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Initial Environmental Examination (Draft)

Project Number: 51366-001

March 2019

PRC: Gui’an New New Urbanization Smart Transport System Development Project

Main Report

Prepared by the Government of Gui’an New District for the Asian Development Bank (ADB)

CURRENCY EQUIVALENTS (as of January 2019)

Currency unit – (CNY) CNY1.00 = $0.147 $1.00 = CNY 6.79

ABBREVIATIONS

ADB – Asian Development Bank AQG – Air Quality Guideline AVAS – Acoustic Vehicle Alerting System BEDGA – Bureau of Economic Development of Gui’an New District BOD5 – 5-Day Biochemical Oxygen Demand C&D – Construction and Demolition CNY – Chinese Yuan CO – Carbon Monoxide COD – Chemical Oxygen Demand CPS – Country Partnership Strategy CRVA – Climate Risk and Vulnerability Assessment EA – Executing Agency EHS – Environment, Health and Safety EIA – Environmental Impact Assessment EIR – Environmental Impact Report EIRF – Environmental Impact Registration Form EIT – Environmental Impact Table EMoP – Environmental Monitoring Plan EMP – Environmental Management Plan EMS – Environmental Monitoring Station EPB – Environmental Protection Bureau EPD – Environmental Protection Department EPL – Environmental Protection Law EV – Electric Vehicle FSR – Feasibility Study Report GDAD – Gui'an Direct Administrative District GDP – GEPB – Gui’an New District Environmental Protection Bureau GGAND – Government of Gui’an New District GHG – Greenhouse Gas GNDMC – Gui’an New District Management Committee GRM – Grievance Redress Mechanism HC – Hydrocarbon IA – Implementing Agency ICV – Intelligent Connected Vehicle ICVSDZ – Intelligent Connected Vehicle System Demonstration Zone IEE – Initial Environmental Examination ITS – Intelligent Transport System IMn – Permanganate Index IPCC – International Panel On Climate Change MEE – Ministry of Ecology and Environment MoC – Ministry of Construction NH3-N – Ammonia Nitrogen NO2 – Nitrogen Dioxide NOX – Nitrogen Oxides

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O&G – Oil and Grease OSPF – Office of the Special Project Facilitator PAH – Poly-Aromatic Hydrocarbon PAM – Project Administration Manual PCU – Passenger Car Equivalent PIU – Project Implementation Unit PM – Particulate Matter PM10 – Particulate Matter with diameter ≤ 10 micrometers PM2.5 – Particulate Matter with diameter ≤ 2.5 micrometers PME – Powered Mechanical Equipment PMO – Project Management Office PMO EHSO – Project Management Office Environment, Health and Safety Officer PRC – People’s Republic of RP – Resettlement Plan SO2 – Sulfur Dioxide SPS – Safeguard Policy Statement SS – Suspended Solids STI – Sustainable Transport Initiative TN – Total Nitrogen TP – Total Phosphorus TSP – Total Suspended Particulates VOC – Volatile Organic Compound WHO – World Health Organization

WEIGHTS AND MEASURES oC – degree centigrade μ – micron cm – centimeter h – hour ha – hectare km – kilometer km/h – kilometer per hour km2 – square kilometer m – meter m2 – square meter m3 – cubic meter m/s – meter per second m3/d – cubic meter per day m3/s – cubic meter per second mg/l – milligram per liter mg/m3 – milligram per cubic meter mm – millimeter s – second t – metric ton y – year

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NOTE In this report, “$” refers to US dollars.

This initial environmental examination is a document of the borrower. The views expressed herein do not necessarily represent those of ADB's Board of Directors, Management, or staff, and may be preliminary in nature. Your attention is directed to the “terms of use” section of this website.

In preparing any country program or strategy, financing any project, or by making any designation of or reference to a particular territory or geographic area in this document, the Asian Development Bank does not intend to make any judgments as to the legal or other status of any territory or area.

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CONTENTS

EXECUTIVE SUMMARY XI A. Introduction xi B. Project Description xi C. Project Benefits xii D. Project Impacts and Mitigation Measures xii E. Environmental Management Plan xiii F. Information Disclosure, Consultation and Participation xiv G. Key EMP Implementation Responsibilities xiv H. Risks and Assurances xiv I. Conclusion xv I. INTRODUCTION 1 II. POLICY, LEGAL, AND ADMINISTRATIVE FRAMEWORK 4 A. Applicable ADB Policies, Regulations and Requirements 4 B. ADB Assistance to PRC 5 C. PRC Public Transport Policies 5 D. PRC Environmental Legal Framework 6 E. Intelligent Connected Vehicles (ICV) 9 F. PRC Environmental Impact Assessment Framework and Procedures 9 G. Project Domestic Environmental Assessment 10 H. Environmental Standards 11 I. International Agreements 19 III. DESCRIPTION OF THE PROJECT 20 A. The Project 20 B. Rational 20 C. Impact, Outcome and Outputs 23 D. Detailed Project Description 24 E. Associated Facilities 49 F. Budget and Time Schedule 49 G. Implementation Arrangements 50 IV. DESCRIPTION OF THE ENVIRONMENT 52 A. Location 52 B. Physical Resources 53 C. Ecology and Sensitive Resources 67 D. Socioeconomic Conditions 76 V. ANTICIPATED ENVIRONMENTAL IMPACTS AND MITIGATION MEASURES 82 A. Project Zone of Influence 82 B. Anticipated Impacts Associated with Project Location, Detailed Design and Pre-Construction Phase 83 C. Anticipated Construction Phase Impacts and Mitigation Measures 84 D. Anticipated Operation Phase Impacts and Mitigation Measures 95 E. Cumulative, Indirect and Induced Impacts 118 F. Climate Risk 119 G. Associated Facilities 120 H. Positive Impacts and Environmental Benefits 122 VI. ANALYSIS OF ALTERNATIVES 126 A. No-Project Alternative 126 B. Bus Station Locations 126 C. Bus Types 126

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D. Road Alignments and Types 128 E. Pavement Options 129 F. Bridge Options 129 VII. INFORMATION DISCLOSURE, CONSULTATION AND PARTICIPATION 131 A. PRC and ADB Requirements for Disclosure and Public Consultation 131 B. Information Disclosure during Project Preparation 131 C. Consultation and Participation during Project Preparation 132 D. ICVSDZ Consultation 138 E. Future Plans for Public Participation 138 VIII. GRIEVANCE REDRESS MECHANISM 140 A. Introduction 140 B. ADB Requirements 140 C. Current GRM Practices in the PRC 140 D. Project GRM 140 IX. CONCLUSIONS 142 A. Expected Project Benefits 142 B. Adverse Impacts and Mitigation Measures 142 C. Risks and Assurances 143 D. Overall Conclusion 148 APPENDICES 149 Appendix A: Project Environmental Management Plan (EMP) Appendix B: Domestic Environmental Assessment Approval Appendix C: Bus Station Plans Appendix D: Bus Station Facilities Appendix E: Bus Station Site Descriptions Appendix F: Charging Station Site Descriptions Appendix G: Charging Station Plans Appendix H: Project Emissions Calculations Appendix I: Climate Risk Vulnerability Assessment Appendix J: Stakeholder Communication Strategy Appendix K: Intelligent Connected Vehicle System Demonstration Zone (ICVSDZ) Component

List of Tables

Table 1: Applicable PRC environmental laws, regulations and decrees...... 7 Table 2: PRC EIA Guidelines...... 8 Table 3: Applicable PRC environmental standards...... 11 Table 4: Comparison of PRC ambient Air Quality Standards (GB3095-2012) and WHO ambient air quality guidelines...... 13 Table 5: Emission Standards of Cooking Fumes (GB18483-2001)...... 14 Table 6: Level II Limits, Table 1, Emission Standards for Odor Pollutants (GB14554-93) ...... 14 Table 7: PRC Environmental Quality Standards for Noise (GB3096-2008)...... 14 Table 8: PRC Noise Emission Standard for Construction Site Boundary (GB12523- 2011) and relevant international guidelines...... 15 Table 9: PRC Surface Water Ambient Quality Standard (GB3838-2002)...... 15 Table 10: Groundwater standard (Class III, GB/T14848-93 Quality Standard for Ground Water)...... 16 Table 11: PRC Standards for discharging wastewater from construction sites (GB8978– 1996)...... 17

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Table 12: Soil Quality Standard GB15618-1995...... 17 Table 13: Environmental standards and guidelines applicable to the project...... 18 Table 14: Applicable international agreements with the PRC as a signatory...... 19 Table 15: Bus stations to be established in the GDAD...... 28 Table 16: Technical data of BEB fleet, GDAD...... 30 Table 17: Description and location of proposed charging stations...... 32 Table 18: Supporting road network, urban core area, GDAD...... 37 Table 19: Supporting road network work intersection types, GDAD...... 39 Table 20: Supporting road network materials composition by component...... 41 Table 21: Supporting road network works, GDAD...... 41 Table 22: Predicted annual daily average daily traffic flows (vehicles/day), supporting road network works, GDAD, at short-term, mid-term and long-term horizons...... 43 Table 23: Predicted traffic composition by vehicle type (%), supporting road network works, GDAD, at short-term, mid-term and long-term horizons...... 44 Table 24: Predicted hourly daytime (6:00 to 22:00) and nighttime (22:00 to 6:00) traffic flows (vehicles/hour), supporting road network works, GDAD, at short-term, mid-term and long-term horizons...... 44 Table 25: Project estimated cost...... 50 Table 26: Project financing plan...... 50 Table 27: Land development planning In the GDAD, 2013-2030...... 56 Table 28: Ambient air quality monitoring results, GDAD, June 2018...... 61 Table 29: Compliance of ambient air quality monitoring results with applicable standards...... 61 Table 30: Water quality monitoring data, W1 - Qingyutang cross-section of Maxian River...... 62 Table 31: Water quality monitoring data, W2 - Qiaobian cross-section of Maxian River...... 62 Table 32: Water quality monitoring data, W3 - Kaisa cross-section of Machang River. 63 Table 33: Water quality monitoring data, W4 - Kaizhang Reservoir cross-section of Gan River...... 63 Table 34: Water quality monitoring data, W5 - Gui’an Yungu channel of Gan River. .... 64 Table 35: Water quality monitoring data, W6 - Chetian Village cross-section of Chetian River...... 64 Table 36: Water quality monitoring data, W7 - Siya Cross-section of Siya River...... 65 Table 37: Daytime ambient noise monitoring data, GDAD, June 2018...... 66 Table 38: Current and planned urban greenspace, GDAD...... 67 Table 39: Sensitive receptors near bus stations, and applicable standards...... 70 Table 40: Sensitive receptors near supporting roads, and applicable standards...... 73 Table 41: Sensitive receptors near charging stations, and applicable standards...... 74 Table 42: Other sensitive receptors...... 75 Table 43: Project districts and townships...... 77 Table 44: Comparison of GDP (in CNY) in the City to Guizhou Province and China...... 77 Table 45: Comparison of per capita disposable income in 2017...... 78 Table 46: Existing public transport lines in the GDAD...... 79 Table 47: Vehicle related fugitive dust generation and relationship to vehicle speed and road cleanliness. Unit: kg/vehicle km...... 86 Table 48: Water spraying and dust suppression at construction site test results...... 86 Table 49: Road works construction machinery noise intensity at full load/power, no noise shields...... 87 Table 50: Road construction machinery noise intensity at full load/power at different distances from source, no noise shields...... 88 Table 51: Road construction machinery noise levels compliance with relevant standard, no noise shields...... 88 Table 52: Predicted bus station construction machinery noise intensity at full load/

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power at different distances from source, no noise shields...... 89 Table 53: Predicted bus station construction machinery noise intensity at sensitive sites and compliance with relevant standard (assumes 2.5 m construction boundary wall and noise barriers)...... 89 Table 54: Predicted charging station construction machinery noise intensity at sensitive sites and compliance with relevant standard (assumes 2.5 m construction boundary wall and noise barriers)...... 92 Table 55: Pollutant concentration in road runoff...... 95 Table 56: Bus station on-site wastewater treatment facilities...... 96 Table 57: Vehicle emission factors used in air quality modelling...... 98 Table 58: Predicted NO2 pollution intensities on project roads...... 98 Table 59: Predicted worst case 1-hour NO2 concentrations on all project roads compared to PRC Standard and WHO AQG...... 100 Table 60: Predicted worst case 1-hour NO2 concentrations at sensitive receptors near or adjacent to project roads compared to PRC Standard and WHO AQG... 100 Table 61: Predicted worst case 24-hour NO2 concentrations on all project roads compared to PRC Standard...... 102 Table 62: Predicted worst case 24-hour NO2 concentrations at sensitive receptors near or adjacent to project roads compared to PRC Standard...... 102 Table 63: Predicted average annual NO2 concentrations on all project roads compared to PRC Standard...... 104 Table 64: Predicted average annual NO2 concentrations at sensitive receptors near or adjacent to project roads compared to PRC Standard...... 104 Table 65: Predicted bus station noise source levels, dB (A)...... 106 Table 66: Predicted impact of bus station noise sources at various distances, dB (A)...... 106 Table 67: Predicted maximum noise emissions, 7.5 m from vehicles, on project supporting roads, GDAD, for short-term, mid-term and long-term horizons during operation (unit: dB)...... 108 Table 68: Supporting roads predicted worst case future traffic noise (dB) under three time horizons. Yellow shading designates a predicted exceedance of the Level IVa standard, blue shading designates a predicted exceedance of the Level II standard, Environmental Quality Standard for Noise (GB 3096 - 2008)...... 110 Table 69: Supporting roads predicted future traffic noise (dB(A)) at sensitive receptors, under three time horizons. Predicted noise levels are in compliance with PRC standards, but there are some predicted exceedances of WHO AQGs (highlighted in yellow)...... 115 Table 70: Charging station predicted noise sources, (dB(A))...... 115 Table 71: Predicted noise impacts during operation, (dB(A))...... 116 Table 72: Associated facility road project approvals (for project supporting roads). ... 121 Table 73: Associated facility road EIA approvals (for project supporting roads)...... 121 Table 74: Associated facility road EIA approvals (for bus stations)...... 123 Table 75: Associated facilities for under road municipal infrastructure...... 125 Table 76: Parameters for bus type comparison environmental calculations...... 127 Table 77: GHG and air quality Impact of electric buses versus for Gui’an...... 128 Table 78: Bridge design options. Option 1 was selected on preliminary basis...... 130 Table 79: Summary of public consultation and participation meetings, GDAD...... 132 Table 80: Issues raised during public consultation and project proponent responses. 138

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List of Figures

Figure 1: Guizhou Gui’an New District New Urbanization Smart Transport System Development Project...... 2 Figure 2: ITS roadside detection and monitoring equipment...... 25 Figure 3: Location of ITS Big Data Services Center, GDAD...... 26 Figure 4: Location of Bus Stations, GDAD...... 29 Figure 5: Battery powered electric bus produced by BYD, Hanzhou PRC...... 31 Figure 6: Example of existing charging station near the High Technology Industrial Park in the GDAD...... 33 Figure 7: Two-nozzle bus charger at existing charging station near the High Technology Industrial Park in the GDAD...... 33 Figure 8: Control building, existing charging station near the High Technology Industrial Park in the GDAD...... 34 Figure 9: Electrical control equipment, existing charging station near the High Technology Industrial Park in the GDAD...... 34 Figure 10: Example of parking lot charger, GDAD...... 35 Figure 11: Supporting road network and planned future land use, core area, GDAD. .. 35 Figure 12: Supporting road network and current land use, core area, GDAD...... 36 Figure 13: Cross-section diagram, main roads...... 38 Figure 14: Cross-section diagram, sub-main road...... 38 Figure 15: Cross-section diagram, branch roads...... 39 Figure 16: Underground pipeline layout, main roads. Submain and branch roads will utilize a similar underground pipeline layout...... 42 Figure 17: Changfeng Road Longhu Bridge, which will utilize a diagonal-span cable stay arch design (preliminary design)...... 43 Figure 18: ICVSDZ 1-3-13 model, with a data center which collects and analyses data retrieved from three platforms for thirteen applications...... 46 Figure 19: Gui’an New Area High-End Equipment Industry Park and indicative testing roads for ICVs...... 47 Figure 20: Overall project implementation chart...... 50 Figure 21: GDAD in relation to Gui’an New District and Guiyang, the capital of Guizhou...... 52 Figure 22: GDAD topography...... 53 Figure 23: GDAD elevation profile from west (left) to east (right)...... 54 Figure 24: GDAD elevation profile from north (left) to south (right)...... 54 Figure 25: GDAD landuse plan for 2020 planning horizon...... 55 Figure 26: Climatograph, Guiyang City...... 57 Figure 27: Wind rose, Guiyang Longdongbao Airport...... 57 Figure 28: Water resources in the GDAD...... 58 Figure 29: Current water resources in the core area of the GDAD with elevations. Green dots indicate control gates...... 59 Figure 30: Drinking water source protection zones in the GDAD...... 60 Figure 31: Location of GEPB air quality monitoring stations in the GDAD...... 60 Figure 32: Location of GEPB water quality monitoring points in the GDAD...... 61 Figure 33: Location of GEPB sound quality monitoring points in the GDAD...... 66 Figure 34: Planned urban development area (highlighted in red) within the GDAD. .... 68 Figure 35: Aerial and ground images from project road 12-H4...... 69 Figure 36: Aerial images showing degree of development and vegetation clearance in area of project roads 7-H11, 10-Z4, and 1-#5 (right)...... 70 Figure 37: Aerial images showing Tonji Hospital boundary in relation to #5 Road ...... 74 Figure 38: Road network, GDAD...... 79 Figure 39: Existing bus routes in the GDAD...... 81 Figure 40: Project zone of influence...... 82 Figure 41: Map of spoil disposal sites in the GDAD...... 85

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Figure 42: Contour map of predicted worst case 1-hour NO2 concentrations on project roads...... 101 Figure 43: Contour map of predicted worst case 24-hour NO2 concentrations on project roads...... 103 Figure 44: Contour map of predicted annual NO2 concentrations on project roads.... 105 Figure 45: Supporting roads predicted future traffic noise (dB), 2020 time horizon, daytime...... 112 Figure 46: Supporting roads predicted future traffic noise (dB), 2020 time horizon, nighttime...... 112 Figure 47: Supporting roads predicted future traffic noise (dB), 2026 time horizon, daytime...... 113 Figure 48: Supporting roads predicted future traffic noise (dB), 2026 time horizon, nighttime...... 113 Figure 49: Supporting roads predicted future traffic noise (dB), 2034 time horizon, daytime...... 114 Figure 50: Supporting roads predicted future traffic noise (dB), 2034 time horizon, nighttime...... 114 Figure 51: GHG emissions of LNG buses and BEBs...... 127 Figure 52: Reductions in grid factor in China over time...... 128 Figure 53: Changfeng Road Longhu Bridge, diagonal-span cable-stay arch design option...... 129 Figure 54: Changfeng Road Longhu Bridge, steel tube arch design option...... 129 Figure 55: Changfeng Road Longhu Bridge, intertwined twin-wave arch design option...... 130 Figure 56: Locations of public consultation and participation meetings, GDAD...... 132 Figure 57: BEGDA letter to local governments requesting public consultation meetings...... 133 Figure 58: Public consultation meetings, September 27th to 31st, 2018...... 134 Figure 59: Translation of the public consultation questionnaire...... 135 Figure 60: Example of completed public consultation questionnaire...... 137

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EXECUTIVE SUMMARY

A. Introduction i. This is the Initial Environmental Examination (IEE) report for report for the proposed Guizhou Gui’an New District New Urbanization Smart Transport System Development Project (the project) in Guizhou Province in the People’s Republic of China (PRC). The Gui'an New District has a total area of 1,750 km2, though the focus of the project is the Gui’an Direct Administrative District (GDAD), which is under the authority of the Gui’an New District Management Committee (GNDMC) and has an area of 470 km2.

ii. ADB’s environmental safeguard requirements are specified in the Safeguard Policy Statement (SPS, 2009). The project has been screened and classified by ADB as Environment Category B, requiring the preparation of an IEE (this report) including an environmental management plan (EMP). The EMP is presented in Appendix A.

iii. This report has been prepared based on a domestic Feasibility Study Report (FSR); a domestic environmental impact table (EIT) report; additional baseline data collection and analyses undertaken by the domestic EIT consultant under the direction of an ADB PPTA team; site visits and analyses conducted by the PPTA team; ADB review mission discussions and agreements with relevant government agencies; and, consultations with affected persons and stakeholders.

B. Project Description

iv. The proposed project will assist the GNDMC in developing innovative solutions for green transport infrastructure and mitigating potential traffic congestion and other related negative environmental impacts by providing high-technology clean-energy, intelligent transport systems.

v. The project will be implemented through three outputs:

(i) Output 1: Intelligent transport system designed and installed. A comprehensive intelligent transport system (ITS) will be developed to provide an integrated solution to address traffic management, safety and infrastructure capacity issues. The ITS will cover all aspect of the transport system, including private and commercial vehicles, public transport, non-motorized transport (bicycles and pedestrians), parking, and other services.

(ii) Output 2: Sustainable transport infrastructure built. Bus stations with multimodal connectivity, smart parking lots and supporting urban roads will be developed. This infrastructure will work together with ITS elements to optimize infrastructure and overall urban mobility. New zero-emission buses will be purchased to increase the bus route coverage in the GDAD and reduce emissions from public transport services. In addition, electric charging stations for both private and public vehicles will be installed throughout the area. Information about the status of buses and charging stations will be readily available to operators and users as part of the ITS. In addition, an Intelligent Connected Vehicle System Demonstration Zone (ICVSDZ) for research and development of Intelligent Connected Vehicle (ICVs) and associated technologies will be established, including a data center platform, the application of information technologies in transport infrastructure within a designated testing zone: a controlled industrial park and 2.5 km of adjacent public open-roads. The ICVSDZ component will be further developed during detailed design.

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(iii) Output 3: Smart transport capacity strengthened. Capacity strengthening activities will be provided to ensure relevant and up-to-date ITS and clean transport technology is available at design, implementation, and operation phases. Project management consulting services, including environmental technical support, will be provided. vi. The project is estimated to cost $495.47 million, of which ADB has been requested to finance $200 million from its ordinary capital resources. The GGAND will finance the remaining $295.47 million equivalent. The construction period will be 3.5 to 4 years from 2019 to 2023. The project is expected to begin full operation in 2024, and will have a 30 year life span.

C. Project Benefits vii. The project will benefit 1.4 million residents of the GDAD by 2030, including both public transport users and non users. Users will benefit from the improved transit service provide by the zero-emission bus stations and buses. Residents who are non-users will also benefit from access to car charging stations, reduced traffic congestion, improved road access safety, and reduced air pollution.

D. Project Impacts and Mitigation Measures viii. The project zone of influence is defined as:

i) 200 m zones around the boundary of the bus stations with respect to noise impacts, and 500 m zones with respect to air pollution impacts; ii) 200 m zones perpendicular to either side of the roads with respect to noise impacts, and 500 m zones with respect to air pollution impacts; and iii) 50 m zones around charging stations (if not within project bus stations) and associated substations. iv) 50 m zone around the ICVSDZ testing area. ix. Siting and Land Acquisition. The project will acquire 698.57 mu (46.57 ha) of land. The project has been classified as resettlement category B and a Resettlement Plan (RP) with time-bound actions has been prepared under a separate process, supported by a due diligence review by ADB social safeguard specialists. The PMO will appoint a dedicated Safeguards officer to handle all safeguard aspects. The PMO team will be supported by the PMC in the implementation of the RP. An external monitoring agency will be hired to monitor the RP implementation. x. Construction Phase. Potential negative construction phase environmental impacts are short-term and localized, and are associated with fugitive dust, construction noise, wastewater, solid waste, disruption of traffic, and risks to worker health and safety. These will be effectively mitigated through good construction and health and safety practices, including construction soil and spoil management; dust controls including site watering and the use of ready-mix concrete; noise controls including limiting times when noisy activities can occur, selecting low noise equipment and scheduling materials delivery to avoid densely populated or sensitive areas; water quality protection measures including managing site runoff and provision of worker sanitary facilities; good solid and hazardous waste management practices; and good health, safety and emergency response procedures. Construction will not affect any parks, protected areas or rare or threatened flora or fauna species.

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xi. Operation Phase. Potential negative operation phase impacts include runoff from roads and stations which may pollute surface waters; wastewater produced at the stations; emissions from vehicles on the project roads; noise from stations, buses and cars; hazardous materials from bus service areas; end-of-life buses and batteries that require replacement; and potential safety risks from ICV testing. These impacts will be effectively mitigated through good design, including, for example, road-side bio-retention facilities to treat storm water runoff, and noise control measures incorporated into bus station design; good waste and health and safety management practices including effective recycling of busses and bus batteries; and good ICV testing and safety plans and practices.

xii. Climate Change. A Climate Risk and Vulnerability Assessment (CRVA) was undertaken for the project (Appendix I). Compared to the historical baseline, the annual average maximum temperature is projected to increase by 1.48 °C and 2.01 °C, respectively, in the near-term future to 2050 under the low and high scenarios, and by 2.88 °C to 5.02 °C, respectively, in the long-term future to 2100. Annual average minimum temperature is projected to increase by 1.35 °C and 1.72 °C under the low and high scenarios, respectively, in the near-term future to 2050, and by 2.47 °C and 4.60 °C in the long-term future to 2100. xiii. Annual average precipitation is projected to increase by 2.1% in the near-term future to 2050 and decrease by 6.5% in the long-term future to 2100 under the low scenario. Under the high scenario, it is projected to increase by 5.8% in the near future to 2050 and increase by 7.4% in the long-term future to 2100, respectively. These projected results indicate that the annual precipitation in Gui’an is likely to be roughly steady in the future under the low scenario, but will increase by 5.8 to 7.4% under the high scenario. xiv. The highest risk that climate change likely poses to the project areas in Gui’an is higher flood peak flows because of increased intensity of storm events. The CRVA recommended climate change adaptation measures to augment the design peak runoff inflow and flood of relevant drainage. To be conservative, the CRVA recommended that the intensity of design storms be augmented by 10% in designing road systems and sizing drainage pipes/channels that are associated with the transport infrastructure works in this project for climate change adaptation. This recommendation has been incorporated into all project design decisions that require estimated magnitude of design (rainfall, flood) events. In addition, the potential effects of increased storm peak flows due to climate change will also be considered in siting the locations of important facilities and water-proofing project components including electrical equipment.

E. Environmental Management Plan xv. A comprehensive EMP was developed to ensure: (i) implementation of identified mitigation and management measures to avoid, reduce, mitigate, and compensate for anticipated adverse environment impacts; (ii) implementation of monitoring and reporting; and (iii) project compliance with the PRC’s relevant environmental laws, standards and regulations and ADB’s SPS. Organizational responsibilities and budgets are clearly identified for execution, monitoring and reporting. xvi. The EMP includes a project-level grievance redress mechanism (GRM), established to receive and facilitate resolution of complaints about the project during the preconstruction, construction and operation phases. The GRM includes procedures for receiving grievances, documenting key information, and evaluating and responding to the complainants in a reasonable time period.

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F. Information Disclosure, Consultation and Participation xvii. The domestic EIT (in Chinese) is available on request at the PMO, and was disclosed on the Construction Project EIA Publicity System of Guizhou Province website (http://202.98.194.159:6661/wwgs/index.jsp). xviii. Four public consultation and participation meetings were conducted during project preparation at sites spread across the GDAD, selected so as to maximize coverage of project activities. A total of 118 representatives from the affected areas attended the meetings, and a questionnaire was distributed. The results show that 100% of participants anticipate that the project will have a positive effect on the local economy, and 98% indicated that they support the project (94%) or find it acceptable (4%). xix. As the ICVSDZ component will be further developed during detailed design, only preliminary stakeholder consultations have been undertaken, including meetings with the Gui’an New Area Police Department, the Planning and Construction Bureau, the Land Resource Bureau, the Economic Development Bureau, and representatives of the Gui’an New Area High-End Equipment Industry Park. Representatives from the industrial park Investment Department, Development Department, Operations Department and Legal Department also participated. xx. Meaningful consultation will continue throughout detailed design, construction and operation phases, including information disclosure by the project proponent, posting of project information on community notice boards, and ICVSDZ public consultations.

G. Key EMP Implementation Responsibilities xxi. The GGAND will be the EA, but will be represented by the Bureau of Economic Development of Gui’an New District (BEDGA). A project management office (PMO) has been established under the EA to manage the project implementation on a daily basis, and will act as the implementing agency (IA). xxii. Three project implementation units (PIUs) will be established under the guidance of the PMO in (i) Construction Investment Company, (ii) Culture and Tourism Investment Company, and (iii) Industrial Investment Company. The three PIUs will assist the PMO in the implementation of supporting roads, bus hubs and buses, and charging stations, respectively. These companies are Gui’an state-owned enterprises and have technical experience in project implementation, operation and maintenance. The PMO will be in-charge of all other project components and subcomponents, including ITS, bus terminal and depot construction, ICVSDZ and capacity development.

H. Risks and Assurances xxiii. The project has few unusual technical risks and conventional engineering designs with proven reliability and performance will be adopted. From an environment safeguards perspective, the main risk relates to the failure of the PMO, PIUs and operational units to monitor environmental impacts and implement the EMP during the construction and operation phases. There are also potential safety risks associated with autonomous ICV testing. These risks will be mitigated by (i) providing training in environmental management and ICV safety; (ii) appointing qualified project implementation consultants including an Independent ICV Expert Team; (iii) following appropriate project implementation monitoring and mitigation arrangements; (iv) ADB conducting regular project reviews; and (v) project assurances covenanted in the loan and project agreements with ADB.

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I. Conclusion xxiv. The project IEE has: (i) identified potential negative environment impacts and established mitigation measures; (ii) assessed public support from the project beneficiaries and affected people; (iii) established a project GRM; and (iv) prepared a project EMP, including environmental management and supervision structure, environmental mitigation and monitoring plans, and capacity building and training. xxv. It is concluded that the project will not result in adverse environmental impacts that are irreversible, diverse, or unprecedented. Any minimal adverse environmental impacts associated with the project will be prevented, reduced, or minimized through the implementation of the project EMP.

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I. INTRODUCTION

1. This is the Initial Environmental Examination (IEE) report for the proposed Guizhou Gui’an New District New Urbanization Smart Transport System Development Project (the project) in Guizhou Province in the People’s Republic of China (PRC) (Figure 1). The Gui'an New District has a total area of 1,750 km2, though the focus of the project is the Gui’an Direct Administrative District (GDAD), which is under the authority of the Gui’an New District Management Committee (GNDMC) and has an area of 470 km2.

2. The proposed project will assist the GDAD in developing innovative solutions for green transport infrastructure and mitigating potential traffic congestion and other related negative environmental impacts by providing high-technology clean-energy intelligent transport systems.1

3. The project will be implemented through three outputs:

(i) Output 1: Intelligent transport system designed and installed. A comprehensive intelligent transport system (ITS) will be developed to provide an integrated solution to address traffic management, safety and infrastructure capacity issues. The ITS will cover all aspect of the transport system, including private and commercial vehicles, public transport, non-motorized transport (bicycles and pedestrians), parking, and other services.

(ii) Output 2: Sustainable transport infrastructure built. Bus stations with multimodal connectivity, smart parking lots and supporting urban roads will be developed. This infrastructure will work together with ITS elements to optimize infrastructure and overall urban mobility. New zero-emission buses will be purchased to increase the bus route coverage in the GDAD and reduce emissions from public transport services. In addition, electric charging stations for both private and public vehicles will be installed throughout the area. Information about the status of buses and charging stations will be readily available to operators and users as part of the ITS. In addition, an Intelligent Connected Vehicle System Demonstration Zone (ICVSDZ) for research and development of ICV and associated technologies will be established, including a data center platform, the application of information technologies in transport infrastructure, and closed-road testing of three ICVs in a fenced and access- controlled industrial park and 2.5 kilometers (km) of adjacent public open-roads.

(iii) Output 3: Smart transport capacity strengthened. Capacity strengthening activities will be provided to ensure relevant and up-to-date ITS and clean transport technology is available at design, implementation, and operation phases. Project management consulting services, including environmental technical support, will be provided.

4. The project will benefit 1.4 million residents of the GDAD by 2030, including both public transport users and non users. Users will benefit from the improved transit service provide by the zero-emission bus stations and buses. Residents who are non-users will also benefit from access to car charging stations, reduced traffic congestion, improved road safety, and reduced air pollution.

1 The project is included in the People's Republic of China: Country Operations Business Plan (2017–2019).

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Figure 1: Guizhou Gui’an New District New Urbanization Smart Transport System Development Project.

Source: ADB, 2019.

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5. The project is estimated to cost $495.47 million. The construction period will be 3.5 to 4 years from 2019 to 2023. The Government of Gui’an New District (GGAND) will be the EA, but will be represented by the Bureau of Economic Development of Gui’an New District (BEDGA). A project management office (PMO) has established to manage the project implementation on a daily basis, and will act as the implementing agency (IA).

6. ADB’s environmental safeguard requirements are specified in the Safeguard Policy Statement (SPS, 2009). The project has been screened and classified by ADB as Environment Category B, requiring the preparation of an IEE (this report) including an environmental management plan (EMP). The EMP is presented in Appendix A.

7. This report has been prepared based on domestic Feasibility Study Reports (FSRs) (approval expected in March 2019);2 a technical due diligence review of the FSR undertaken by ADB PPTA technical specialists;3 an approved domestic environmental impact table (EIT) report;4 additional baseline data collection and analyses undertaken by the domestic EIT consultant under the direction of the PPTA team; site visits and analyses conducted by the PPTA team; ADB review mission discussions and agreements with relevant government agencies; and consultations with affected persons and stakeholders.

2 Feasibility Study Report for Public Transportation Infrastructure Construction Project in Gui’an New District, 2018; Feasibility Study Report for Road Network Enhancement Project in Gui'an Central District (Phase I), 2018; Feasibility Study Report for Electric Vehicle Charging Network in Gui’an New District, 2018; Feasibility Study Report on Autonomous Vehicle and Cooperative Vehicle Infrastructure System, 2018. 3 TA-9437 PRC: Supporting Project Preparation - Subproject: Guizhou Gui'an New District Smart Transport System Development. 4 Construction Project Environmental Impact Statement, Guizhou Gui’an New District New Urbanization Smart Transport System Development Project. Owner: Economic Development Bureau of Gui’an New District Administration Committee, Guizhou Province. Prepared by the Environment Science Institute. Approved 16 January by Gui’an New Area EPB.

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II. POLICY, LEGAL, AND ADMINISTRATIVE FRAMEWORK

A. Applicable ADB Policies, Regulations and Requirements

8. The major applicable ADB policies, regulations, requirements and procedures for environmental management and environmental impact assessment (EIA) are the Safeguard Policy Statement (SPS, 2009) and the Environmental Safeguards – A Good Practice Sourcebook (2012), which jointly provide the basis for this IEE. The SPS promotes good international practice as reflected in internationally recognized standards such as the World Bank Group’s EHS Guidelines. The policy is underpinned by the ADB Operations Manual for the SPS (OM Section F1, 2010).

9. The SPS establishes an environmental review process to ensure that projects undertaken as part of programs funded through ADB loans are environmentally sound, are designed to operate in compliance with applicable regulatory requirements, and are not likely to cause significant environment, health, social, or safety hazards.

10. At an early stage in the project cycle, typically the project identification stage, ADB screens and categorizes proposed projects based on the significance of potential project impacts and risks. Project screening and categorization are undertaken to:

i) reflect the significance of the project’s potential environmental impacts; ii) identify the type and level of environmental assessment and institutional resources required for the safeguard measures proportionate to the nature, scale, magnitude and sensitivity of the proposed project’s potential impacts; and, iii) determine consultation and disclosure requirements.

11. A project’s environment category is determined by the category of its most environmentally sensitive component, including direct, indirect, induced, and cumulative impacts. ADB assigns a proposed project to one of the following categories:

i) Category A. Proposed project is likely to have significant adverse environmental impacts that are irreversible, diverse, or unprecedented; impacts may affect an area larger than the sites or facilities subject to physical works. A full-scale EIA including an environmental management plan (EMP), is required. ii) Category B. Proposed project’s potential environmental impacts are less adverse and fewer in number than those of category A projects; impacts are site-specific, few if any of them are irreversible, and impacts can be readily addressed through mitigation measures. An IEE, including an EMP, is required. iii) Category C. Proposed project is likely to have minimal or no adverse environmental impacts. No EIA or IEE is required although environmental implications need to be reviewed. iv) Category FI. Proposed project involves the investment of ADB funds to, or through, a financial intermediary.

12. The project has been classified by ADB as environment category B, requiring the preparation of an IEE (this report).

13. The SPS 2009 requires a number of additional considerations, including: (i) project risk and respective mitigation measures and project assurances; (ii) project-level grievance redress mechanism; (iii) definition of the project area of influence; (iv) physical cultural resources damage prevention analysis; (v) climate change mitigation and adaptation; (vi) occupational and community health and safety requirements (including emergency preparedness and response); (vii) economic displacement that is not part of land acquisition; (viii) biodiversity conservation and natural resources management requirements; (ix)

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provision of sufficient justification if local standards are used; (x) assurance of adequate consultation and participation; and (xi) assurance that the EMP includes an implementation schedule and measurable performance indicators. These requirements, which may not be covered in the domestic EIT, have been considered, and all applicable environmental requirements in the SPS 2009 are covered in this IEE.

14. During the design, construction, and operation of a project the SPS also requires the borrower to follow environmental standards consistent with good international practice, as reflected in internationally recognized standards such as the World Bank Group’s Environment, Health and Safety Guidelines (hereafter referred to as the EHS Guidelines).5 The EHS Guidelines includes both general EHS guidelines and industry sector guidelines. The general EHS Guidelines contains (i) environmental guidelines on discharge effluent, air emissions, and other numerical guidelines; (ii) occupational health and safety guidance; (iii) community health and safety guidance; and (iv) construction and decommissioning guidelines.

15. The EHS guidelines also include performance indicators and prevention and control approaches that are normally acceptable to ADB and are generally considered to be achievable at reasonable costs by existing technology. When host country regulations differ from these levels and measures, the borrower/client is to achieve whichever is more stringent. If less stringent levels or measures are appropriate in view of specific project circumstances, the borrower/client is required to provide justification for any proposed alternatives.

B. ADB Assistance to PRC

16. The project is aligned with the key thrusts of ADB's assistance to the PRC under the PRC Country Partnership Strategy (CPS)6 in the areas of: (i) managing climate change and the environment, such as transportation modes with lower emissions and energy consumption, sustainable urban public transport systems; and (ii) supporting inclusive economic growth (reducing poverty and inequality), so as to promote integrated, green, inclusive and competitive urban development, focusing on small and medium-sized cities in less-developed regions that can be used as a model for other cities in Asia and support city cluster development, including urban infrastructure development and institutional coordination.7 The focus on public transport and multi-modal integration also fits well with ADB's Sustainable Transport Initiative (STI).8

C. PRC Public Transport Policies

17. A number of high level policy decisions have emphasized that public transport is a PRC national priority:  The PRC Thirteenth Five-Year Plan (2016–2020) prioritizes implementing public transport policy, speeding up development of large-capacity public transport, and encouraging green travel operations.

5 World Bank Group, Environmental, Health, and Safety Guidelines, April 30, 2007, Washington, USA. http://www.ifc.org/ifcext/enviro.nsf/Content/EnvironmentalGuidelines 6 Asian Development Bank. 2016. Transforming partnership: People’s Republic of China and Asian Development Bank, 2016-2020. Manila. 7 Transit-oriented development refers to mixed-use residential and commercial areas designed to maximize access to public transport and facilitate pedestrian movement. A transit-oriented development is typically centered on a transit station (train station/metro station/bus terminal), surrounded by relatively high-density development with progressively lower-density development further from the high capacity public transport facility. 8 The STI, approved by ADB management on 20 July 2010, has set a new direction for ADB's transport sector efforts to promote more environmentally and socially sustainable transport solutions in DMCs in line with ADB's Strategy 2020.

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 The Ministry of Construction (MoC) issued Opinions on Prioritizing the Development of Urban Public Transport (No. 38 urban construction[2004]) in March 2004, emphasizing the role of urban transport planning, speeding up the construction of public transport infrastructure such as multi-modal hubs and depots, optimizing the operation structure of public transport, and ensuring public transport priority.  In September 2006 the General Office of Guizhou Provincial People's Government issued Implementation Opinions on Prioritizing the Development of Urban Public Transport (No. 91 of the Guizhou Provincial Office of Public Transport). The objectives are to give priority to the development of public transport, and to direct city governments to implement in accordance with the national public transport strategy.  In December 2012 the State Council issued the Opinions on Prioritizing the Development of Urban Public Transport (No. 64, National Development [2012]. The document requires cities to speed up the transformation of urban transport development, highlights the social benefit of urban public transport, puts public transport development in the primary position in urban transport development, and focusses on improving urban public transport security. It also stresses the importance of planning regulations so that land resources can be secured for the development public transport infrastructure.  In 2017 the Government of Gui'an New Area District (GGAND) commissioned the China Urban Planning and Design Institute to prepare "Gui'an New District Public Transportation Planning".

18. With respect to land use planning, in January 2014 the State Council released the Official Reply of State Council on approving the Establishment of Guizhou Gui’an New District, and in June 2014, the Provincial Government approved the Masterplan of Gui’an New District (2013-2030).

19. Overall, the proposed project is fully consistent with and supportive of the PRC public transport policy framework, and the urban planning framework for the Gui’an New District and the GDAD.

D. PRC Environmental Legal Framework

20. The environmental protection and management system in the PRC consists of a well- defined hierarchy of regulatory, administrative and technical institutions. At the top level the People’s Congress of the PRC has the authority to pass and revise national environmental laws; the Ministry of Ecology and Environment (MEE) under the State Council promulgates national environmental regulations; and the MEE either separately or jointly with the Administration of Quality Supervision, Inspection and Quarantine issues national environmental standards and guidelines. Provincial and local governments can also issue provincial and local environmental regulations and guidelines in accordance with the national ones. In addition, national and local five-year environmental protection plans form an important part of the legal framework.

21. Key PRC environmental laws are listed in Table 1, including associated regulations and decrees that support their implementation. Guidelines for EIA implementation are listed in Table 2.

22. The most far-reaching legislation on pollution prevention and control is the Environmental Protection Law (EPL) (1989, amended 2014, effective 2015 and item 2 in Table 2), which sets out key principles for the nation’s pollution control system, including the “Three Simultaneities policy,9 the application of pollution levy’s, and EIA requirements. The

9 The “Three Simultaneities Policy” requires the design, construction, and operation of pollution control and treatment facilities to occur simultaneously with the project design, construction, and operation.

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implementation of the “Three Simultaneities” was further strengthened by implementation decrees (items 26 and 28 Table 1) and the Construction Project Environmental Protection Management Regulation (item 17 Table 1).

Table 1: Applicable PRC environmental laws, regulations and decrees. Issued/ No. Laws Updated 1 Environmental Impact Assessment Law 2016 2 Environmental Protection Law 2015 3 Atmospheric Pollution Prevention and Control Law 2015 4 Occupational Disease Prevention and Control Law 2011 5 Water and Soil Conservation Law 2011 6 Water Pollution Prevention and Control Law 2010 7 Urban and Rural Planning Law 2008 8 Solid Waste Pollution Prevention and Control Law 2005 9 Water Law 2002 10 Cultural Relics Protection Law 2002 11 Noise Pollution Prevention and Control Law 1999 12 Labor Law 1995 Regulations 13 Atmospheric Pollution Prevention and Control Action Plan (State Council Announcement 2013 No. 37) 14 Policy on Integrated Techniques for Air Pollution Prevention and Control of Small 2013 Particulates (MEE Announcement No. 59) 15 Planning Environmental Impact Assessment Regulation 2009 16 Cultural Relics Protection Law Implementation Regulation 2003 17 Construction Project Environmental Protection Management Regulation 1998 18 Wild Plant Protection Regulation 1996 Decrees and Announcements 19 Directory for the Management of Construction Project EIA Categorization (MEE Decree 2015 2015-33) 20 Measures for Public Participation in Environmental Protection (MEE Decree 2015-35) 2015 21 Management Measures for Environmental Impact Post Assessment of Construction 2015 Projects (on trial) (MEE Decree 2015-37) 22 Government Information Disclosure of Construction Project EIA (on trial) (MEE 2013 Announcement No. 103) 23 Measures for Environmental Supervision (MEE Decree 2012-21) 2012 24 Requirement for Preparation of EIA Report Summary (MEE Announcement 2012-51) 2012 25 Strengthening of EIA Management for Prevention of Environmental Risk (MEE 2012 Announcement 2012-77) 26 Opinion from the State Council on Important Tasks for Strengthening Environmental 2011 Protection (State Council Announcement 2011-35) 27 Management Measures for Operation of the Environmental Complaint Hotline (MEE 2010 Decree 2010-15) 28 Management Procedures for the Supervision, Inspection and Environmental Acceptance 2009 of Construction Projects under the “Three Simultaneities” (on trial) (MEE Announcement 2009-150) 29 Specifications on the Management of Urban Construction and Demolition Waste (Ministry 2005 of Construction Decree 2005-139) 30 Management Measures for Inspection and Acceptance of Environmental Protection at 2001 Construction Project Completion (MEE Decree 2001-13) Source: ADB PPTA consultants.

23. The amended EPL further defines enforcement and supervision responsibilities for all levels of environmental protection authorities, imposes stricter obligations and more severe penalties on enterprises and construction units regarding pollution prevention and control, and allows for environmental public interest litigation including through nongovernment organizations. The procedures and requirements for the technical review of EIA reports by authorities have been specified (Table 2, item 4), and environmental inspection and

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enforcement on design, installation, and operation of project-specific environmental protection and control measures are regulated under the “Three Simultaneities” (Table 1, items 5, 15, 25, 26, and 28).

Table 2: PRC EIA Guidelines. Guidelines Date 1 HJ 192-2015 Technical Criterion for Ecosystem Status Evaluation 2015 2 HJ 130-2014 Technical Guidelines for Planning EIA - General Principles 2014 3 HJ 663-2013 Technical Regulation for Ambient Air Quality Assessment (on trial) 2013 4 HJ 2.1-2011 Technical Guidelines for EIA – General Program 2011 5 HJ 19-2011 Technical Guidelines for EIA – Ecological Impact 2011 6 HJ 616-2011 Guidelines for Technical Review of EIA on Construction Projects 2011 7 HJ 623-2011 Standard for the Assessment of Regional Biodiversity 2011 8 HJ 630-2011 Technical Guideline on Environmental Monitoring Quality 2011 Management 9 Technical Guidelines for EIA - Public Participation (public comment version), (Jan. 2011 2011) 10 HJ 610-2011 Technical Guidelines for EIA – Groundwater Environment 2011 11 HJ 2.4-2009 Technical Guidelines for EIA – Acoustic Environment 2009 12 HJ 2.2-2008 Technical Guidelines for EIA – Atmospheric Environment 2008 13 HJ/T 393-2007 Technical Specifications for Urban Fugitive Dust Pollution 2007 14 JG/J 146-2004 Environmental and Hygiene Standards for Construction Sites 2004 15 HJ/T 2.3-1993 Technical Guidelines for EIA – Surface Water Environment 1993 Source: ADB PPTA consultants.

24. Public participation and environmental information disclosure provisions are among the most significant changes introduced in the amended EPL, further supported by the decrees on the preparation of EIA summaries for the purpose of public disclosure (Table 1, item 24), information disclosure on construction project EIAs by government (Table 1, item 22), method for public participation in environmental protection (Table 1, item 20), and technical guidelines for public participation in EIAs.

25. For grievance redress, a hotline number (12369) was established in March 2011 at each level of environmental protection authority throughout the nation for receiving and resolving environmental complaints, in accordance with the Management Measures for Operation of the Environmental Complaint Hotline (MEE Decree [2010] No. 15] (Table 1, item 27).

26. The PRC also provides protection for community health and occupational health and safety through the Labor Law (1994) (Table 1, item 12), the Occupational Disease Prevention and Control Law (2001) (Table 1, item 4), and environmental and hygiene standards for construction sites.

27. With respect to electric vehicle (EV) batteries, Interim Measures for the Administration of Recycling and Utilization of New Energy Vehicles' Power Battery was jointly issued by the Ministry of Industry and Information Technology, the Ministry of Science and Technology, the Ministry of Environmental Protection, the Ministry of Transport, the Ministry of Commerce, the General Administration of Quality Supervision, Inspection and Quarantine, and became effective on August 1, 2018. EV manufacturers are responsible for the recovery of EV batteries. They are required to set up recycling channels and service outlets where old batteries can be collected, stored, and transferred to specialty recyclers. In 2018 the Ministry of Information and Technology also issued Interim Provisions on the Management of Traceability of Recycling and Utilization of New Energy Vehicles. Together with battery makers and their sales units, EV manufacturers must set up a “traceability” system that

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enables the identification of owners of discarded batteries. Battery makers are also encouraged to adopt standardized and easily dismantled product designs to help automate the recycling process. They must also provide technical training for vehicle makers to store and dismantle old batteries.

E. Intelligent Connected Vehicles (ICV)

28. The primary ICV regulation in the PRC is the Management Regulation for Intelligent Connected Vehicle Road Testing (for trial implementation), jointly issued by the Ministry of Public Security (MPS), the Ministry of Industry and Information (MII), and the Ministry of Transportation (MoT) in April 2018. ICV testing will be managed by relevant provincial and authorities10, usually through the formation of a Steering Committee, which will report back to the three national ministries. The regulations require the presence in test vehicles of a safety driver with at least three years driving experience and a clean record over the past 12 months. Testing companies are responsible for training their safety drivers, providing support in emergency situations on the road, and assume full liability for the vehicle’s actions during testing. Test vehicles must be new and able to switch from self-driving mode to manual operation efficiently, safely and instantly. They must have the capacity for real-time monitoring, recording, and storing of vehicle status, control mode information (self-driving or manual), location, direction and speed. Vehicles must also record environment perception and response data, headlight and turn signal status, and provide 360-degree video monitoring.

29. The ICV regulatory framework in the PRC and other countries is described in more detail in Appendix K.

F. PRC Environmental Impact Assessment Framework and Procedures

30. EIA Administrative Framework. The PRC administrative framework consists of national, provincial, and local (city and county) environmental protection authorities. The national authority is the MEE, which promulgates laws, regulations, administrative decrees, technical guidelines, and environmental quality and emission standards on EIA and pollution prevention and control. At the provincial level there are Environmental Protection Departments (EPDs), which act as gatekeepers for EIA and pollution prevention and control in the provinces. They are often delegated authority by the MEE to approve EIA reports for development planning and construction projects, except for those projects with national interest or which cross provincial boundaries. Local (city or county level) Environmental Protection Bureaus (EPB) enforce environmental laws and conduct environmental monitoring within city or county limits. EPBs can also be delegated the authority to approve EIA reports by the provincial EPDs. EPDs and EPBs are supported by Environmental Monitoring Stations (EMS), which are subsidiaries of EPDs or EPBs and are qualified entities to carry out environmental monitoring.11

31. The PRC has an EIA qualification and registration system, and only qualified and registered institutes and individuals are allowed to prepare EIAs. Under MEE Decree 2015- 36, as of 1 November 2015 qualified institutes for conducting EIAs for construction projects in the PRC can no longer be a subsidiary of an environmental authority responsible for approving EIAs.

10 Includes industry and information technology departments, traffic management departments subordinate to the public security organ and the transportation departments of provinces, autonomous regions, municipalities directly under the central government, municipalities with independent planning status, and the Production and Construction Corps. 11 In this report, “environmental monitoring” refers to the activity of collecting environmental data either through in-situ measurements or through sampling followed by laboratory testing of samples.

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32. EIA Legal Framework. EIA in the PRC is governed by the Environmental Impact Assessment Law (2002) (Table 1, item 1), covering EIAs for (i) plans (such as new development areas and new industrial parks) and strategic environmental assessments (SEA); and (ii) construction projects. This was followed by the promulgation of two regulations: the Construction Project Environmental Protection Management Ordinance (1998) (Table 1, item 17) and the Planning Environmental Impact Assessment Regulation (2009) (Table 1, item 15), both of which require early screening and environmental categorization.

33. EIA Procedures. Under MEE decree Directory for the Management of Construction Project Environmental Impact Assessment Categorization (MEE Decree 2015-33) (1, item 19), classifies EIAs for construction projects into three categories with different reporting requirements, based on the significance of potential environmental impacts and the environmental sensitivity12 of the project site:

i) Projects with significant adverse environmental impacts, for which a full environmental impact report (EIR) is required; ii) Projects with adverse environmental impacts which are of a lesser degree and/or significance than those of Category A, for which a tabular environmental impact report (EIT) is required; and iii) Projects unlikely to have adverse environmental impacts, for which an environmental impact registration form (EIRF) is required.

34. EIR and EITs report are generally equivalent to ADB’s Category A EIA and Category B IEE reports, respectively. The EIRF is similar to an ADB Category C.

35. EIA Follow-Up Actions. In 2015 the MEE issued decree Management Measures for Environmental Impact Post Assessment of Construction Projects (MEE Decree 2015-37, item 21). Under this decree a trial program was implemented on 1 January 2016 requiring follow-up actions 3 to 5 years after commencement of project operation for large infrastructure and industrial projects or projects located in environmentally sensitive areas. These actions include environmental monitoring and impact assessment to verify the effectiveness of environmental protection measures and to undertake any corrective actions that might be needed. The decree also specifies that the institute that did the original impact assessment for the project cannot undertake environmental impact post assessment for the same project.

36. EIA Guidelines. The MEE has issued a series of technical guidelines for preparing EIAs (Table 2). These include impact assessment guidelines on general EIA implementation and principles, atmospheric environment and ambient air quality, noise, surface water, groundwater, ecology and regional biodiversity, biodiversity monitoring, quality management on environmental monitoring, and public participation.

G. Project Domestic Environmental Assessment

37. Under MEE Decree Management Measures for Environmental Impact Post Assessment of Construction Projects (MEE Decree 2015-37) the project was classified as

12 Environmentally sensitive areas are defined in the Decree, and include: (i) nature reserves and protected areas, scenic areas, world cultural and natural heritage sites, drinking water source protection zones; (ii) basic farmland and grassland, forest parks, geological parks, important wetland, natural woodland, critical habitats for endangered plant and animal species, important aquatic spawning/nursery/ wintering/migration grounds, regions suffering from water resource shortage, serious soil erosion areas, desertification protection areas, eutrophic water bodies; and (iii) inhabited areas with major residential, health care, scientific research, and administration functions, cultural heritage protection sites, and protection areas with historical, cultural, scientific, and ethnic values.

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requiring the preparation of an EIT report. The report was prepared by Bijie Environmental Science Research Co. Ltd. The company has a 9 EIA engineers, and is certified by the MEE to undertake EIAs until 2020, including common construction projects.

38. The domestic EIT report was reviewed by Gui’an New Area Environmental Protection Bureau (GEPB). A draft report was submitted in early September 2018, and a revised report was submitted in December 2018. The EIT report was formally approved by GEPB on 16 January 2019 (Appendix B).

H. Environmental Standards

39. PRC Environmental Standards. Standards issued by the MEE generally consist of environmental quality (ambient) standards applicable to the receiving environment, and emission standards applicable to the pollution source. The former includes standards for ambient air quality, noise and vibration, surface water, groundwater, soil, etc. The latter includes standards for integrated wastewater discharge, construction and community noise, odor and air pollutants, etc. (Table 3).

40. As noted above, ADB’s SPS requires borrowers to follow environmental standards consistent with good international practice, as reflected in internationally recognized standards such as the World Bank Group’s EHS Guidelines. When host country regulations differ from these levels and measures, the borrower is to achieve whichever is more stringent. If less stringent levels or measures are appropriate in view of specific project circumstances, the borrower is required to provide justification for any proposed alternatives.

Table 3: Applicable PRC environmental standards. No. Standards 1 GB3095-2012 Ambient Air Quality Standards 2 GB16297-1996 Air Pollutant Integrated Emission Standards 3 GB3096-2008 Environmental Quality Standard for Noise 4 GB3838-2002 Environmental Quality Standards for Surface Water 5 GB8978-1996 Integrated Wastewater Discharge Standard 6 GB22337-2008 Emission Standard for Community Noise 7 GB10070-88 Standard of Environmental Vibration in Urban Area 8 GB12523-2011 Emission Standard of Environmental Noise for Boundary of Construction Site 9 GB/T 15190-2014 Technical Specifications for Regionalizing Environmental Noise Function 10 GB12348-2008 Noise Standards for Industrial Enterprises at Site Boundary 11 GB50118-2010 Design Specifications for Noise Insulation of Buildings for Civil Use 12 GB14554-93 Emission Standards for Odor Pollutants 13 GB/T 14848-93 Quality Standard for Ground Water 14 GB15618-1995 Environmental Quality Standard for Soils 15 GB50210-94 Standard for Flood Control 16 GB11340-2005 Limits and Measurement Methods for Crankcase Pollutants from Heavy-duty Vehicles Equipped with Pressure Ignition Engines 17 GB17691-2005 Emission Limits and Measurement Methods for Exhaust Pollutants from Vehicle Compression-Ignition and Gas Fueled Ignition Engines 18 GB18285-2005 Limits and Measurement Methods for Exhaust Pollutants from Vehicles Equipped with Ignition Engines 19 GB18352-2005 Limits and Measurement Methods for Emissions from Light Duty Vehicles Source: ADB PPTA Consultants and domestic EIT report (2018).

Air Quality

41. Ambient air quality limits are intended to indicate safe exposure levels for the majority of the population, including the very young and the elderly, throughout an individual’s lifetime.

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Limits are given for one or more specific averaging periods, typically one-hour average, 24- hour average, and/or annual average. The longer averaging period such as one year is more applicable to assessing impacts from multiple or regional sources, while shorter averaging periods such as 24 hours and 1 hour are more applicable to assessing short-term impacts from project-related activities such as from peak hour traffic or daily or peak construction activities. The PRC’s updated Ambient Air Quality Standards (GB3095-2012) has two classes of limit values; Class 1 standards apply to special areas such as nature reserves and environmentally sensitive areas, and Class 2 standards apply to all other areas, including urban and industrial sites. The PRC standards for Class 2 areas are applicable for the project.13

42. The World Health Organization (WHO) Air Quality Guidelines (AQGs) are international standards and are adopted in the EHS Guidelines. In addition to guideline values, interim targets (IT) are given for each pollutant as incremental targets in a progressive reduction of air pollution.

43. The WHO AQGs and corresponding PRC standards are presented in Table 4. From a review of the table it can be observed that:

(i) For TSP, there are PRC standards but no corresponding WHO AQGs. (ii) For PM10 PRC Class 2 annual average and 24-hour average standards meet WHO IT-1 guidelines (there are no 1-hour average standards or guidelines for PRC or WHO) but not the WHO AQG. (iii) For PM2.5 PRC Class 2 annual and 24-hour standards meet WHO IT-1 guidelines (there are no 1-hour standards or guidelines for either PRC or WHO) but not the WHO AQG. (iv) For NO2 the PRC standard is equivalent to the WHO annual average guidelines, there is no WHO 24-hour average guideline; and the 1-hour average PRC standard is equivalent to the WHO AQG. 3 (v) For SO2 WHO only has a 24-hour average guideline (0.125 mg/m ), which is slightly lower than the PRC standard (0.150 mg/m3).

44. Overall the PRC standards show a high degree of equivalency to the WHO AQG or IT-1 values. The PRC Class 2 standards are adopted for use in this report for general ambient air quality assessment, but WHO AQGs will be used for effects monitoring at sensitive receptors.

13 On 29 February 2012, the China State Council approved the roadmap for ambient air quality standards to improve the environment and human health. The Ambient Air Quality Standards (GB3095-2012) prescribes the first-ever limits for PM2.5. It also modified the previous area classifications by combining Class III (special industrial areas) with Class II (residential, mixed use areas).

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Table 4: Comparison of PRC ambient Air Quality Standards (GB3095-2012) and WHO ambient air quality guidelines. PRC GB3095-2012 WHO/EHS Guidelines Air Quality 3 3 Averaging Period (μg/m ) (μg/m ) Parameter Class I Class II Interim Targets AQG 1-year 80 200 n/a n/a TSP 24-hour 120 300 n/a n/a 1-year 40 70 30 - 70 20 PM10 24-hour 50 150 75 - 150 50 1-year 15 35 15 - 35 10 PM2.5 24-hr 35 75 37.5 - 75 25 1-year 20 60 n/a n/a SO2 24-hour 50 150 50 - 125 20 1-hour 150 500 n/a n/a 1-year 40 40 n/a 40 NO2 24-hour 80 80 n/a n/a 1-hour 200 200 n/a 200 8-hour n/a n/a 160 100 O3 1-hour n/a n/a n/a n/a 24-hour 4,000 4,000 n/a n/a CO 8-hour n/a n/a 30 1-hour 10,000 10,000 n/a n/a Note: n/a = not applicable. Source: WHO Air Quality Guidelines (2006) in IFC EHS Guidelines (2007), and PRC GB3095-2012.

Fugitive Particulate Matter

45. Fugitive emission of particulate matter such as dust from construction sites is regulated under PRC‘s Air Pollutant Integrated Emission Standard (GB16297-1996), which sets 120 mg/m3 as the maximum allowable emission concentration and ≤ 1.0 mg/m3 as the concentration limit at the boundary of construction sites (with no specification on particle diameter). There is no equivalent standard recommended in the EHS Guidelines, and the PRC standard is adopted for use in this report.

46. With respect to the emission of asphalt fumes, GB16297-1996 sets the limit at 75 mg/m3.

Exhaust Gasses

47. Exhaust gasses discharged from bus stations are regulated under PRC Emission Standard of Air Pollutant for Gasoline Filling Stations (GB20952-2007). Cooking fumes are regulated under the “small” class, Emission Standard of Cooking Fumes (Trial) (GB18483- 2001) (Table 5). The Emission Standards for Odor Pollutants (GB14554-93) also applies (Table 6).

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Table 5: Emission Standards of Cooking Fumes (GB18483-2001). Facility Size Parameter Small Medium Large Maximum allowable emission concentration 2.0 (mg/m3) Minimum removal efficiency of cleaning facilities 60 75 85 (%) Source: Domestic EIT, 2018.

Table 6: Level II Limits, Table 1, Emission Standards for Odor Pollutants (GB14554-93) Pollutant Unit Standard Limit Odor concentration Dimensionless 20 Ammonia mg/m3 1.5 Hydrogen sulfide mg/m3 0.06 Source: Domestic EIT, 2018.

Noise

48. Table 7 presents the relevant PRC Environmental Quality Noise Standards (GB3096- 2008) compared with relevant international guidelines from the WHO (as presented in the EHS Guidelines). The classes within the standards are not directly comparable as the PRC noise standards are set in different zones and WHO standards concern noise at specific receptors. Traffic noise and noise at sensitive receptors need different standards to be applied: the PRC Environmental Quality Noise Standards (GB3096-2008) will be used for traffic noise while the EHS Guidelines will be applied for noise based on types of receptors.

Table 7: PRC Environmental Quality Standards for Noise (GB3096-2008). PRC Standards International Standards Comparison Leq dB(A) One Hour Leq dB(A) Class Day Night Day Night 06-22h 22-06h 07-22h 22-07h 0: Areas needing extreme quiet, 50 40 Classes are not such as special health zones WHO Class I: WHO Class I: directly comparable, I: Mainly residential; and cultural 55 45 Residential, Residential, but PRC Class II and educational institutions institutional, institutional, standards exceed II: Mixed residential, commercial 60 50 educational: 55 educational: 45 WHO Class II and industrial areas standards. PRC III: Industrial areas 65 55 WHO Class II: WHO Class II: standards will be used IVa: Area within 35 m on both 70 55 industrial, Industrial, for traffic noise while sides of urban trunk roads commercial: 70 Commercial: 70 the EHS Guidelines (Class II and above) will be applied for IVb: Both sides of railway lines 70 60 noise based on types of receptors. Source: WHO Noise Quality Guidelines (1999) in IFC EHS Guidelines (2007), and PRC GB3096-2008.

49. Table 8 presents the relevant PRC and international standards (US EPA, IFC EHS Guideline: Occupational Health and Safety Standards) for on-site construction noise. The PRC’s Emission Standard of Environmental Noise for Boundary of Construction Site (GB12523–2011) regulates construction noise, limiting construction noise levels at the construction site boundary to 70 dB(A) in the day time (0600–2200 hours) and 55 dB(A) at night (2200–0600 hours).

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Table 8: PRC Noise Emission Standard for Construction Site Boundary (GB12523-2011) and relevant international guidelines. Day Leq dB(A) Night Leq dB(A) International Standards Leq dB(A) IFC EHS Guideline, Occupational Health US EPA: 85 (day, 8 hour 70 55 and Safety: 85 (Equivalent level LAeq, exposure) 8h); 110 (Maximum LAmax, fast) Source: US EPA, IFC Occupational Health and Safety Standard, and PRC GB12523-2011.

Surface Water

50. PRC’s Surface Water Ambient Quality Standard (GB3838-2002) defines five water quality classes for different environmental functions (Table 9). Class I is the highest quality, suitable for head waters and national nature reserves. Class II is suitable for drinking water sources in Class I protection areas, habitats for rare aquatic organisms, breeding grounds for fish and crustaceans, and feeding grounds for fish fry. Class III is suitable for drinking water sources in Class II protection areas, wintering grounds for fish and crustaceans, migration routes, water bodies for aquaculture and capture fishery, and swimming activities. Class IV is suitable for general industrial use and non-contact recreational activities. Class V is the worst quality, suitable only for agricultural and scenic water uses. For rivers within the project area the Class III standard is applicable. For Hongfeng Lake and Songbaishan Reservoir, the Class II standard applies.

Table 9: PRC Surface Water Ambient Quality Standard (GB3838-2002). Water Quality Category Parameter I II III IV V pH 6-9 6-9 6-9 6-9 6-9 90% saturation or Dissolved oxygen (DO) [mg/L] ≥6 ≥5 ≥3 ≥2 ≥7.5 Permanganate index (IMn) [mg/L] ≤2 ≤4 ≤6 ≤10 ≤15 Chemical oxygen demand (COD) [mg/L] ≤15 ≤15 ≤20 ≤30 ≤40 5-day Biochemical oxygen demand (BOD5) ≤3 ≤3 ≤4 ≤6 ≤10 [mg/L] Ammonia nitrogen (NH3-N) [mg/L] ≤0.15 ≤0.5 ≤1.0 ≤1.5 ≤2.0 Total phosphorus (as P) [mg/L] ≤0.02 ≤0.1 ≤0.2 ≤0.3 ≤0.4 Lakes & reservoirs ≤0.01 ≤0.025 ≤0.05 ≤0.1 ≤0.2 Total nitrogen (lakes, reservoirs, as N) [mg/L] ≤0.2 ≤0.5 ≤1.0 ≤1.5 ≤2.0 Copper (Cu) [mg/L] ≤0.01 ≤1.0 ≤1.0 ≤1.0 ≤1.0 Zinc (Zn) [mg/L] ≤0.05 ≤1.0 ≤1.0 ≤2.0 ≤2.0 Fluoride (as F-) [mg/L] ≤1.0 ≤1.0 ≤1.0 ≤1.5 ≤1.5 Selenium (Se) [mg/L] ≤0.01 ≤0.01 ≤0.01 ≤0.02 ≤0.02 Arsenic (As) [mg/L] ≤0.05 ≤0.05 ≤0.05 ≤0.1 ≤0.1 Mercury (Hg) [mg/L] ≤0.0005 ≤0.0005 ≤0.0001 ≤0.001 ≤0.001 Cadmium (Cd) [mg/L] ≤0.001 ≤0.005 ≤0.005 ≤0.005 ≤0.01 Chromium (Cr, hexavalent) [mg/L] ≤0.01 ≤0.05 ≤0.05 ≤0.05 ≤0.1 Lead (Pb) [mg/L] ≤0.01 ≤0.01 ≤0.05 ≤0.05 ≤0.1 Cyanide (CN) [mg/L] ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤0.2 Volatile phenol [mg/L] ≤0.002 ≤0.002 ≤0.005 ≤0.01 ≤0.1 Total petroleum hydrocarbon (TPH) [mg/L] ≤0.05 ≤0.05 ≤0.05 ≤0.5 ≤1.0 Anionic surfactant (=LAS) [mg/L] ≤0.2 ≤0.2 ≤0.2 ≤0.3 ≤0.3 Sulfide [mg/L] ≤0.05 ≤0.1 ≤0.2 ≤0.5 ≤1.0 Fecal coliform bacteria [number/L] ≤200 ≤2000 ≤10000 ≤20000 ≤40000 Source: IFC EHS Guidelines (2007) and PRC GB3838-2002.

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Groundwater

51. The PRC’s Groundwater Water Ambient Quality Standard (GB/T14848-93) is presented in Table 10. The Class III standard is applicable to the project. There is no equivalent standard recommended in the EHS Guidelines, and the PRC standard is adopted for use in this report.

Table 10: Groundwater standard (Class III, GB/T14848-93 Quality Standard for Ground Water). No Parameter Unit Class III Standard 1 pH - 6.5-8.5 2 CODMn mg/l 3.0 3 Sulfate mg/l 250 4 Chloride mg/l 250 5 Volatile Phenols mg/l 0.002 6 Total hardness (CaCO3) mg/l 450 7 Nitrate NO3- mg/l 20 8 Nitrite NO2- mg/l 0.02 9 Ammonia Nitrogen NH3-N mg/l 0.2 10 Molybdenum mg/l 0.1 1 Cyanide mg/l 0.05 12 Cadmium mg/l 0.01 13 Chromium VI mg/l 0.05 14 Arsenic mg/l 0.05 15 Zinc mg/l 1.0 16 Fluoride mg/l 1.0 17 Lead mg/l 0.05 18 Iron mg/l 0.3 19 Manganese mg/l 0.1 20 Copper mg/l 1.0 21 Selenium mg/l 0.01 22 Total coliforms /L 3.0 Source: ADB PPTA Consultants and GB/T14848-93.

Wastewater

52. Discharge of wastewater from construction sites is regulated under the PRC’s Integrated Wastewater Discharge Standard (GB8978–1996) (Table 11). The Class 1 standard applies to discharge into Class III water bodies under GB3838–2002; the Class 2 standard applies to discharge into class IV and V water bodies; and the Class 3 standard applies to discharge into municipal sewers going to municipal wastewater treatment plants (WWTPs) with secondary treatment. No new discharge of wastewater into Class I and II water bodies is allowed. The EHS Guidelines does not have ambient water quality standards, and recognizes the use of national and local ambient water quality criteria, and the PRC standards are adopted for use in this report.

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Table 11: PRC Standards for discharging wastewater from construction sites (GB8978– 1996). Class 1 Class 2 Class 3 Parameter (Discharge into Class III (Discharge into Class IV (Discharge into water bodies) and V water bodies) municipal sewers) pH no unit 6-9 6-9 6-9 SS mg/L 70 150 400 BOD5 mg/L 20 30 300 COD mg/L 100 150 500 TPH mg/L 5 10 20 Volatile phenol mg/L 0.5 0.5 2.0 Ammonia Nitrogen NH3-N mg/L 15 25 --- PO42- (as P) mg/L 0.5 1.0 --- Anionic Surfactants mg/L 5.0 10 20 Source: PRC GB8978-1996.

Solid Waste

53. For waste oil generated from maintenance and oil sludge produced from oil/water separator tanks, the Standard for Pollution Control on Hazardous Waste Storage (GB18597- 2001) and its revision in 2013 apply.

54. For general solid waste, the Standard for Pollution Control on the Storage and Disposal Site for General Industrial Solid Wastes (GB18599-2001) and its revision in 2013 apply.

Soil Quality

55. Soil quality in the PRC is divided into three classes according to the Environmental Quality Standard for Soils (GB15618-1995). Class 1 represents the best and Class 3 the worst (Table 12). The EHS Guidelines do not have standards for soil quality.

Table 12: Soil Quality Standard GB15618-1995. Maximum Allowable Concentration (mg/kg dry weight) Parameter Class 1 Class 2 Class 3 pH Back ground <6.5 6.5-7.5 >7.5 >6.5 Cadmium (Cd) 0.20 0.30 0.30 0.60 1.0 Mercury (Hg) 0.15 0.30 0.50 1.0 1.5 Arsenic (As) Paddy 15 30 25 20 30 Dry land 15 40 30 25 40 Copper (Cu) Farm land 35 50 100 100 400 Orchard --- 150 200 200 400 Lead (Pb) 35 250 300 350 500 Chromium (Cr) Paddy 90 250 300 350 400 Dry land 90 150 200 250 300 Zinc (Zn) 100 200 250 300 500 Nickel (Ni) 40 40 50 60 200 DDT 0.05 0.50 1.0 666 (Lindane) 0.05 0.50 1.0 Source: PRC GB15618-1995.

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Summary of Environmental Standards applicable to the Project

56. Table 13 presents the environmental standards and guidelines applicable to the Project, which reflects the requirements set forth by the Gui’an EPB as presented in the domestic EIT report, and the ADB SPS (2009) guidance on the use of international standards.

Table 13: Environmental standards and guidelines applicable to the project. Parameter / Area Applicable Standards and Remarks of Concern Guidelines Yearly average: PM10: 0.070 mg/m3 PM2.5: 0.035 mg/m3 SO2: 0.06 mg/m3 NO2: 0.04 mg/m3 CO: 4.0 mg/m3 Daily average: TSP: 0.30 mg/m3 Ambient Air Quality Standard Ambient air quality PM10: 0.15 mg/m3 (GB3095-2012), Class II PM2.5: 0.075 mg/m3 SO2: 0.15 mg/m3 NO2: 0.08 mg/m3 CO: 4.0 mg/m3 Hourly average: SO2: 0.50 mg/m3 NO2: 0.20 mg/m3 CO: 10.0 mg/m3 Maximum allowable emission concentration: Particulate matter (PM): 120 mg/m3 Fumes from asphalt plant: 40 mg/m3 during production Construction air Air Pollutant Integrated Emission and 75 mg/m3 during mixing pollutant emission Standard (GB16297-1996) Limits for fugitive emission: PM: ≤1.0 mg/m3 at construction site boundary Fumes from asphalt plant: no obvious emission at asphalt production plant Environmental Quality Standard for Class IVa areas: Noise (GB3096-2008): Day time: 70 dB(A)  Class IVa for areas within 35 m Night time: 55 dB(A) from the boundary line of roads Class II areas:  Class II for areas 35 to 200 m Day time: 60 dB(A) Environmental from the boundary line of roads Night time: 50 dB(A) noise Residential, institutional, and educational receptor Day time: 55 dB(A) Night time: 45 dB(A) WHO Noise Level Guideline Industrial; and commercial receptor Day time: 70 dB(A) Night time: 70 dB(A) Noise level at construction site boundary: Day time: 70 dB(A) Emission Standard of Environmental Night time: 55 dB(A) Construction noise Noise for Boundary of Construction Noise level within construction site: Site (GB12523-2011) Day time: 60 dB(A) Night time: 50 dB(A) Environmental Quality Standards for  Class II standard for Hongfeng Lake and Songbaishan Surface water Surface Water (GB3838-2002), see Reservoir (drinking water source) quality Table 9.  Class III for rivers within the project area. Wastewater Integrated Wastewater Discharge Discharge into Class III water body:

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Parameter / Area Applicable Standards and Remarks of Concern Guidelines discharge Standard (GB8978-1996) COD: ≤100 mg/l BOD5: ≤20 mg/l SS: ≤70 mg/l TPH: ≤5 mg/l NH3-N: ≤15 mg/l Discharge into sewers: COD: ≤500 mg/l BOD5: ≤300mg/l SS: ≤400mg/l TPH: ≤30 mg/l Environmental Approaches and measures appropriate to mitigate adverse WB EHS Guidelines: Environment adverse impacts impacts from the project activities Occupational WB EHS Occupational Health and Approaches and measures appropriate to mitigate adverse health and safety Safety Guidelines impacts from the project activities Community health WB EHS Community Health and Approaches and measures appropriate to mitigate adverse and safety Safety Guidelines impacts from the project activities Construction and WB EHS Construction and Approaches and measures appropriate to mitigate adverse Decommissioning Decommission Guidelines impacts from the project activities Source: Domestic EIT report (2018) and PPTA consultant.

I. International Agreements

57. Relevant International Agreements. The PRC is a signatory to a number of international agreements relevant to environment protection. Those relevant to the project, along with the dates of signing by the PRC, are listed in Table 14.

Table 14: Applicable international agreements with the PRC as a signatory. PRC Signing No. Name of Agreement Agreement Objective Date 1 Convention Concerning the 1985.12.12 Conserving cultural and natural heritage sites. Protection of the World Cultural and Natural Heritage 2 Montreal Protocol on Substances 1989.01.01 To protect the ozone layer by controlling emissions of That Deplete the Ozone Layer substances that deplete it 3 United Nations Framework 1994.03.21 To achieve stabilization of greenhouse gas concentrations in Convention on Climate Change the atmosphere at a low enough level to prevent dangerous anthropogenic interference with the climate system 4 Kyoto Protocol to the United 2005.02.23 To further reduce greenhouse gas emissions by enhancing the Nations Framework Convention national programs of developed countries aimed at this goal on Climate Change and by establishing percentage reduction targets for the developed countries Source: ADB PPTA consultants.

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III. DESCRIPTION OF THE PROJECT

A. The Project

58. The proposed project will establish an urban transport network in the GDAD, including a comprehensive intelligent transport system (ITS); 20 new bus stations; 200 new clean energy, battery-electric buses (BEBs); 21 electric vehicle charging stations; 8.2 km of supporting urban roads; and increased smart transport know-how and technical capacity.

B. Rational

59. Strategic Context. In the western region of the PRC economic growth has been slower than in the coastal provinces, and there are many areas in the region which still have relatively low levels of urbanization and infrastructure development. Guizhou, in southwestern PRC, has a population of 35 million, of which 46% are urban and 36.1% of whom are ethnic minorities. In 2017, Guizhou had one of the lowest gross domestic products (GDP) per capita in the PRC: CNY 37,956 ($5,590), or 63.6% of the PRC average (CNY 59,660 or $8,786), and its poverty rate of 7.75% was more than double the national rate (3.1%). Increased urbanization, better infrastructure, and improved connectivity to markets, employment opportunities, and social services can reduce the high incidence of poverty in Guizhou and its surrounding regions..

60. Recognizing the importance of reducing both the development gap between the western-region and the coastal provinces, and urban-rural income inequality, the “Twelfth Five-Year Plan for Further Promoting the Economy of the Western Regions” was approved in 201214. The plan includes the development of new cities and transport infrastructure projects to improve connectivity and economic development in the region, but, importantly, also emphasizes the importance of ecological protection and environmentally sustainable growth. Guizhou is in the River Economic Belt and is an important province to develop the southwest and far west regions. In the Thirteenth Five-Year Plan, a similar emphasis on the region continued.

61. The Gui’an New District was established as a new city in January 2014 by the PRC’s State Council, with the development objective of becoming an economic driver of western PRC and Guizhou. The key strategies for the district are to develop a high-level technology innovation hub to attract talent and business, encourage innovation and high-tech industrial development, and conserve the natural environment to ensure a healthy and green city and foster eco-tourism. This is in line with China’s new urban development which places increasing importance on innovation and coordination, eco-friendly policies, and the significant of people-centered development and urbanization.

62. The Gui’an New District has as area of 1,795 km2, a population of 0.73 million in 2016, and a target population of 2.3 million in 2030. The Gui'an Direct Administrative Area (GDAD) has an area of 470 km2 comprising over 20 villages or towns located between and originally under the jurisdiction of Guiyang city ( and City) and City (Pingba County and ). The GDAD forms the core of the Gui’an New District, and in the future the city will expand south and west ward to cover the whole district. The current population of GDAD is 330,000 people in 2017, and the planned population

14 Government of the PRC. Twelfth Five-Year Plan for Western Regions. .

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growth will be double by 2020, and by 2030 is expected to reach 1.4 million, including 1.1 million local residents and 0.3 million college students and tourists. Gui’an is growing exponentially, with GDP expected to increase by about 58% annually from CNY 17 billion in 2015 to CNY 150 billion in 2020, targeting a composition of 11% agriculture, 56% industry, and 33% service sector development, reflecting the government’s focus on urbanization.15

63. Challenges. Urban transport in the PRC has been a key driver for high rates of economic development, urbanization, and quality of life. However, rapid growth has also strained transportation systems, resulting in overcrowded road networks, poor traffic management, parking difficulties, inadequate provision and use of public transport, high traffic incidents, and increased fuel consumption and emissions that contribute to pollution and climate change. The PRC has recognized the challenge of balancing the need for development, particularly in the western region, and the problems and challenges that arise from urbanization, emphasizing the need to improve urban development systems and processes to overcome these challenges. ADB has also recognized that going forward, urbanization must focus on integrated solutions that are green, competitive, resilient and inclusive to help build more livable cities.

64. As a new city, Gui’an has the opportunity to follow a new urban development path, learning from the challenges experienced by other cities. Gui’an can focus on economic growth and urbanization that is grounded in environmentally friendly development, innovation, integration and people-centered urbanization. To prevent key challenges related to mobility and establish a sustainable transport system, including preventing congestion and minimizing air pollution, an integrated transport system that is characterized by high public transport utilization is required. Development of intelligent transport systems (ITS) that connect all modes of transport, facilitate travel demand management measures and provide a seamless user experience to public transport users, particularly users switching between transport modes, is the foundation of sustainable mobility, a key pillar of sustainable urbanization and the development of more livable cities.

65. The GDAD has four distinct economic zones (city center, technology, universities, and tourism). Gui’an has a comprehensive master plan, but different areas of the city are developing at different rates, and transport modes are being developed independently of one another which pose a challenge for integration. Integration of the transport network and incorporation of future demand within and between the four economic zones is a key challenge. Without modern transport planning and technologies, problems experienced in other urban centers are likely to occur. Inadequate provision of information for traffic planning and transport user decision making, fossil-fuel reliant vehicle fleets and poor traffic management are key underlying causes of urban transport challenges. Gui’an targets the public transport modal share to reach 60% and green transport modal share to be 80% by 2030. Without active forward planning and technological innovation, these targets will be difficult to achieve.

66. In addition to inadequate physical connectivity, Gui’an will experience other problems if the transport systems being developed cannot communicate with one another. For road infrastructure, without system integration and communication, traffic signaling cannot be optimized, traffic will not flow smoothly, and congestion will be exacerbated. For rail and public transport infrastructure, a lack of integrated systems will reduce the ability to plan and develop timetables that meet the needs of users. Without this information and seamless integration between public transport modes, users will find public transport too difficult and opt for other transport options such as private vehicles, resulting in less than optimal

15 Government of the PRC, State Council. 2015. National Economy and Social Development Thirteenth Five- Year Plan, 2016–2020. Beijing.

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ridership and modal share. Further, these systems will not be able to capture or share real time data and information such as traffic flow, incidents, parking, timetables, weather and so forth that would enable transport users and operators to manage demand, make informed decisions and optimize their transport journeys. This will lead to inefficient allocation of resources, inefficient logistics, poor utilization of services, poor connectivity, and reduced mobility within the urban environment and hinder the ability to attract residents, businesses and tourists, thus constraining economic growth.

67. Proposed Solutions. Technology plays a crucial role in developing sustainable transport networks and systems. ITS can connect transport networks across modes, improving efficiency, coordination and safety. It utilizes information and communication technology in vehicles and transport infrastructure to collect, manage, and distribute information to improve transport outcomes. ITS utilizes a range of technologies which provide critical information to enable services such as coordinated incident and emergency response systems, smart traffic management, parking management, public transport management, share-bike management, fleet vehicle management, freight logistics optimization, route planning, transport timetables, and integrated hub management.

68. These ITS services provide various transport users and operators with critical information for decision making, enabling safer and more coordinated use of transport networks, optimizing infrastructure utilization. One of the key ITS services is traffic demand management, which utilizes traffic data, trends, and user needs to understand transport demand and redistribute users through the system, either over time or to alternative routes. This enables people and freight to move freely through urban environments, reducing congestion and, in turn, emissions, improving the quality of the urban environment and enabling economic growth.

69. Developing a sustainable transport system includes the provision and use of clean energy public transport modes such as electric buses which are proven to reduce greenhouse gas and local emissions in cities. Proper planning in the selection and operation of clean energy buses including their important core component, charging stations, will avoid increased emissions from transport as the population in Gui’an expands. Implementation of electric buses in a system which encourages the use of public and active transport through a seamless user experience, resulting in a high public transport modal share, will improve the overall mobility and sustainability of the urban transport system and compound the positive impact of the technology.

70. ITS technologies and services can be complemented by advances in vehicle technology such as autonomous vehicles, electric vehicles and electric buses to provide more environmentally friendly and efficient transport services. The adoption of these high- level technologies and their integration into the urban fabric is crucial for the development of sustainable urban transport systems. Up-front planning and design of an efficient, integrated urban transport system in new cities is crucial to avoid the problems of historic, car-centric transportation systems and achieve the vision for sustainable economic growth.

71. Value added by ADB assistance. Under ADB’s Strategy 2030, the proposed project will focus on two of the seven operational priorities: (i) tackling climate change, building climate and disaster resilience, and enhancing environmental sustainability, and (ii) making cities more livable. ADB will help Gui’an to explore new and existing technologies and approaches to urbanization that encourages integrated, green, inclusive urban development and make cities more livable . ADB will add value to Gui’an by introducing new technologies and best practice in project design and implementation, including international expertise at the forefront of ITS development and clean transport technology. ADB will also transfer knowledge in sustainable, inclusive and participatory urban transport planning, design, and operation.

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72. To ensure that the introduction of the ITS results in more inclusive, gender-sensitive transport solutions, project development has utilized human-centered design. During project preparation, extensive user and stakeholder feedback was gathered to identify innovation opportunities regarding the ITS, buses and bus stations. The human-centered design research also guided the design of communication and participation mechanisms.16 The communication strategy focuses on integrating stakeholder inputs into the planning and implementation of the ITS and transport infrastructure so road users including underrepresented groups can participate in providing solutions to key issues on accessibility and mobility. Behavior change communication campaigns will be launched to increase patronage for public buses and other green transport modes. Furthermore, the Social Development and Gender Action Plan provides a contribution to narrow the digital divide in GDAD.

C. Impact, Outcome and Outputs

73. The impact of the project will be increased economic activity in the GDAD. The outcome will be efficiency of the GDAD transport system is increased. The project will have three outputs:

Output 1: Intelligent transport system (ITS) designed and installed. The component aims to develop a comprehensive ITS suite, including development of a real-time traffic and road-weather monitoring system; setting up a big data servces center17; creating of a multi-modal transport system management and operation center; and establishment of an integrated traffic operations and security and emergency management system.

Output 2: Sustainable transport infrastructure built. To promote maximum public transportation use, the transport system must be flexible and enable users to switch seamlessly between modes, including walking, cycling, buses, trains and cars.

(i) A total of 20 bus stations will be built, including six hub stations, 11 terminal stations, and three bus depots. This infrastructure will work together with ITS elements to optimize infrastructure and overall urban mobility; (ii) A total of 200 clean energy buses will be purchased to increase the bus route coverage and reduce emissions from public transport services; (iii) A regional network of 21 electric charging stations for both private and public vehicles to encourage green vehicles and reduce emissions; (iv) A network of [approximately] 8.16 km of new urban roads will be constructed in the core of the GDAD as part of the transport network backbone. These roads will provide access to key existing north-south and east-west trunk roads and will be equipped with ITS equipment; and (v) An ICVS demonstration zone for research and development of ICVS and associated technologies will be set up, which includes the application of

16 Human-centered design is an approach to innovation that aims to make products and systems user-friendly by focusing on the users, their needs, and by applying human factors/ergonomics. This approach enhances effectiveness and efficiency, improves human well-being, user satisfaction, accessibility and sustainability; and counteracts possible adverse effects of use on human health, safety and performance. ISO 9241- 210:2010(E). 17 Center will be setup in an existing office space, no civil works involved.

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information technologies in transport infrastructure, upgrading of background test vehicles and data center platform in designated area.18

Output 3: Smart transport capacity strengthened. Capacity strengthening activities will be provided to ensure relevant and up-to-date ITS and clean transport technology is available at design, implementation, and operation phases. ADB will transfer knowledge and international prevailing practices on sustainable urbanization, including integrated smart transport planning, design, operation and maintenance. Consulting services for supervision and project management will be provided. Community outreach programs on gender sensitive public transport and ITS will also be conducted. The project will provide consulting services for supervision and project management, including ICVSDZ related knowledge transfer.

D. Detailed Project Description

i) Intelligent Transport System

74. Objectives. The GDAD has been planned to be the most dynamic growth pole in south western PRC and Guizhou. It will be developed into a safe, orderly, accessible, low- carbon, sustainable smart city. One of the means to achieve this type of growth is the development of an intelligent transport system (ITS) which incorporates advanced information processing technology, data communication technology, electronic sensing technology, control technology, internet, and cloud computing methods in a big data services center, among other technologies.

75. The ITS component will accelerate better and faster development of surface transportation in the GDAD, and provide a base for the deployment of smart city functions. It will also support the operation and maintenance of safe, convenient, efficient, and green travel for citizens. The component aims to develop an interconnected system to support use, regulation, operations, and maintenance of all surface modes of transport such as pedestrians, buses, taxis, shared mobility services, bicycles, passenger cars, and freight vehicles. It will also provide multimodal hub traffic information, law enforcement management information, and road construction and maintenance information, and real time traffic operations monitoring. Multimodal traffic information will be utilized by traffic control authorities, and will be made available to the general public through terminals along the road, in bus stations, ticketing offices, and parking lots.

76. Subcomponents. The ITS component will consist of four subcomponents: (i) a real- time traffic and road-weather monitoring system; (ii) a big data service center; (iii) a multi- modal transportation systems management and operations center; and (iv) an integrated traffic operations, and security and emergency management system.

(i) Real time data on traffic and weather conditions will be collected through video surveillance cameras, traffic flow detectors, vehicle-mounted smart terminals, parking space monitors, charging facilities, RFID, roadside identification devices, and roadway weather sensors (Figure 2). This data will be stored, managed, and maintained in the Big Data Services Center (subcomponent ii).

18 The ICVS demonstration zone design will follow the Administrative Measures of Road Test for Intelligent Connected Vehicles (for trial implementation) jointly issued by the Ministry of Industry and Information Technology, the Ministry of Public Security and the Ministry of Transport on April 12, 2018.

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Figure 2: ITS roadside detection and monitoring equipment.

HD zoom camera, used to collect data such as traffic flows Fisheye panoramic camera, used to view information such at road cross-sections, vehicle speed at road cross- as road operation and congestion in real time. sections, and vehicle speed at road sections.

Wireless geomagnetic detector, used to detect information such as speed and traffic flow of road cross-section.

RFID detector (wireless radio frequency identification DSRC detector (dedicated short-range communication detector), used to detect the speed of vehicles on the roads technology detector), will be installed in roads with slower with fast pass capability such as expressways or highways. running speeds such as trunk and secondary trunk roads. (Based on its principle and characteristics, RFID has a (DSRC is more accurate in detecting slow-moving vehicles higher accuracy in detecting fast-moving vehicles than than fast-moving vehicles.) slow-moving vehicles.)

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ITS roadside detection and monitoring equipment continued.

Water detector. These will primarily be installed under overpasses, low-lying roads and other places where water accumulates frequently. It can monitor water pooling and provide data support for emergency drainage through ultrasonic water level detection technology.

Remote sensing monitor. Through infrared rays, the remote sensing monitor detects road surface conditions such as dryness, humidity, frost, black ice, ice and snow, and water thickness in real time, and provides data support for emergencies in extreme weather events. Source: BTI, 2018.

Figure 3: Location of ITS Big Data Services Center, GDAD.

Source: PMO, 2018; Google Earth, 2018.

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(ii) The Big Data Services Center will adopt standard cloud platform architecture to build elastic computing clusters, open-source storage clusters, load balancing clusters, and relational database clusters. The infrastructure required for the center is includes X86 type servers, storage devices, network switches, routers and other hardware. The Big Data Services Center will be housed on one floor of the Citizen’s Center, currently under construction, and no new building construction will be required. The building is being constructed in compliance with all relevant PRC building and fire codes, and health and safety requirements.

The Big Data Services Center building will be connected to municipal power, water supply and sewage infrastructure. Water consumption is estimated at 8.25 m3/day, and wastewater generation at 7.03 m3/day. Sewage will be discharged to the Huchao WWTP. Solid waste, estimated at 50 kg/day, will be collected by the municipal sanitation department.

(iii) The multi-modal transportation systems management and operations center subcomponent will create different management systems for different modes, like, buses, taxis, bicycles, passenger cars and freight vehicles. A parking management system and a law enforcement management system will also be created. Data from these different management systems will flow to the multi-modal transportation systems management and operations center to analyze and manage different services. These management systems will include back-end servers and app type software for mobile devices for use by the public, and software for different government agencies.

(iv) This integrated traffic operations, and security and emergency management system includes software and computer network systems, splicing display systems, video monitoring systems, video conference systems, E-conference systems, and command and dispatch system. This will effectively monitor real time multi-modal operations. Data will be used by traffic utility bureaus.

ii) Sustainable Transport Infrastructure

77. Bus Stations. A total of 20 bus stations will be established, including 6 hub stations, 11 terminal stations and 3 bus depots.

Hub Stations: 6 hub stations, with a total combined area of 46,914 m2. Hub stations will allow passengers to transfer from one bus route to another without having to depart the station. They will include passenger waiting halls, driver’s rest rooms, canteens, washrooms, station management offices, route dispatching offices, smart monitor rooms, parking spaces, and electric charging facilities. Mixed land use will be typically planned around hub stations for future development. For some stations transfers to rail may be developed at a later stage.

Terminal Stations: 11 bus terminal stations, with a total combined area of 30,847 m2. These are stations where a bus route starts, terminates, or both. They will typically include station management offices, route dispatching offices, smart monitor rooms, washrooms, parking spaces, and electric charging facilities.

Depot Stations: 3 bus depot stations, with a total combined area of 100,310 m2. These will be facilities where buses are stored, maintained and repaired. They will typically include station management offices, repair workshops, overnight and longer parking spaces, electric charging facilities, and facilities for storage and management of hazardous materials including fuel, oils, etc.

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78. This infrastructure will work together with ITS elements to optimize infrastructure and overall urban mobility. The feasibility study for this subcomponent has incorporated human- centered design 19 research to ensure user-friendliness and consequently high public transport uptake. Developing ITS components alongside this infrastructure will produce real- time information systems that provide users with seamless end-to-end journey planning facilities including intuitive wayfinding, public transport information and parking systems.

79. The bus stations are summarized in Table 15, and locations are shown in Figure 4. Individual station site plans are presented in Appendix C. Facilities to be included in each station are presented in Appendix D. Bus station site descriptions including satellite and site photos are presented in Appendix E.

Table 15: Bus stations to be established in the GDAD. Land area Building Station Type District Township Village(s) (m2) area (m2) 1. Hub Stations 46,914 2,929 1.1 Gaofeng Passenger Pingba Gaofeng Dalege 4,007 241 1.2 Machang Public Transportation Pingba Machang Chuanxin 5,124 312 1.3 Biguiyuan Huaxi Huchao Xiaba 12,000 827 1.4 South University Town Huaxi Dangwu Wenggang 7,697 455 1.5 Yunman Lake Pingba Machang Jiahe 10,086 606 1.6 North Fukang Road-Xuanshui Road Pingba Machang Ganhe, Kaizhang 8,000 488 2. Terminal Stations 30,847 1,858 2.1 Shuangxi Road-Bai Ma Avenue Pingba Machang Chaunxin 2,168 130 2.2 Xinghu Community Huaxi Huchao Huchao 2,281 140 2.3 North of the Xingyue Community Huaxi Huchao Qishan 2,621 162 2.4 East of Gaofeng High School Pingba Gaofeng Dalege 1,200 70 2.5 Machang Township Pingba Machang Liujiacun 6,173 369 2.6 High Technology Industrial Park Huaxi Dangwu Maocao 2,511 149 2.7 Dong Qing Road-Si Ya Road Huaxi 2,998 178 2.8 Comprehensive Bonded Zone Pingba Machang Ganhe 2,121 124 2.9 South of Xingan Avenue Pingba Machang Wenggang 2,091 130 2.10 Minbo Park Pingba Machang Guangxing 3,287 199 2.11 Gui’an Chuangu Huaxi College Wenggang 3,396 207 3. Depots 100,310 8,593 3.1 Central Area Huaxi Huchao Malu 15,945 3825 3.2 University Town Huaxi Dangwu Zhenlong, Dangwu 45,523 2135 3.3 East Machang Pingba Machang Longshan 38,842 2633 TOTAL 178,071 13,380 Source: PMO, 2018. Note: the difference in size between building area and land area is due to parking and charging areas.

19 Human-centered design is an approach to innovation that aims to make products and systems user-friendly by focusing on the users, their needs, and by applying human factors/ergonomics. This approach enhances effectiveness and efficiency improves human well-being, user satisfaction, accessibility and sustainability; and counteracts possible adverse effects of use on human health, safety and performance. ISO 9241- 210:2010(E).

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Figure 4: Location of Bus Stations, GDAD.

Source: PMO, 2018; Google Earth, 2018.

80. Bus stations will receive electrical power from the grid via local distribution network and treated municipal water supply via municipal DN 100 pipes at 0.35 Mpa pressure. Water usage at stations is estimated at 300 m3/day and the domestic EIT confirms this demand can be met by the municipal water supply. Domestic wastewater (estimated at 250 m3/day) will be pre-treated in septic tanks and then discharged to the municipal wastewater distribution system for treatment in a municipal wastewater treatment (MWWT) plant. Wastewater from canteens will pass through oil-water separators before being discharged and wastewater from the depot station maintenance workshops will be pretreated in oil-water separators and septic-tanks, before discharge into the municipal wastewater system and treatment in one of five MWWT plants. The domestic EIT confirms that the MWWTs have the capacity to treat the effluent. Receiving MWWTs are all required to meet the Level I A standard in the national Discharge Standards of Pollutants for Municipal Wastewater Treatment Plant.

81. Rainwater runoff from bus stations will be collected, treated in oil-water separators, and then discharged to the domestic storm water systems. Wastewater from depots will be reused after passing through oil-water separators.

82. Fire alarm and response systems will be installed. Water for firefighting in stations will be sourced from municipal fire hydrants, while depots will be equipped with indoor hydrants. Heating, air condoning and ventilation systems will also be installed, including in maintenance shops and washrooms. Stations will be equipped with 60 kW slow chargers at bus depots, and 120 and 180 kW fast chargers at bus terminals and depots.

83. The South University Town Hub Station, Yunman Lake Hub Station and Central Area Depot Stations will be equipped with canteens. Fumes generated in canteens will be

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collected and treated in electrostatic fume purifiers before being vented in roof top stacks sited away from any adjacent houses or apartments.

84. Low noise equipment will be selected where possible, and all noisy machinery will be enclosed with the stations. Stations will be equipped with noise reduction measures including double glazed windows, and sound reduction measures will be implemented such as disallowing use of horns. As the buses are electric (see below), they do not produce significant sound while at the stations. Solid wastes will be collected and disposed by qualified waste collection companies, with materials recycled to the extent possible.

85. Battery-Electric Buses. China is a leader in in zero-emission bus technology, and had approximately 99% of the 385,000 electric buses on the roads worldwide in 2017.20 Modern battery electric buses (BEBs) can have a range of up to 250 km with just one charge, and are particularly well suited to urban routes. Urban driving involves extensive accelerating and braking, and BEBs can recharge much of the kinetic energy back into the batteries in braking situations, reducing brake wear on the buses. Urban BEB fleets are typically cheaper to operate than comparable diesel bus fleets,21 and the use of low emission BEBs over diesel can significantly improve air quality in cities.

86. The project will procure two hundred 12 m long BEBs (Table 16 and Figure 5). The buses will be powered through electricity stored in on-board 260 kW lithium-ion (Li-ion) batteries, charged at the bus depots and stations, and at 21 electric charging stations to be established by the project. Batteries will have a guarantee of 8 years minimum lifespan at 80% state-of-charge (SOC). This type of battery set has proven able to meet the daily demands of a majority of typical bus routes days with one fast-charge during the day and slow-charging during the night.

87. The average project bus route length will be 14.3 km 1-way and take 45 minutes. Due diligence has confirmed that the routes (gradients, length) and the climatic conditions in Gui’an pose no problem for the proposed BEBs.

Table 16: Technical data of BEB fleet, GDAD. Parameter Bus Data Number and size of buses 200 12 m buses with AC Daily and annual distance driven 200 km / 55,000 km Electricity usage average and in summer 1.15 kWh / 1.38 kWh/km Battery pack required (for summer with 10% reserve and 90% 260 kWh SOC) Station chargers 60 kW AC slow chargers for overnight charging 180 or 120 kW AC fast chargers Estimated capital expenditure after subsidy (based on the 900,000 RMB estimated range and efficiency per bus option and provincial plus city subsidy of 50% of the national subsidy ) Estimated capital expenditure chargers per bus 120,000 RMB Estimated electricity cost 0.55 RMB/kWh Estimated annual electricity cost per bus 35,000 RMB Source: ADB PPTA consultant, 2018.

20 Bloomberg, 2018. 21 Kyle Field, No Need to Wait: Electric Buses Are Cost-Competitive Transit Buses Today, in CleanTechnia, 29 April 2018; https://www.greenbiz.com/article/city-buses-are-about-swiftly-electrify; and Electric Buses in Cities: Driving Towards Cleaner Air, and Lower CO2, produced by C40’s Financing Sustainable Cities Initiative and Bloomberg New Energy Finance, March 29, 2018.

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Figure 5: Battery powered electric bus produced by BYD, Hanzhou PRC.

Source: WRI, 2017.

88. Buses will be charged by 60 kW slow chargers at bus depots and 120 and 180 kW fast chargers at bus terminals and depots. Slow chargers will be reserved at night for buses and fast chargers during specific off-peak hours for buses. Buses may also be charged through a regional network of 21 electric charging stations to be established by the project (see below).

89. Buses will be equipped with onboard systems to communicate with the traffic management control and data centers. For pedestrian safety buses will also be equipped with Acoustic Vehicle Alerting Systems (AVAS), which will emit warning sounds at speeds less than 30 km/h.

90. Charging Stations. A regional network of 21 electric charging stations for both private and public vehicles will be established (Table 17). Ten of the stations will be established within existing facilities and parking lots, while the remainder will be established on existing state-owned land (8 stations) or acquired cultivated land (3 stations). The stations will have a combined total area of 45,750 m2. The charging stations and points will be operated by the Industrial Investment Company (IIC).

91. Charging stations will be equipped with automated 120 kW and 180 kW DC quick chargers, each having two or more plug-in nozzles. These chargers will be capable of meeting the quick-charge requirements of small, medium-sized and large electric vehicles. In total there will be 611 chargers providing 1,322 charging spaces. Appendix F presents charging station site descriptions, and Appendix G presents charging station site plans and other details.

92. Charging stations will be equipped with intelligent monitoring systems, displaying reservation and operating status of the charging points in real time on a large screen, and providing online reservations and payment via mobile applications. All electrical equipment including transformers and switchgear will be located within the stations. Power will be sources from adjacent substations via the grid, and no new substations will be required. Water supply and sanitation will be provided through municipal underground connections (per station water usage is estimated at 2 m3/day, and sewage 1.7 m3/day). Solid waste will be collected by the municipal sanitation department. Charging stations will be equipped with fire alarms and suppression systems, and will be landscaped with appropriate vegetation for local conditions.

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Table 17: Description and location of proposed charging stations. Charging Building Rain Shelter Green Total Area # Name/Location Capacity (DC) Spaces Area (m2) Area (m2) Area (m2) (m2) 36 @ 120 kW 72 1 Gui’an Rail Station 4,763 46 @ 180 kW 138 6 @ 120 kW 12 2 Financial Harbor 1,189 16 @ 180 kW 48 10 @ 120 kW 20 3 Commercial Complex 3 1,749 10 @ 180 kW 30 8 @ 120 kW 16 4 Civil Center 1,909 11 @ 180 kW 33 5 Longshan Industrial Park 16 @ 120 kW 32 624 837 6 Electronic Information Industry Park 20 @ 120 kW 40 676 1,766 7 Stirling Industrial Park 15 @ 120 kW 30 536 728 Gui’an Digital Economic Industrial 10 @ 120 kW 20 8 697 Park 4 @ 180 kW 12 11 @ 120 kW 14 9 Yungu (B Block) 799 7 @ 180 kW 33 10 Gui’an New Area Free Trade Zone 31 @ 120 kW 62 1263 1,640 11 Yueliang Lake 36 @ 120 kW 72 83 1179 111 2,400 12 Liangjiang Road 33 @ 120 kW 66 76 1084 193 2,269 13 West Coast 25 @ 120 kW 50 95 782 198 2,515 14 Tianfu Road 25 @ 120 kW 50 176 806 561 3,297 South Park of the High-end Industrial 15 6 @ 120 kW 12 166 203 346 1,250 Park 16 South Shuangxi Road 45 @ 120 kW 90 199 1477 424 3,713 17 Xinmin Road 27 @ 120 kW 54 84 854 217 2,088 9 @ 120 kW 18 West Simeng Road 24 59 409 84 908 2 @ 180 kW 19 Fengming Road 110 @ 120 kW 220 174 3591 367 6,538 20 Qingqu Road 28 @ 120 kW 56 106 925 337 2,474 21 Huantienhuchao Station 8 @ 120 kW 16 168 273 701 2,220

Source: Charging Stations FSR, 2018.

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Figure 6: Example of existing charging station near the High Technology Industrial Park in the GDAD.

Source: PPTA Consultant, 2018.

Figure 7: Two-nozzle bus charger at existing charging station near the High Technology Industrial Park in the GDAD.

Source: PPTA Consultant, 2018.

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Figure 8: Control building, existing charging station near the High Technology Industrial Park in the GDAD.

Source: PPTA Consultant, 2018.

Figure 9: Electrical control equipment, existing charging station near the High Technology Industrial Park in the GDAD.

Source: PPTA Consultant, 2018.

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Figure 10: Example of parking lot charger, GDAD.

Source: PPTA Consultant, 2018.

93. Supporting Roads. The project will construct a new supporting road network in the urban core area of the GDAD. The roads will provide access to key existing north-south and east-west trunk roads, and will be equipped with ITS equipment. (Figure 11 and Figure 12). The 13 road network will have a total length of 8.163 km and will include 2 urban main roads 2.784 km in total length with a 44 m standard cross section width; 1 urban sub-main road 1.429 km in length with a 31 m in standard cross section width; and 10 urban branch roads 3.874 km in total length with standard cross section width ranging from 18 to 24 m (Table 18).

Figure 11: Supporting road network and planned future land use, core area, GDAD.

High Speed Rail Station

Changfeng Bridge

Source: Transport FSR, 2018.

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Figure 12: Supporting road network and current land use, core area, GDAD.

Source: Transport FSR, 2018; and Google Earth, 2018. Note: road alignments avoid all existing and planned buildings, and no demolition will be required.

94. Cross-section diagrams are presented for the two main roads in Figure 13; for the submain road in Figure 14; and the 10 branch roads in Figure 15. A summary of intersection types for the 13 roads is presented in Table 19. All intersection will be at-grade for ease of access for pedestrians and cyclists. All junctions will be signalized, and designed to minimize conflicts and ensure smooth traffic flow.

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Table 18: Supporting road network, urban core area, GDAD. No. Name Road Length Boundary Design Description Class (km) Line Speed Width (m) (km/h) Runs from Tian He Tan Avenue in the north to 1 #5 Road Main 1.920 44 50 Jing’an Avenue in the south. Will be the main north-south road in the core area. Northern Extends Zhanqian Road to Extension the north and provides 2 of Main 0.864 44 50 access to the National Zhanqian Security Agency and Public Road Security Bureau. Runs from Tian He Tan Avenue in the north to Xinmin Road in the south. It Changfeng 3 Sub-main 1.493 31 40 provides access to the core Road (Z7) area, including the financial section. Includes Changfeng Bridge. Provides access to core area 4 H6 Road Branch 0.453 24 30 from Zhanqian Road. Provides access to core area 5 Z3 Road Branch 0.395 24 30 from H6 Road. Provides access to core area 6 H8 Road Branch 0.338 24 30 from Zhanqian Road. Provides access to core area 7 H11 Road Branch 0.339 24 30 from Zhanqian Road. Provides access to core area 8 H12 Road Branch 0.227 24 30 from Zhanqian Road. Provides access to core area 9 H13 Road Branch 0.417 24 30 from Zhanqian Road. North-south road connecting 10 Z4 Road Branch 0.741 24 30 H11, H12 and H13 to Jingan Avenue. Provides access to the 11 Z8 Road Branch 0.162 18 30 financial section. Provides access to the 12 H4 Road Branch 0.297 24 30 financial section and Bai Ma Avenue. Provides access to a 13 H1 Road Branch 0.517 18 30 citizen’s center and Bai Ma Avenue. 8.163 Source: Transportation Infrastructure FSR, 2018.

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Figure 13: Cross-section diagram, main roads.

Source: Transportation Infrastructure FSR, 2018.

Figure 14: Cross-section diagram, sub-main road.

Source: Transportation Infrastructure FSR, 2018.

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Figure 15: Cross-section diagram, branch roads.

Source: Transportation Infrastructure FSR, 2018.

Table 19: Supporting road network work intersection types, GDAD. Name Roads Intersected Type of Intersection Planning Branch Road H14 Cross Intersection Planning Branch Road H13 T Intersection Xinmin Road Cross Intersection Planning Road H11 T Intersection Planning Road H8 T Intersection #5 Road Liujin Road Cross Intersection

Planning Road H6 T Intersection Planning Road H4 Cross Intersection Yingong Road Cross Intersection Planning Branch Road H2 Cross Intersection Tianhe Tan Avenue T Intersection Northern Extension of 5# Road Cross Intersection Zhanqian Road Planning secondary trunk main T Intersection Xinmin Road T Intersection Planning Road H10 T Intersection Planning Road H9 T Intersection Liujin Road Cross Intersection Planning Road H4 Cross Intersection Changfeng Road(Z7) Yingong Road Cross Intersection Planning Road H3 Cross Intersection Planning Road H2 Cross Intersection Planning Road H1 T Intersection Tianhe Tan Avenue T Intersection Zhanqian Road T Intersection Planning Road Z1 Cross Intersection H6 Planning Road Z3 Cross Intersection Planning Road Z3 T Intersection Planning Road H6 T Intersection Z3 Planning Road H7 T Intersection

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Name Roads Intersected Type of Intersection Liujin Road Cross Intersection Planning Road H8 T Intersection Zhanqian Road T Intersection H8 Planning Road Z3 T Intersection 5# Road Cross Intersection Zhanqian Road T Intersection H11 Planning Road Z4 T Intersection 5# Road Cross Intersection Zhanqian Road T Intersection H12 Planning Road Z2 T Intersection Planning Road Z4 T Intersection Zhanqian Road T Intersection Planning Road Z2 Cross Intersection H13 Planning Road H14 Cross Intersection 5# Road T Intersection Planning Road H11 T Intersection Xinmin Road Cross Intersection Planning Road H12 T Intersection Z4 Planning Road H13 Cross Intersection Planning Road H14 Cross Intersection Central Avenue T Intersection Yingong Road T Intersection Z8 Planning Road H4 T Intersection Planning Changfeng Road T Intersection H4 Planning Road Z8 T Intersection Baima Avenue T Intersection Planning Changfeng Road T Intersection H1 Baima Avenue Cross Intersection Planning trunk main T Intersection Source: Domestic EIT, 2018.

95. Roads will be constructed of asphalt concrete. Table 20 presents a summary of road structures and material compositions, while Table 21 presents a summary of works.

96. Road side landscaping will be provided (Figure 13 to Figure 15), and banks will be vegetated to control erosion. For road banks with a slope height of less than 2 m, grass will be spray sowed; when slope heights are more than 2 m but less than 4 m, 3D mat grass- planting will be used; and when slope heights are greater than 4 m, rhombic grid mats will be used, where grass is planted in square grids. In total 101,595 m2 of slope protection will be provided.

97. Project roads will be constructed utilizing innovative technologies to collect and treat storm water, including pervious pavement and bio-retention facilities. Runoff will be collected and treated in 2.5 m wide bio-retention facilities located in the green belts along both sides of the roads. The facilities are designed to remove contaminants and sediments from storm water runoff. Storm water will be diverted to the treatment area, which will consist of a grass buffer strip, sand bed, ponding area, organic or mulch-layer, and soil and plants. The runoff will pass first over or through a sand bed, which will slow the runoff's velocity, distributing it evenly along the length of the ponding area, which consists of a surface organic layer and the underlying planting soil. The ponding area will be graded with a central depressed area. The water will collect to a depth of up 50 to 200 mm and will gradually infiltrate the bio- retention area or be evapotranspired. For Road #2 (Northern Extended Section of Zhanqian Road), any remaining treated storm water will be discharged to the Lanhua River. For all other roads, any remaining treated storm water rainwater will be discharged into the Chetian River. The design capacity of the system was increased by 10% to account for predicted increased rainfalls resulting from climate change (see Climate Risk Vulnerability Assessment (CRVA) in Appendix I). In addition, the potential effects of increased storm peak flows due

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to climate change will also be considered in siting the locations of important facilities and water-proofing project components including electrical equipment.

98. Other municipal infrastructure that will be integrated under roadways include electrical power, communications, water supply, natural gas, and sewage (Figure 16).

Table 20: Supporting road network materials composition by component. Road Non-motor vehicle Sidewalk pavement Bridge deck Motor vehicle lane structure and Type lane structure and structure and pavement structure composition composition composition and composition - Top surface course: 5 cm fine - Modified asphalt grade asphalt concrete mastic macadam - Middle surface course: 5 cm mixture medium grain grade asphalt Pavement structure - medium grain concrete layer from top to bituminous - Bottom surface course: 7 cm bottom: concrete coarse grain grade asphalt - pervious - Bridge deck Main concrete bituminous Pavement structure waterproof coat: 8 - Bottom seal coat: emulsified concrete; 19.5 layer from top to cm C40 bridge bitumen slurry seal cm C20 pervious bottom: deck reinforced - Base course: 36 cm 5% cement concrete base - 6.5 cm pervious concrete pavement stabilized macadam course; brick; 3 cm bonded - Total thickness of - Subbase course: 20 cm graded - 15 cm graded leveling course; bridge deck asphalt broken stone broken stone thickness C20 pavement: 10 cm - Total thickness: 73 cm subbase course. pervious concrete; - Top surface course: thickness - Non-motor thickness graded SMA-13 asphalt mastic vehicle lane broken stone. - Bottom surface course: thickness cross slope - Total thickness: AC20 bituminous concrete slurry concave green 39.5 cm Sub - Seal coat: 0.6 cm thickness belt has a slope Main/ emulsified asphalt of 1.5%. - Branch - Base course: 32 cm thickness - Total thickness: cement stabilized macadam 39.5 cm - Subbase course: graded broken stone - Total thickness: 64.0 cm Source: Domestic EIT, 2018.

Table 21: Supporting road network works, GDAD. Unit Quantity Item Civil works km 8.163 1 Excavation m3 703791 2 Fill m3 825259 3 Fill to purchase m3 121468 4 Slope protection engineering m2 101595 5 Bridge engineering m 76 6 Water supply engineering m 1401.3 7 Stormwater drainage engineering m 2569.0 8 Sewage engineering m 1751.6 9 Power pipeline engineering m 3269.6 10 Integrated communication engineering m 2569.0 11 Gas pipeline engineering m 1167.7 12 Land acquisition (Mu) Mu 538.66 Source: Domestic EIT, 2018.

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Figure 16: Underground pipeline layout, main roads. Submain and branch roads will utilize a similar underground pipeline layout.

Source: Domestic EIT, 2018.

99. Roadside facilities will include:

Traffic Safety - Warning, traffic direction and other signs; painted road lines, lanes markings, etc.; guardrails; traffic control lamps and signals; and pedestrian cross walks.

Public Transit, Non-motorized Vehicle Lanes, Sidewalks - Bus stops will be sited in accordance with urban layout and bus routes. Bus stop platforms will be 3 m wide and 45 m long. Non-motorized vehicles lanes (bikes, small electric vehicles) will be installed on both sides of roads.

Lighting - Single-arm street lights will be installed in the green belts on both sides of the roads, at 30 m intervals. High efficiency LED lamps will be utilized.

Landscaping - 2.5 m wide green belts will be installed on both sides of roads, and along the centerline. Rapid growing ecologically appropriate plants, shrubs and shade trees will be selected

Sanitation - Roadside garbage and recycling cans will be situated every 80 to 100 m.

100. One bridge will be constructed, the Changfeng Road Longhu Bridge which will cross Longhu Lake, an artificial water body that has not yet been fully constructed. The bridge will be 76 m in length and 31 m wide (including sidewalk, 14.5 m roadway, and two 2.5 m non- motorized vehicle lanes), the same as the roads accessing it. The bridge deck will be 3 m above the water surface.

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101. The preliminary design is a diagonal-span arch, with the bridge deck supported by cables from a single arch that spans the bridge diagonally (Figure 17). However the design will be finalized in the detailed design stage after site geotechnical surveys and safety and flood assessments.

Figure 17: Changfeng Road Longhu Bridge, which will utilize a diagonal-span cable stay arch design (preliminary design).

Source: Domestic EIT, 2018.

102. Total traffic flows for the road network is presented in Table 22, traffic composition in Table 23 and peak daytime and nighttime traffic flows at short-term (2020), mid-term (2026) and long-term (2034) horizons in Table 24. Traffic predictions were provided by the roads component Design Institute, and are based on development plans in the Gui’an New District Public Transport Master Plan (2018-2030), economic development forecasts for the area, estimated distribution of the total traffic demand, and estimate the traffic load on each specific road based on the distribution of traffic demand, travelling time and vehicle costs. The mains and submains are designed to meet traffic flows for the next 20 years, and the branch roads for the next 15 years.

Table 22: Predicted annual daily average daily traffic flows (vehicles/day), supporting road network works, GDAD, at short-term, mid-term and long-term horizons. No. Name Road Class 2020 2026 2034 1 #5 Road Main 16,254 22,314 26,442 2 Northern Ext. of Zhanqian Road Main 15,751 21,623 25,625 3 Changfeng Road (Z7) Sub-main 9,954 13,664 16,193 4 H6 Road Branch 5,362 7,361 8,723 5 Z3 Road Branch 5,195 7,131 8,451 6 H8 Road Branch 5,831 8,005 9,487 7 H11 Road Branch 5,530 7,591 8,996 8 H12 Road Branch 5,664 7,775 9,214 9 H13 Road Branch 4,859 6,671 7,905 10 Z4 Road Branch 5,061 6,947 8,233

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No. Name Road Class 2020 2026 2034 11 Z8 Road Branch 4,859 6,671 7,905 12 H4 Road Branch 5,211 7,154 8,478 13 H1 Road Branch 5,362 7361 8,723 Total 94,894 130,270 154,375 Source: domestic EIT, 2018.

Table 23: Predicted traffic composition by vehicle type (%), supporting road network works, GDAD, at short-term, mid-term and long-term horizons. Traffic flow in study years 2020 2026 2034 Compact vehicle 45 52 60 Middle-sized vehicle 34 30 34 Oversize vehicle 21 18 6 Source: domestic EIT, 2018.

Table 24: Predicted hourly daytime (6:00 to 22:00) and nighttime (22:00 to 6:00) traffic flows (vehicles/hour), supporting road network works, GDAD, at short-term, mid-term and long- term horizons. Prediction results Time Road Compact Vehicles Mid-sized Vehicles Large Vehicles Horizon Daytime Nighttime Daytime Nighttime Daytime Nighttime 2020 265 133 200 100 124 62 5# Road 2026 436 218 252 126 151 75 2034 645 322 365 183 64 32 Northern Extended 2020 257 128 194 97 120 60 Section of 2026 423 211 244 122 146 73 Zhanqian Road 2034 625 313 354 177 63 31 2020 162 81 123 61 76 38 Changfeng Road 2026 267 134 154 77 92 46 (Z7) 2034 395 197 224 112 39 20 2020 87 44 66 33 41 20 H6 Road 2026 144 72 83 42 50 25 2034 213 106 121 60 21 11 2020 85 42 64 32 40 20 Z3 Road 2026 139 70 80 40 48 24 2034 206 103 117 58 21 10 2020 95 48 72 36 44 22 H8 Road 2026 156 78 90 45 54 27 2034 231 116 131 66 23 12 2020 90 45 68 34 42 21 H11 Road 2026 148 74 86 43 51 26 2034 219 110 124 62 22 11 2020 92 46 70 35 43 22 H12 Road 2026 152 76 88 44 53 26 2034 225 112 127 64 22 11 2020 79 40 60 30 37 18 H13 Road 2026 130 65 75 38 45 23 2034 193 96 109 55 19 10 2020 83 41 62 31 39 19 Z4 Road 2026 136 68 78 39 47 24 2034 201 100 114 57 20 10 2020 79 40 60 30 37 18 Z8 Road 2026 130 65 75 38 45 23 2034 193 96 109 55 19 10

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Prediction results Time Road Compact Vehicles Mid-sized Vehicles Large Vehicles Horizon Daytime Nighttime Daytime Nighttime Daytime Nighttime 2020 85 42 64 32 40 20 H4 Road 2026 140 70 81 40 48 24 2034 207 103 117 59 21 10 2020 87 44 66 33 41 20 H1 Road 2026 144 72 83 42 50 25 2034 213 106 121 60 21 11 Source: domestic EIT, 2018.

iii) Intelligent Connected Vehicle System Demonstration Zone

103. The following is a summary of the preliminary concept for the ICVSDZ component. It is summary in that a more thorough description is provided in Appendix K22; and it is preliminary in that as the ICVSDZ component is not scheduled to begin implementation until 2 to 3 years after project approval, and as ICV is a fast growing technology, the exact technologies that will be selected for ICV testing are as yet somewhat uncertain. Therefore, the ICVSDZ component preliminary concept will be further refined during implementation.

104. ICVs are equipped with a variety of sensors to perceive their surroundings, and communication technologies to communicate with drivers, other cars on the road, roadside infrastructure, and data support and traffic management platforms. Advanced control systems interpret sensory information to make intelligent navigation decisions. ICVs that are currently in operation are usually guided vehicles, meaning a driver is in the vehicle to override and react to situations when needed. Future generation of ICVs will replace this with fully autonomous operation.

105. Potential benefits of ICVs include increased traffic flows and reduced traffic congestion; increased safety including a reduction in traffic collisions, injuries and related insurance and other costs; increased mobility access for children, the elderly, disabled, and the poor; increased vehicle fuel efficiency; and reduced emissions of CO2 and other pollutants

106. The ICVSDZ component will establish a demonstration zone for research and development of ICV and associated technologies. It will include establishing a data center platform, and the application of information technologies to be installed in transport infrastructure at designated ICVSDZ, which are a fenced and access-controlled industrial park and 2.5 km of adjacent public open-roads. In summary, the component will:

(i) Procure, install, configure, and synchronize software and hardware for enabling communication and smart management through establishing a datacenter in an existing premise in the ICVSDZ. (ii) Procure, install and configure Internet-of-Things (IoT) enabled information communication systems using cloud technology architecture for traffic management and control. (iii) Procure, install and configure associated ICV communication infrastructure at the designated ICVSDZ.

22 Appendix K includes ICV Regulatory Framework; Preliminary Component Concept Description; Indicative ICV Testing Plan; Indicative ICV Safety Management Plan; Public Consultation and Information Disclosure; and Grievance Redress Mechanism.

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107. The ICVSDZ component will adopt a 1-3-13 approach, with one data center which collects and analyses data retrieved from three different software and hardware infrastructure platforms for thirteen applicationsError! Reference source not found.).

108. The ICV Integrated Data Center (the “1” in the 1-3-13 approach) hosts software, hardware and communication equipment that facilitates data communication, automated decision processing, and bi-directional communication with test vehicles and traffic systems in the ICV demonstration testing zone.

109. The three ICV software and hardware infrastructure platforms (the “3” in the 1-3-13 approach) are (i) Intelligent Connected Vehicle Operation Support Platform; (ii) Multimode Wireless Communication System Platform; and, (iii) Intelligent Transport Demonstration Application Platform.

Figure 18: ICVSDZ 1-3-13 model, with a data center which collects and analyses data retrieved from three platforms for thirteen applications.

Source: ICVSDZ FSR, 2018.

110. These platforms can accommodate and run thirteen applications (the “13” in the 1-3- 13 approach) of any ICV testing:

(i) Integrated video surveillance system; (ii) Traffic signal control system; (iii) Edge computing system; (iv) High-precision positioning system; (v) Weather monitoring system; (vi) V2x traffic guidance system; (vii) Lte-v2x communication system; (viii) 5g-v2x communication system; (ix) Nb-iot communication system; (x) Wi-Fi communication system; (xi) Smart parking lot; (xii) Automatic driving demonstration application system; and (xiii) Photovoltaic + energy storage + charging pile integrated system.

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111. ICV test activities will take place within the 40 ha fenced and access controlled Gui’an New Area High-End Equipment Industry Park and 2.5 km of adjacent public open- roads (Figure 19). No new buildings or roads will be constructed under the ICVSDZ component, and equipment will be installed either in existing buildings or on existing roads. The ICVSDZ component under the project only involve setting up ICT infrastructure for ICV testings, but it does not include actual testing of ICVs, which shall be carried out by an eligible testing applicant in accordance with the PRC requirements on ICV testing.23

112. As noted above, the ICVSDZ component description is presented in more detail in Appendix K.

Figure 19: Gui’an New Area High-End Equipment Industry Park and indicative testing roads for ICVs.

Source: PMO, 2018 and Google Earth, 2019.

iv) Capacity Building

113. Experience and capacity of the Borrower. The GDAD is a newly established economic zone and the GGAND has limited experience or the required staff in developing and operating innovative green transport systems. Trainings and study tours are needed for GGAND officials and related government staff to understand the ITS system, especially its importance and impacts to the new district development, as well as to gain experience in developing and operating an ITS. Long-term capacity also needs to be built up though implementing this project and the technical assistance programs under the project.

23 the Administrative Measures of Road Test for Intelligent Connected Vehicles (for trial implementation) jointly issued by the Ministry of Industry and Information Technology, the Ministry of Public Security and the Ministry of Transport on April 12, 2018.

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114. Experience and capacity of the PMO. A Project Management Office (PMO) has been established for the project preparation and implementation. Currently, the PMO has only a few staff (one permanent staff and two contracted staff), which is not adequate to manage the project preparation and implementation according to general practice of similar ADB financed projects in the PRC. Although the PMO will need to recruit experienced staff and obtaining more training, substantial external assistance will also be needed during project implementation, mainly for project management, construction supervision, social and benefit monitoring, procurement and contract management, and compliance with ADB’s safeguard policy and requirements.

115. Experience and capacity of the project implementation units (PIUs). Part of the project subcomponents will be implemented by other government’s investment companies/platforms in Gui’an (PIUs). The PIUs have not yet had any experience in ADB financed projects. Short term training is needed, mainly in project planning, financial management, FIDIC contracts, and ADB’s safeguard policies. Some of the PIUs will be the operators of the assets created under the project. These operators need to understand and adopt advanced concept and technology in operating and managing the assets, like green transport, public transport, transport-oriented development, asset valuation and management, and performance-based maintenance.

116. Training provided during project preparation. PPTA consultants have provided substantial training during project preparation to the PMO, related government agencies, the IAs, and the FSR consultants, focusing on ADB’s policies and procedures, public transport experiences and practices, ITS advanced concepts and technologies, and ADB safeguard requirements. This training have substantially increased the knowledge of related staff on ADB financed projects, including policies, procedure, and requirements. However, this training alone is not adequate, and needs to be extended in scope and/or repeated as necessary.

117. Proposed technical support and capacity development program. Based on a capacity assessment and the general practice of implementing ADB financed projects, substantial consulting services will be needed. The major consulting services during implementation are:

1. Project management consultant (PMC), mainly on project planning, procurement and recruitment, contract management, financial management, report preparation, safeguards, capacity development programs implementation, etc. 2. Technical supports, mainly on implementations of the ITS and public transport components. 3. Construction supervision (CS), providing third-party construction supervisions and quality controls at project sites and ensuring compliance with FIDIC conditions. 4. Environment monitoring, facilitating EMP implementation, carrying out regular monitoring and preparing monitoring reports, and ensuring compliance ADB’s environment safeguard policy (additional information is presented in the EMP, Appendix A). 5. DMF and social impact monitoring and evaluation, carrying out annual monitoring and evaluation (M&E) program to collect and assess the data specified in the DMF and GAP. 6. LARP implementation monitoring, facilitating LARP implementation, monitoring impacts, providing trainings, and ensuring compliance ADB’s policies on involuntary resettlement. 7. ICV technical and testing verification support, ICV safety manangement, ICV testing safety assessment .

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118. The government intends to recruit a domestic consulting firm for the above aspects of 1, 2, and 5; recruit separate consulting firms for the 4 and 6; and recruit 3 or 4 construction supervision consulting firms respectively for the ITS and the sustainable transport infrastructure. TORs will be prepared to clearly describe the purpose, tasks, outputs, implementation schedule, expert requirements, and cost estimations of the consulting services. Recruitment of ICV consultants is discussed in Appendix K.

119. The following study tours are also planned:

1. Overseas study tour, overseas study tour for the GGAND officials to learn advanced concept and practice abroad by focusing on ITS development and operation, TOD, new district development, and asset management. 2. Overseas trainings, short-term trainings for the PMO and IA’s technical staff to learn project management, ITS implementation, green and public transport, etc. 3. Domestic study tour, domestic study tour for the GGAND’s official, PMO and IA’s technical staff to learn experiences of implementing ADB financed projects, ITS implementation and operation, etc.

120. The PMO, PIUs, Project Management Contactors, CSC and construction contractors will receive training on the ADB SPS (2009); PRC safeguard requirements; development and implementation of environment, health and safety (EHS) plans during construction and operation; implementation of the EMP, the EMoP, and the GRM; and typical good construction EHS plans and practices (Appendix A). Training will be provided by the LIEC.

121. ICVSDZ component training is discussed in Appendix K, and includes domestic and international training for key stakeholders to develop capacity for ICV system demonstration zone implementation.

122. Detailed plans for the training and study tours will be formulated and organized by the PMO during project implementation, with the assistance from the PMC.

E. Associated Facilities

123. Associated facilities are facilities that are not funded as part of a project but whose viability and existence depend exclusively on the project, or whose goods or services are essential for successful operation of the project.

124. The project supporting roads will provide access to key existing north-south and east- west trunk roads, and these trunk roads (Tianhetan Avenue, Jin’an Avenue, Zhanqian Road and Baima Avenue) are considered as associated facilities. The roads on which the bus stations will be situated are also considered to be associated facilities.

125. In addition, facilities that connect to the municipal power, water supply and other infrastructure that will be integrated under roadways are considered associated facilities.

F. Budget and Time Schedule

126. The project is estimated to cost $495.47 million, including local taxes and duties (estimated at $16.48 million) and financial charges (Table 25), of which ADB has been requested to finance $200 million from its ordinary capital resources. The Government of Gui’an New District (GGAND) will finance the remaining $295.47 million equivalent (Table 26). The Government of the PRC will on-lend the loan proceeds to the Guizhou Province, and re-lend again to the GDAD under the same terms and conditions as it receives from

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ADB. The GGAND will bear the taxes, duties, interest rate variation, and foreign exchange risk on the loan.

Table 25: Project estimated cost. Item Amounta A. Base Cost 1. ITS Development 92.96 2. Sustainable Transport Infrastructure Development 205.09 3. Capacity Strengthening 12.07 4. Project Preparation and Management 107.76 5. Land Acquisition and Resettlement 3.21 Subtotal (A) 421.10 B. Contingencies 53.06 C. Financial Charges During Implementation 21.31 Total (A+B+C) 495.47 a Includes taxes and duties of $16.48 million. Such amount does not represent an excessive share of the project cost. The government will finance all taxes and duties. Note: Numbers may not sum precisely because of rounding. Source: ADB and government estimates.

Table 26: Project financing plan. Amount Share of Total Source ($ million) (%) Asian Development Bank 200.00 40.4% Gui’an Government 295.47 59.6% Total 495.47 100.0% Source: ADB and government estimates, 2018.

127. The project implementation period will be from 2019 to 2023, with a 3.5 to 4 year construction period (Figure 20). The project is expected to begin full operation in 2024.

Figure 20: Overall project implementation chart.

2019 2020 2021 20222023 2024 Outputs/Activity I II III IV I II III IV I II III IV I II III IV I II III IV I II III IV A. ITS Development 1. Detailed design 2. Developer and equipment procurement 3. ITS development

B Transport Infrastructure Works and Equipment Procurement 1. Detailed design preparation 2. Civil works procurement 3. Bus hub/station/depot construction 4. Charging station construction 5. Supporting road construction 6. Intelligent connected vehicles system demonstration zone 7. Electric bus procurement

C. Consulting Services and Capacity Strengthening 1. Consulting services recruitment 2. Project implementation management 3. Thematic studies 4. Capacity strengthening and study tour Source: ADB, FSR reports.

G. Implementation Arrangements

128. The Government of Gui’an New District (GGAND) will be the EA, but will be represented by the Bureau of Economic Development of Gui’an New District (BEDGA). A

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project management office (PMO) has been established under the EA to manage the project implementation on a daily basis, and will act as the implementing agency (IA).

129. The primary responsibilities of the PMO at the project preparation stage include (i) coordination with central/provincial governments, ADB, and related government agencies; (ii) preparing required reports and obtaining approvals from upper level governments/authorities; (iii) organizing project preparation activities, such as consultant recruitment and report preparation (project proposal, feasibility studies, land acquisition and resettlement plan, environment and social assessments, etc.); and, (iv) arranging project implementation.

130. During implementation, the PMO will be responsible for (i) coordination among central/provincial governments, ADB, the EA, and related government agencies and entities; (ii) implementation planning, arrangement, and quality control; (iii) loan disbursement and financial management; (iv) compliance of environment and social safeguards; (v) procurement and contract management; and (iv) direct implementation of some project subcomponents.

131. The PMO will be led by the director of the BEDGA and will be suitably staffed, including a qualified Environment, Health and Safety Officer (PMO EHSO), who will take overall responsibility for supervising the implementation of environment mitigation measures, coordinating the project level GRM and preparing monitoring reports for submission by the IA to ADB.

132. Three project implementation units (PIUs) will be established under the guidance of the PMO in the (i) Construction Investment Company (CIC); (ii) Culture and Tourism Investment Company (CTIC); and (iii) Industrial Investment Company (IIC). The three PIUs will assist the PMO in the implementation of supporting roads, bus hubs and buses, and charging stations, respectively. These companies are Gui’an state-owned enterprises and have technical experience in project implementation, operation and maintenance. Each PIU will identify a qualified staff member to be responsible for environment, health and safety issues.

133. The PMO will be in-charge of all other project components and subcomponents, including the ITS, bus terminal and depot construction, ICVSDZ and capacity development components.

134. In the operation phase the CTIC will be responsible for the operation of the bus fleet, and all bus stations (hubs, terminal stations, depots); the IIC will be is responsible for operation of the charging stations; and the CIC will be responsible for the operation of the road component.

135. Environment related implementation arrangements are discussed in more detail in the EMP (Appendix A). ICVSDZ implementation arrangements are discussed in Appendix K.

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IV. DESCRIPTION OF THE ENVIRONMENT

A. Location

136. The project is situated within the GDAD, Gui’an New District, Guizhou Province, PRC.

137. Guizhou Province is located in south-central China, although it is typically considered to be part of (Figure 1). It is bounded to the north by Province and Municipality, to the east by Province, to the south by the Zhuang Autonomous Region of , and to the west by Province. The province is comprised of 9 municipalities and 88 counties (including county level cities and districts). Its capital is Guiyang City.

138. Guiyang City is located in the center of Guizhou Province. It has an area of 8,034 km2, and is comprised of 6 districts, one county-level city, and three counties.

139. Gui’an New District, China’s eighth state-level new district, was established in January 2014 by the PRC’s State Council, with the development objective of becoming an economic driver of western PRC and Guizhou Province. The district has a total area of 1,750 km2.

140. Gui’an Direct Administrative District (GDAD), the focus of the project, has an area of 470 km. It is a subdivision of the Gui’an New District, and is under the authority of the Gui’an New District Management Committee (GNDMC). Located southwest of Guiyang City and northeast of Anshun City, it is a new urban development covering 21 townships in 4 counties and districts of Guiyang and Anshun cities (Figure 21).

Figure 21: GDAD in relation to Gui’an New District and Guiyang, the capital of Guizhou.

Guiyang City

GDAD Gui’an New District

Source: Google Maps 2018, PMO 2018.

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B. Physical Resources

141. Topography. Guizhou Province is situated on the eastern portion of the Yungui Plateau, an old eroded plateau which connects with plateau areas in Yunnan. Located between the Plateau of Tibet and the hilly regions of Hunan and Guangxi, the Yungui Plateau forms part of a continuously ascending profile, its altitude increasing from about 700 meters above sea level (masl) in eastern Guizhou to about 2,000 masl in the west.

142. The Sichuan Basin to the north and the Guangxi Basin to the south are both the results of faulting. The entire terrain of Guizhou thus slopes at a steep angle from the center toward the north, east, and south. In areas adjacent to Sichuan and Hunan in the north and east, the elevation is about 700 masl, while the province’s southern slopes descend some 500 to 600 m into Guangxi. Accordingly, rivers in the province generally flow in three directions, north, east, and south.

143. Guizhou Province is generally considered to be a mountainous province. The Yungui Plateau, which is composed mostly of limestone and basalt, has undergone complicated and extensive folding, faulting, and stream erosion and consequently displays abrupt relief, an example of which is the famous near Anshun in the southwest. Incised valleys, steep gorges, and cliffs are common. In the limestone areas the characteristic landscape consists of highly developed formations.

144. The GDAD is located in central Guizhou where the plateau topography is broad and flatter. As shown in Figure 22, the northern and eastern portions of the district are generally flat, though there hilly areas in the west and, to a lesser extent, in the south.

Figure 22: GDAD topography.

Source: Google Maps 2018, PMO 2018.

145. Elevations in the district range from approximately 1,130 to 1,400 masl. Topography decreases slightly from the west to east (Figure 23), and from the north to the south and

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(Figure 24). The highest elevation in the area is 1415 masl at Gaofeng Mounting, about 5.8 km west of Yunman Lake hub station.

Figure 23: GDAD elevation profile from west (left) to east (right).

Source: Google Earth 2018, PMO 2018.

Figure 24: GDAD elevation profile from north (left) to south (right).

Source: Google Earth 2018, PMO 2018.

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146. Landuse. Figure 25 presents the GDAD landuse plan to 2020, which was developed in 2013. As part of China’s eighth state-level new district, the GDAD is undergoing rapid development, particularly in the northern core urban area, the central township of Macheng, the eastern township of Dangwu, and the western township of Gaofeng.

Figure 25: GDAD landuse plan for 2020 planning horizon.

Source: Charging Station Design Institute 2018.

147. The Gui’an New District Masterplan (2013-2020) designates 220 km2 for urban development, including 60.5 km2 of residential land, 16.1 km2 of public administration and service areas, and 23.7 km2 of parkland (Table 27). According to the masterplan, currently Gui’an is undergoing massive urban development.

148. Seismicity. The PRC classifies seismic intensity into 12 grades under the China Seismic Intensity Table (GB/T 17742-2008), based on the severity of “shaking” of the earth surface and the extent of potential impact. According to the China Seismic Ground Motion Parameters Zoning Map (GB18306-2015), the project area is relatively stable with a seismic basic intensity of Grade 6, with a peak ground acceleration of 0.05 g, a 10% probability of exceedance in 50 years, and a return period of 475 years. The Grade 6 seismicity intensity will be applied for the design and construction bus stations, charging stations, and roads as per the requirements of Code for Seismic Design of Buildings (GB 5011-2010).

149. Climate. Guizhou Province is located in the subtropical climatic zone, though its climate is tempered by its low latitude and high elevation. It is dry and cold in the winter and spring, and wet and mild in summer and autumn. The average annual temperature is 12 to 15 oC, while monthly average 24-hour temperature ranges from 5.1 °C in January to 23.9 °C in July. Annual rainfall is 1,000 to 1,400 mm, the majority of which falls in the summer months.

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Table 27: Land development planning In the GDAD, 2013-2030.

Land Use Area km2 Planned GDAD Urban Areas Residential areas 60.5 Public administration and public service area 16.1 Administrative office space 1.5 Land for cultural facilities 1.4 Education and scientific research sites 9.7 Of Which: Sports sites 1.4 Health sites 1.7 Land for social welfare 0.4 Land for commercial and service facilities 13.0 Development, and manufacturing sites 4.5 Industrial land 37.1 Logistics and warehouse space 7.4 Roads and transportation facilities 44.8 Of Which: City roads 40.9 Utilities 4.5 Green space 32.1 Of Which: Parks 23.7 Subtotal 220.0 Other GDAD Development Areas Country area 40 Transportation 17.6 Public utility 0.7 Special landuse 9.7 landuse 0 Other 2 Subtotal 70 Total Planned Development Area 290 Source: Gui’an Masterplan 2013-2030 (2014).

150. The annual mean temperature in the GDAD is 14.1 oC. The mean temperature in the coldest month (January) is 3.8 oC and 22.7 oC in the hottest month (July). The maximum and minimum recorded temperatures are 34.5 and -8.6 oC, respectively. On average there are 279 frost-free days per year. Mean annual precipitation is 1,186.3 mm, mostly occurring in the summer months, and the maximum recorded daily precipitation is 221.2 mm. The annual mean relative humidity is 81%, and there is an annual average of 15.3 fog days. Annual mean sunshine duration is 1310.8 hours. A climatograph for Guiyang city is presented in Figure 26.

151. Annual mean wind speed is 2.7 m/s. The prevailing wind direction is from the SSE in summer and from the NE winter (Figure 27). The annual frequency of calm winds is 12%.

152. Surface Water Rivers and Reservoirs. The GDAD is part of the Wu River basin, which in turn is a tributary of the Yangtze River, which drains to the East China Sea.

153. Surface water resources in the project area are presented in Figure 28. These resources include two main artificial reservoirs, several smaller reservoirs, and several small rivers:

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Figure 26: Climatograph, Guiyang City.

Source: https://en.climate-data.org/location/2303/.

Figure 27: Wind rose, Guiyang Longdongbao Airport.

Source: https://www.windfinder.com/windstatistics/guiyang_longdongbao_airport

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 Hongfeng Lake is an artificial lake created in 1960. A portion of the lake is located in the northwest corner of the new district. Hongfeng Lake drains north to the Maotiao River, a secondary tributary of Yangtze River. It has a drainage area of 1,596 km2 and a total available capacity of 442,000,000 m3, making it one of the biggest artificial lakes in Guizhou Province. The lake was designated as a National Scenic Area by the State Council in 1988. Hongfeng Lake was originally established for reservoir storage, but now serves multiple functions including power generation, flood control, industrial and agricultural water source, drinking water source, tourism, water sports, and, ecological regulation.  Songbaishan Reservoir is located in the southeast corner of the district. The reservoir drains north into the Huaxi Reservoir and River, both of which are outside of the GDAD, and then to the Naming River, the , and then the Wu River. Constructed in 1958, the reservoir utilizes a 52.5 m tall concrete double arch dam, and has a drainage area of 139 km2 and a total storage capacity is 47.60 million m3. The reservoir functions include flood protection, urban water supply, and irrigation.  Other smaller reservoirs include the Kechou and Wangguan reservoirs.  In addition to the Huaxi Reservoir/River, there are two small rivers through the south western portion of the district, the Yanchang and the Maxian (also called Yankong), both of which flow north into Honfeng Lake. Other small rivers/streams include the Chetian and the Machang.

Figure 28: Water resources in the GDAD.

Hongfeng Lake

Wangguan Reservoir

Yanchang River Huaxi River Songbaishan Maxian River Reservoir

Kechou Reservoir

Source: Google Earth 2016, and DEIA 2018.

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154. Project supporting roads are situated in the urban core area of the GDAD. The entire core area has previously been completely modified and cleared, and most of it is currently a construction site. Water resources in the area will consist of a series of artificial channels flowing from the Wangguan Reservoir through the urban core and draining to the Huaxi River. The Wangguan Reservoir is at an elevation of 1,240 masl, and is used for flood control and recreation. Water flow will be controlled by a series of control gates (Figure 29).

Figure 29: Current water resources in the core area of the GDAD with elevations. Green dots indicate control gates.

Source: Google Earth 2016, and DEIA 2018.

155. Figure 30 presents a map of drinking water source protection zones for the GDAD. In accordance with Article 15 of the Guizhou Province Drinking Water Source Environmental Protection Measures (Trial), no bus stations are located within the Class I or Class II protection zones. Several stations are located within the quasi protection zone. This is common in many urban areas, and is allowed under article 15 of the Guizhou Province Drinking Water Source Environmental Protection Measures (Trial) as they are not allowing papermaking, electroplating, printing & dyeing, brewing or other prohibited activities in this quasi protection zone.

156. Baseline Environmental Data. Baseline environmental data in the GDAD was collected from monitoring undertaken by the GEPB.

Air Quality

157. Air quality was assessed based on monitoring undertaken at eight GEPB monitoring stations (Figure 31). According to the Monthly Report on Environmental Quality of Gui’an New District (Jun. 2018), the average 1 and 24 hour concentration of NO2 and SO2, and the average 24 hour concentration of TSP and PM10 at all stations were in compliance with the Class II limits specified in the Ambient Air Quality Standards (GB3095-2012) (Table 28 and

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Table 29). This indicates that the project area has relatively good air quality.

Figure 30: Drinking water source protection zones in the GDAD.

Source: Guizhou Province Drinking Water Source Environmental Protection Measures (Trial) and Google Earth (2017).

Figure 31: Location of GEPB air quality monitoring stations in the GDAD.

Source: GEPB, 2018.

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Table 28: Ambient air quality monitoring results, GDAD, June 2018. Average 24-hour Pollutant Concentration (μg/m3) No. Station Name PM2.5 PM10 SO2 NO2 CO O3 G1 Machang Town 50 7 28 31 0.63 91 G2 High-Tech Park 47 71 29 32 0.63 94 G3 Gaofeng Mountain 46 70 25 28 0.73 90 G4 Administration Commission 13 26 12 12 0.51 61 G5 University Town 22 36 8 17 1.04 73 G6 Gaofeng Town 10 19 20 13 0.34 81 G7 Songbaishan 10 25 10 19 0.55 11 G8 Business Center 11 26 13 9 0.39 67 Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

Table 29: Compliance of ambient air quality monitoring results with applicable standards. Applicable Air Quality Actual Air Quality Exceedance Air Quality Class of No. Station Name Class (GB3095-2012) Class, June 2018 of Standard Previous Month G1 Machang Town Level II Level II - Level II G2 High-Tech Park Level II Level II - Level II G3 Gaofeng Mountain Level II Level II - Level II G4 Administration Commission Level II Level I - Level I G5 University Town Level II Level I - Level I G6 Gaofeng Town Level II Level I - Level I G7 Songbaishan Level I Level I - Level I G8 Business Incubator Level II Level I - Level I Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

Water Quality

158. Surface water quality was assessed based on monitoring undertaken at eight GEPB monitoring stations (Figure 32) in June 2018. Water quality in the Maxian River, Chetian River, Machang River and Ganhe River is good, and is in compliance with Level III standard in the Environmental Quality Standards for Surface Water (GB3838-2002) (Table 30 to Table 35).

Figure 32: Location of GEPB water quality monitoring points in the GDAD.

Source: GEPB, 2018.

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Table 30: Water quality monitoring data, W1 - Qingyutang cross-section of Maxian River. Level III (GB/T14848−2017) surface water standard ≥5 ≤6 ≤20 ≤4 ≤1.0 ≤0.2 ≤1.0 ≤1.0 ≤1.0 ≤1.0 ≤0.01 ≤0.05 ≤0.0001 ≤0.005 ≤0.05 Monitoring Water 6-9 (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator temperature Ammonia Total Hexavalent (0C) pH DO CODMn CODCr BOD5 TP Copper Zinc Fluoride Selenium Arsenic Mercury Cadmium nitrogen nitrogen chromium Monitoring 0.00 0.000 0.000 0.0000 15.3 7.14 7.8 5 10 1.8 0.38 0.06 2.20 0.00008 0.32 0.00041 0.004 mean value 007 12 01 5 In conformity —— Yes Yes Yes —— Yes Yes Yes —— Yes Yes Yes Yes Yes Yes Yes Yes with standard Level III (GB/T14848−2017) surface water standard ≤0.05 ≤0.2 ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤10000 ≤250 ≤250 ≤10 ≤0.3 ≤0.1 (m3/s) (m/s) (mg/L) (μs/cm) —— Monitoring (mg/L) (mg/L) (mg/L) (mg L) (mg/L) (mg/L) (pcs/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator Volatile Petro- Fecal Mang- Flow Flow Cond- Suspen- Lead Cyanide LAS Sulfide Sulfate Chloride Nitrate Iron —— phenol leum coliform anese rate velocity uctivity ded solid Monitoring 0.00 0.00 0.00009 0.004 0.01 0.05 0.005 1550 32 4 0.89 0.00012 3.65 0.38 317 21 —— mean value 03 082 In conformity Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes —— —— —— Yes —— with standard Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

Table 31: Water quality monitoring data, W2 - Qiaobian cross-section of Maxian River. Level III (GB/T14848−2017) surface water standard ≥5 ≤6 ≤20 ≤4 ≤1.0 ≤0.2 ≤1.0 ≤1.0 ≤1.0 ≤1.0 ≤0.01 ≤0.05 ≤0.0001 ≤0.005 ≤0.05 Monitoring Water 6-9 (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator temperature Ammonia Total Hexavalent (0C) pH DO CODMn CODCr BOD5 TP Copper Zinc Fluoride Selenium Arsenic Mercury Cadmium nitrogen nitrogen chromium Monitoring 0.000 0.000 0.000 0.000 0.0000 17.2 7.02 7.3 4.4 14 2.3 0.38 0.06 2.42 0.24 0.00041 0.004 mean value 08 67 12 01 5 In conformity —— Yes Yes Yes —— Yes Yes Yes —— Yes Yes Yes Yes Yes Yes Yes Yes with standard Level III (GB/T14848−2017) surface water standard ≤0.05 ≤0.2 ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤10000 ≤250 ≤250 ≤10 ≤0.3 ≤0.1 (m3/s) (m/s) (mg/L) (μs/cm) —— Monitoring (mg/L) (mg/L) (mg/L) (mg L) (mg/L) (mg/L) (pcs/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator Volatile Petro- Fecal Mang- Flow Flow Cond- Suspen- Lead Cyanide LAS Sulfide Sulfate Chloride Nitrate Iron —— phenol leum coliform anese rate velocity uctivity ded solid Monitoring 0.00 0.000 0.00009 0.004 0.01 0.05 0.005 1950 32 4 0.88 0.00012 2.89 0.32 264 32 —— mean value 03 82 In conformity Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes —— —— —— Yes —— with standard Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018. 62

Table 32: Water quality monitoring data, W3 - Kaisa cross-section of Machang River. Level III (GB/T14848−2017) surface water standard ≥5 ≤6 ≤20 ≤4 ≤1.0 ≤0.2 ≤1.0 ≤1.0 ≤1.0 ≤1.0 ≤0.01 ≤0.05 ≤0.0001 ≤0.005 ≤0.05 Monitoring Water 6-9 (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator temperature Ammonia Total Hexavalent (0C) pH DO CODMn CODCr BOD5 TP Copper Zinc Fluoride Selenium Arsenic Mercury Cadmium nitrogen nitrogen chromium Monitoring 0.000 0.000 0.000 0.000 0.0000 15.1 7.22 6.6 5.2 14 2.0 0.28 0.12 1.74 0.29 0.00041 0.004 mean value 08 67 12 01 5 In conformity —— Yes Yes Yes —— Yes Yes Yes —— Yes Yes Yes Yes Yes Yes Yes Yes with standard Level III (GB/T14848−2017) surface water standard ≤0.05 ≤0.2 ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤10000 ≤250 ≤250 ≤10 ≤0.3 ≤0.1 (m3/s) (m/s) (mg/L) (μs/cm) —— Monitoring (mg/L) (mg/L) (mg/L) (mg L) (mg/L) (mg/L) (pcs/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator Volatile Petro- Fecal Mang- Flow Flow Cond- Suspen- Lead Cyanide LAS Sulfide Sulfate Chloride Nitrate Iron —— phenol leum coliform anese rate velocity uctivity ded solid Monitoring 0.00 0.000 0.00009 0.004 0.01 0.07 0.005 2500 36 4 0.74 0.00012 1.78 0.16 361 25 —— mean value 03 82 In conformity Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes —— —— —— Yes —— with standard Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

Table 33: Water quality monitoring data, W4 - Kaizhang Reservoir cross-section of Gan River. Level III (GB/T14848−2017) surface water standard ≥5 ≤6 ≤20 ≤4 ≤1.0 ≤0.2 ≤1.0 ≤1.0 ≤1.0 ≤1.0 ≤0.01 ≤0.05 ≤0.0001 ≤0.005 ≤0.05 Monitoring Water 6-9 (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator temperature Ammonia Total Hexavalent (0C) pH DO CODMn CODCr BOD5 TP Copper Zinc Fluoride Selenium Arsenic Mercury Cadmium nitrogen nitrogen chromium Monitoring 0.000 0.000 0.000 0.000 0.0000 15.1 7.11 7.5 2.8 12 2.3 0.18 0.06 1.30 0.24 0.00041 0.004 mean value 08 67 12 01 5 In conformity —— Yes Yes Yes —— Yes Yes Yes —— Yes Yes Yes Yes Yes Yes Yes Yes with standard Level III (GB/T14848−2017) surface water standard ≤0.05 ≤0.2 ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤10000 ≤250 ≤250 ≤10 ≤0.3 ≤0.1 (m3/s) (m/s) (mg/L) (μs/cm) —— Monitoring (mg/L) (mg/L) (mg/L) (mg L) (mg/L) (mg/L) (pcs/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator Volatile Petro- Fecal Mang- Flow Flow Cond- Suspen- Lead Cyanide LAS Sulfide Sulfate Chloride Nitrate Iron —— phenol leum coliform anese rate velocity uctivity ded solid Monitoring 0.00 0.000 0.00009 0.004 0.01 0.05 0.005 1250 58 4 0.50 0.00012 —— —— 257 11 —— mean value 03 82 In conformity Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes —— —— —— Yes —— with standard Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

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Table 34: Water quality monitoring data, W5 - Gui’an Yungu channel of Gan River. Level III (GB/T14848−2017) surface water standard ≥5 ≤6 ≤20 ≤4 ≤1.0 ≤0.2 ≤1.0 ≤1.0 ≤1.0 ≤1.0 ≤0.01 ≤0.05 ≤0.0001 ≤0.005 ≤0.05 Monitoring Water 6-9 (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator temperature Ammonia Total Hexavalent (0C) pH DO CODMn CODCr BOD5 TP Copper Zinc Fluoride Selenium Arsenic Mercury Cadmium nitrogen nitrogen chromium Monitoring 0.000 0.000 0.000 0.000 0.0000 16.1 6.96 7.4 3.6 10 1.8 0.32 0.08 4.03 0.28 0.00041 0.004 mean value 08 67 12 01 5 In conformity —— Yes Yes Yes —— Yes Yes Yes —— Yes Yes Yes Yes Yes Yes Yes Yes with standard Level III (GB/T14848−2017) surface water standard ≤0.05 ≤0.2 ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤10000 ≤250 ≤250 ≤10 ≤0.3 ≤0.1 (m3/s) (m/s) (mg/L) (μs/cm) —— Monitoring (mg/L) (mg/L) (mg/L) (mg L) (mg/L) (mg/L) (pcs/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator Volatile Petro- Fecal Mang- Flow Flow Cond- Suspen- Lead Cyanide LAS Sulfide Sulfate Chloride Nitrate Iron —— phenol leum coliform anese rate velocity uctivity ded solid Monitoring 0.00 0.000 0.00009 0.004 0.01 0.05 0.005 745 36 4 2.74 0.00012 0.35 0.14 366 15 —— mean value 03 82 In conformity Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes —— —— —— Yes —— with standard Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

Table 35: Water quality monitoring data, W6 - Chetian Village cross-section of Chetian River. Level III (GB/T14848−2017) surface water standard ≥5 ≤6 ≤20 ≤4 ≤1.0 ≤0.2 ≤1.0 ≤1.0 ≤1.0 ≤1.0 ≤0.01 ≤0.05 ≤0.0001 ≤0.005 ≤0.05 Monitoring Water 6-9 (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator temperature Ammonia Total Hexavalent (0C) pH DO CODMn CODCr BOD5 TP Copper Zinc Fluoride Selenium Arsenic Mercury Cadmium nitrogen nitrogen chromium Monitoring 0.000 0.000 0.000 0.000 0.0000 15.9 7.14 8.6 3.0 5 1.0 0.22 0.08 2.58 0.34 0.00041 0.004 mean value 08 67 12 01 5 In conformity —— Yes Yes Yes —— Yes Yes Yes —— Yes Yes Yes Yes Yes Yes Yes Yes with standard Level III (GB/T14848−2017) surface water standard ≤0.05 ≤0.2 ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤10000 ≤250 ≤250 ≤10 ≤0.3 ≤0.1 (m3/s) (m/s) (mg/L) (μs/cm) —— Monitoring (mg/L) (mg/L) (mg/L) (mg L) (mg/L) (mg/L) (pcs/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator Volatile Petro- Fecal Mang- Flow Flow Cond- Suspen- Lead Cyanide LAS Sulfide Sulfate Chloride Nitrate Iron —— phenol leum coliform anese rate velocity uctivity ded solid Monitoring 0.00 0.000 0.00009 0.004 0.01 0.05 0.005 3350 50 6 1.88 0.00012 2.41 0.2 424 14 —— mean value 03 82 In conformity Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes —— —— —— Yes —— with standard Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

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Table 36: Water quality monitoring data, W7 - Siya Cross-section of Siya River. Level III (GB/T14848−2017) surface water standard ≥5 ≤6 ≤20 ≤4 ≤1.0 ≤0.2 ≤1.0 ≤1.0 ≤1.0 ≤1.0 ≤0.01 ≤0.05 ≤0.0001 ≤0.005 ≤0.05 Monitoring Water 6-9 (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator temperature Ammonia Total Hexavalent (0C) pH DO CODMn CODCr BOD5 TP Copper Zinc Fluoride Selenium Arsenic Mercury Cadmium nitrogen nitrogen chromium Monitoring 0.000 0.000 0.000 0.000 0.0000 15.1 7.11 7.5 2.8 12 2.3 0.18 0.06 1.30 0.24 0.00041L 0.004L mean value 08L 67L 12L 01L 5L In conformity —— Yes Yes Yes —— Yes Yes Yes —— Yes Yes Yes Yes Yes Yes Yes Yes with standard Level III (GB/T14848−2017) surface water standard ≤0.05 ≤0.2 ≤0.005 ≤0.05 ≤0.2 ≤0.2 ≤10000 ≤250 ≤250 ≤10 ≤0.3 ≤0.1 (m3/s) (m/s) (mg/L) (μs/cm) —— Monitoring (mg/L) (mg/L) (mg/L) (mg L) (mg/L) (mg/L) (pcs/L) (mg/L) (mg/L) (mg/L) (mg/L) (mg/L) indicator Volatile Petro- Fecal Mang- Flow Flow Cond- Suspen- Lead Cyanide LAS Sulfide Sulfate Chloride Nitrate Iron —— phenol leum coliform anese rate velocity uctivity ded solid Monitoring 0.004 0.00 0.005 0.000 0.00012 0.00009L 0.01L 0.05L 1250 58 4 0.50 —— —— 257 11 —— mean value L 03L L 82L L In conformity Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes —— —— —— Yes —— with standard Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

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159. With respect to groundwater, the domestic EIT reports that groundwater quality in the project area is in compliance with Level III water quality specified in the Quality Standard for Groundwater (GB/T14848−2017).

Noise

160. Urban noise levels were assessed based on monitoring undertaken at ten GEPB monitoring stations (Figure 33). According to the Monthly Report on Environmental Quality of Gui’an New District (Jun. 2018), noise levels are in compliance with Class II standard in Environmental Quality Standard for Noise (GB3096-2008) (Table 37).

Figure 33: Location of GEPB sound quality monitoring points in the GDAD.

Source: GEPB, 2018.

Table 37: Daytime ambient noise monitoring data, GDAD, June 2018.

Daytime Complies Monitoring No. Standard with Point Leq Lmax Lmin L10 L50 L90 SD dB(A) dB(A) dB(A) dB(A) dB(A) dB(A) dB(A) Standard? N1 Dangwu Village 56.3 69.6 47.6 59.9 52.8 50.1 4.1 60 Yes N2 Huchao Village 54.9 65.7 48.2 57.3 53.8 49.6 3.1 60 Yes N3 Machang Town 53.6 65.0 47.6 56.0 52.6 50.6 3.2 60 Yes N4 Gaofeng Town 56.9 70.7 47.8 59.9 53.6 50.3 4.0 60 Yes N5 University Town 52.2 73.1 47.7 52.7 50.3 49.1 2.6 55 Yes Fugui Ankang N6 55.3 76.4 45.3 57.2 49.1 46.9 4.5 60 Yes Community N7 Pingzhai 56.7 72.6 47.8 59.2 52.9 50.1 3.8 60 Yes

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Daytime Complies Monitoring No. Standard with Point Leq Lmax Lmin L10 L50 L90 SD dB(A) dB(A) dB(A) dB(A) dB(A) dB(A) dB(A) Standard? Community Electronic N8 Information 53.3 62.7 46.0 55.5 52.7 50.4 2.7 65 Yes Industrial Park High-end N9 Equipment 51.9 58.6 47.7 54.6 50.8 49.3 2.2 65 Yes Industrial Park Temporary N10 Administrative 54.8 65.3 47.7 57.1 52.3 50.0 3.5 55 Yes Center Source: Monthly Report on Environmental Quality of Gui’an New District, June 2018.

C. Ecology and Sensitive Resources

161. Ecology – Parks and Green Space. The Gui’an New District has a total area of 1,750 km2, of which 220 km2 has been designated for urban development within the 470 km2 GDAD. As noted above, by 2030 this urban development area is to include 60.5 km2 of residential land, 16.1 km2 of public administration and service areas, and 23.7 km2 of parkland (Table 27). Of the planned 23.7 km2 of parkland in the GDAD, as of Jan 2019 4.1 km2 of parkland has been established. Table 38 presents additional information on the parklands and greenspace to be developed within the urban area of the GDAD.

Table 38: Current and planned urban greenspace, GDAD. Type of Existing Areas Planned Areas Main Species Vegetation Greenspace (km2), Jan 2019 (km2), 2030 Coverage % Pers, Zelkova serrata, 65-80 Ginkgoaceae, Sophora Japonica, Latanus hisanica, (Hemsl.) Sarg., Cerasus lannesiana, Cinnamomum Parks camphora (L.) Presl., Magnolia Grandiflora Greenspace in 2.6 15.1 Linn, Salix matsudana, Salix babylonica, Industrial Areas Koelreuteria paniculata Laxm, Acer palmatum 'Atropurpureum', Sapindus mukorossi, Ilex crenatacv.Convexa, . Boundary Zone Osmanthi Fragrantis, Liquidamba spp., 85-95 Greenspace Phyllostachys nigra, Cinnamomum (separating two or camphora (L.) Presl, Cedrus deodara, 0.0 2.5 more industrial, Malus x micromalus, Manglietia insignis utility, residential, (Wall.) Bl. etc.) sites Cinnamomum camphora, Michelia figo, 20-35 Greenspace in other Celtis Sinensis, Ginkgo biloba, Latanus land uses (industrial, hisanica, Magnolia denudata, Magnolia 1.5 2.1 utility, commercial, grandiflora, Zelkova serrata, Acer residential, etc. palmatum, Cerasus lannesiana, Manglietia insignis (Wall.) Bl., fragrans Subtotal 4.1 19.6 Total 23.7 Source: GGAND, 2019. Note: The above table refers to the 220 km2 area within the 470 km2 GDAD that has been designated for urban development. It does not include greenspace in the remainder of the GDAD outside of the planned urban development area.

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162. Figure 34 shows the planned urban development area of the GDAD. It can be noted from the figure that there are still large areas of forest cover, vegetated hills and lakes that are within the GDAD but not within the planned urban development area.

Figure 34: Planned urban development area (highlighted in red) within the GDAD.

Source: Gui’an New District Masterplan (2013-2020) and Google Earth, 2019.

163. Ecology – Project Sites. All project bus station sites (hub, terminal and depot stations) are situated in areas that have been already developed. Original vegetation cover has been previously removed, and existing site vegetation is either farmland (some of which is temporary by non-landowners), barren land, grasses and shrubs, or low value roadside landscaping. Some sites such as the University Town Bus Depot are covered with building debris. However, hub station 1-2 (Machang Public Transportation) is located near to a hill which retains a significant amount of forest cover. A summary of site description and vegetation cover for the 20 bus station sites is presented in Appendix E.

164. Charging stations will also be situated in urban areas that have been previously developed, along the main roads in the new district, in core functional areas, and along the secondary roads in the new district, in the administrative office area, functional & industrial parks, theme parks and tourist attractions of cultural and scenic spots, public parking lots, and the core link points of University Town (Appendix F).

165. Project supporting roads are situated in the urban core area of the GDAD. The entire core area has previously been completely modified and cleared, and most of it is currently a construction site (Figure 35 and Figure 36). Little or no original vegetation remains.

166. Based on the domestic EIT, site surveys and records review, there are no known rare or endangered flora or fauna, species with international, national or provincial protection

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status, areas of natural or critical habitat24, parks, nature reserves, or areas with special national, regional or local ecological significance within or adjacent to any of the project sites. The only known site with Physical Cultural Resources (PCRs) is East of Gaofeng High School terminal station, which has a number of family graves near it.25

167. Sensitive Receptors. The domestic EIT report identifies 335 sensitive receptors for air and noise impacts in the bus station zone of influence, including 89 schools, 37 hospital, and 209 residential areas, as summarized in Table 39.26 Sensitive receptors in the area of the supporting roads are presented in Table 40. Other sensitive receptors are summarized in Table 42.

Figure 35: Aerial and ground images from project road 12-H4.

Road 12-H4 will provide Project roads 12-H4 (bottom) and 11-78 (from Starting point of road 12-H4. access to the urban core from center to top) Bai Ma Avenue, above. Source: PMO 2018, PPTA consultants 2018, and Google Earth 2018 (Google Earth image is dated June 2017).

24 Natural habitat is land and water areas where the biological communities are formed largely by native plant and animal species, and where human activity has not essentially modified the area’s primary ecological functions. Critical habitat are areas with high biodiversity value, including habitat required for the survival of critically endangered or endangered species; areas having special significance for endemic or restricted- range species; sites that are critical for the survival of migratory species; areas supporting globally significant concentrations or numbers of individuals of congregatory species; areas with unique assemblages of species or that are associated with key evolutionary processes or provide key ecosystem services; and areas having biodiversity of significant social, economic, or cultural importance to local communities (Environment Safeguards: A Good Practice Sourcebook, ADB, 2012). 25 PCRs are broadly defined as covering all types of tangible cultural heritage, including movable or immovable objects, sites, structures, groups of structures, and natural features and landscapes that have archaeological, paleontological, historical, architectural, religious, aesthetic or other cultural significance. PCR are human- made objects, natural features, or a mix of the two. They may be located in urban or rural areas and may be above or below ground or underwater. They may be known and listed on official inventories, but often they are undiscovered (Environment Safeguards: A Good Practice Sourcebook, ADB, 2012). 26 Project zone of influence is discussed in Section V.

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Figure 36: Aerial images showing degree of development and vegetation clearance in area of project roads 7-H11, 10-Z4, and 1-#5 (right).

Source: PMO 2018, Google Earth 2018 (Google Earth image is dated June 2017). Note: road alignments avoid all existing and planned buildings, and no demolition will be required.

Table 39: Sensitive receptors near bus stations, and applicable standards. Sensitive Receptors – Noise Sensitive Receptors – Air Quality Sensitive Receptors Outputs Environmental Quality Standard for Ambient Air Quality Standards - Other Noise (GB3096-2008), Level I or II (GB3095-2012), Level II 1. Hub Stations 1 Gaofeng Passenger Gaofeng town residential area to Gaofeng town residential area to north, Hub north and west, 35 to 200 m from west and south, 35 to 500 m, 100 site boundary. 46 households with households, 400 persons. 184 persons. Yangjiaxinzhai residential area, 35 (GB3096-2008, Level II) households, 140 persons, 200 to 500 m to the north. Maomaodong residential area, 35 households, 140 persons, 350 to 500 m to the southeast. 2 Machang Public Yangliushao residential area 60 to Yangliushao residential area 60 to 500 Forested hilly area Transportation Hub 200 southwest from site. 10 southwest from site. 55 households, immediately adjacent households, 40 persons. 220 persons. to the northwest of (GB3096-2008, Level II) site. 3 Biguiyuan Hub Residential area, 90 to 200 m to the Residential area, 90 to 500 m to the west, 300 households, 1200 west, 600 households, 2400 persons. persons. (GB3096-2008, Level II) 4 South University Town Huofodun residential area, 70 to Huofodun residential area, 70 to 500 m, Hub 200 m, 4 households, 16 persons. 4 households, 16 persons.

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Sensitive Receptors – Noise Sensitive Receptors – Air Quality Sensitive Receptors Outputs Environmental Quality Standard for Ambient Air Quality Standards - Other Noise (GB3096-2008), Level I or II (GB3095-2012), Level II (GB3096-2008, Level II) Huangpozhai residential area, 18 households, 72 persons, 250 to 500 m to the southeast. Yanjiaozhai residential area, 16 households, 64 persons, 210 to 500 m to the northeast. 5 Yunman Lake Hub Yunman Lake Tourist Resort 120 to Yunman Lake Tourist Resort 120 to 200 m to the north. 200 m to the north. Jiahexiazha residential area 60 to Jiahexiazha residential area 60 to 500 130 m to the west, 15 households, m to the west, 28 households, 112 60 persons. persons. Adjacent to Yunman Lake (90 m to the east). Shangba reservoir is 400 m to the north of the site. It functions as an irrigation source and for short-time storage. (GB3096-2008, Level II) 6 North Fukang Road- Ganhe residential area 90 to 200 m Ganhe residential area 90 to 500 m to Treed area to the Xuanshui Road Hub to the northeast, 150 households, the northeast, 300 households, 800 south of the site. 600 residents. persons. (GB3096-2008, Level II) 2. Terminal Stations 1 Shuangxi Road-Bai Ma - - Avenue 2 Xinghu Community Huchao Primary School, 180 Huchao Primary School, 180 persons, persons, 120 m to the south. 120 m to the south. (GB3096-2008, Level I) Residential area of Huchao Village, 32 households, 128 persons, 40 to 500 m Huchao Village, 40 to 200 m to the to the south. south, 18 households, 72 persons. Residential area of Huchao Village, 50 (GB3096-2008, Level I) households, 200 persons, 300 to 500 m to the east. Xinghuyun Community, 260 households, 1040 persons, 280 to 500 m to the northwest. 3 North of the Xingyue Xingyue Community No. 7, 70 to Xingyue Community No. 7, 70 to 500 m Community 200 m to the south, 260 to the south, 550 households, 2200 households, 1,040 persons. persons. (GB3096-2008, Level II) 4 East of Gaofeng High Gaofeng Middle School, 180 m to Gaofeng Middle School, 180 m to the 20+ family graves School the southwest, 1,800 persons. southwest, 1,800 persons. located to the SE of (GB3096-2008, Level I) Residential area of Gaofeng Town, 32 the site. to 500 m to the southwest, 200 Residential area of Gaofeng Town, households, 800 persons. 32 to 200 m to the southwest, 95 Xiaozhai residential area, 10 households, 380 persons. households, 40 persons, 295 to 500 m (GB3096-2008, Level II) to the northeast. Yangjiaxinzhai residential area, 35 households, 140 persons, 396 to 500 m to the southeast. Dalege Village, 32 households, 128 persons, 290 to 500 m to the north.

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Sensitive Receptors – Noise Sensitive Receptors – Air Quality Sensitive Receptors Outputs Environmental Quality Standard for Ambient Air Quality Standards - Other Noise (GB3096-2008), Level I or II (GB3095-2012), Level II 5 Machang township Machang Middle School 100 m to Machang Middle School 100 m to the the southeast, 3000 persons. southeast, 3000 persons. (GB3096-2008, Level I) Residential area of Machang Town, 12 to 500 m to the north, west and south, Residential area of Machang Town, 105 households, 420 persons. 12 to 200 m to the north, west and south, 35 households, 140 persons. (GB3096-2008, Level II) 6 High Technology Residential area of Guoluo Village Residential area of Guoluo Village 100 Industrial Park 100 to 200 m to the south, 3 to 500 m to the south, 7 households, 28 households, 12 persons. persons. (GB3096-2008, Level II) 7 Dong Qing - Si Ya GuiZhou Institute of Light Industry, GuiZhou Institute of Light Industry, 110 Road 110 to 200 m to the northeast, to 500 m to the northeast, 11000 11000 persons. persons. Guiyang College of Traditional Guiyang College of Traditional Chinese Chinese Medicine, 75 to 200 m to Medicine, 75 to 2500 m to the the southwest, 11000 persons. southwest, 11000 persons. (GB3096-2008, Level I) 8 Comprehensive Ganhe Community 70 to 200 m to Ganhe Community 70 to 500 m to the Bonded Zone the west, 150 households, 600 west, 300 households, 800 persons. persons. (GB3096-2008, Level II) 9 South of Xingan Yangliushao Residential area, 50 to Yangliushao Residential area, 50 to Avenue 200 m to the northeast, 20 500 m to the northeast, 55 households, households, 80 persons. 220 persons. (GB3096-2008, Level II) 10 Minbo Park No. 5708 Factory, 20 persons, 6 m No. 5708 Factory, 20 persons, 6 m to to the southwest. the southwest. Xiaojingdapo, 20 households, 80 Xiaojingdapo, 40 households, 160 persons, 55 to 200 m to the south. persons, 55 to 500 m in all directions. (GB3096-2008, Level II) 11 Gui’an Chuangu Extensive residential areas in all Extensive residential areas in all Small watercourse. directions, 30 to 200 m. directions, 30 to 500 m. (GB3096-2008, Level II) 3. Bus Depots 1 Central Area Bus Depot Malu Village, 145 to 200 m to the Malu Village, 145 to 500 m to the east, east, 3 households, 12 persons. 8 households, 32 persons. (GB3096-2008, Level II) 2 University Town Bus Kulijing residential area, 3 Kulijing residential area, 7 households, Depot households, 12 persons, 170 to 200 28 persons, 170 to 500 m to the north. m to the north. Zhoubo residential area, 20 (GB3096-2008, Level II) households, 80 persons, 250 to 500 m to the east. Dixiayuan residential area, 12 households, 48 persons, 340 to 500 m to the south. 3 East Machang Bus Commercial and residential building Commercial and residential building Depot under construction, 180 to 200 m to under construction, 180 to 500 m to the the south, 50 households, 200 south, 150 households, 600 persons. persons. Xiaoganhe residential area, 35 households, 140 persons, 300 to 500 m

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Sensitive Receptors – Noise Sensitive Receptors – Air Quality Sensitive Receptors Outputs Environmental Quality Standard for Ambient Air Quality Standards - Other Noise (GB3096-2008), Level I or II (GB3095-2012), Level II (GB3096-2008, Level II) to the east. Source: Domestic EIT, 2018.

Table 40: Sensitive receptors near supporting roads, and applicable standards. Sensitive Receptors – Noise Sensitive Receptors – Air Quality Sensitive # Road Environmental Quality Standard for Ambient Air Quality Standards Receptors - Noise (GB3096-2008), Level I or II (GB3095-2012), Level II Other Tongji Hospital, 70 m to hospital 1 #5 Road property boundary. (GB3096-2008, Level I) National Security Bureau, 5 m east. National Security Bureau, 5 m east. Integrated Service Center of Public Integrated Service Center of Public Security Security Bureau of Gui’an New Bureau of Gui’an New District, 5 m east. Northern District, 5 m east. Tongji Hospital, 500 m to hospital property 2 Extension of (GB3096-2008, Level II) boundary. Zhanqian Road Tongji Hospital, 500 m to hospital property boundary. (GB3096-2008, Level I) Civic Center, 5m. Civic Center, 5m. Financial Harbour, 5m. Financial Harbour, 5m. Changfeng Road 3 Gui’an Center, 5m. Gui’an Center, 5m. (Z7) (GB3096-2008, Level II) Museum of Architecture and Arts, 60 m east. Archives, 230 south. 4 H6 Road - - 5 Z3 Road - - 6 H8 Road - - 7 H11 Road - - 8 H12 Road - - 9 H13 Road - - 10 Z4 Road - - Financial Harbour, 5m. Financial Harbour, 5m. 11 Z8 Road (GB3096-2008, Level II) Museum of Architecture and Arts, 60 m east. Financial Harbour, 5m. Financial Harbour, 5m. 12 H4 Road (GB3096-2008, Level II) Museum of Architecture and Arts, 60 m east. Civic Center, 5m. Civic Center, 5m. 13 H1 Road (GB3096-2008, Level II) Archives, 230 m south. Source: Domestic EIT, 2018.

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Figure 37: Aerial images showing Tonji Hospital boundary in relation to #5 Road and Northern Extension of Zhanqian Road.

Source: PMO 2018, Google Earth 2019.

Table 41: Sensitive receptors near charging stations, and applicable standards. Sensitive Receptors – Noise Sensitive Receptors – Air Quality Outputs Environmental Quality Standard for Ambient Air Quality Standards Noise (GB3096-2008), Level II (GB3095-2012), Level II 1 Gui’an Rail Station Gui’an Rail Station, 0-200 m Gui’an Rail Station, 0-500 m 2 Financial Harbor Financial Harbor , 0-200 m Financial Harbor , 0-500 m 3 Commercial Complex 3 Commercial Complex 3, 0-200 m Commercial Complex 3, 0-200 m 4 Civil Center Civil Center, 0-200 m Civil Center, 0-200 m Longshan Industrial Park, 300 persons, Longshan Industrial Park, 300 persons, 5 Longshan Industrial Park 0-200 m 0-500 m Office area of Electronic Information Office area of Electronic Information Industry Incubation Park, 200 persons Industry Incubation Park, 200 persons Electronic Information Industry 6 Some residents in Yinhe street, 20 Some residents in Yinhe street, 20 Park households and 80 persons, 135-200 m households and 80 persons, 135-500 m to the west to the west Stirling Industrial Park, 500 persons, 0- Stirling Industrial Park, 500 persons, 0- 200 m to the SE 200 m to the SE 7 Stirling Industrial Park Residents in Liujiazhuang village, 40 households and 160 persons, 270-500 m N Gui’an Digital Economic Gui’an Digital Economic Industrial Park, Gui’an Digital Economic Industrial Park, 8 Industrial Park 0-200 m 0-500 m 9 Yungu (B Block) Yungu (B Block), 400 persons, 0-200 m Yungu (B Block), 400 persons, 0-200 m

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Sensitive Receptors – Noise Sensitive Receptors – Air Quality Outputs Environmental Quality Standard for Ambient Air Quality Standards Noise (GB3096-2008), Level II (GB3095-2012), Level II Ganhe Village residents, 80-200 m to Ganhe Village residents, 80-500 m to the west the west Gui’an New Area Free Trade Gui’an New Area Free Trade Zone, 200 Gui’an New Area Free Trade Zone, 200 10 Zone persons, 0-200 m persons, 0-500 m 11 Yueliang Lake Some residences, 75-200 m Some residences, 75-500 m Management office of Gui’an New 12 Liangjiang Road Area, 300 persons, 80-500 m to the SE Some residents of Heishitou village, Some residents of Heishitou village, 7 13 West Coast 120-200 m SW households and 28 persons, 120-500 m SW 14 Tianfu Road Some residences, 75-200 m Some residences, 75-500 m Some residents in Guoluo village, 3 Some residents of Guoluovillage, 10 South Park of the High-end 15 households and 12 persons, 100-200 m households and 40 persons, 100-500 m Industrial Park to the S to the S Some residents, 50 to 200 m Some residents of Jiguanshao village, 16 South Shuangxi Road 30 households and 120 persons, 230 to 500 m N Residents of Dongqingshu village, 20 households and 80 persons, 280-500 m to the SW 18 West Simeng Road Residents of Zhangchong village, 15 households and 60 persons, 200-500 m SE Management office of Gui’an New Area, Management office of Gui’an New 19 Fengming Road 300 persons, 130-200 m to the SW Area, 300 persons, 130-500 m to the SW Huchao middle school, 30 households, Some residents of Siyang road, 30 120 persons, 130 m-200 m W households and 120 persons, 105-500 21 Huantienhuchao Station Some residents of Siyang road, 105-200 m N m N Source: Domestic EIT, 2018.

Table 42: Other sensitive receptors. Receptor Protection Area Standard Environmental Quality Standards for Hongfeng Lake Watershed Surface Water (GB3838-2002), Class II Environmental Quality Standards for Songbaishan Reservoir Watershed Surface Water (GB3838-2002), Class II Maxian River River Surface water Chetian River River Dishui River River Environmental Quality Standards for Lanhua River River Surface Water (GB3838-2002), Class III Lengfan River River Machang River River Groundwater aquifer in Standard for Groundwater Quality Groundwater All groundwater the project area (GB/T14848-2017), Level III Ecological Soil, vegetation, and Do not destroy natural vegetation, or cause Within 500 m around sites environment animals soil loss Source: Domestic EIT, 2018.

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168. As Gui’an is undergoing massive new urban development, sensitive receptors may change overtime. In order to correctly capture sensitive receptors for the project, regular assessment, verification of identified sensitive receptors and identification of new sensitive receptors shall be carried out during pre-construction, construction, and operation phases of the project. Sensitive receptors are given special attention in the assessment of impacts (Section V) and the EMP (Appendix A), including the environmental monitoring program.

D. Socioeconomic Conditions

169. Area and Population Guizhou Province has an area of 176,167 km2 and a population of 35.8 million (2017).27 Guiyang City as a whole has an area of 8,034 km2 and a population of 4.70 million permanent residents in 2018, of which approximately 3.48 million lived in urban areas, giving an urbanization rate of 74%; 51.2% of the population is male and 48.8% is female. Demographically Guizhou is one of China's most diverse provinces. Minority groups such as the Miao/Hmong and Yao account for more than 37% of the population.

170. Gui’an New District, China’s eighth state-level new district, was established in January 2014 by the PRC’s State Council with a total area of 1,750 km2. The current population is 730,000 people (2016) 28, and according to the Gui’an New District Masterplan, the planned population growth is 1.3 million by 2020 and 2.3 million by the end of 2030. The area has been undergoing rapid urbanization since 2014.

171. The Gui’an Direct Administrative District (GDAD), the focus of the project, has an area of 470 km. It is a subdivision of the Gui’an New District, and is under the authority of the Gui’an New District Management Committee (GNDMC). It is comprised of more than 20 villages or towns located between and originally under the jurisdiction of Guiyang city (Huaxi District and Qingzhen City) and Anshun city (Pingba County and Xixiu District). It includes a core area, the Machang Science and Technology New City, the University Town, and Gaofeng Township District.

172. The GDAD has a population of 180,000 permanent residents (2017)29, of which 30.05% live in urban areas; 49.15% are female; 3.47% are classified as poor; and 36.72% are minorities, including Miao (about 53%), Buyi (about 40%), Gelao (about 2.6%), and Yi, Dong, Bai, Tujia, Hui, Manchu and Zhuang (collectively comprising 4.4%). There are also an estimated 150,000 faculty, students and others in the University Town, giving a total estimated GDAD population in 2017 of 330,000.30 The population is projected to double by 2020, and reach 1.4 million, including 1.1 million local residents and 0.3 million college students and tourists, by 2030.31

173. The two districts and four townships of the GDAD are described in Table 43.

27 Guizhou Provincial Bureau of Statistics, 2017. 28 GDAD Statistical Office, 2017. 29 GDAD Statistical Office, 2018. 30 GDAD Statistical Office, 2018; PMO; and PPTA consultants. 31 Gui’an New District Public Transport Plan (2018-2030).

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Table 43: Project districts and townships. Area District Township 2 Population Other (km )  2017 per capita net income approximately Gaofeng 105.26 38,625 12,000 CNY  Includes 28 villages, one community and 260 village groups Pingba  Minority population is 25,000, comprised Machang 198.5 53,124 mainly of Miao and Buyi  2017 per capita net income 7,890 CNY  Agriculture is the main income source of villagers  Includes 18 administrative villages, 66 natural villages and 99 village groups Dangwu 63.4 23,753  Population comprised of Han, Miao and Buyi. Huaxi  2017 per capita net income 13,200 CNY.  Includes 19 administrative villages, 51 natural Huchao 111.39 55,750 villages, one community and 71 village groups  2017 per capita net income 8,100 CNY Source: PPTA consultants. Population data is 2016 and totals 171,000.

174. Economy Guizhou is a relatively poor and economically underdeveloped province, but it is rich in natural, cultural and environmental resources. Its gross domestic product (GDP) was 1.35 trillion CNY in 2017, 63.6% of the PRC average, ranking it 25th in the country. However, its GDP growth rate has been in the top 3 of provinces in China for 7 consecutive years. Natural resource industries include timber and forestry, and it is one of China’s major producers of tobacco. Other important industries include electricity generation, a large portion of which is exported to and other provinces, and mining, especially coal, limestone, arsenic, gypsum, and oil shale.

175. The rural poverty ratio in Guizhou is 18.0%, is much higher than the national rate of 7.2%. The average disposable income per capita in Guizhou was CNY 15,121 in 2016, well below the coastal regions and the national average of CNY 23,821.

176. In 2017, Guiyang’s GDP was 353.80 billion CNY, a year-on-year increase of 11.3%. Of this, the output value ratio of primary, secondary, tertiary industries was 4.8/38.2/57.0. In 2017 Guiyang’s per capita GDP was CNY 74,493, higher than the provincial and national averages (Table 44) and a year-on-year increase of 9.2%. 177.

Table 44: Comparison of GDP (in CNY) in the Guiyang City to Guizhou Province and China. GDP Primary Secondary Per Tertiary Industry Growth Area (CNY Industry Industry Capita Rate Billion) Output % Output % Output % GDP PRC 82,712.2 6,546.8 7.92 33,462.3 40.46 42,703.2 51.63 6.9 59,660 Guizhou 1354.1 202.1 14.93 544.0 40.17 608.0 44.90 10.2 37,956 Guiyang City 353.8 14.7 4.15 137.5 38.86 201.5 56.95 11.3 74,493 Source: 2017 Economic and Social Development Statistical Bulletins (National, Guizhou, Guiyang); Guiyang Statistical Yearbook (2018).

178. Per capita disposable income of Guiyang urban residents and rural residents was higher in 2017 than the provincial average, but lower than the national average. As with the rest of China urban incomes were considerably higher than rural ones (Table 45).

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Table 45: Comparison of per capita disposable income in 2017. Per Capita Disposable Income (CNY)

Urban Rural PRC 36,396 13,432 Guizhou Province 29,080 8,869 Guiyang City 32,186 14,264 Gui’an New District 27,137 12,517 Source: Guiyang Statistical Yearbook (2018).

179. The Gui’an New District is a state-level economic zone established in January 2014 by the PRC’s State Council, with the development objective of becoming an economic driver of western PRC and Guizhou Province. There are three development objectives for the district: i) develop a high-level technology innovation hub to attract talent and business and encourage innovation and high-tech industrial development; ii) conserve the natural environment to ensure a healthy and green city; and; iii) foster eco-tourism. In 2017 the Gui’an New District had a gross industrial output value of 20.07 billion CNY, up 270% from the previous year; total retail sales of consumer goods of 9 billion CNY, up 757.1%; per capita disposable income of urban residents of 27,137 CNY, and per capita disposable income of rural residents of 12,517 CNY.

180. Education. Guiyang had 36 institutions of higher education in 2017, with 350,000 undergraduate and 16,800 postgraduate students. There are 217,000 students in high school, 147,000 students in middle school, and 370,000 students in primary school. There is a “University Town”, constructed to concentrate the higher education resources of Guiyang. To date 14 universities or colleges have established campuses in the University Town, with a total of about 90,000 students.

181. Road Network and Public Transit. There is an existing road network in the GDAD, (Figure 38), though it is undergoing extensive expansion, including the supporting roads that the project will construct. Existing trunk highways include expressway, national highway 320, provincial highway 102 and county road 001 that go through central and northern part of the district. The Dangwu-to-Machang expressway and Jinyang-to- Qingzhen urban trunk road have been recently constructed. The Guihuang Highway (national highway 320) has been upgraded into an urban expressway while the Qingzhen-to- Machang Expressway and other regional trunk roads are at the design stage.

182. The Longdongbao International Airport is 36 km from the center of the GDAD. The Gui-Kun Railway and Hu-Lin Freight Designated Railway Line goes through the district; the Guiyang railway station is 50 km from the district, and the Guiyang south station is 54 km.

183. The GDAD public transit system is at an early stage in development. Currently there are 9 public transit lines, the first of which was put into operation in July 2014 (Table 46 and Figure 39). These public lines typically extend from the existing trunk mains such as Gui’an Avenue, Baima Avenue, Jinma Avenue, Qianzhong Road, etc. The existing bus fleet is comprised of 20 Liquefied Natural Gas (LNG) 12 m buses, 35 electric 12 m buses and 48 electric 8 m buses. The current bus operations suffer from low efficiency and low coverage.

184. Currently there are no bus stations in the GDAD. Overnight parking of buses is through on-street parking, and at some temporary parking lots at the University Town South Ring Highway-Huayan Road Interchange, in front of the City College Square, and at the Huaxi Luoping Hub.

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Figure 38: Road network, GDAD.

Source: Google Maps, 2018.

Table 46: Existing public transport lines in the GDAD. Single Trip Line From To Distance (km) 701 Bus Administration Committee Guiyang Museum 40.1 702 Bus Administration Pingba farmland 14.9 Qingzhen vocational education 703 Bus Administration Committee 20.5 town 704 Bus Yunman Lake Luoping hub in Huaxi 28 705 Bus Administration Committee Comprehensive bonded zone 18.5 Gui’an Ring Road Administration Committee Administration Committee 16 No. 1 Bus Gui’an No. 4 Bus Comprehensive bonded zone University Town 26 Gui’an No. 5 Bus Administration Committee University Town 34 BRT 39 Total 237 Source: PMO, 2018.

185. Water Supply. The GDAD is currently served by the Xiaozhai water supply plant, located on the East site of S102 road. It became operational in April 2016, and has a design capacity is 200,000 m3/d. The plant is designed to supply a 160 km2 area of GADD, with a supplied population of 600,000 persons.

186. Wastewater Treatment. There are five urban wastewater treatment plants (WWTPs)

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under planning or in operation in the GDAD: the Gaofeng WWTP (3,200 m3/d in phase I and 6,400 m3/d in phase II); Machang WWTP (20,000 m3/d in phase I and 25,000 m3/d in phase II); Huchao WWTP (40,000 m3/d in phase I and 120,000 m3/d in phase II); Nabu WWTP and Longshan WWTP (30,000 m3/d in phase I and 60,000 m3/d in phase II), and Longshan WWTP (20,000 m3/d in phase I and 35,000 m3/d in phase II). The total treatment capacity of all the five WWTPs is to 246,400 m3/d which can serve more than 695,000 people. The effluent of all the five WWTPs is required to be in compliance with Class IA standard of GB18918-2002.

187. Solid Waste Management. There are sanitary 3 landfills in the new district area: Qingzhen Municipal Solid Waste Landfill (MSWL) (in Qingzhen City, a county-level city under the jurisdiction of Guiyang); and Pingba MSWL and Xixiu MSWL, both in Anshun City. Municipal solid waste from Gui'an New District Area is transported to these landfills for disposal.32 The landfills have been designed, and are operated, according to relevant PRC standards for sanitary landfills.33

188. Hazardous Waste Management. There are several MEE permitted hazardous waste management facilities in Guizhou province, including the City Hongfa Mercury-contained Product Disposal Co. Ltd, and Tongren Yinhu Chemical Industry Co. Ltd.34 According to Gui'an New District Masterplan EIA, hazardous waste from the new district will be sent to Guizhou Provincial Hazardous Waste Treatment Center for treatment and disposal.

32 Masterplan of Gui’an New District (2013-2030) Environmental Impact Assessment. 33 The standards and regulations include: a. For landfill construction: i. Pollution control standard of domestic solid waste landfill (GB16889-2008) ii. Technical standard of domestic solid waste landfill (GB50869-2013) iii. Technical guidance of domestic solid waste handling (No. 61, 2010) iv. Engineering project construction standard of domestic solid waste landfill (124-2009) v. Leakage prevention system engineering technical standard of domestic solid waste landfill (CJJ113- 2007) vi. Geotechnical engineering standard of domestic solid waste landfill (CJJ176-2012) vii. Leachate treatment engineering standard of domestic solid waste landfill (HJ 564-2010) b. For landfill operation: i. Operation and Maintenance technical standard of domestic solid waste landfill (CJJ93-2011) ii. Environmental monitoring technical standard of domestic solid waste landfill (GB/T18772-2008) iii. Site closure technical standard of domestic solid waste landfill (CJJ112-2007) 34 http://www.basel.int/Countries/Countryfactsheets.

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Figure 39: Existing bus routes in the GDAD.

Source: PMO, 2018.

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V. ANTICIPATED ENVIRONMENTAL IMPACTS AND MITIGATION MEASURES

189. This chapter presents an assessment of potential impacts in the project zone of influence, and associated mitigation measures. Pre-construction, construction and operation phases are each considered separately. Mitigation measures are presented in detail in the EMP (Appendix A).

A. Project Zone of Influence

190. The project zone of influence is defined as:

i) 200 m zones around the boundary of the bus stations, with respect to noise impacts, and 500 m zones with respect to air pollution impacts; ii) 200 m zones perpendicular to either side of the roads with respect to noise impacts, and 500 m zones with respect to air pollution impacts; and iii) 50 m zones around charging stations. iv) 50 m zone around the ICVSDZ testing area.

191. The project zone of influence is presented in Figure 40.

Figure 40: Project zone of influence.

Source: FSR (2018), EIT (2018), Google Earth (2018), and PPTA consultants. Note: red circles represent 500 m zone around bus stations, smaller red dots represent 50 m around charging stations, pink is the 50 m zone around the ICVSDZ testing area (Gui’an New Area High-End Equipment Industry Park and test roads), and orange is 500 m zone to either side of project supporting roads.

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B. Anticipated Impacts Associated with Project Location, Detailed Design and Pre-Construction Phase

192. Siting and Land Acquisition. Project construction of bus stations, charging stations, and some other works will require the acquisition of 698.57 mu (46.57 ha) of land, of which 481.96 mu (32.13 ha) is state-owned land, and 216.61 mu (14.44 ha) is collectively owned (including 209.41 mu of cultivated land and 7.2 mu of woodland). The land acquisition will not impact any residential units and there will be no house demolition. A total of 161 households with 697 persons will be affected marginally by land acquisition, since agriculture accounts for less than 2% of household income. The average land loss rate is about 6% of the total land and non-significant in nature. The following mitigation measures will be implemented:

i) The Project has been classified as resettlement category B and a Resettlement Plan (RP)35 with time-bound actions has been prepared under a separate process, supported by a due diligence review by ADB social safeguard specialists.

193. Measures to be Implemented during Pre-construction. A number of environmental management measures will be implemented in the pre-construction phase to ensure the project’s environment management readiness (see EMP). These include:

i) Institutional Strengthening

a. Recruitment, including (a) appointment of a qualified Environment, Health and Safety Officer (PMO EHSO) within the PMO by the IA; (b) contracting of a Loan Implementation Environmental Consultant (LIEC) by the IA; (c) contracting of a qualified 3rd party Environmental Monitoring Company by the IA to conduct environmental quality monitoring.

b. Prior to the start of construction, the construction phase institutional strengthening and training program will be delivered by the LIEC (Table 6, Appendix A). The training will focus on ADB’s and PRC’s relevant environmental, health and safety laws, regulations and policies; implementation of the EMP, environmental monitoring, chance find procedures for PCRs, and the GRM. Training will be provided to the IA, relevant PMO staff, and contractors.

c. ICVSDZ institutional strengthening is discussed in Appendix K, and will include (a) appointment of a qualified ICV Safety Officer within the PMO; (b) engagement by the PMO of an Independent ICV Expert Team including national and international ICV safety, technical and innovation specialists; and (c) domestic and international training for key stakeholders to develop capacity for ICV system demonstration zone implementation.

ii) Re-Identification and Updating of Sensitive Receptors in the IEE: Any changes in sensitive receptors to the project shall be checked, and the sensitive receptors tables will be updated in the IEE or as an addendum to the IEE to reflect any significant changes.

35 Resettlement Plan and Due Diligence Report for Guizhou Gui’an New District New Urbanization Smart Transport System Development Project, 2018.

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iii) Grievance Redress Mechanism. In accordance with the GRM (see Chapter IX and Appendix A), the PMO EHSO will assume overall responsibility for the GRM. GRM training will be provided for PMO members and GRM access points. The PMO will issue public notices to inform the public within the project area of the GRM, and contact information (GRM website address, PMO address and telephone number, PMO contact point email address) for the PMO and local entry points (e.g. contractors) will be disseminated at all major access points. The PMO EHSO will develop and maintain a Complaints Register to document all complaints.

iv) Updating the EMP: Mitigation measures defined in this EMP and the EMoP will be updated based on final technical design, including design of, where required, bus stations access roads. This will be undertaken by the EIA Institute under the supervision of the PMO EHSO and the LIEC. The updated EMP will be submitted to GEPB and ADB for approval, and disclosed on the ADB website.

v) Tender Documents: All EMP obligations will be included in tender documents and will explicitly reference the EMP and EMoP.

C. Anticipated Construction Phase Impacts and Mitigation Measures

194. Impact Screening. Potential impacts during bus station, charger station and road construction could include air pollution (particularly dust), noise, water pollution, solid waste and poor occupational health and safety practices.

195. Potential air quality impacts could occur due to fugitive dust generated at construction sites from stockpiles of uncovered earth materials, vehicles hauling materials, and vehicle emissions. The use of powered mechanical equipment (PME) during construction activities will generate noise. Construction activities will generate process wastewater and construction workers will produce wastewater and solid waste, although as this is an urban project, there will be no requirement for worker camps or on-site canteens. Construction works will produce construction and demolition (C&D) wastes including excavated earth materials. Workers will face occupational health and safety issues working on construction sites. Potential impacts are assessed and addressed below. Identified impacts are short-term and localized, and can be readily addressed through the application of good construction site environmental management and health and safety practices in accordance with PRC requirements and the EHS Guidelines.

196. The ICV testing does not involve physical works or construction, but ICV testing poses certain safety risks related to communication network disturbances and outages; mechanical failures; poor test site conditions; poor operation and maintenance practices; and inappropriate behavior actions of test drivers, maintenance staff and other workers. These risks are assessed in Appendix K, and testing and safety plans are presented to mitigate the risks.

1. Impact on Physical Resources

197. Soil Erosion and Spoil. Construction activities such as excavation and filling activities may lead to surface erosion. The most vulnerable soil erosion areas include excavation sites, spoil sites, temporary construction sites, and other areas where surface soil is disturbed. Soil erosion can also be more serious on slopes or near water bodies. Construction activities may also generate surplus spoil. According to the EIT, project excavation and fill will be:

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- 612,400 m3 and 56,400 m3 respectively for the bus station construction, with 249,800 m3 of fill generated; - 56,400 m3 and 33,200 m3 respectively for the bus station construction, with 23,100 m3 of fill generated; and - 703,800 m3 and 825,300 m3 respectively for the road works, with 121,500 m3 of fill generated.

198. To minimize soil erosion and spoil production, good construction soil and spoil management construction practices will be adopted, including managing site storm water and runoff, appropriate storing of fill, stockpile management, balancing fill and cut to the extent possible, and ensuring appropriate disposal of spoil (see EMP). There four legal spoil disposal sites in the GDAD designated by Gui'an New Area Comprehensive Law Enforcement Bureau, which will be used for final disposal of spoil that cannot be otherwise reused (Figure 41).

Figure 41: Map of spoil disposal sites in the GDAD.

Source: domestic EIT, 2018.

199. Air Quality. Fugitive dust generated from vehicle movement and hauling loads (especially if loads are uncovered), demolition and earth works, and equipment exhaust fumes are expected to be the main air pollutants during the construction stage. Fugitive emissions are regulated under PRC’s Air Pollutant Integrated Emission Standard (GB16297- 1996), which sets 120 mg/m3 as the maximum allowable emission concentration and ≤ 1.0 mg/m3 as the concentration limit at the boundary of construction sites (with no specification on particle diameter).

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200. According to the EIT, dust from vehicle movement accounts for over 60% of fugitive dust at construction sites. In the dry season where the problem is most serious, vehicle related fugitive dust can be calculated as follows:

 85.0 75.0 Q .0 123V 5W 8.6  P 5.0 

Where: Q - flying dust generated by vehicle driving, kg/km per vehicle; V - vehicle speed, km/h; W - vehicle carrying capacity, t; P - amount of dust on the road surface, kg/m2.

201. Table 47 presents the relationship between fugitive dust generation and vehicle speed and road cleanliness, and shows that reduced vehicle speeds and reduced on road dust and dirt both reduce fugitive emissions. Table 48 presents the results of water spraying as a mitigation technique.

Table 47: Vehicle related fugitive dust generation and relationship to vehicle speed and road cleanliness. Unit: kg/vehicle km. Amount of dust on the road surface Vehicle speed 0.1 0.2 0.3 0.4 0.5 1.0 (kg/m2) (kg/m2) (kg/m2) (kg/m2) (kg/m2) (kg/m2) 5 (km/h) 0.0283 0.0476 0.0646 0.0801 0.0947 0.1593 10 (km/h) 0.0566 0.0953 0.1291 0.1602 0.1894 0.3186 15 (km/h) 0.0850 0.1429 0.1937 0.2403 0.2841 0.4778 20 (km/h) 0.1133 0.1905 0.2583 0.3204 0.3788 0.6371 Source: domestic EIT, 2018.

Table 48: Water spraying and dust suppression at construction site test results. Distance (m) 5 20 50 100 No Water Hourly average 10.14 2.89 1.15 0.86 concentration of Spraying TSP With Water 3 2.01 1.40 0.67 0.60 (mg/m ) Spraying Source: domestic EIT, 2018.

202. Wind-borne fugitive dust can also be generated from construction activities, uncovered earth material stockpiles on construction sites and spoil storage and disposal areas. Equipment, especially if unmaintained, can generate exhaust contains SO2, CO, NO2 and other pollutants.

203. On-site asphalt batching can also generate toxic fumes. However, only pre-mixed commercial asphalt will be procured negating the need for asphalt mixing on construction sites, and asphalt fumes will only be generated during road paving. Fumes will contains small quantities of toxic and hazardous chemicals such as volatile organic compounds (VOCs) and poly-aromatic hydrocarbons (PAHs), however in the road construction area there are no inhabitants or sensitive receptors. Asphalt fumes generated during road paving with commercial asphalt will be considerably less than fumes that would have been generated if doing on site batching, and once the paved asphalt is cooled to <82o C asphalt fumes will be reduced substantially and then be totally eliminated when the asphalt is

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solidified. Impacts will thus be short-term in duration, localized in scale, low in magnitude, and in line with typical road works that occur on a daily basis in cities.

204. The EIT predicts unmitigated compliance with the Ambient Air Quality Standard (GB3095-1996) at 150 m downwind of TSP generating activities or locations. To minimize fugitive dust production good practice air quality construction measures will be implemented as described in the EMP, including controlling vehicle speeds, covering loads, and watering surfaces. With mitigation measures the amount of dust can be reduced by 70% or more and the impact area be reduced to within 100 m downwind of earth work activities. Particular attention will be paid to dust suppression near sensitive receptors identified in the IEE. Overall impacts will be short-term and localized, and in line with typical construction works that occur on a daily basis in cities throughout China and the world.

205. Noise – Roads Component. Noise will be emitted by PME used during road construction, including excavators, bull dozers, rollers and transport vehicles (Table 49).

Table 49: Road works construction machinery noise intensity at full load/power, no noise shields. No. Equipment Distance from Noise level Remarks source (m) dB (A) 1 Wheel loader 5 90 Hydraulic type 2 Grader 5 90 3 Vibratory road roller 5 86 Wheel type 4 Bulldozer 5 86 5 Hydraulic wheel 5 84 excavator 6 Paver 5 87 7 Air compressor 5 78 The greater the carrying Transport (Trucks, 8 7.5 89 capacity of the truck, the dump trucks) higher the noise level 9 Mobile crane 7.5 89 Source: Table C.3.1 of Appendix C in the Specifications for Environmental Impact Assessment of Roads (JTGB03-2006).

206. The EIT used the sound impact model in the Technical Guidelines for Noise Impact Assessment HJ2.3-2009:  r      LA r LA r0  20lg   r0 

Where: LA r - noise level value at r away from the noise source, dB(A);

LA r0  - noise level value at the reference position r0, dB(A); r - distance from the predicted point to the noise source, m; r0 - distance from the reference point to the noise source, 1m.

207. Table 50 presents the predicted noise levels of the machinery running at full load, and Table 51 shows the distance from noise source at which compliance with the relevant standard is met. It can be seen that construction machinery, without shields, is in compliance with Emission Standard of Environment Noise for Boundary of Construction Site (GB12523- 2011) at 50.0 m or less in the daytime and at a maximum of 280 m at nighttime.

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Table 50: Road construction machinery noise intensity at full load/power at different distances from source, no noise shields. Machinery type and Distance from noise source No. noise levels at 5 10 20 40 60 80 100 150 200 distance dB (A) m m m m m m m m m 1 Wheel loader 90 80.4 78.0 71.9 68.4 65.9 64.0 60.5 58.0 2 Grader 90 80.4 78.0 71.9 68.4 65.9 64.0 60.5 58.0 3 Vibratory road roller 86 80.0 74.0 67.9 64.4 61.9 60.0 56.5 54.0 4 Bulldozer 86 80.0 74.0 67.9 64.4 61.9 60.0 56.5 54.0 5 Hydraulic wheel 84 78.0 72.0 65.9 62.4 59.9 58.0 54.5 52.0 excavator 6 Paver 87 81.0 75.0 68.9 65.4 62.9 61.0 57.5 55.0 7 Air compressor 78 72.0 66.0 59.9 56.4 53.9 52.0 48.5 46.0 Note: The source intensity at 5m in the table is extracted from Table C.3.1 of Appendix C in the Specifications for Environmental Impact Assessment of Roads (JTGB03-2006).

Table 51: Road construction machinery noise levels compliance with relevant standard, no noise shields. Distance in conformity with the Standard value No. Machinery type Standard (JTGB03-2006) Daytime Nighttime Daytime Nighttime 1 Wheel loader 70 55 50 281.2 2 Grader 70 55 50 281.2 3 Vibratory road roller 70 55 31.5 177.4 4 Bulldozer 70 55 31.5 177.4 5 Hydraulic wheel excavator 70 55 25.1 140.9 6 Paver 70 55 35.4 199.1 7 Air compressor 70 55 12.6 70.6 Source: domestic EIT, 2018.

208. To mitigate potential road construction noise good construction site noise management practices in accordance with PRC requirements and EHS Guidelines will be adopted, and monitoring will be undertaken at sensitive sites and compared against WHO noise guidelines.

209. Noise – Bus Stations. Bus station construction noise includes machinery noise, construction works noise and transport vehicle noise. Machinery noise is mainly caused by machinery such as excavator, bull dozers, and concrete vibrators; construction work noise is associated with dismantling of existing works, building erection, etc.; and transport vehicle noise refers to associated traffic noise. Of these sources machinery noise has the greatest impact on the acoustic environment, and thus was the focus of the assessment in the EIT.

210. To assess noise levels at sensitive sites generated by multiple noise sources, the following model was used:  n  1.0 LI Leq T   10lg10  i10 

Where: Leq T  - total noise level at the predicted point, dB(A); n - number of outdoor noise source(s).

211. Table 52 presents predicted construction noise levels at various distances from the source.

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Table 52: Predicted bus station construction machinery noise intensity at full load/power at different distances from source, no noise shields. Noise Noise level at distance from source Main noise Characteristics of noise Works level LPAdB(A) source source dB(A) 10m 30m 60m 120m 240m Bulldozer 87.5 59.5 59.0 44.0 38.0 31.9 Excavator 86.5 58.5 49.0 43.0 37.0 30.9 The noise spreads in random Earthwork Road roller 82.5 54.5 45.0 39.0 33.0 26.9 directions Transport 85 57.0 47.5 41.5 35.5 29.4 vehicle Percussion 83.5 55.5 46.0 40.0 34.0 27.9 Foundation drill The noise spreads in random construction Air directions 98.5 70.5 61.0 55.0 49.0 43.0 compressor Structure Vibrator 96 68.0 59.5 52.6 46.5 40.4

construction Electric saw 106 78.0 68.5 62.5 56.5 50.4 Grinding 102 74.0 64.5 58.5 52.5 46.4 The exterior wall of buildings machine Finishing can attenuate the influence of Cutting 100 72.0 62.5 56.5 50.5 44.4 the noise. machine Source: domestic EIT, 2018.

212. Table 53 presents predicted construction noise levels at the sensitive sites (residential areas, schools, etc.) identified in Table 39, and compliance with the relevant standard (Level I or II) of Environmental Quality Standard for Noise (GB3096-2008). The table assumes the same level of construction noise for both day and night times. The results show that daytime earthworks foundation works noise levels are predicted to be in compliance with the relevant standards. There are some predicted exceedances for structure construction. However, the majority of exceedances are related to works at night time or finishing, and are due to the proximity of the sensitive sites to the construction sites. For finishing it should be noted that predicted exceedances do not take into account the very significant noise attenuation that is expected as the building will be at lock-up stage with walls and roofs.

Table 53: Predicted bus station construction machinery noise intensity at sensitive sites and compliance with relevant standard (assumes 2.5 m construction boundary wall and noise barriers). Predicted noise levels by construction stages dB(A) and compliance with relevant standard Sensitive Sites Earthworks Foundation Structures Finishing Day Night Day Night Day Night Day Night Level II, Environmental Quality Standard for Noise (GB3096-2008): Applicable Standard 60 dB at daytime and 50 dB at nighttime) Hub Stations Gaofeng town residential area, 50.12 59.12 62.12 69.12 Gaofeng Passenger Hub Compliance with the Standard Yes No Yes No No No No No Yangliushao residential area, Machang Public 45.44 54.43 57.44 64.44 Transportation Hub Compliance with the Standard Yes Yes Yes No Yes No No No Residential area, Biguiyuan 41.92 50.92 53.92 60.92 Hub

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Predicted noise levels by construction stages dB(A) and compliance with relevant standard Sensitive Sites Earthworks Foundation Structures Finishing Day Night Day Night Day Night Day Night Compliance with the Standard Yes Yes Yes No Yes No No No Huofodun residential area, 44.09 53.09 56.09 63.09 South University Town Hub Compliance with the Standard Yes Yes Yes No Yes No No No Jiahexiazha residential area and Tourist Center, Yunman 46.19 55.19 58.19 65.19 Lake Hub Compliance with the Standard Yes Yes Yes No Yes No No No Ganhe residential area, North Fukang Road-Xuanshui Road 41.91 50.92 53.92 60.92 Hub Compliance with the Standard Yes Yes Yes No Yes No No No Terminal Stations Residential area of Huchao 48.96 57.96 60.96 67.96 Village, Xinghu Community TS Compliance with the Standard Yes Yes Yes No No No No No Xingyue Community, North of 44.09 53.09 56.09 63.09 Xingyue Community TS Compliance with the Standard Yes Yes Yes No Yes No No No Gaofeng residential area, East 44.09 53.09 56.09 63.09 of Gaofeng High School TS Compliance with the Standard Yes Yes Yes No Yes No No No Residential areas of Machang 59.41 68.41 71.41 78.41 Town, Machang Township TS Compliance with the Standard Yes Yes No No No No No No Guoluo Village residential area, High Technology 41 50 53 60 Industrial Park Compliance with the Standard Yes Yes Yes Yes Yes Yes Yes Yes Ganhe settlement, Comprehensive Bonded Zone 44.09 53.09 56.09 63.09 TS Compliance with the Standard Yes Yes Yes Yes Yes Yes Yes Yes Yangliushao residential area, 47.02 56.02 59.02 66.02 South of Xingan Avenue TS Compliance with the Standard Yes No Yes No Yes No No No Residential area, Wenggang Village, 70 m from terminal 44.09 53.09 56.09 63.09 station Compliance with the Standard Yes Yes Yes No Yes No No No Xiaojing and Dapo residential 46.19 55.19 58.19 65.19 areas, Minbo Park Compliance with the Standard Yes Yes Yes No Yes No Yes No Bus Depots Malu Hamlet residential area, 37.77 46.77 49.77 56.77 Central Area Bus Depot Compliance with the Standard Yes Yes Yes Yes Yes Yes Yes Yes Kulijing residential area, 36.39 45.39 48.39 55.39 University Town Bus Depot Compliance with the Standard Yes Yes Yes Yes Yes Yes Yes Yes Commercial and residential building under construction, 35.89 44.89 47.89 54.89 East of Machang Bus Depot Compliance with the Standard Yes Yes Yes Yes Yes Yes Yes No

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Predicted noise levels by construction stages dB(A) and compliance with relevant standard Sensitive Sites Earthworks Foundation Structures Finishing Day Night Day Night Day Night Day Night Level I, Environmental Quality Standard for Noise (GB3096-2008): Applicable Standard 55 dB at daytime and 45 dB at nighttime) Sensitive Sites Huchao Primary School, 39.41 48.41 51.41 58.41 Xinghu Community TS Compliance with the Standard Yes Yes Yes No Yes No No No Gaofeng Middle School, East 35.89 44.89 47.89 54.89 Gaofeng Middle School TS Compliance with the Standard Yes Yes Yes Yes Yes No Yes No Machang Middle School, 41 50 53 60 Machang Township TS Compliance with the Standard Yes Yes Yes No Yes No No No Guiyang College of Traditional Chinese Medicine, Dong Qing 43.49 52.49 55.49 62.49 Lu - Si Ya Road TS Compliance with the Standard Yes Yes Yes No No No No No Guizhou Light Industry Technical College, Dong Qing 40.17 49.17 52.17 59.17 Lu - Si Ya Road TS Compliance with the Standard Yes Yes Yes No Yes No No No Source: domestic EIT, 2018.

213. To mitigate bus station construction noise to acceptable levels, good practice construction noise management measures in accordance with PRC requirements and the EHS Guidelines will be applied, including selecting low noise equipment, ensuring equipment has appropriate mufflers, scheduling high noise activities during daytime and restricting construction at nighttime, and using temporary noise barriers at sensitive areas identified in Table 41. Construction phase noise monitoring will be undertaken at sensitive sites and compared to WHO guidelines, and mitigation measures will be adjusted if necessary based on the monitoring results.

214. Noise – Charging Stations. Ten of the stations will be established in existing parking lots, while the remainder will be established on existing state-owned land (8 stations) or acquired cultivated land (3 stations). Installation of charging station in existing facilities, such as underground parking lots, will generate sound levels similar to typical facility renovations, and can be mitigated through good construction practices.

215. Construction of 11 new charging stations will generate noise from machinery operation as previously indicated in Table 52. Construction noise at adjacent receptors was modeled in the EIA using used the sound impact model in the Technical Guidelines for Noise Impact Assessment HJ2.3-2009, described above. The modelling assumed basic mitigations such as 2.5 m boundary walls at the construction site, and noise reduction barriers at the sensitive receptors. The results, presented in Table 54, assume the same level of construction noise for both day and night times. The results show that daytime construction works noise levels are predicted to be in compliance with the relevant standards. There are however some predicted exceedances for nighttime foundation work. As with bus stations, to mitigate construction noise to acceptable levels, good practice construction noise management measures will be applied. In addition, construction phase noise monitoring will be undertaken at sensitive sites and compared to WHO guidelines, and mitigation measures will be adjusted if necessary based on the monitoring results.

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216. Water Quality. Inappropriate disposal of construction wastewater (from construction site runoff, drainage of excavation and drilling, pouring and curing concrete, washing construction equipment and vehicles, and oil-containing wastewater from machinery repairs) could potentially pollute nearby water bodies and clog local drains. Workers will also generate domestic wastewater, and it is estimated that there will be a peak of 500 workers during construction.

Table 54: Predicted charging station construction machinery noise intensity at sensitive sites and compliance with relevant standard (assumes 2.5 m construction boundary wall and noise barriers). Predicted noise levels by construction stages dB(A) and compliance with relevant standard Sensitive Sites Earthworks Foundation Structures Day Night Day Night Day Night Level II, Environmental Quality Standard for Noise (GB3096-2008): Applicable Standard 60 dB at daytime and 50 dB at nighttime) Management office of Gui’an new area, 130 southwest of 38.72 47.72 50.72 Fengming road. Result Yes Yes Yes No Yes Yes Huchao middle school, 130m 38.72 47.72 50.72 west of Huantie-Huchao station Result Yes Yes Yes No Yes Yes Some residents in Heishitou village, 120m south of West 39.42 48.42 51.42 Coast Result Yes Yes Yes Yes Yes Yes Some residents of Guoluo village, 100m south of High-end 41 50 53 equipment industrial park Result Yes Yes Yes Yes Yes Yes Source: domestic EIT, 2018.

217. It should be noted that there are no sensitive surface water resources near the project sites, and no sites are located in Class I drinking source groundwater protection zones. Nonetheless, to prevent pollution of water resources, good practice wastewater management practices will be implemented, including housing of workers in local accommodation in accordance with IFC/EBRD worker accommodation guidance (there will be no worker camps onsite) such that sewage produced from living quarters is collected in the municipal sewage system and will be treated in municipal wastewater treatment plants. Temporary toilets will be provided on-site and effluent will be regularly emptied and disposed off-site into the sewage system. Construction wastewater from each site will be directed to temporary detention and settling ponds or tanks, and then treated and recycled for use in dust control. All necessary measures will be undertaken to prevent construction materials and waste from entering drains and water bodies, and maintenance of construction equipment and vehicles will not be allowed on sites so as to reduce wastewater generation.

218. Solid Waste. Solid waste generated during construction will include construction and demolition (C&D) waste dominated by excavated spoil and pavement, and domestic refuse generated by construction workers (0.5 kg/worker).36

36 Note – earthworks and spoil are discussed above, and are not included in this section.

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219. Relatively little demolition is required for the bus station sites, but C&D will include some building rubble from several bus and charging station sites which have been used for building material disposal, and which will need to be rehabilitated. C&D in the EIT from the bus station construction is estimated at 2,600 t, and for the road component is estimated at 806 t. Refuse generated by construction workers is estimated at 91.25 t/year. Inappropriate waste storage and disposal could affect soil, groundwater, and surface water resources, and hence, public health and sanitation.

220. To prevent environmental degradation good solid waste management practices will be adopted in accordance with PRC requirements and EHS Guidelines, including reusing and recycling C&D wastes to the extent possible, providing construction and domestic waste containers at all construction sites, and ensuring all wastes that cannot be reused or recycled are disposal at a licensed MSWL. Building rubble will be tested and either reused as fill if appropriate or treated as hazardous if testing so indicates. Sites will be excavated and resurfaced with clean fill in accordance with relevant PRC regulations and EHS Guidelines.

221. Hazardous Materials. Inappropriate transportation, storage, use and spills of petroleum products and hazardous materials can cause soil, surface and groundwater contamination.

222. These potential impacts will be effectively mitigated through good practice hazardous materials management in accordance with relevant PRC regulations and EHS Guidelines. This will include appropriate hazardous materials transport, storage and disposal, and the development of spill response procedures.

2. Impact on Ecological Resources

223. Flora and Fauna, Protected Areas. All project sites are developed and modified industrial, commercial and residential and urban environments. Original vegetation cover has been previously removed, and existing site vegetation is either farmland (some of which is temporary by non-landowners), barren land, grasses and shrubs, or low value roadside landscaping. Some sites such as the University Town Bus Depot are covered with building debris. Based on the EIT and site surveys, there are no known rare or endangered flora or fauna, species with international, national or provincial protection status, areas of natural or critical habitat, parks, nature reserves, or areas with special national, regional or local ecological significance within or adjacent to any of the sites. However, hub station 1-2 (Machang Public Transportation) is located near to a hill which retains a significant amount of forest cover.

224. Bridge construction is not expected to have any negative impacts on aquatic ecology as the water body is artificial and will not be filled until after construction is complete.

225. Although the project is not expected to have a negative impact on flora and fauna, measures will be implemented to protect any remaining forested areas, and green landscaping will be implemented at the bus stations and along the roadways (see EMP).The planting of native trees will improve urban quality, provide shade and screening and is in line with the vision for Gui’an New District as a green urban development.

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3. Impact on Socioeconomic Resources

226. Occupational Health and Safety. Construction may cause physical hazards to workers from noise and vibration, dust, handling heavy materials and equipment, falling objects, work on slippery surfaces, electrocution, fire hazards, chemical hazards such as toxic fumes and vapors, and others risks.

227. To address these risks the Contractor’s Environment, Health and Safety Officer will develop and implement an Occupational Health and Safety Plan (OHSP), maintain records concerning health, safety and welfare and regularly report on accidents, incidents and near misses. The OHSP will provide adequate precautions to protect the health and safety of their workers, including but not necessarily limited to construction site sanitation, including waste removal and provision of potable water and sanitation facilities; occupational safety, including provision of appropriate personal protective equipment (PPE) such as safety hats, shoes, goggles, ear plugs and respiratory masks; electrical safety; traffic safety; emergency response, including procedures for medical, fire and other emergencies; and training. The OHSP will be reviewed and approved by the LIEC and PMO.

228. Community Health and Safety. Traffic congestion may worsen as construction traffic in the urban area increases during rush hours, causing temporary inconvenience to traffic, residents, commercial operations, and institutions and the risk of accidents. The project may also contribute to road accidents through the use of heavy machinery on existing roads, temporarily blocking pavements for pedestrians etc.

229. Construction sites for bus stations are in some cases located close to residential areas, presenting a potential threat to public health and safety. Assessments of dust and construction noise impacts indicate that with the implementation of mitigation measures described in this report, such impacts will not adversely affect nearby sensitive receptors and the public health of occupants at these sensitive receptors. There are no existing residential or commercial areas in the vicinity of the project roads, and thus there construction does not pose a risk to community health and safety.

230. Construction may require relocation of municipal utilities such as power, water, communication cables. Temporary suspension of services (planned or accidental) can affect the economy, industries, businesses and residents’ daily life.

231. Installation of roadside detection and monitoring equipment for the ITS and ICVSDZ components may pose a risk to existing traffic and to workers.

232. To mitigate potential impacts on community health and safety contractors will implement good practice community health and safety measures, including traffic safety measures, informing residents about construction activities and potential disruptions, and prohibiting the public from entering construction sites.

233. Physical Cultural Resources. Based on both sites surveys and a review of relevant literature, the only known site with PCRs is East of Gaofeng High School terminal station, which has a number of family graves near it. This area, which is outside of the station boundary, will be demarcated as a no-go zone. There are no other sites with known PCRs within the work site footprints. However, construction activities have the potential to disturb as yet unknown subsurface PCRs.

234. To address this issue, a Chance Find Procedure, developed in in accordance with PRC’s Cultural Heritage Protection Law, will be established and training will be provided by the LIEC on what constitutes a PCR and the Chance Find Procedure. The procedure will be

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activated if any chance finds of PCRs are encountered at bus depots or other sites (see EMP).

D. Anticipated Operation Phase Impacts and Mitigation Measures

235. Impact Screening. Potential negative operation phase impacts include runoff from roads and stations which may pollute surface waters; wastewater produced at the stations; emissions from vehicles on the project roads; noise from stations, buses and cars; hazardous materials from bus service areas; end-of-life buses and batteries that require replacement; safety risks on the project roads; and potential safety risks from ICV testing. These impacts can be effectively mitigated through good design, including, for example, road-side bio-retention facilities to treat storm water runoff, and noise control measures incorporated into bus station design; good waste and health and safety management practices including effective recycling of busses and bus batteries; and good ICV testing and safety plans and practices. All facility designs will be in accordance with PRC requirements and health and safety requirements of the EHS Guidelines.

1. Impact on Physical Resources

236. Runoff and Storm Water. Rain events will generate runoff from the project roads and bus stations. Depending on the amount and type of traffic, rainfall intensity, and season, runoff may be contaminated with suspended sediments, petroleum products and high organic loads. Chang'an University studied pavement runoff on the Xi'an - Sanyuan Highway under a one hour rainfall event generating 81.6 mm of precipitation; water samples were collected and analyzed at different times during the rainfall event, and the results are presented in Table 55. The results indicate that pollution levels are highest during the initial 20 to 30 minutes of rainfall.

Table 55: Pollutant concentration in road runoff. Item 5-20 min 20-40 min 40-60 min Average value pH 7.0-7.8 7.0-7.8 7.0-7.8 7.4 SS (mg/L) 231.42-158.22 158.22-90.36 90.36-18.71 100 BOD5 (mg/L) 7.34-7.30 7.30-4.15 4.15-1.26 5.08 Petroleum 22.30-19.74 19.74-3.12 3.12-0.21 11.25 pollutant (mg/L) Source: domestic EIT, 2018.

237. To reduce runoff and potential contamination of surface and groundwater, projects roads will use innovative technologies to collect and treat storm water, including pervious pavement and bio-retention facilities. Runoff will be collected and treated in 2.5 m wide project constructed bio-retention facilities, located in the green belts along both sides of the roads. These facilities are designed to remove contaminants and sediments from storm water runoff. Storm water is diverted to the treatment area, which consists of a grass buffer strip, sand bed, ponding area, organic or mulch-layer, and soil and plants. The runoff passes first over or through a sand bed, which slows the runoff's velocity, distributing it evenly along the length of the ponding area, which consists of a surface organic layer and the underlying planting soil. The ponding area is graded with a central depressed area. The water collects to a depth of up to 15 cm and gradually infiltrates the bio-retention area or is evapotranspired. The systems will be sized to be able to collect even high intensity rainfall to avoid directly flushing to the river, and bio-retention areas will be graded to divert any excess runoff away.

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238. Bus stations will also be equipped with drainage systems. Runoff will be directed to on-site oil-water separators, and then discharged to the municipal storm water systems.

239. Wastewater and Sewage. All wastewater and sewage will be pretreated on site and then either reused or further treated in one of five municipal Waste Water Treatment Plants (WWTP). Wastewater from stations canteens will be directed to grease traps (5 m3 for hub and terminal stations, and 10 m3 for bus depots), and then to the municipal sewerage system for treatment in a WWTP. Wastewater from the depot maintenance facilities will first be treated in oil-water separators, and then reused for site maintenance. Sewage generated at all stations will be pre-treated in on-site septic tanks, and then discharged to the sewerage system for treatment in a WWTP. Table 56 presents the sizing of oil-water separators and septic tanks for the bus stations. Oil-water separators and septic tanks will be routinely maintained in accordance with the manufacturer’s instructions.

240. Wastewater from maintenance shops resulting from floor washing or other sources will be directed to both oil-water separators and settling basins, and then to the municipal sewerage system for treatment in a WWTP. All discharges of canteen and maintenance shop wastewater and sewage will be required to meet the Level III limit of the Integrated Wastewater Discharge Standard (GB8979-1996).

241. Operation of the roads will not directly generate sewage, although they will include municipal infrastructure such as sewage pipelines. The sewer lines along the roads will discharge various interceptor lines, and then to the Huchao WWTP.

Table 56: Bus station on-site wastewater treatment facilities. Grease Oil-Water Septic Tank Station Type Trap Separator 3 WWTP 3 3 Size m Size m Size m 1. Hub Stations 1.1 Gaofeng Passenger 5 TBD Gaofeng 1.2 Machang Public Transportation 5 TBD Machang 1.3 Biguiyuan 5 TBD Huchau 1.4 South University Town 5 TBD Nanbu 1.5 Yunman Lake 5 TBD Machang 1.6 North Fukang Road-Xuanshui Road 5 TBD Longshan 2. Terminal Stations 2.1 Shuangxi Road-Bai Ma Avenue 5 TBD Machang 2.2 Xinghu Community 5 TBD Huchau 2.3 North of the Xingyue Community 5 TBD Huchau 2.4 East of Gaofeng High School 5 TBD Gaofeng 2.5 Machang Township 5 TBD Machang 2.6 High Technology Industrial Park 5 TBD Longshan 2.7 Dong Qing Lu-SiYa Road 5 TBD Nanbu 2.8 Comprehensive Bonded Zone 5 TBD Longshan 2.9 South of Xingan Avenue 5 TBD Machang 2.10 Minbo Park 5 TBD Huchau 2.11 Gui’an Chuangu Terminal Station 3. Depots 3.1 Central Area 10 5 TBD Huchau 3.2 University Town 10 5 TBD Nanbu 3.3 East Machang 10 5 TBD Machang TOTAL Source: Public Transport FSR, 2018. TBD – to be determined during detailed design.

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242. The capacities of the five municipal WWTPs have been assessed, and all are capable of handling planned population growth and the loads that are expected to be generated through project operation.

243. Air Quality – Bus Fleet. Operation of the 200 zero-emission electric buses will result in substantial reductions in emissions compared to operation of a similar fossil fueled bus fleet, or the provision of equivalent transportation through private cars. No additional mitigations are required.

244. Air Quality – Bus Stations. Bus station canteens will generate fumes from cooking (primarily oily smokes fumes) and waste food. According to survey data in China, the concentration of oil in cooking fumes from similar facilities is approximately 8 mg/m3. To address potential odor problems, fumes will be collected and treated in electrostatic fume purifiers before being vented in roof top stacks electrostatic fume purifiers before being vented in roof top stacks sited away from any adjacent houses or apartments. The electrostatic fume purifiers have an efficiency rate of over 85%, and the emission concentration are predicted to be approximately 1.2 mg/m3, which is in compliance with the relevant standard of 2.0 mg/m3 in Emission Standard of Cooking Fume (GB18483-2001) (Trial). Overall it is predicted that the small amounts of cooking fumes produced will be quickly dispersed from the roof top discharge flues and will have no negative impact on the environment.

245. If non-electric buses use the stations, engines will be required to be shut down immediately upon parking, and no idling will be allowed.

246. Air Quality – Supporting Roads. Air pollution will be generated from vehicles operating on the project’s 8.163 km of supporting roads. Air pollutants in vehicle exhaust include NO2, CO, HC and PM. Of these, the EIT identified NO2 as the critical air pollutant, meaning that if predicted NO2 concentrations comply with the applicable standard, other pollutants such as CO, HC and PM typically also comply with their respective standards.

247. Maximum predicted ambient air NO2 concentrations from road traffic were calculated in the domestic EIT utilizing ADMS 3 (Atmospheric Dispersion Modelling System), an advanced atmospheric pollution dispersion model for calculating concentrations of atmospheric pollutants emitted both continuously from point, line, volume and area sources, or intermittently from point sources. It was developed by Cambridge Environmental Research Consultants (CERC) of the UK in collaboration with the UK Meteorological Office, National Power plc (now INNOGY Holdings plc) and the University of Surrey. The model includes algorithms which take into account: downwash effects of nearby buildings within the path of the dispersing pollution plume; effects of complex terrain; effects of coastline locations; wet deposition, gravitational settling and dry deposition; short term fluctuations in pollutant concentration; chemical reactions; radioactive decay and gamma-dose; pollution plume rise as a function of distance; jets and directional releases; averaging time ranging from very short to annual; and condensed plume visibility. The system also includes a meteorological data input preprocessor.

248. Modelling was undertaken over a grid 7 x 4.5 km, for a zone 200 m on either side of the project roads. Meteorological data for Guiyang City in 2016 were used as a model input. Vehicle emission intensity of NO2 for each project road was calculated utilizing maximum predicted traffic flows (hour, daily and annual), road length and vehicle emission factors and the following formula:

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3 1 j    Q  Ai Eij 3600 i1

Where: Qj - gaseous pollutant emission intensity, mg/s·m; Ai - hourly traffic volume of vehicle by type in the prediction year, vehicle/h; Eij - emission factor of vehicle by type in the prediction year running on the highway, mg/(vehicle·m).37

249. Vehicle emission factors are presented in Table 57, and predicted NO2 pollution intensities are presented in Error! Reference source not found..

Table 57: Vehicle emission factors used in air quality modelling. Vehicle type Pollutant type 2020 2025 2035

Compact vehicle NO 0.165 0.09 0.06 X Mid-sized vehicle NO 0.204 0.111 0.072 X Large vehicle NOX 3.35 2.0 2.0 Source: domestic EIT, 2018. Note: NO2 /NOX ratio = 0.9

Table 58: Predicted NO2 pollution intensities on project roads. Prediction Predicted NO Road section 2 year Intensity, mg/s·m 2020 0.0617 # 5 Road 2026 0.0461 2034 0.0435 2020 0.0595 Northern Extended Section of 2026 0.0446 Zhanqian Road 2034 0.0421 2020 0.0379 Changfeng Road (Z7) 2026 0.0284 2034 0.0265 2020 0.0200 H6 2026 0.0152 2034 0.0143 2020 0.0197 Z3 2026 0.0149 2034 0.0137 2020 0.0222 H8 2026 0.0166 2034 0.0156 2020 0.0210 H11 2026 0.0158 2034 0.0149 2020 0.0212 H12 2026 0.0160 2034 0.0150 H13 2020 0.0184

37 Current emission factors were based on Limits and Measurement Methods for Emissions from Light-duty Vehicles (China Stage III and IV) (GB18352.3-2005). For 2026 and 2034, emission factors are based on Stage III, IV and V in Limits and Measurement Methods for Emissions from Light-duty Vehicles (China Stage V) (GB18352.5-2013) and Limits and Measurement Methods for Exhaust Pollutants from Compression Ignition and Gas Fuelled Positive Ignition Engines of Vehicles (China Stage III, IV, and V) (GB17691-2005).

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Prediction Predicted NO Road section 2 year Intensity, mg/s·m 2026 0.0136 2034 0.0129 2020 0.0195 Z4 2026 0.0143 2034 0.0136 2020 0.0212 Z8 2026 0.0160 2034 0.0150 2020 0.0198 H4 2026 0.0149 2034 0.0137 2020 0.0200 H1 2026 0.0152 2034 0.0143 Source: domestic EIT, 2018.

250. Terrain data was provided free of charge by http://datamirror.csdb.cn/dem/files/ys.jsp, with an accuracy of 3 seconds (approximately 90 m).

Predicted worst case hourly, daily and annual NO2 concentrations at the roads and adjacent sensitive receptors are in compliance with the relevant Level II limit in Ambient Air Quality Standards (GB3095-2012) and WHO AQGs (Table 59 to Table 64 and Figure 42 to Figure 44). Emissions will easily disperse, and are not expected to have significant impacts.

251. GHGs and PM2.5. Project operation will result in increased emission of GHGs and PM2.5 (compared to if the project did not proceed) including emissions directly as a result of the project from operations of the BEBs and bus stations, and induced impacts resulting from increased road traffic and non-BEB use of the bus stations. Over the period 2022-2049 these have been estimated to be an annual average of 49,758 tons of CO2 (4,381 direct and 45,758 tons induced) and 0.33 tons PM2.5 (all induced) (see Appendix H). These impacts are typical of similar urban transport systems, and can be mitigated by requiring non-electric buses to shut down engines upon arrival, with no idling allowed. Further, impacts will be at least in part off-set by the 32.1 km2 of greenspace being developed within the urban area of the GDAD (Table 27 and Table 38).

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Table 59: Predicted worst case 1-hour NO2 concentrations on all project roads compared to PRC Standard and WHO AQG. Level II limit in Maximum Predicted Ambient Air Percentage of PRC Standard 1-hour NO2 Quality Standards PRC Standard Pollutant Time Horizon / WHO AQG Concentration (GB3095-2012) / WHO AQG Exceeded? (mg/m3) / WHO AQG (%) (mg/m3) 2020 0.0344 17.20 No NO2 2026 0.0257 0.20 12.85 No 2034 0.0243 12.15 No Source: domestic EIT, 2018.

Table 60: Predicted worst case 1-hour NO2 concentrations at sensitive receptors near or adjacent to project roads compared to PRC Standard and WHO AQG. Level II limit in Maximum Predicted Ambient Air Percentage of PRC Standard / 1-hour NO2 Quality Standards Location Time Horizon PRC Standard / WHO AQG Concentration (GB3095-2012) WHO AQG (%) Exceeded? (mg/m3) / WHO AQG (mg/m3) 2020 0.0239 11.95 No National Security 2026 0.0179 8.95 No Bureau 2034 0.0169 8.45 No Public Security 2020 0.006 3.00 No Bureau 2026 0.0045 2.25 No Comprehensive 2034 No Business Center 0.0042 2.10 2020 0.0258 12.90 No Tonji Hospital 2026 0.0193 9.65 No 2034 0.0182 9.10 No 2020 0.0087 4.35 No Civic Center 2026 0.0066 3.30 No 2034 0.0062 0.20 3.10 No 2020 0.0276 13.80 No Archives 2026 0.0208 10.40 No 2034 0.0196 9.80 No 2020 0.0167 8.35 No Financial Center 2026 0.0125 6.25 No 2034 0.0118 5.90 No 2020 0.0061 3.05 No Architectural Art 2026 0.0046 2.30 No Museum 2034 0.0043 2.15 No 2020 0.0239 11.95 No Gui’an Center 2026 0.0179 8.95 No 2034 0.0169 8.45 No Source: domestic EIT, 2018.

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Figure 42: Contour map of predicted worst case 1-hour NO2 concentrations on project roads.

2020 2026 2034 Source: domestic EIT, 2018.

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Table 61: Predicted worst case 24-hour NO2 concentrations on all project roads compared to PRC Standard. Level II limit in Average Predicted Ambient Air Percentage 24-hour NO2 Standard Pollutant Time Horizon Quality Standards of Standard Concentration Exceeded? (GB3095-2012) (%) (mg/m3) (mg/m3) 2020 0.0174 21.75 No NO2 2026 0.013 0.08 16.25 No 2034 0.0123 15.38 No Source: domestic EIT, 2018. Note: there is no WHO 24-hour NO2 AQG.

Table 62: Predicted worst case 24-hour NO2 concentrations at sensitive receptors near or adjacent to project roads compared to PRC Standard. Level II limit in Worst Case Ambient Air Percentage Predicted 24-hour Standard Location Time Horizon Quality Standards of Standard NO2 Concentration Exceeded? (GB3095-2012) (%) (mg/m3) (mg/m3) 2020 0.0065 8.13 No National Security 2026 0.0049 6.13 No Bureau 2034 0.0046 5.75 No Public Security 2020 0.0025 3.13 No Bureau 2026 0.0019 2.38 No Comprehensive 2034 No 0.0018 2.25 Business Center 2020 0.0072 9.00 No Tonji Hospital 2026 0.0054 6.75 No 2034 0.0051 6.38 No 2020 0.0029 3.63 No Civic Center 2026 0.0022 2.75 No 2034 0.0021 0.08 2.63 No 2020 0.0084 10.50 No Archives 2026 0.0063 7.88 No 2034 0.006 7.50 No 2020 0.0063 7.88 No Financial Center 2026 0.0047 5.88 No 2034 0.0044 5.50 No 2020 0.0019 2.38 No Architectural Art 2026 0.0015 1.88 No Museum 2034 0.0014 1.75 No 2020 0.0065 8.13 No Gui’an Center 2026 0.0049 6.13 No 2034 0.0046 5.75 No Source: domestic EIT, 2018. Note: there is no WHO 24-hour NO2 AQG.

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Figure 43: Contour map of predicted worst case 24-hour NO2 concentrations on project roads.

2020 2026 2034 Source: domestic EIT, 2018.

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Table 63: Predicted average annual NO2 concentrations on all project roads compared to PRC Standard. Level II limit in Percentage Average Predicted Ambient Air Quality of PRC PRC Standard / Annual NO2 Pollutant Time Horizon Standards (GB3095- Standard / WHO AQG Concentration 2012) WHO AQG Exceeded? (mg/m3) / WHO AQG (mg/m3) (%) 2020 0.00426 10.65 No NO2 2026 0.00319 0.04 7.98 No 2034 0.00301 7.53 No Source: domestic EIT, 2018.

Table 64: Predicted average annual NO2 concentrations at sensitive receptors near or adjacent to project roads compared to PRC Standard. Level II limit in Percentage Worst Case Ambient Air Quality of PRC PRC Standard / Predicted Annual Location Time Horizon Standards (GB3095- Standard / WHO AQG NO2 Concentration 2012) WHO AQG Exceeded? (mg/m3) / WHO AQG (mg/m3) (%) 2020 0.00103 2.58 No National Security 2026 0.00077 1.93 No Bureau 2034 0.00073 1.83 No Public Security 2020 0.00054 1.35 No Bureau 2026 0.00040 1.00 No Comprehensive 2034 No 0.00038 0.95 Business Center 2020 0.00084 2.10 No Tonji Hospital 2026 0.00063 1.58 No 2034 0.00060 1.50 No 2020 0.00064 1.60 No Civic Center 2026 0.00048 1.20 No 2034 0.00046 0.04 1.15 No 2020 0.00149 3.73 No Archives 2026 0.00112 2.80 No 2034 0.00106 2.65 No 2020 0.00188 4.70 No Financial Center 2026 0.00141 3.53 No 2034 0.00133 3.33 No 2020 0.00024 0.60 No Architectural Art 2026 0.00018 0.45 No Museum 2034 0.00017 0.43 No 2020 0.00103 2.58 No Gui’an Center 2026 0.00077 1.93 No 2034 0.00073 1.83 No Source: domestic EIT, 2018.

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Figure 44: Contour map of predicted annual NO2 concentrations on project roads.

2020 2026 2034 Source: domestic EIT, 2018.

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252. Noise – Bus Stations. Operation phase noise will be primarily generated from electric buses and cars arriving and leaving stations; station equipment operation; maintenance works, and passengers. Electric buses expected noise levels will be 60-70 dB(A) at a distance of 1 m, considerably lower than diesel buses which range from 80 to 85 dB(A). Car noise levels are 75-80 dB(A). Station equipment such as fans and water pumps will all be located indoors. Stations will be equipped with noise reduction measures including double glazed windows, which is predicted to result in a noise reduction of about 25 dB(A). Noisy equipment will be located in insulated rooms which should provide approximately 30 dB(A) reduction.

253. Predicted noise levels from bus station operation unmitigated and with reduction measures (station walls, double lased windows, and sound insulation) are presented in Table 65. Predicted noise levels at various distances from the noise sources are presented in Table 66.

Table 65: Predicted bus station noise source levels, dB (A). Noise Reduction intensity Source from noise Noise Source Location after intensity control reduction measures measures Entrance and exit of Electric Bus 60-70 - 60-70 the station Entrance and exit of Car 75-80 - 75-80 the station Crowd Waiting corridor 65-70 - 65-70 Water pump Equipment chamber 75-85 30 45-55 Ventilation Equipment chamber 70-75 30 40-45 system Maintenance Maintenance center 75-80 25 50-55 Source: domestic EIT, 2018.

Table 66: Predicted impact of bus station noise sources at various distances, dB (A). Noise value plus background value Noise Predicted value by distance intensity (daytime) Item after 5m 10m 20m 30m 50m 100m 5m 10m 20m 30m 50m 100m reduction Electric Bus 60-70 55 50 45 42 38 33 59.1 57.7 57.2 57.0 57.0 56.9 Car 75-80 66 60 54 54 46 40 66.5 61.7 58.7 57.8 57.2 56.9 Crowd 65-70 56 50 44 40 36 30 59.5 57.7 57.1 57.0 56.9 56.9 Water pump 45-55 41 35 29 25 21 15 57.0 56.9 56.9 56.9 56.9 56.9 Ventilation 40-45 31 25 19 16 11 5 56.9 56.9 56.9 56.9 56.9 56.9 system Maintenance 50-55 41 35 29 25 21 15 57 56.9 56.9 56.9 56.9 56.9 Source: domestic EIT, 2018. Note: background noise is considered to be 56.9 dB(A), the maximum value in Monthly Environmental Quality Report of Gui'an New District (June 2018), in the daytime.

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254. The results in Table 66 indicate that electric bus noise is below background noise, as are most other bus station noises, and thus bus station operation noise will not have any significant impact. Vibration from bus operation will also be very low, and according to the EIT will only have a very low impact within 30 m from the road, and no impact after 50 m. Nonetheless, noise control measures will be put in place, including selecting low noise equipment where possible; the afore mentioned noise reduction measures such as insulation, vibration reduction measures and double glazed windows in the station buildings; prohibiting use of horn while in the stations; not allowing idling of any fossil fueled buses that use the stations; and planting of evergreen vegetation around the stations to act as a noise barrier.

255. Noise – Supporting Roads.

Noise Level

256. Traffic noise was predicted using the methodology in the PRC “Code for Environmental Impact Assessment of Highway Construction Projects”, which predicts noise levels at 7.5 m from the source. As vehicles are unsteady noise sources, the average radiated sound level by vehicle size class and speed was calculated based on the design speed of the project (30, 40, and 50 km/h), and the following formula:

1 V vi  [k1  ui  k 2  ] k3  ui  k 4 120

ui  N单车道小时 [i  m  1( i ]) Where: vi - estimated vehicle speed of type i vehicle; k1, k2, k3, k4 - regression coefficients (see below); u i - equivalent vehicle number; N - hourly vehicle number on a single track;  i - model ratio of vehicle type; m - weighting factor of vehicle type; V- design vehicle speed; And: Predicted vehicle speed regression coefficiencies Vehicle k1 k2 k3 k4 m Small size - .061748 149.65 -0.000023696 -0.02099 1.2102 Medium size -0.057537 149.38 -0.000016390 -0.01245 0.8044 Large size -0.051900 149.39 -0.000014202 -0.01254 0.70957

257. The noise level of each size of vehicle, L0i (at 7.5 m) was calculated as follows:

Large vehicles: L0L =22.0 + 36.32 lgVL Medium vehicles: L0M =8.8 + 40.48 lgVM Small vehicles: L0S =12.6+34.73 lgVS Note: VL, VM and VS represent the vehicle speeds of large, medium and small size vehicles.

258. Predicted worst case traffic noise levels at 7.5 m for short-term (2020), mid-term (2026) and long-term (2034) horizons, are presented in Table 67.

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Table 67: Predicted maximum noise emissions, 7.5 m from vehicles, on project supporting roads, GDAD, for short-term, mid-term and long-term horizons during operation (unit: dB).

Road and Vehicle Short-term (2020) Mid-term (2026) Long term (2034) No. Design Speed Size Day Night Day Night Day Night Small 68.93 69.07 68.79 69.01 68.64 68.96 5# road 1 Medium 68.66 68.32 68.87 68.47 69.02 68.61 (50 km/h) Large 75.65 75.42 75.80 75.52 75.90 75.59 North Small 68.94 69.07 68.80 69.02 68.66 68.97 expansion of 2 Medium 68.64 68.31 68.85 68.46 69.00 68.59 Zhanqian road (50 km/h) Large 75.64 75.41 75.79 75.51 75.88 75.58 Changfeng Small 65.59 65.71 65.47 65.66 65.34 65.62 3 road (Z7) Medium 64.69 64.36 64.89 64.51 65.05 64.63 (40 km/h) Large 72.10 71.88 72.24 71.97 72.33 72.04 Small 61.23 61.36 61.09 61.31 60.94 61.26 H6 4 Medium 59.67 59.33 59.88 59.49 60.04 59.62 (30 km/h) Large 67.59 67.36 67.74 67.46 67.84 67.53 Small 61.24 61.37 61.11 61.32 60.97 61.27 Z3 5 Medium 59.65 59.32 59.86 59.47 60.02 59.60 (30 km/h) Large 67.58 67.35 67.72 67.45 67.82 67.52 Small 61.20 61.35 61.04 61.30 60.88 61.24 H8 6 Medium 59.72 59.37 59.93 59.53 60.08 59.67 (30 km/h) Large 67.63 67.38 67.78 67.49 67.87 67.57 Small 61.22 61.36 61.08 61.30 60.92 61.25 H11 7 Medium 59.69 59.34 59.90 59.51 60.05 59.64 (30 km/h) Large 67.60 67.37 67.75 67.47 67.85 67.55 Small 61.21 61.35 61.06 61.30 60.90 61.25 H12 8 Medium 59.70 59.36 59.91 59.51 60.06 59.65 (30 km/h) Large 67.61 67.38 67.76 67.48 67.86 67.55 Small 61.26 61.37 61.14 61.33 61.01 61.29 H13 9 Medium 59.62 59.30 59.82 59.44 59.97 59.56 (30 km/h) Large 67.55 67.33 67.69 67.43 67.79 67.49 Small 61.24 61.37 61.12 61.32 60.98 61.27 Z4 10 Medium 59.64 59.31 59.84 59.46 60.00 59.59 (30 km/h) Large 67.57 67.34 67.71 67.44 67.81 67.51 Small 61.26 61.37 61.14 61.33 61.01 61.29 Z8 11 Medium 59.62 59.30 59.82 59.44 59.97 59.56 (30 km/h) Large 67.55 67.33 67.69 67.43 67.79 67.49 Small 61.23 61.36 61.09 61.31 60.97 61.27 H4 12 Medium 59.67 59.33 59.88 59.49 60.02 59.60 (30 km/h) Large 67.59 67.36 67.74 67.46 67.82 67.52 Small 61.23 61.36 61.09 61.31 60.94 61.26 H1 13 Medium 59.67 59.33 59.88 59.49 60.04 59.62 (30 km/h) Large 67.59 67.36 67.74 67.46 67.84 67.53 Source: domestic EIT, 2018.

Noise Impact

259. Noise impacts from project roads was assessed using data from Table 67 and the

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model presented in A.2 of Appendix A of Technical Guidelines for Noise Impact Assessment - Acoustic Environment (HJ 2.4 - 2009):

 Ni   5.7  1  2  Leq )( ih  (LOE)i 10lg  10lg  10lg   L 16  TVi   r    

Where: Leq )( ih - Hourly equivalent sound level of Class i vehicles, dB(A), usually classified as for oversized vehicles, middle-sized vehicles and compact vehicles;

(LOE)i — Speed of Class i vehicle is Vi, km/h; the energy at a horizontal distance of 7.5m is in A-weighted sound pressure level in average, dB(A); Ni - Average hourly traffic flow of Class i vehicles passing through a certain prediction point during daytime and nighttime, vehicles/h; R - The distance from the lane centerline to the predicted point, m; (A12) suitable for noise prediction at prediction points with r > 7.5m. Vi - Average speed of Class i vehicles, km/h; T - The time to calculate equivalent sound level, 1h;  1 ,  2 — The opening angle and radian from the prediction point to both ends of the road section of limited length

260. Traffic noise was predicted for three time horizons (2020, 2026 and 2034), at a height of 1.2 m above the ground, including background noise38, and corrected for factors such as pavement type (asphalt or cement), roadside embankments, attenuation from roadside buildings, and reflection at intersections. The results are presented in Table 68 and are mapped in Figure 45 to Figure 50. The results show that though noise levels increase over time in conjunction with increased traffic flows, the worst case predicted noise levels are generally in compliance with both applicable PRC standards at all three time horizons (the Level IVa standard of 70 dB(A) in the day and 55 dB(A) at night) applies to the area within 35 m from the boundary line, and the Level II standard of (60 dB(A) in the day and 50 dB(A) at night) which applies to the area greater than 35 m away from the road boundary line):

- With respect to the Level IVa standard (within 35 m from the boundary line), there are only two very slight predicted exceedances for year 2034 nighttime noise at #5 Road and Northern extension of Zhanqian Road, at 22 m from the center line. All other predicted noise levels are in compliance with the standard. - With respect to the Level II standard (greater than 35 m away from the road boundary line), there are only minor predicted exceedances for years 2026 and 2034 at 40 to 60 m from the boundary line for 5 Road and Northern extension of Zhanqian Road, and one exceedance for Changfeng Road (Z7).

261. The predicted exceedances are minor in magnitude, nighttime only, and limited to areas immediately adjacent to the roads. To mitigate potential impacts the domestic EIT states that the first row of houses built adjacent to the 13 supporting roads shall not be used for residential or educational purposes (especially schools, hospitals, nursing homes), and the function of those houses shall be considered carefully during design. In addition, noise levels will be monitored and mitigations measures will be put in place if warranted, such as noise barriers.

38 Background noise based on Environmental Impact Report of Tencent Qixing Data Center Project (Phase I) in Gui'an New District, February 2018.

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Table 68: Supporting roads predicted worst case future traffic noise (dB) under three time horizons. Yellow shading designates a predicted exceedance of the Level IVa standard, blue shading designates a predicted exceedance of the Level II standard, Environmental Quality Standard for Noise (GB 3096 - 2008). Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 22m 30m 40m 60m 80m 100m 125m 150m 175m 200m #5 Road (Main) Daytime 57.4 56.1 54.8 53.1 51.8 50.8 49.9 49.1 48.4 47.8 2020 Nighttime 51.9 49.9 48.0 45.4 43.5 42.1 40.6 39.4 38.4 37.5 Daytime 57.7 56.3 55.1 53.3 52.0 51.1 50.1 49.3 48.6 48.1 2026 Nighttime 54.9 53.5 52.3 50.5 49.3 48.3 47.3 46.5 45.9 45.3 Daytime 58.5 57.2 55.9 54.2 52.9 52.0 51.0 50.2 49.5 48.9 2034 Nighttime 55.5 54.2 52.9 51.1 49.9 48.9 48.0 47.2 46.5 45.9 Northern extension of Zhanqian Road (Main) Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 22m 30m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 57.3 55.9 54.7 52.9 51.7 50.7 49.7 48.9 48.3 47.7 2020 Nighttime 51.8 49.8 47.9 45.3 43.4 41.9 40.5 39.3 38.3 37.4 Daytime 57.5 56.2 54.9 53.2 51.9 51.0 50.0 49.2 48.5 47.9 2026 Nighttime 54.7 53.4 52.1 50.4 49.1 48.2 47.2 46.4 45.7 45.1 Daytime 58.4 57.1 55.8 54.0 52.8 51.8 50.9 50.1 49.4 48.8 2034 Nighttime 55.4 54.0 52.8 51.0 49.8 48.8 47.8 47.0 46.4 45.8 Changfeng Road (Z7) (Sub-main) Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 15.5m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 56.7 55.6 52.6 50.8 49.6 48.6 47.6 46.9 46.2 45.6 2020 Nighttime 52.0 50.4 45.8 43.2 41.3 39.9 38.4 37.2 36.2 35.3 Daytime 57.2 56.1 53.1 51.3 50.1 49.1 48.1 47.4 46.7 46.1 2026 Nighttime 53.3 51.6 47.1 44.4 42.6 41.1 39.6 38.5 37.5 36.6 Daytime 57.9 56.8 53.8 52.0 50.8 49.8 48.8 48.0 47.4 46.8 2034 Nighttime 54.3 53.2 50.1 48.4 47.1 46.2 45.2 44.4 43.7 43.2 H6 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20M 40m 60m 80m 100m 125m 150m 175m 200m Daytime 54.1 50.7 46.2 43.5 41.6 40.2 38.7 37.5 36.5 35.7 2020 Nighttime 51.0 47.6 43.1 40.4 38.5 37.1 35.6 34.5 33.4 32.6 Daytime 55.3 51.9 47.4 44.7 42.8 41.4 39.9 38.8 37.7 36.9 2026 Nighttime 51.7 48.3 43.8 41.2 39.3 37.8 36.4 35.2 34.2 33.3 Daytime 55.7 53.5 50.4 48.7 47.4 46.5 45.5 44.7 44.0 43.5 2034 Nighttime 52.2 48.8 44.3 41.7 39.8 38.3 36.9 35.7 34.7 33.8 Z3 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 53.9 50.6 46.0 43.4 41.5 40.0 38.6 37.4 36.4 35.5 2020 Nighttime 50.8 47.5 42.9 40.3 38.4 37.0 35.5 34.3 33.3 32.4 Daytime 55.1 51.8 47.2 44.6 42.7 41.3 39.8 38.6 37.6 36.7 2026 Nighttime 51.6 48.2 43.7 41.0 39.1 37.7 36.2 35.0 34.0 33.2 Daytime 55.6 53.3 50.3 48.5 47.3 46.3 45.4 44.6 43.9 43.3 2034 Nighttime 52.1 48.7 44.2 41.5 39.7 38.2 36.7 35.6 34.6 33.7 H8 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 54.4 51.1 46.5 43.9 42.0 40.6 39.1 37.9 36.9 36.0 2020 Nighttime 51.3 48.0 43.4 40.8 38.9 37.5 36.0 34.8 33.8 32.9 Daytime 56.1 53.8 50.8 49.0 47.8 46.8 45.9 45.1 44.4 43.8 2026 Nighttime 52.1 48.7 44.2 41.5 39.7 38.2 36.7 35.6 34.6 33.7 Daytime 56.6 54.4 51.4 49.6 48.4 47.4 46.4 45.6 45.0 44.4 2034 Nighttime 52.6 49.2 44.7 42.0 40.2 38.7 37.3 36.1 35.1 34.2 H11 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m 2020 Daytime 54.2 50.8 46.3 43.7 41.8 40.3 38.9 37.7 36.7 35.8

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Nighttime 51.1 47.7 43.2 40.6 38.7 37.2 35.8 34.6 33.6 32.7 Daytime 55.4 52.0 47.5 44.9 43.0 41.5 40.1 38.9 37.9 37.0 2026 Nighttime 51.8 48.5 43.9 41.3 39.4 38.0 36.5 35.3 34.3 33.4 Daytime 55.8 53.6 50.6 48.8 47.6 46.6 45.6 44.8 44.2 43.6 2034 Nighttime 52.4 49.0 44.5 41.8 39.9 38.5 37.0 35.8 34.8 34.0 H12 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 54.3 50.9 46.4 43.8 41.9 40.4 39.0 37.8 36.8 35.9 2020 Nighttime 51.2 47.8 43.3 40.7 38.8 37.3 35.9 34.7 33.7 32.8 Daytime 55.5 52.1 47.6 45.0 43.1 41.6 40.2 39.0 38.0 37.1 2026 Nighttime 51.9 48.6 44.0 41.4 39.5 38.1 36.6 35.4 34.4 33.6 Daytime 55.9 53.7 50.7 48.9 47.7 46.7 45.7 44.9 44.3 43.7 2034 Nighttime 52.5 49.1 44.6 41.9 40.0 38.6 37.1 35.9 34.9 34.1 H13 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 53.6 50.3 45.7 43.1 41.2 39.7 38.3 37.1 36.1 35.2 2020 Nighttime 50.5 47.2 42.6 40.0 38.1 36.7 35.2 34.0 33.0 32.1 Daytime 54.8 51.5 46.9 44.3 42.4 41.0 39.5 38.3 37.3 36.4 2026 Nighttime 51.3 47.9 43.4 40.7 38.9 37.4 35.9 34.8 33.8 32.9 Daytime 55.3 53.0 50.0 48.3 47.0 46.0 45.1 44.3 43.6 43.0 2034 Nighttime 51.8 48.4 43.9 41.2 39.4 37.9 36.5 35.3 34.3 33.4 Z4 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 53.8 50.4 45.9 43.3 41.4 39.9 38.5 37.3 36.3 35.4 2020 Nighttime 50.7 47.3 42.8 40.2 38.3 36.8 35.4 34.2 33.2 32.3 Daytime 55.0 51.6 47.1 44.5 42.6 41.1 39.7 38.5 37.5 36.6 2026 Nighttime 51.4 48.1 43.5 40.9 39.0 37.6 36.1 34.9 33.9 33.1 Daytime 55.5 53.2 50.2 48.4 47.2 46.2 45.2 44.5 43.8 43.2 2034 Nighttime 52.0 48.6 44.1 41.4 39.5 38.1 36.6 35.4 34.4 33.6 Z8 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 53.6 50.3 45.7 43.1 41.2 39.7 38.3 37.1 36.1 35.2 2020 Nighttime 50.5 47.2 42.6 40.0 38.1 36.7 35.2 34.0 33.0 32.1 Daytime 54.8 51.5 46.9 44.3 42.4 41.0 39.5 38.3 37.3 36.4 2026 Nighttime 51.3 47.9 43.4 40.7 38.9 37.4 35.9 34.8 33.8 32.9 Daytime 55.3 53.0 50.0 48.3 47.0 46.0 45.1 44.3 43.6 43.0 2034 Nighttime 51.8 48.4 43.9 41.2 39.4 37.9 36.5 35.3 34.3 33.4 H4 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 53.9 50.6 46.0 43.4 41.5 40.1 38.6 37.4 36.4 35.5 2020 Nighttime 50.8 47.5 42.9 40.3 38.4 37.0 35.5 34.3 33.3 32.5 Daytime 55.1 51.8 47.2 44.6 42.7 41.3 39.8 38.6 37.6 36.8 2026 Nighttime 51.6 48.2 43.7 41.0 39.2 37.7 36.3 35.1 34.1 33.2 Daytime 55.6 53.3 50.3 48.6 47.3 46.3 45.4 44.6 43.9 43.3 2034 Nighttime 52.1 48.7 44.2 41.5 39.7 38.2 36.8 35.6 34.6 33.7 H1 Predicted Traffic Noise (dB) at Different Horizontal Distances from Road Centerline Time Horizon 12m 20m 40m 60m 80m 100m 125m 150m 175m 200m Daytime 54.1 50.7 46.2 43.5 41.6 40.2 38.7 37.5 36.5 35.7 2020 Nighttime 51.0 47.6 43.1 40.4 38.5 37.1 35.6 34.5 33.4 32.6 Daytime 55.3 51.9 47.4 44.7 42.8 41.4 39.9 38.8 37.7 36.9 2026 Nighttime 51.7 48.3 43.8 41.2 39.3 37.8 36.4 35.2 34.2 33.3 Daytime 55.7 53.5 50.4 48.7 47.4 46.5 45.5 44.7 44.0 43.5 2034 Nighttime 52.2 48.8 44.3 41.7 39.8 38.3 36.9 35.7 34.7 33.8 Source: domestic EIT, 2018.

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Figure 45: Supporting roads predicted future traffic noise (dB), 2020 time horizon, daytime.

Source: domestic EIT, 2018.

Figure 46: Supporting roads predicted future traffic noise (dB), 2020 time horizon, nighttime.

Source: domestic EIT, 2018.

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Figure 47: Supporting roads predicted future traffic noise (dB), 2026 time horizon, daytime.

Source: domestic EIT, 2018.

Figure 48: Supporting roads predicted future traffic noise (dB), 2026 time horizon, nighttime.

Source: domestic EIT, 2018.

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Figure 49: Supporting roads predicted future traffic noise (dB), 2034 time horizon, daytime.

Source: domestic EIT, 2018.

Figure 50: Supporting roads predicted future traffic noise (dB), 2034 time horizon, nighttime.

Source: domestic EIT, 2018.

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262. Noise – Supporting Roads and Sensitive Receptors. An analysis was also undertaken on predicted road noise impacts on sensitive receptors identified in Table 40. All receptors are within 35m of the project supporting roads boundary lines. The modelling results, presented in Table 69, show that predicted noise levels at all sensitive sites are in compliance with Level IVa standard of 70 dB(A) in the day and 55 dB(A) at night) which applies to the area within 35 m from the boundary line, and the Level II standard of (60 dB(A) in the day and 50 dB(A) at night) which applies to the area greater than 35 m away from the road boundary line. There are some slight predicted exceedances of the WHO Noise Level Guideline (in the EHS Guidelines) for residential, institutional, and educational receptors of 55 dB(A) day time and 45 dB(A) night time, and noise barriers will be installed at these facilities, in particular at Tonji Hospital. Noise monitoring will be undertaken at these receptors, and if required sound barriers will be put in place to ensure actual noise level compliance with WHO guidelines.39

Table 69: Supporting roads predicted future traffic noise (dB(A)) at sensitive receptors, under three time horizons. Predicted noise levels are in compliance with PRC standards, but there are some predicted exceedances of WHO AQGs (highlighted in yellow). 2020 2025 2030 Sensitive Point Daytime Nighttime Daytime Nighttime Daytime Nighttime National Security Bureau 50.71 44.12 50.95 44.69 51.10 44.95 Integrated Service Center of Public Security Bureau of 52.08 43.72 52.48 44.42 52.71 44.73 Gui'an New District Tongji Hospital 55.93 51.97 56.43 52.72 56.96 53.23 Civic Center 49.37 40.29 49.39 40.36 49.41 40.44 Financial Harbor 52.66 47.64 52.99 48.21 53.39 48.75 Gui'an Center 51.86 43.35 52.15 43.91 52.46 44.34 Source: domestic EIT, 2018. Notes: Includes background noise, considered as the average value of noise monitored at Xincun Village (49.25 dB(A) in the daytime and 39.80 dB(A) in the nighttime), in Environmental Impact Report of Tencent Qixing Data Center Project (Phase I) in Gui’an New District, February 2018.

263. Noise – Charging Stations. Noise from charging station operation will be generated from equipment operation and users, both people and vehicles (Table 70). Low noise equipment will be selected where possible, noisy machinery will be installed in insulated equipment rooms, and the building walls will be insulated for sound protection. Predicted charging station operating noise impacts with sound proofing mitigations in place are presented in Table 71.

Table 70: Charging station predicted noise sources, (dB(A)). Noise Source Location Source strength Vehicles Entrances / exists of the station 75-80 People Inside station 65-70 Equipment Inside station 50-55 Source: domestic EIT, 2018.

39 As noted in Chapter II, the PRC Environmental Quality Noise Standards (GB3096-2008) will be used for traffic noise while the EHS Guidelines will be applied for noise based on types of receptors.

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Table 71: Predicted noise impacts during operation, (dB(A)). Impact value by distance accumulated with Predicted impact value by distance Noise background noise Noise level after 5 10 20 30 50 100 Source 5 10 20 30 50 100 mitigation m m m m m m m m m m m m Day1 Day Day Day Day Day Vehicles 75-80 66 60 53.9 50.5 46 40 66.52 61.7 58.7 57.8 57.2 56.9 People 65-70 56 50 43.9 40.4 36 30 59.5 57.7 57.1 57 56.9 56.9 Equip- 50-55 41 35 28.7 25.4 21 15 57 56.9 56.9 56.9 56.9 56.9 ment Source: domestic EIT, 2018. Notes: 1 The EIT only calculated day time noise due to limited operation after 22:00 h. Background noise refers to the maximum day time value of 56.9 dB(A) according to “monthly report of environmental background noise of Gui’an New Area” (June 2018). 2 There are no residences this close to the charging stations.

264. The results in Table 71 indicate that the largest noise sources are from users and their vehicles, and that an up to an 9.6 dB(A) increase may occur at a distance of 5 m. To further mitigate noise, i) use of horns while in or entering or leaving the station will be prohibited, and idling of engines will not be allowed; ii) low-noise equipment, will be selected where possible; iii) as noted above, noisy equipment will be installed in sound insulated equipment rooms, and building wall will also be sound insulated; iv) sites will be surrounded by vegetation; v) sound barriers will be installed between charging stations and any adjacent sensitive receptors. Overall, with these mitigations in place, charging station operation is not expected to cause significant changes in the sound quality of the current regional acoustic environment or impact surrounding residents.

265. Domestic Solid Waste. Solid waste generated during the bus station and fleet phase will primarily consist of domestic garbage generated from passengers and operational staff, and will include plastic bags, paper and other trash, estimated at 108 t/year. The following solid waste management measure will be implemented:

i) Bus stations, depots, buses and charging stations will be equipped with appropriate garbage and recycling containers.

ii) Domestic garbage and recyclables will be collected on a regular basis. Recyclables will be collected by an appropriate recycling facility, and garbage by the local sanitation department for disposal at a municipal solid waste landfill.

266. Bus Recycling. Over the lifetime of the project it is expected that some buses will need to be replaced due to either mechanical failure or accident. Buses will be recycled to the maximum extent possible. The Gui'an Culture and Tourism Investment Company (PIU for the bus station construction and owner and operator of the electric buses) will be responsible for overseeing vehicle scraping and recycling. They will entrust the procedure to a nationally certified vehicle write-off company who will be responsible for all aspects of vehicle scrapping and recycling in accordance with relevant PRC regulations, including the Regulations on Vehicle Recycling Management.

267. Hazardous Materials and Waste. Toxic, hazardous, and harmful materials present in the operation of the project include used batteries40, used lubricating oil and grease (O&G)

40 Bus batteries in China have a typical life span of 8 years (based on a reserve ratio of minimum 10% and an SOC of 90%).

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from maintenance facilities, and sludge for oil-water separators and septic tanks. Inappropriate waste storage and disposal could affect soil, groundwater, and surface water resources, and hence, public health and sanitation.

268. These potential impacts will be effectively mitigated through good practice hazardous materials management in accordance with relevant PRC regulations. This will include appropriate hazardous materials transport, storage and disposal, battery reuse or recycling, and the development of emergency spill response procedures.

269. When a battery capacity is lower than 80%, it will no longer be used on buses. It will be moved to a battery cluster within the bus stations to provide electricity for slow chargers working in the night time. When capacity is too low to function in that manner, they will be recycled.

270. PRC Interim Measures for the Administration of Recycling and Utilization of New Energy Vehicles' Power Battery (2018) August 1, 2018 makes EV manufacturers responsible for the recovery and recycling of EV batteries. In compliance with the Interim Measures, and to ensure appropriate battery recycling, the battery providers will be responsible for collection, recycling (or reuse again if possible) of batteries. Battery providers will also be required to have a “traceability” system that enables the identification of owners of discarded batteries, and easily dismantled product designs to help automate the recycling process.

271. Groundwater Protection. Some bus stations are located in quasi-groundwater drinking water source protection zone. There is a risk of battery or other leaks polluting these water resources. To mitigate these risks, regular vehicle maintenance will be undertaken to ensure safe battery operation, and an emergency spill response plans (as noted above) will be developed. Bus stations will be equipped with drainage systems. Runoff will be directed to on-site oil-water separators, and then discharged to the municipal storm water systems. Fuels, oil, chemicals and other hazardous materials will be stored within a secured impermeable weatherproof facility with a storage capacity of at least 110% of the capacity of the hazardous materials stored (and at least 300 m from drainage structures, important water bodies and other sensitive receptors.

272. Occupational Health and Safety. Station operation includes physical hazards to workers from vehicle traffic, noise and vibration, dust, handling heavy materials and equipment, falling objects, work on slippery surfaces, electrocution, fire hazards, chemical hazards such as toxic fumes and vapors, and others risks.

273. To address these risks the operators Environment, Health and Safety Officer will undertake a risk assessment and implement an Occupational Health and Safety Plan (OHSP) to address the risks, maintain records concerning health, safety and welfare and regularly report on accidents, incidents and near misses. The OHSP will provide adequate precautions to protect the health and safety of their workers, including but not necessarily limited to sanitation, including waste removal and provision of potable water and sanitation facilities; occupational safety, including provision of appropriate personal protective equipment (PPE) such as safety hats, shoes, goggles, ear plugs and respiratory masks; electrical safety; traffic safety; emergency response, including procedures for medical, fire and other emergencies; and training in accordance with EHS Guidelines. The OHSP will be reviewed and approved by the LIEC and PMO.

274. Traffic Safety. Operation of the zero emission modern bus network includes inherent risk of traffic accidents. This risk will be mitigated through regularly inspect and maintaining corridor roads and drains, appropriate training and licensing of bus drivers and provision of PPE; strict enforcement of traffic laws and regulations, especially speed limits.

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275. Traffic safety risks on the supporting roads will be mitigated through good design, including the provision of lanes for pedestrians and non-motorized vehicles and improved designs of road junctions and frequent pedestrian crossings; and strict enforcement of traffic laws.

276. Preliminary ICV Testing and Safety plans are presented in Appendix K. These plans will be develop in detail during implementation with the support of a national and international ICV Expert Team, prior to the initiation of any ICV closed or open-road test activities.

277. Ecology. Project operation is not expected to have any significant negative impacts on flora and fauna. All project sites are situated within modified industrial, commercial and residential and urban environments. Based on the EIT and site surveys, there are no known rare or endangered flora or fauna, species with international, national or provincial protection status, areas of natural or critical habitat, parks, nature reserves, or areas with special national, regional or local ecological significance within or adjacent to any of the sites.

278. Bridge operation is not expected to have any negative impacts on aquatic ecology. First, the water body is artificial and does not, and will not, have any rare or endangered aquatic species. Secondly, all runoff from the bridge will be collected and directed to the bio- retention facilities, not the water body.

279. Visual Aesthetics. The overall visual character of the project zone of influence is that of an area undergoing rapid urbanization. The bus stations and roads being developed by the project, along with the associated green landscaping, are a positive contribution that are fully compatible with the existing and planned surrounding urban facilities and infrastructure.

E. Cumulative, Indirect and Induced Impacts

280. Cumulative impacts are defined as the combination of multiple impacts from existing projects, the proposed project, and anticipated future projects that may result in significant adverse and/or beneficial impacts that cannot be expected in the case of a stand-alone project. With respect to the construction phase, the project is a very small part of the large scale urban development that is the GDAD. The very small scale of project works are such that they are not expected to have any appreciable negative impacts over and above the urban development that has been underway since 2014.

281. Indirect impacts are adverse and/or beneficial environmental impacts which cannot be immediately traced to a project activity but can be causally linked. Induced impacts are adverse and/or beneficial impacts on areas and communities from unintended but predictable developments caused by a project which may occur later or at a different location.

282. The supporting roads will provide access to the core area of the GDAD, and the ITS, bus stations, zero-emission buses and charging stations will improve public transport in the overall GDAD area. These project outputs have been developed in accordance with the Master Plan of Gui’an New District (2013-2030). With their completion traffic function and public transport service will be improved, and there will be positive indirect economic and health benefits to residents.

283. Traffic on the project supporting roads and bus station operation will result in induced emissions, estimated to be an annual average of 45,377 tons of CO2 and 0.33 tons PM2.5 (2022-2049) (Appendix H). These impacts are typical of similar urban transport systems. Overall, the projects influence on traffic flows and urban development has been assessed

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within the context of the relevant urban plans and are considered appropriate. Significant negative indirect or induced impacts are not anticipated.

F. Climate Risk

284. A Climate Risk and Vulnerability Assessment (CRVA) was undertaken for the project (Appendix I).

285. Methodology. Data from the Coupled Model Inter-comparison Project Phase 5 (CMIP5) climate models for the project area were compiled and reviewed. The downscaled climate scenarios that were derived from the General Circulation Model (GCM) runs conducted under the CMIP5 were established for the Gui’an New District. The CRVA was conducted for greenhouse gas emission scenarios known as Representative Concentration Pathways (RCPs) used in the Fifth Assessment Report by the Intergovernmental Panel on Climate Change (IPCC).

286. The CMIP5 climate projections were obtained through model simulations for four different scenarios, RCP2.6, RCP4.5, RCP6.0, and RCP8.5, respectively, which represent different levels of greenhouse gas emission. The scenario of RCP2.6 represents the lowest level of greenhouse gas emission that corresponds to the agreed outcomes of the agreement (no more than 2.0 °C of temperature increase over pre-industrial). RCP4.5 and RCP6.0 are the medium and high scenarios but their differences are mainly in late of this century with little difference by 2050. RCP8.5 is the extreme case that represents the highest level of emission with the most significant degree of climate change.

287. In the CRVA a conservative approach was adopted to use the RCP4.5 as a reference scenario and RCP8.5 as a challenging scenario. Future climate hazards, such as floods and temperature extremes, etc. were derived by analyzing these two scenarios at a local level. This is to ensure that both the climate change impact assessment and the resulting proofing measures are adequate for the proposed project components.

288. The simulated climate data from the General Circulation Model (GCM) used in the CRVA include both the historical baseline and future timeframes under both the RCP 4.5 and RCP 8.5 scenarios, respectively. The historical scenario covers the GCM precipitation data for a 55-year historical baseline period from 1950 to 2005, while the RCP4.5 and RCP8.5 scenarios include a 80-year projection period (2021-2100). The GCM model data for each period of time scale can be viewed as a statistical realization of that climatic period.

289. The precipitation and temperature data from the GCM were applied in the CRVA to project future climate change conditions. A combination of different RCP and climate sensitivities could be used to characterize the future climate change scenarios and their associated uncertainty ranges. The RCP4.5 scenario with low-climate sensitivity and RCP8.5 with high-climate sensitivity were used as an indicator of the corresponding low and high bound of the uncertainty range. Projected precipitation/temperature data were obtained for the following three climate change scenarios: Historical, RCP 4.5 and RCP 8.5.

290. Three key period timeframes were defined for the CRVA: 1) PA, the past 30 years from 1976 to 2005; 2) NF, the near-term future from 2021 to 2050; and 3) LF, the long-term future from 2071 to 2100. Projected climate variables (such as maximum temperature, minimum temperature and precipitation) that may cause hazardous to the proposed project in Gui'an were obtained for the three periods, respectively.

291. CRVA Results. Compared to the historical baseline, the annual average maximum temperature is projected to increase by 1.48°C and 2.01°C, respectively, in the near-term future to 2050 under the low and high scenarios, and by 2.88°C to 5.02°C, respectively, in

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the long-term future to 2100. For the annual average minimum temperature, it is projected to increase by 1.35°C and 1.72°C under the low and high scenarios, respectively, in the near- term future to 2050, and by 2.47°C and 4.60°C in the long-term future to 2100.

292. The annual average precipitation is projected to increase by 2.1% in the near-term future to 2050 and decrease by 6.5% in the long-term future to 2100 under the low scenario (RCP4.5). Under the high scenario (RCP8.5), it is projected to increase by 5.8% in the near future to 2050 and increase by 7.4% in the long-term future to 2100, respectively. These projected results indicate that the annual precipitation in Gui’an is likely to keep roughly steady in the future under the low RCP4.5 scenario, but will increase by 5.8 to 7.4% under the high RCP8.5 scenario.

293. The projected largest change takes place in the month of June, when the rainfall is the most intensive during the year. Precipitation in June is projected to increase significantly compared to the baseline condition, whereas in other months of the year, precipitation does not change significantly. Overall, rainfall is projected to increase in the future in the project under the high climate change scenario. Climate change will possibly lead to a rainfall increase, which implies an increased flood risk in the future.

294. The climate change in Gui’an tends to have more impact on the intensity of more frequent smaller storms at the reoccurrence intervals of 2 to 10 years, and has less impact on larger storms that have 20 to 100 years of return period. Overall, the long-term (to 2010) impact to a 5-year storm, which is often used as the standard storm for drainage design, is projected to be up to approximately 10% under the low RCP4.5 scenario and up to approximately 20% under the RCP8.5 scenario. For the short-term future to 2050, the impact of climate change is an increase by about 5 to 12% to the intensity of 2 to 5-year storm events. Generally speaking, rainfall intensity will be on average about 10% higher for storms with 2 to 5-year return periods in the project area due to climate change.

295. The highest risk that climate change may impose to the project areas in Gui’an is higher flood peak flows because of increased intensity of storm events. The CRVA recommends climate change adaptation measures to augment the design peak runoff inflow and flood of relevant drainage. To be conservative, the CRVA recommended that the intensity of design storms be augmented by 10% in designing road systems and sizing drainage pipes/channels that are associated with the transport infrastructure works in this project for climate change adaptation. This recommendation has been incorporated into all design decisions that require estimated magnitude of design (rainfall, flood) events.

G. Associated Facilities

296. Associated facilities are facilities that are not funded as part of a project but whose viability and existence depend exclusively on the project, or whose goods or services are essential for successful operation of the project.

297. Project Supporting Roads. The project supporting roads will provide access to key existing north-south and east-west trunk roads, and these trunk roads (Tianhetan Avenue, Jin’an Avenue, Zhanqian Road and Baima Avenue) are considered as associated facilities.

298. A review was undertaken which demonstrates that the associated facility roads were developed with all necessary project approvals (Table 72) and in accordance with relevant PRC environmental requirements (Table 73).

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Table 72: Associated facility road project approvals (for project supporting roads). Road Name Associated FSR Owner FSR Approved Year of Status Remarks by Approval (Year built or planned) Tianhetan FSR for Tianhetan 1 2 Avenue Avenue Project GGCI EDB Aug 2013 2015/16 Originally, the name of Jin’an FSR for Central Jin’an Avenue GGCI1 EDB2 March 2014 2015/16 Avenue was Avenue Project Central Avenue in the FSR FSR for the Public Traffic Network in the Functional 1 3 Zhanqian Road Region before GGCI AAB April 2016 2017/18 Gui’an High-speed Railway Station Originally, the name of Baima FSR for Jinma 4 5 December Baima Avenue Avenue Project AC DRC 2012 2014/15 Avenue was Jinma Avenue in the FSR Source: PMO, 2018. Notes: 1 Guizhou Gui’an Construction Investment Co., Ltd 2 Economic Development Bureau of Gui’an New District 3 Administrative Approval Bureau of Gui’an New District 4 Administrative Committee of Gui’an New District 5 Development and Reform Committee of Gui’an New District

Table 73: Associated facility road EIA approvals (for project supporting roads). Name of the EIA prepared by FSR Approved Year of Approval Remarks Road by Tianhetan 1 2 Avenue GTSRI DPE Feb 2014 Originally, the name of Jin’an Avenue Jin’an Avenue EPB3 Nov 2013 was Central Avenue in the FSR Zhanqian Road Originally, the name of Baima Avenue Zhanqian Road EPB3 June 2016 was Jinma Avenue in the FSR Baima Avenue DPE2 Dec 2012 Source: PMO, 2018. Notes: 1 Guizhou Transport Science & Research Institute Co., Ltd. 2 Department of Environmental Protection of Guizhou Province 3 Environmental Protection Bureau of Gui’an New District

299. Bus Station Roads. The roads on which the bus stations will be situated are also considered to be associated facilities. A review of available information indicates that the existing associated facility roads were developed in accordance with relevant PRC environmental requirements (Table 74). Those roads that are not yet built will need to undergo appropriate assessment in accordance with PRC requirements.

300. Under Road Municipal Infrastructure. Facilities that connect to the municipal power, water supply and other infrastructure that will be integrated under project supporting roadways are also considered associated facilities. Some such as water supply and sewage will be connected to existing systems, but for others such as communications, power and natural gas, empty conduits will be installed allowing for future installation of communication cables or pipelines when needed. A review of available information indicates that the existing associated facilities for under road infrastructure were developed in accordance with relevant PRC environmental requirements (Table 75). For cables and pipelines that are installed in

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empty conduits in the future, all necessary PRC permits and clearances must be obtained.

H. Positive Impacts and Environmental Benefits

301. The project will benefit 1.4 million residents of the GDAD by 2030, including both public transport users and residents in general.

(i) Once operational, ridership on the bus network is expected to reach 70,000 passenger trips per day. Users will benefit from a quiet, intelligent and highly efficient, zero-emission bus system. Residents who are non-users will also benefit from access to car charging stations, reduced traffic congestion, improved road safety, and reduced air pollution.

(ii) Traffic on the supporting roads in the core area is expected to reach a peak of 11,323 pcu/hour and total 142,540 pcu/day by 2030. Users will experience travel on a safe road network that is environmentally sustainable and friendly to both non-motorized and pedestrian traffic.

(iii) An efficient public transport system will reduce the costs of transport in serving major urban and industrial areas and transport hubs, and will provide better accessibility to employment and services in the GDAD. It will enhance economic growth compared to the existing public transport system.

(iv) Benefits from improved traffic flows and reduced congestion from ITS implementation include:

(a) a 50% crash rate reduction and a 5% fatality rate reduction per crash due to speed limit enforcement; (b) reduced journey time by car of 10% as a result of reduced congestion, traffic signal coordination, parking management, weather warning and incident management; (c) reduced journey time by bus of 15% and increased bus modal share by 10% as a result of a bus information management system, reduced congestion, bus priority measures, traffic signal coordination, weather warning and incident management; (d) reduced vehicle operating costs by 8% as a result of less congestion and reduced stop-start traffic conditions; and, (e) reduced vehicle emissions by 8% due to less congestion and reduced stop-start traffic conditions.

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Table 74: Associated facility road EIA approvals (for bus stations). Status Associated Construction Operating EIA Approved No. Station Name (Year built EIA Status EIA Prepared by Comments Road(s) Agency Agency by or planned) 1 Hub Stations Gaofeng To be To be To be 1-1 Wanhua Avenue 2023 Planned To be Determined Passenger Determined Determined Determined Shuangxi Road Machang Public To be To be To be 1-2 and Tianxuan 2023 Planned To be Determined Transportation Determined Determined Determined Road Guizhou Transport Guizhou Construction Comprehensive Science Research Environmental 1-3 Biguiyuan Jinma Avenue 2014 Investment Law Enforcement Approved Institute Shares Co., Protection Company Bureau Ltd Department Guizhou Transport Construction Comprehensive South University Science Research 1-4 Pingan Avenue 2021 Investment Law Enforcement Approved Gui'an EPB Town Institute Shares Co., Company Bureau Ltd Comprehensive Approved, but Historical Secondary Trunk 1-5 Yunman Lake 2015 Not Available Law Enforcement unable to Not Available Not Available information Main Bureau verify unavailable Guiyang Institute of Guizhou Gui'an Comprehensive survey and design North Fukang- North Fukang 1-6 2015 Resettlement and Law Enforcement Approved Co. Ltd, China hydro- Gui'an EPB Xuanshui Road Road Investment Group Bureau power consultancy group. 2 Terminal Stations

Guizhou Construction Comprehensive Shuangxi Road- Environmental 2-1 Baima Avenue 2016 Investment Law Enforcement Approved Bai Ma Avenue Protection Company Bureau Department Construction Guiyang Institute of 2-2 Xinghu Community Huchao Road 2023 Investment to be determined Approved survey and design Gui'an EPB

Company Co. Ltd, Power China North of the Comprehensive Information to 2-3 Xingyue Zhaoxia Road 2018 Law Enforcement be collected Community Bureau

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Status Associated Construction Operating EIA Approved No. Station Name (Year built EIA Status EIA Prepared by Comments Road(s) Agency Agency by or planned) East of Gaofeng To be To be To be To be Determined To be 2-4 Gaofeng Branch 2023 High School Determined Determined Determined Determined Machang To be To be To be To be Determined To be 2-5 Machang township 2021 Secondary Determined Determined Determined Determined High Technology To be To be To be To be Determined To be 2-6 Songbaishan Road 2021 Industrial Park Determined Determined Determined Determined Comprehensive Dong Qing Road - Dongqing Road- Information to 2-7 2014 Law Enforcement Si Ya Road Siya Road be collected Bureau Guizhou Transport Guizhou Construction Comprehensive Comprehensive Science Research Environmental 2-8 Jinma Avenue 2014 Investment Law Enforcement Approved Bonded zone Institute Shares Co., Protection Company Bureau Ltd Department The extension Guizhou Transport Construction Comprehensive of Xing'an South of Xingan Science Research 2-9 Xing'an Avenue 2014 Investment Law Enforcement Approved Guiyang EPB Avenue is to Avenue Institute Shares Co., Company Bureau be constructed Ltd by 2023 To be To be To be To be Determined To be 2-10 Minbo Park Guangxing Road 2023 Determined Determined Determined Determined Branch Road To be To be To be To be Determined To be 2-11 Gui’an Chuangu 2023 (unnamed) Determined Determined Determined Determined 3 Depots

Construction Comprehensive Guiyang Institute of Central Area Bus 3-1 Hulei Road 2015 Investment Law Enforcement Approved survey and design, Gui'an EPB Depot Company Bureau Hydro China Guizhou Transport Construction Comprehensive Depot access College town Bus Science Research 3-2 Ankang Avenue 2015 Investment Law Enforcement Approved Gui'an EPB road to be Depot Institute Shares Co., Company Bureau built by 2022 Ltd East Machang Bus To be To be To be To be Determined To be 3-3 Donghuang Road 2023 Depot Determined Determined Determined Determined Source: PPTA consultant, PMO.

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Table 75: Associated facilities for under road municipal infrastructure. Under Road Utility Length (m) Connection Status Associated Facility Approval Status Municipal water supply 1,401.3 To be connected to existing Xiaozhai WTP EIT pipeline municipal water supply approved by GEPB, system and Xiaozhai Water Approval No. 2016(34). Treatment Plant (WTP). Capacity is 200,000 m3/day. Municipal sewage pipeline 1,751.6 To be connected to existing Huchao MWWT EIT Huchao Waste Water approved by GEPB, Treatment Plant (WWTP). Approval No. 2014(16). Capacity is 40,000 m3/d in phase I and 120,000 m3/d in phase II. Municipal stormwater 2,6569.0 Runoff will first be collected Bio-retention facilities pipeline and treated in project and stormwater constructed roadside bio- pipelines approved by retention facilities. The water GEPB under project EIT, collects to a depth of up to 15 Approval No. 2019(3). cm and gradually infiltrates the bio-retention area or is evapotranspired. For Road #2 (Northern Extended Section of Zhanqian Road), any remaining treated storm water will be discharged to the Lanhua River. For all other roads, any remaining treated storm water rainwater will be discharged into the Chetian River. Electrical power conduit 3,269.6 Conduit only. Power lines will Leizhuang 110 kV be installed in the future by substation EIT report power company, and approved by GEPB connected to the Leizhuang 2016(3). 110 kV substation. Communications conduit 2,569.0 Conduit only. Communication Communication cables cables may be installed in the may be installed in the future by companies such as future. If so, all China Mobile and China necessary PRC permits Unicom and clearances must be obtained. Natural gas conduit 1,167.7 Conduit only. Pipeline will be Natural gas source and installed in the future by distribution network may natural gas power company. be developed in the future. If so, it will need to undergo environmental assessment as required by PRC regulations, and must obtain all necessary permits and clearances. Source: PMO, 2019.

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VI. ANALYSIS OF ALTERNATIVES

302. An analysis of project alternatives was undertaken during the feasibility phase to determine the most financially and technically feasible way of achieving the project objectives while minimizing environmental and social impacts.

A. No-Project Alternative

303. The consequences of the ‘no-project’ alternative are overcrowded road networks, poor traffic management, parking difficulties, inadequate provision and use of public transport, high traffic incidents, and increased fuel consumption and emissions that contribute to pollution and climate change. Development of the ITS, bus stations, and low emission buses is crucial for continued economic growth and sustainable urbanization. These systems are particularly important in new urban areas, where cities have the opportunity to learn from the challenges experienced in other cities and instead develop more intelligent, integrated, sustainable urban transport systems.

304. With the project, the GDAD will have an extensive, cleaner and sustainable public transport system. Overall, the benefits of the project are significant and long-term, and the no-project alternative is rejected.

B. Bus Station Locations

305. The locations of the proposed bus stations were dictated by the Public Transportation Plan of Gui’an New District (2020-2030), prepared by the China Urban Planning Design and Research Institute; the Special Plan for Integrated Transport in Core Area of Gui’an New District; and by land assigned for public infrastructure by the Gui’an Planning Bureau. Sites were selected based on factors such as population distribution, expected passenger flows, bus routes, the locations of other transport infrastructure such as subway stations, land use and land use zoning. Some proposed sites were rejected due to non-suitability, and at other sites facility boundaries were adjusted to fit local conditions.

C. Bus Types

306. A comparison was undertaken of battery powered electric buses (BEBs) to Liquefied Natural Gas (LNG) buses complying with the Chinese National (CN) vehicle emission standard V. LNG buses are currently used in Gui’an and CN V is the standard in force for new buses in China. Calculations for determination of the GHG impact were made based on direct or tank-to-wheel (TTW) emissions and indirect or well-to-wheel (WTW) emissions. The latter includes upstream fuel extraction, refinery and distribution as well as methane slip, and for electric buses emissions from the production of electricity including grid losses. Calculations were performed using the International Panel On Climate Change (IPCC) approach based on the net calorific value and the emission factor of fuels plus methane slip. The impact of BEBs on reduced NOx emissions is also included, based on combustion emissions. For other pollutants no significant impact is expected as LNG buses have only marginal PM emissions. Table 76 shows main parameters used for calculations.

307. Figure 51 compares GHG TTW and WTW emissions of LNG and BEBs per kilometer. BEBs reduce around 40% of GHG emissions compared to LNG buses (WTW comparison). GHG reductions are expected to increase as the Chinese electricity grid is getting greener (Figure 60). The average national carbon factor of the grid decreased on average 3% per annum over the last 15 years.

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Table 76: Parameters for bus type comparison environmental calculations. Parameter Value Source Number of buses 200 buses FSR Annual mileage 55,000 km Average in Chinese cities (see ADB, 2018); compatible with estimate of Gui’an bus operator Energy consumption LNG bus: 27 kg/100 km Average in 16 Chinese cities, see BEB: 1.15 kWh/km ADB, 2018 NCV and EFCO2 of LNG NCV: 48 MJ/kg IPCC, 2006 EFCO2: 56.1 gCO2/MJ Methane slip NG bus TTW: 1.3% ICCT, 2015 WTT: 2.3% Global Warming Potential of 28 IPCC, 2013 methane NOx emission LNG bus CN V 2.5 g/km EEA, 2016 based on COPERT model Carbon factor of electricity of 0.63 kg CO2/kWh Based on NDRC, 2015 published Guizhou Province in IGES, 2018 WTT mark-up factor LNG 29% UNFCCC, 2014 Source: ADB PPTA Team.

Figure 51: GHG emissions of LNG buses and BEBs.

Source: ADB PPTA Team.

308. Table 77 shows the environmental impact per bus per annum and for the fleet of 200 buses per annum and for the lifetime of buses (8 years). Additionally, electric buses have lower noise levels than LNG units although the difference is not as that large as compared to diesel units.

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Figure 52: Reductions in grid factor in China over time.

Source: Calculated by ADB PPTA Team with data from OECD and IEA; based on net electricity generation (production minus losses).

Table 77: GHG and air quality Impact of electric buses versus for Gui’an. Parameter Per bus per annum Fleet per annum Fleet lifetime GHG TTW reductions 45 tons 8,900 tons 71,000 tons GHG WTW reductions 26 tons 5,200 tons 41,000 tons NOx reductions 140 kg 28 tons 220 tons Source: ADB PPTA Team.

309. The economic value of emission reductions from using electric buses as compared to LNG was calculated based on the value per avoided ton of emissions. For CO2 the social cost of carbon taken is 300 RMB/tCO2 and for NOx the value taken for PR China is 6,770 RMB/t41. This results in annual economic savings of the fleet due to reduced emissions of 1.7 million RMB. 90% of this economic saving is due to reduced GHG emissions and 10% due to reduced NOx emissions.

D. Road Alignments and Types

310. Road alignments and types (including cross section design) were dictated in detail by the Master Plan of Gui’an New District (2013-2030), and the Detailed Control Plan for the Development of Downtown Area in Gui’an New District (2020-2030), prepared by the China Urban Planning Design and Research Institute. It is understood that various alignments were considered during the planning process.

41 Based on IMF, 2014 with USD of 2010 updated to USD 2017 and converted to RMB at an exchange rate of 6.6 RMB per USD; the social cost of carbon is the same figure worldwide whilst the NOx figure is specifically for China.

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E. Pavement Options

311. The project roads will be constructed of asphalt concrete pavement because it is relatively easy to apply and repair, and has lower traffic noise compared to rigid cement concrete. However where site conditions are suitable sections of water permeable brick will be utilized which will allow storm water to penetrate the road surface and be diverted directly to the bio-retention facilities, reducing over-road runoff.

F. Bridge Options

312. Three bridge design options were considered in the roads FSR: a diagonal-span cable-stayed arch design (Figure 53); a steel tube arch design (Figure 54); and an intertwined twin-wave arch design (Figure 55).

Figure 53: Changfeng Road Longhu Bridge, diagonal-span cable-stay arch design option.

Source: Roads FSR, 2018.

Figure 54: Changfeng Road Longhu Bridge, steel tube arch design option.

Source: Roads FSR, 2018.

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Figure 55: Changfeng Road Longhu Bridge, intertwined twin-wave arch design option.

Source: Roads FSR, 2018.

313. Based on an analysis of design and technology reliability, costs and visual appearance, the first option (diagonal-span cable-stayed arch) was selected (Table 78). However, the design selection will be finalized during detailed design after site geotechnical surveys and safety and flood assessments.

Table 78: Bridge design options. Option 1 was selected on preliminary basis. Option 1 Option 2 Option 3 Item Diagonal-span cable- Intertwined twin-wave Steel tube arch bridge stayed arch bridge arch bridge Span Main span 70m, Main span 60m, Main span 70m, Arrangement rise span ratio 1/5 rise span ratio 1/5 rise span ratio 1/7 Length 90 90 90 Surface Area m2 2,520 2,520 2,520 Complicated stress Single arch ring, easy Many member bars, may Implementation distribution, difficult to to build difficult to build construct Arch ring takes space of Flood Control Sufficient clearance clearance. May obstruct Sufficient clearance Requirement under bridge flood Maintenance Low cost Relatively low cost Relatively low cost Simple style, good Novel style, good visual Aesthetics Novel and modern style visual affect impact Cost estimates 1,512 2,120 2,530 (10,000 CNY) Source: Roads FSR, 2018.

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VII. INFORMATION DISCLOSURE, CONSULTATION AND PARTICIPATION

A. PRC and ADB Requirements for Disclosure and Public Consultation

314. Meaningful participation and consultation during project planning, feasibility study, design and implementation is an important environment safeguards requirement. It can directly reflect the public’s perceptions of environmental quality in the project’s area of influence.

315. PRC Requirements. Public participation and environmental information disclosure provisions are among the most significant changes introduced in the amended Environmental Protection Law (2014). The legislative framework also includes decrees on the methods for public participation in environmental protection (Table 1, item 20), information disclosure on construction project EIAs by government (item 22), preparation of EIA summaries for public disclosure (item 24), and technical guidelines for public participation in EIAs (Table 2, item 9). The public disclosure and consultation process undertaken during the preparation of the EIT was undertaken in compliance with the relevant PRC requirements.

316. ADB Requirements. ADB’s SPS (2009) has specific requirements for information disclosure and public consultation. Information disclosure involves delivering information about a proposed project to the general public and to affected communities and other stakeholders, beginning early in the project cycle and continuing throughout the life of the project. Information disclosure is intended to facilitate constructive engagement with affected communities and stakeholders over the life of the project.

317. The SPS requires that borrowers take a proactive disclosure approach and provide relevant information from environmental assessment documentation directly to affected peoples and stakeholders. In addition, in order to make key documents widely available to the general public, the SPS requires submission to ADB for posting on the ADB website as follows: ii) a draft full EIA (including the draft EMP) at least 120 days prior to ADB Board consideration, and/or environmental assessment and review frameworks before project appraisal, where applicable; iii) the final EIA/IEE; iv) a new or updated EIA/IEE and corrective action plan prepared during project implementation, if any; and v) environmental monitoring reports. 318. The SPS also requires that the borrower carry out consultation with affected people and other concerned stakeholders, including civil society, and facilitate their informed participation. Consultations should include presentations on environmental impacts, benefits and mitigation measures, the project GRM, and ADB's Accountability Mechanism. For category A projects, such consultations should include consultations both at an early stage of EIA field work and when the draft EIA report is available.

B. Information Disclosure during Project Preparation

319. The domestic EIT (in Chinese) is available on request at the PMO, and was disclosed on the Construction Project EIA Publicity System of the Guizhou Province website (http://202.98.194.159:6661/wwgs/index.jsp).

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C. Consultation and Participation during Project Preparation

320. Four public consultation and participation meetings were conducted during project preparation (Table 79) at sites spread across the GDAD. The sites were selected so as to maximize coverage of project activities (Figure 56).

Table 79: Summary of public consultation and participation meetings, GDAD. Date Location Relevant Project Activities - Machang Public Transportation Hub - North Fukang Road-Xuanshui Road Hub - South of Xingan Avenue Terminus August 27th, 2018 Machang Town - Machang Township Terminus - East Machang Bus Depot - Yunman Lake Hub - Comprehensive Bonded Zone Terminus - Minbo Park Terminus - Biguiyuan Hub August 29th, 2018 Huchao Town - North of the Xingyue Community Terminus - Central Area Bus Depot - Xinghu Community Terminus - Gaofeng Passenger Hub August 30th, 2018 Gaofeng Town - East of Gaofeng High School Terminus, - South University Town Hub - Gui’an Chuangu Terminus August 31st, 2018 Dangwu Town - Dongqing-Siya Road Terminus - University Town Bus Depot - High Technology Industrial Park Terminus Source: PMO, 2018.

Figure 56: Locations of public consultation and participation meetings, GDAD.

Source: PMO, 2018.

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321. The public participation and consultation meetings were organized by the EA – the Bureau of Economic Development of Gui’an (BEDGA). Letters were sent to local government officials in each meeting location (Figure 57), and the local governments organized the meetings and invited the stakeholders, with an emphasis on residents within 500 m of the bus stations. It should be noted that there are no residents live nearby Shuangxi Road-Bai Ma Avenue TA. There are also no residents living in the area of the road construction component. A total of 118 representatives from the affected areas attended the meetings.

Figure 57: BEGDA letter to local governments requesting public consultation meetings.

Unofficial Translation

To: Machang Town, Gaofeng Town, Dangwu Town and Huchao County:

For the preparation of Gui’an New District New Urbanization Smart Transport System Development Project, public participation and consultation are required to be held for related stakeholders. Please help to inform the principals of the village committees and the villagers nearby the proposed project sites and organized the public consultation in the local government office.

Attachments: 1. Agenda for the public consultation for Gui’an New District New Urbanization Smart Transport System Development Project 2. Questionnaire for Gui’an New District New Urbanization Smart Transport System Development Project Source: PMO, 2018.

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322. In the Machang Town meeting the proponent was represented by the PMO, the domestic EIT Institute (Bijie Environment Science Institute) and the Head of Machang Economic Office; and local government was represented by the Village Party Branch Secretary. In the Huchau County the proponent was represented by the PMO, the domestic EIT Institute, and the Deputy Head of Huchao Economic Office; and local government was represented by the Village Party Branch Secretary, and the Village Director. In the Gaofeng Town meeting the proponent was represented by the PMO, the domestic EIT Institute, and the Deputy Head of Gaofeng Economic Office; and local government was represented by the Village Party Branch. In the Dangwu Town meeting, the proponent was represented by the PMO, the domestic EIT Institute and the head of Dangwu Economic Office; and local government was represented by the Village Director.

323. At each meeting the PMO made a general presentation about the scope of the project including key components such as ITS, bus stations, clean energy bus procurement, charging stations, land procurement and total investment. A project briefing note was also distributed. The EIA Institute then presented the findings of the draft EIT, including potential environmental impacts and mitigation measures during construction and operation phases, and next steps. ADB’s environmental safeguard requirements with an emphasis on the implementation of the EMP and GRM were also presented. This was followed by a question and answer period (Figure 58). A questionnaire was also distributed (Figure 59 and Figure 60).

Figure 58: Public consultation meetings, September 27th to 31st, 2018.

Machang meeting. Huchao meeting.

Gaofeng meeting. Dangwu meeting. Source: PMO, 2018.

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Figure 59: Translation of the public consultation questionnaire.

Gui’an New District New Urbanization Smart Transport System Project Public Consultation Meeting Questionnaire

Name: ………………………………………………………………………………......

Occupation: ………………………………………………………………………......

Gender: ………………………………………………………………………………......

Address: ………………………………………………………………………......

1. Prior to this meeting were you aware of the proposed project? ☐ Yes ☐ No

2. If yes, how did you learn about the project? ………………………………………………………………………………………………...... …… …………………………………………………………………………………………......

3. In your opinion, what are the major environment issues in your areas? (Multiple choices OK)

☐ Outdoor air pollution ☐ Indoor air pollution ☐ Noise ☐ Surface water pollution ☐ Ground water Pollution ☐ Soil contamination ☐ Solid waste ☐ Lack of green space ☐ I do not know ☐ Other concern, please specify: ………………………………………………………………………………………………...... …… …………………………………………………………………………………………......

4. In your opinion, what are the major transportation issues in your areas? (Multiple choices OK)

☐ Lack of Public Transport ☐ Traffic Congestion ☐ Poor Quality Roads ☐ Lack of Roads ☐ Other concerns, please specify: ………………………………………………………………………………………………...... ………………………………………………………………………………………………......

5. Do you agree that the consultants have identified the main potential construction and operation phase environmental impacts?

☐Agree ☐Somewhat Agree ☐Do not Agree ☐Uncertain

6. In your view, what will be the major impacts during project construction?

☐Air pollution ☐Noise ☐Dust ☐Solid waste ☐Wastewater ☐Traffic congestion ☐Ecological Impact

Continued on next page.

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☐Other impacts (please specify):…..……………………………………………………………………… ☐No major impacts

Comments: ..………………………………………………………………………………...... ………………………………………………………………………………………………......

7. After learning about the proposed construction phase mitigation measures, do you agree that they are acceptable?

☐Agree ☐Somewhat Agree ☐Do not Agree ☐Uncertain

8. In your view, what will be the major impacts during project operation?

☐Air pollution ☐Noise ☐Dust ☐Solid waste ☐Wastewater ☐Traffic congestion ☐Ecological Impact ☐Other impacts (please specify):…..……………………………………………………………………… ☐No major impacts

9. After learning about the proposed operation phase mitigation measures, do you agree that they are acceptable?

☐Agree ☐Somewhat Agree ☐Do not Agree ☐Uncertain

10. After careful consideration, do you support the Gui’an New District New Urbanization Smart Transport System Project?

☐Yes ☐No ☐I do not know

11. What do you feel are the major benefits which the Gui’an New District New Urbanization Smart Transport System Project will bring: ………………………………………………………………………………………………...... ……………… ………………………………………………………………………………......

12. Please feel free to provide any other comments: ………………………………………………………………………………………………...... ……………… ………………………………………………………………………………...... ………………………………………………………………………………………………...... ……………… ………………………………………………………………………………...... ………………………………………………………………………………………………...... ……………… ………………………………………………………………………………...... Source: PMO, 2018.

324. In total 118 survey questionnaires were distributed, and 115 (97.5%) were completed and returned. Of those surveyed, the male to female ratio was 64:36, 85% of participants were more than 30 years old, and 43.5% of participants were already aware of the project, while the remaining 56.5% didn’t know about it prior to the public consultation.

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Figure 60: Example of completed public consultation questionnaire.

Source: PMO, 2018.

325. In terms of existing environmental issues in the GDAD, 37.4% of participants considered noise to be the most significant problem, 31.3% indicated solid waste, and 29.6% surface water pollution or groundwater pollution. In terms of potential project impacts during construction, 48.7% expressed concerns about solid waste pollution, 47.8% about noise, and 42.6% about dust. During operation, 36.5% indicated concerns about adverse impacts from solid waste, 31.3% about noise and 21.7% about dust. Most of the participants (73.9%) expect that construction and operation phase mitigation measures proposed in the EIT will be effective or acceptable, and the remaining 26.9% didn’t know.

326. With respect to their overall views on the project, 100% of participants anticipate that the project will have a positive effect on the local economy. 93.9% indicated that they support the project, 4.2% indicated that the project was acceptable, and less than 1% (one person) objected to the project. The PMO subsequently communicated with the one person who objected and the issue was lack of knowledge. The PMO provided further information about the project scope and its benefits to local society, and the person agreed to support the project.42

327. In terms of the question and answer sessions, questions were raised about both solid waste removal and construction wastewater, and the EIA Institute explained the mitigation measures that will be adopted (Table 80). However, many questions were about general operation of the transit system rather than specifically on environmental related issues.

42 PMO email, 13 March 2019.

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Table 80: Issues raised during public consultation and project proponent responses. Project Phase Issues Raised Proponent Responses Construction Domestic solid waste The PMO will negotiate with the Management Execution Bureau of Gui’an New District to reinforce the monitoring the work of environmental sanitation workers to ensure that solid waste is disposed of in a timely manner. Wastewater The wastewater on the construction site will be treated discharge and reused and no construction wastewater discharge will be allowed. Public toilets Public toilets will be included in the bus stations. Overpass There are no overpasses in the project, but there will be light controlled pedestrian crossings at all intersections. Further, if during operation station the need becomes apparent at specific locations, the Economic Development Bureau will assess the need and proceed accordingly. Charging points The project will develop 21 charging stations with 1300+ charging spaces. Once operational, the project will support the mass adoption of clean energy vehicles. Labor employment Villagers nearby the project site will be given priority in labor recruitment. If technical skills are required, training will be provided by the government. Operation Traffic accidents The government will highlight publicity for traffic safety and construct safe access to ensure public safety and security. Labor employment Villagers nearby the project site will be given priority in labor recruitment. If technical skills are required, training will be provided by the government. Source: PMO Public Consultation Meeting Minutes.

D. ICVSDZ Consultation

328. As the ICVSDZ component will be further developed during detailed design, only preliminary stakeholder consultations have been undertaken to date. This includes three meetings and site visits, as described in Appendix K.

E. Future Plans for Public Participation

329. Contractors will be required to communicate and consult with the communities in the project area of influence, especially those near the bus stations. Public notice boards will be setup at each major work site to provide information on the purpose of the project activity, the duration of disturbance, the responsible entities on-site (contractors, IA), and the project level Grievance Redress Mechanism (GRM). Contact information of all GRM entry points and the PMO will be disclosed on the construction site information boards. The GRM is presented in summary in Chapter VIII and in detail in the Environmental Management Plan (EMP) in Appendix A. In addition, the IA will be supported by the Gender, Social and Communication Specialist to develop two-way communication approaches and user-friendly tools (i.e., graphics, bulletins, and using Weibo/WeChat) not just to make up-to-date project information available and accessible but also allow stakeholder feedback. More information on how communications will support continued and regular stakeholder engagement including the dissemination of environmental information is presented in the Stakeholder Communication Strategy in Appendix J.

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330. Project environmental information has, or will be, disclosed as follows: (i) this IEE will be available for review at www.adb.org; (ii) the domestic EIT (in Chinese) is available on request at the PMO and at the Construction Project EIA Publicity System of the Guizhou Province website (http://202.98.194.159:6661/wwgs/index.jsp); and, (iii) environment progress will be reported in quarterly project progress reports and annual environmental monitoring reports, which will be disclosed on the ADB’s project website (www.adb.org).

331. With respect to the ICVSDZ component, additional detailed stakeholder and public consultation will be undertaken during detailed design, and prior to the implementation of any activities (Appendix K). The results of the consultations will be incorporated into the subcomponent design.

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VIII. GRIEVANCE REDRESS MECHANISM

A. Introduction

332. A project grievance is an actual or perceived project-related problem that gives ground for complaint by an affected person (AP). As a general policy, the PMO will work proactively toward preventing grievances through the implementation of impact mitigation measures and community liaison activities that anticipate and address potential issues before they become grievances. In addition, as the project has strong public support, significant grievance are unlikely. Nonetheless, during construction and operation it is possible that unanticipated impacts may occur if mitigation measures are not properly implemented, or unforeseen issues arise. In order to address complaints if or when they arise, a project Grievance Redress Mechanism (GRM) has been developed in accordance with ADB requirements and Government practices. A GRM is a systematic process for receiving, recording, evaluating and addressing AP’s project-related grievances transparently and in a reasonable period of time.

B. ADB Requirements

333. The ADB’s Safeguards Policy Statement (SPS, 2009) requires a project to establish a GRM to receive and facilitate resolution of AP’s concerns and complaints about the project’s environmental performance during construction as well as operation phase of the project. The GRM should be scaled to the risks and adverse impacts of the project; should address affected people’s concerns and complaints promptly, using an understandable and transparent process; should be readily accessible to all sections of the community at no cost and without retribution; and, should not impede access to the PRC’s judicial or administrative remedies.

C. Current GRM Practices in the PRC

334. At the national level a framework to address grievance has been established. State Council Decree No. 431 “Regulations on Letters and Visits” (January 2005) codifies a complaint mechanism at all levels of government, and safeguards the complainants from any retaliation. MEE “Decree No. 34 Environmental Letters and Visits System” provides specific guidelines to establish a system and address environmental complaints. When APs are negatively affected by project activities, they may complain to the contractors and the project company by themselves or through their community organizations, or complain directly to local environmental protection bureaus (EPBs). If the issue is not resolved they may take legal action, though that is typically considered as a last option. The weaknesses of the current system are: (i) the lack of dedicated personnel to address grievances; and (ii) the lack of a specific timeframe for the redress of grievances. The project GRM addresses these weaknesses.

D. Project GRM

335. The objective of the project GRM is to prevent and address community concerns, reduce risks, and assist the project to maximize environmental and social benefits. In addition to serving as a platform to resolve grievances, the GRM has been designed to (i) open channels for effective communication, including the identification of new environmental issues of concern arising from the project; (ii) demonstrate concern about community members and their environmental well-being; and (iii) prevent and mitigate any adverse environmental impacts on communities caused by project implementation and operations. The GRM will be accessible to all members of the community.

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336. The GRM approach is to deal with grievances at a local level first in an efficient manner, and escalate to higher level of authority if the grievance cannot be resolved. The PMO EHSO will be responsible for implementation of the GRM. The PMO EHSO will be supported by the social safeguards unit and the Social, Gender and Communication Specialist to develop materials and online communication tools to ensure that the GRM is promoted and made accessible to affected persons. The details of the GRM, including a time-bound flow chart of procedures, are included in the project EMP (Appendix A).

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IX. CONCLUSIONS

A. Expected Project Benefits

337. The project will benefit 1.4 million residents of the GDAD by 2030, including both public transport users and residents in general.

(i) Once operational, ridership on the bus network is expected to reach 70,000 passenger trips per day. Users will benefit from a quiet, intelligent and highly efficient, zero-emission rapid transit bus system. Residents who are non-users will also benefit from access to car charging stations, reduced traffic congestion, improved road safety, and reduced air pollution.

(ii) Traffic on the supporting roads in the core area is expected to reach a peak of 11,323 pcu/hour and total 142,540 pcu/day by 2030. Users will experience travel on a safe road network that is environmental sustainable and friendly to both non-motorized and pedestrian traffic.

(iii) An efficient public transport system will reduce the costs of transport in serving major urban and industrial areas and transport hubs, and will provide better accessibility to employment and services in the Gui’an New District. It will enhance economic growth compared to the existing public transport system.

(iv) Benefits from improved traffic flows and reduced congestion from ITS implementation include:

(a) a 50% crash rate reduction and a 5% fatality rate reduction per crash due to speed limit enforcement; (b) reduced journey time by car of 10% as a result of reduced congestion, traffic signal coordination, parking management, weather warning and incident management; (c) reduced journey time by bus of 15% and increased bus modal share by 10% as a result of a bus information management system, reduced congestion, bus priority measures, traffic signal coordination, weather warning and incident management; (d) reduced vehicle operating costs by 8% as a result of less congestion and reduced stop-start traffic conditions; and, (e) reduced vehicle emissions by 8% due to less congestion and reduced stop-start traffic conditions.

B. Adverse Impacts and Mitigation Measures

338. The project will permanently acquire 46.57 ha of land. Compensation and resettlement will be implemented which will fully meet applicable PRC and ADB applicable policies and requirements.

339. During construction, dust from construction sites, noise from power mechanical equipment, wastewater and solid wastes generated on construction sites, worker health and safety risks, and traffic disruptions will be primary adverse impacts. Good construction practice management measures will be implemented to reduce these impacts to acceptable levels.

340. Potential operation phase impacts include runoff from roads and stations which may pollute surface waters; wastewater produced at the stations; emissions from vehicles on the

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project roads; noise from stations, buses and cars; hazardous materials from bus service areas; and buses and batteries that require replacement. These impacts can be effectively mitigated through good design, including, for example, road-side bio-retention facilities to treat storm water runoff, and noise control measures incorporated into bus station design; and good waste and health management practices including effective recycling of bus batteries.

341. Operation of the project is not expected to impact any rare or endangered flora or fauna, species with international, national or provincial protection status, areas of natural or critical habitat, parks, nature reserves, or areas with special national, regional or local ecological significance within or adjacent to any of the sites. The project is not expected to impact any physical cultural resources.

C. Risks and Assurances

342. Risks. Most project components have few technical risks and conventional engineering designs with proven reliability and performance will be adopted. From an environment safeguards perspective, the main risk relates to the failure of the PMO, PIUs and operational units to monitor environmental impacts and implement the EMP during the construction and operation phases.

343. There are potential safety risks associated with autonomous ICV testing. These risks will be mitigated by (i) providing training in environmental management and ICV safety; (ii) appointing qualified project implementation consultants including an Independent ICV Expert Team; (iii) following appropriate project implementation monitoring and mitigation arrangements; (iv) ADB conducting regular project reviews; and (v) project assurances covenanted in the loan and project agreements with ADB.

344. Environmental Assurances. Assurances will form part of the loan and project agreements, including:

Project Design

GGAND shall ensure that:

(a) all Works to be carried out under the Project are designed by experienced and qualified design institutes and that sufficient counterpart funds are available for the engagement of such institutes; (b) the qualified design institutes complete relevant geological (including earthquake) and geotechnical investigations for Works in the detailed design phase in accordance with relevant national, provincial and local design codes and standards, incorporate adequate risk mitigation measures into the designs and design all infrastructure and facilities in accordance with national standards and specifications; (c) construction management, quality control, contract management, final completion and acceptance for Works comply with all applicable national, provincial and local laws and regulations; and (d) design of Project structures will include measures to address climate risks.

Operation and Maintenance

GGAND shall ensure that all Good and Works under the Project will be inspected, operated and maintained in accordance with prescribed standards, specifications and regulations, and sound practices.

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GGAND shall (a) prepare sustainable operations and maintenance (“O&M”) plans for all Project Goods and Works; (b) prepare O&M budget plans on an annual basis; and (c) provide sufficient financial and staffing resources for the relevant administrative agencies to implement the O&M plans.

Environment

GPG and GGAND shall ensure that the preparation, design, construction, implementation and operation of the Project and all Project facilities comply with (a) all applicable laws and regulations of the Borrower relating to environment, health and safety; (b) the Environmental Safeguards; and (c) all measures and requirements set forth in the IEE and the EMP, and any corrective or preventative actions (i) set forth in a safeguards monitoring report; or (ii) agreed between GGAND and ADB.

GPG and GGAND shall ensure that verification, confirmation and record of any changes in sensitive receptors be carried out during pre-construction, construction, and operation phases of the project and ensure that any new sensitive receptors are not located in the impact zones for noise and air emissions as established in the IEE.

GPG and GGAND shall ensure that the disposal and recycling of e-buses and batteries comply with the PRC Interim Measures for the Administration of Recycling and Utilization of New Energy Vehicles' Power Battery (2018).

Intelligent Connected Vehicle System Demonstration Zone (ICVSDZ) Testing

GPG and GGAND shall restrict their direct involvement to establish ICVSDZ in accordance with with the PRC Administrative Measures of Road Test for Intelligent Connected Vehicles (For Trial Implementation) ICV Testing Regulations and remain its objectivity in any ICV testing in designated zone.

GPG and GGAND shall ensure that the ICV testing comply with the PRC Administrative Measures of Road Test for Intelligent Connected Vehicles (For Trial Implementation) ICV Testing Regulations.

GGAND shall, prior to commencing road testing of any components of the ICVS, (a) submit to ADB a detailed protocol for testing approval for such component(s), including a health and safety management protocol, which shall be elaborated from the generic testing and safety protocols, in compliance with relevant PRC and SPS requirements.

GGAND shall receive ADB’s endorsement on the detailed protocols, and complete health and safety risks assessment on the ICV testing during the project, including meaningful public consultation and public information disclosure. GGAND shall ensure that a comprehensive health and safety assessment report on the ICVS is prepared and submitted to ADB within 3 months after completion of the ICVS testing. GGAND shall immediately report to ADB on any incident occurring during ICV testings.

GGAND shall make available an adequate budget for ICVS testing, ICVS health and safety due diligence, and ICVS health and safety assessment.

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Land Acquisition and Involuntary Resettlement

GPG and GGAND shall ensure that all land and all rights-of-way required for the Project and all Project facilities are made available to the Project works contractor(s) in a manner and within timeframes compliant with the RP, and that all land acquisition and resettlement activities are implemented in compliance with (a) all applicable laws and regulations of the Borrower relating to land acquisition and involuntary resettlement; (b) the Involuntary Resettlement Safeguards; and (c) all measures and requirements set forth in the RP, and any corrective or preventative actions (i) set forth in a safeguards monitoring report; or (ii) agreed between GGAND and ADB.

Without limiting the application of the Involuntary Resettlement Safeguards, GPG and GGAND shall ensure that no physical or economic displacement takes place in connection with the Project until: (a) the RP has been updated based on a detailed measurement survey and submitted to and cleared by ADB; and (b) compensation and other entitlements have been provided to the displaced persons in accordance with the applicable RP.

Ethnic Minorities

GPG and GGAND shall ensure that the Project does not have any indigenous peoples impacts within the meaning of the SPS. In the event that the Project does have any such impact, GPG shall and shall cause GGAND to, and GGAND shall, to take all steps required to ensure that the Project complies with the applicable laws and regulations of the Borrower and with the SPS.

Human and Financial Resources to Implement Safeguards and Other Requirements

GPG and GGAND shall or shall cause the Project Implementing Agencies to make available the necessary budgetary and human resources to fully implement the EMP, the RP and the SDGAP.

Safeguards – Related Provisions in Bidding Documents and Works Contracts

GPG and GGAND shall ensure that all bidding documents and contracts for Project works contain provisions that require contractors to:

(f) comply with the measures relevant to the contractor set forth in the IEE, the EMP and the RP (to the extent they concern impacts on the respective affected people under the Environmental Safeguards and Involuntary Resettlement Safeguards during construction), and any corrective or preventative actions set forth in (i) a safeguards monitoring report; or (ii) agreed between ADB and GGAND; (g) make available a budget for all such environmental and social measures; (h) provide GGAND with written notice of any unanticipated environmental, resettlement or indigenous peoples or ethnic minorities risks or impacts that arise during construction, implementation or operation of the Project that were not considered in the IEE, the EMP or the RP; (i) adequately record the condition of roads, agricultural land and other infrastructure prior to starting to transport materials and construction; and, (j) reinstate pathways, other local infrastructure, and agricultural land to at least their pre-project condition as soon as possible and no later than the completion of construction.

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Safeguards Monitoring and Reporting

GGAND shall do the following:

(a) submit safeguards monitoring reports to ADB in respect of (i) implementation and compliance with the Environmental Safeguards and the EMP, annually during the construction and implementation of the project and the EMP, and thereafter annually during operation until the issuance of the Project completion report unless a longer period is agreed; and (ii) implementation and compliance with the ADB’s Involuntary Resettlement Safeguards and the RP, semi-annually during the implementation of the Project and the RP until the issuance of the Project completion report unless a longer period is agreed in the RP; and disclose the relevant information from such reports to the respective affected people under the Environmental Safeguards and Involuntary Resettlement Safeguards promptly upon submission; (b) if any unanticipated environmental and/or social risks and impacts arise during construction, implementation or operation of the Project that were not considered in the IEE, the EMP and the RP, promptly inform ADB of the occurrence of such risks or impacts, with detailed description of the event and proposed corrective action plan; (c) no later than the commencement of land acquisition and resettlement activities, engage a qualified external monitoring agency acceptable to ADB to monitor and evaluate resettlement progress, and ensure the carrying out of any verification activities by such agency, and forward semi-annual external resettlement monitoring and evaluation reports to ADB during resettlement implementation and annually for two years after the completion of resettlement implementations; and (d) report any actual or potential breach of compliance with the measures and requirements set forth in the EMP or the RP promptly after becoming aware of the breach.

Conditions for Award of Contracts

GGAND shall ensure that no Works contract is awarded until:

(a) relevant provisions from the EMP have been incorporated into the Works contract; and (b) the RP has been finalized.

Labor Standards, Health and Safety

GPG and GGAND shall, and GGAND shall cause the PMO and contractors and service provides to (a) give equal pay for equal work regardless of gender, ethnicity or social group; (c) give priority to women in the employment and training opportunities generated in the Project’s construction and operation phases; (d) maximize the employment of local people who meet the job and efficiency requirements for Project construction, operation and maintenance; (e) provide workers with adequate on-the-job and safety training; (f) disseminate information on sexually transmitted diseases (including HIV/AIDS) and human trafficking to sub- contractors/employees and local communities surrounding the Project construction sites; (g) implement HIV/AIDS awareness and prevention training for sub- contractors/employees in collaboration with the Center for Disease Control; (h) implement human trafficking awareness activities; (i) provide necessary measures to

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ensure the safety and health of its subcontractors/ employees; and (j) observe local customs concerning acceptable behavior towards the local population.

GGAND shall ensure that the core labor standards and the PRC’s applicable laws and regulations are complied with during Project implementation and that specific provisions are included in bidding documents and contracts financed by ADB under the Project requiring that the contractors, among other things: (a) comply with the PRC’s applicable labor law and regulations and incorporate applicable workplace occupational safety norms; (b) do not use child labor; (c) do not discriminate workers in respect of employment and occupation; (d) do not use forced labor; and (e) do not restrict workers from developing any legally permissible means of expressing their grievances and protecting their rights regarding working conditions and terms of employment.

GGAND shall strictly monitor compliance with the requirements set forth above and provide ADB with regular reports.

Social Development and Gender Action Plan

GGAND shall ensure that (a) the SDGAP is implemented in accordance with its terms in a timely manner; (b) the bidding documents and contracts include relevant provisions for contractors to comply with the measures set forth in the SDGAP; (c) adequate funds and other resources are allocated for implementation of the SDGAP; (d) progress on implementation of the SDGAP, including progress toward achieving key gender outcome and output targets, are monitored and reported in semi-annual progress reports to ADB; (e) key gender outcome and output targets are met, including, but not limited to ensuring (i) women's participation during consultations with the general public in public hearings, in decision-making processes, and in any local decision-making bodies and structures; (ii) the prioritization of job opportunities for women during and after project implementation, and providing appropriate training; (iii) women are included as participating members in project-related seminars, workshops, and meetings; (iv) the collection of sex disaggregated data where appropriate; and (v) focus on women's involvement in the project-related public awareness campaigns; (f) actions under the project include (i) integrating social development aspects in [transport development planning]; (ii) giving local residents, including the poor, education, training and employment opportunities; (iii) participation of residents in project design and implementation; (iv) minimizing and mitigating adverse social impacts, including impacts of construction activities on nearby; and (v) improving public awareness on environmental management and other project-related matters; and (g) SDGAP implementation is monitored and reported in semi-annual progress reports to ADB.

Communication Plan

GGAND shall ensure that the communication plan for the Project, as described in the PAM, is fully implemented and shall devote sufficient financial and other resources to support proper implementation of all plan requirements.

Grievance Redress Mechanism

GGAND shall ensure that a safeguards grievance redress mechanism acceptable to ADB is established in accordance with the provisions of the IEE, the EMP and the RP at the PMO, within the timeframes specified in the IEE, EMP and RP, to consider safeguards complaints.

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Prohibited List of Investments

GPG and GGAND shall ensure that no proceeds of the Loan are used to finance any activity included in the list of prohibited investment activities provided in Appendix 5 of the SPS.

Governance and Anticorruption

GPG and GGAND shall, and GGAND shall cause the PMO and any other government owned or government controlled organizations involved in the Project to (a) comply with ADB’s Anticorruption Policy (1998, as amended) and acknowledge ADB's right to investigate, directly or through its agents, any alleged corrupt, fraudulent, collusive or coercive practices relating to the Project; and (b) agree to cooperate, and cause all other government offices, organizations and entities involved in implementing the Project to cooperate, fully with any such investigation and to extend all necessary assistance, including providing access to all relevant books and records, as may be necessary for the satisfactory completion of any such investigation.

GPG and GGAND shall ensure that relevant provisions of ADB’s Anticorruption Policy (1998, as amended) are included in all bidding documents for the Project, including provisions specifying the right of ADB to audit and examine the records and accounts of GPG, GGAND, the PMO, other government-owned or government- controlled entities involved in the Project, contractors, suppliers, consultants, and other service providers as they relate to the Project.

Change in Ownership

GPG and GGAND shall ensure that in the event any change in ownership or control of any of the Project facilities is anticipated, GGAND will consult with ADB at least 6 months prior to the implementation of such change and will ensure that no such change will impair its ability to perform its obligations under the project agreements or the PAM or to achieve the purposes of the ADB loan.

D. Overall Conclusion

345. The project IEE has: (i) identified potential negative environment impacts and established mitigation measures; (ii) assessed public support from the project beneficiaries and affected people; (iii) established a project GRM; and (iv) prepared a project EMP, including environmental management and supervision structure, environmental mitigation and monitoring plans, and capacity building and training.

346. It is concluded that the project will not result in adverse environmental impacts that are irreversible, diverse, or unprecedented. Any minimal adverse environmental impacts associated with the project will be prevented, reduced, or minimized through the implementation of the project EMP.

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