.9 l/dTrae White Clay Sludge Effluent Ammonium Sodium 53.9 F /d (18,320 I/y) P M19,920 m3/d less Sulphatr Phosphate 60% tds w/w t process losses 1600 kgtd 360 kgtd ow strength wastewater from - ~~~~~~~~~Alkali Recovery Pianl - ;H;;;>d~~~ direct tie ~~~~~~~~ 25~~~~~~~~44 m3/d- Figure S-14 Chengwu Paper Mill -Proposed Pollution Control Process