Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of -Pipavav--Dwarka section of NH-8E in the State of (approx length 445 km) STUP Consultants P. Ltd.

Table of Contents Executive Summary 1. INTRODUCTION ...... 1

1.1 PROJECT BACKGROUND ...... 9 1.2 THE PROJECT ...... 9 1.2.1 Project Description ...... 9 1.2.2 Objectives of the Assignment ...... 11 1.2.3 Scope of EIA ...... 12 1.3 METHODOLOGY FOR EIA ...... 12 1.3.1 Review of Policy, Legal and Administrative Framework ...... 13 1.3.2 Assessment of Baseline Environmental Status ...... 13 1.3.3 Assessment of Alternatives ...... 13 1.3.4 Assessment of Potential Impacts ...... 13 1.3.5 Integration of Environmental Assessments in the Design Process ...... 13 1.3.6 Conduct of Community Consultations ...... 13 1.3.7 Identified Mitigation & Environmental Enhancement Measures ...... 13 1.3.8 Preparation of the Preliminary Environmental Management Plan (EMP) ...... 13 1.4 PROJECT BENEFITS ...... 14 1.5 STRUCTURE OF REPORT ...... 14 2. PROJECT DESCRIPTION ...... 15

2.1 PROJECT BACKGROUND & OBJECTIVES ...... 15 2.2 PROJECT CORRIDOR CHARACTERISTICS ...... 15 2.2.1 Existing Right-of-Way (RoW) ...... 15 2.2.2 Traffic Scenario ...... 16 2.2.3 Land Use and Road side Environments ...... 17 2.2.4 Major Settlements Enroute ...... 19 2.3 SCOPE OF ENVIRONMENTAL IMPACT ASSESSMENT ...... 21 2.4 IMPROVEMENT PROPOSALS ...... 21 2.4.1 Widening Scheme ...... 21 2.4.2 Proposed Bypasses ...... 25 2.4.3 Proposed RoW Width ...... 26 2.4.4 Proposed Median Width ...... 26 2.4.5 Proposed Road Features ...... 26 TOLL PLAZA ...... 28 2.5 INTERSECTIONS ...... 28 2.6 ROAD DRAINAGE ...... 30 2.6.1 Covered Drain below Footpath in Urban Areas...... 30 2.6.2 Road-side Drain ...... 30 2.6.3 Chute Drains ...... 30 2.6.4 Additional Culvert for Field Channel ...... 30 2.6.5 Additional Culvert at Cross Road ...... 30 2.7 SOURCE OF CONSTRUCTION MATERIALS ...... 31 2.7.1 Quarries for Sand ...... 31 2.7.2 Source for Water ...... 31 2.8 GEOTECHNICAL INVESTIGATIONS ...... 32

Environmental Impact Assessment Report 1 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

2.9 HYDRAULIC AND HYDROLOGICAL INVESTIGATIONS ...... 32 2.10 ROAD SAFETY MEASURES ...... 32 2.10.1 Carriageway Markings ...... 32 2.10.2 Traffic Signs ...... 33 2.10.3 Safety Barriers ...... 33 2.11 LAND REQUIREMENT ...... 33 3. LEGAL AND INSTITUTIONAL FRAMEWORK ...... 35

3.1 LEGAL FRAMEWORK ...... 35 Legislation and Regulations: Environmental legislation, regulations and policy guidelines that may apply to this project and government agencies that administer them are summarized in Table 2.1...... 35 3.2 THE LEGAL SETTING ...... 35 3.3 CLEARANCE PROCEDURES ...... 39 3.3.1 The EIA Notification ...... 39 3.3.2 Categorisation and Clearance Requirement for the Present Project ...... 40 4. BASELINE ENVIRONMENTAL STATUS ...... 41

4.1 BACKGROUND...... 41 4.2 STUDY REGION DELINEATION...... 41 4.3 COLLECTION & COLLATION OF DATA ON ENVIRONMENTAL AND SOCIAL FEATURES ...... 42 4.3.1 Primary Data Collection ...... 42 4.3.2 Secondary Data Collection ...... 42 4.4 PHYSICAL ENVIRONMENT ...... 42 4.4.1 Climate and Meteorology ...... 43 4.4.2 Physiography and Terrain ...... 44 Soil ...... 45 Land Use ...... 46 Noise Quality ...... 49 Ecology ...... 57 Institutional Facility...... 58 Coastal Regulation Zone ...... 60 4.5 SOCIAL & CULTURAL ENVIRONMENT ...... 60 4.5.1 Social Environment ...... 60 4.6 SOCIO-ECONOMIC PROFILE ...... 61 4.6.1 Population Distribution ...... 61 4.6.2 Population Density ...... 61 4.6.3 Sex Ratio ...... 62 4.6.4 Vulnerable Population ...... 62 4.6.5 Literacy Rate ...... 62 4.6.6 Workforce Participation ...... 63 4.6.7 Right of Way ...... 63 4.6.8 Cultural Environment ...... 64 5. ANALYSIS OF ALTERNATIVES ...... 65 5.1 INTRODUCTION ...... 65 5.2 WITH OR WITHOUT PROJECT SCENARIO...... 66 5.3 ALIGNMENT SELECTION ...... 66 5.4 ALTERNATIVE PROPOSALS FOR BYPASSES ...... 67 Environmental Impact Assessment 2 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

5.4.1 Bypasses Proposed by R&B ...... 67 5.4.2 Bypasses Proposed by STUP ...... 72 6. STAKEHOLDER CONSULTATION ...... 83 7. ASSESSMENT OF IMPACTS ...... 97

7.1 INTRODUCTION ...... 97 7.2 NATURAL ENVIRONMENT ...... 97 7.2.1 Borrow Pits for Construction of Embankment and Sub-grade ...... 98 7.2.2 Quarries for Aggregates ...... 98 7.2.3 Quarries for Sand ...... 99 7.2.4 Water Resources ...... 99 7.2.5 Air Quality ...... 100 7.2.6 Noise Levels ...... 101 Roadside Trees ...... 102 7.2.7 Fauna ...... 102 7.3 SOCIAL & CULTURAL ENVIRONMENT ...... 102 7.3.1 Impact on Educational Institutes and Hospitals ...... 102 7.3.2 Impact on Cultural Environment ...... 103 8. MITIGATION MEASURES ...... 106

8.1 MITIGATION OF IMPACTS ...... 106 8.1.1 Land Resources ...... 106 8.1.2 Soil Resources ...... 106 8.1.3 Water Resources ...... 110 8.1.4 Air Pollution Control Measures ...... 113 8.1.5 Noise Control Measures ...... 114 8.1.6 Safety Measures during ...... 117 8.1.7 Construction: ...... 117 8.1.8 Bus Stop ...... 120 8.1.9 Avoidance / Enhancement Measures for Cultural Properties ...... 121 8.1.10 Highway Landscaping ...... 121 9. ENVIRONMENT MANAGEMENT PLAN ...... 123

9.1 PRE-CONSTRUCTION STAGE ...... 123 9.1.1 Pre-construction activities by PIU ...... 123 9.1.2 Pre-construction activities by BOT Concessionaire/Independent Engineer ...... 123 9.2 CONSTRUCTION STAGE ...... 123 9.2.1 Construction Stage activities by BOT Concessionaire ...... 123 9.2.2 Construction Stage Activities by PIU...... 124 9.3 OPERATION STAGE ...... 124 9.4 OTHER ACTIVITIES ...... 124 10. ENVIRONMENT MONITORING PLAN ...... 141

10.1 PERFORMANCE INDICATORS ...... 141 10.2 PLAN FOR ENVIRONMENTAL CONDITIONS ...... 142 REPORTING SYSTEM ...... 146 10.3 IMPLEMENTATION ARRANGEMENTS ...... 147 10.4 TRAINING ...... 147 Environmental Impact Assessment 3 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

11. ENVIRONMENTAL BUDGET ...... 148

11.1 ENVIRONMENTAL MANAGEMENT ...... 148

Environmental Impact Assessment 4 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

List of Tables

Table 2.1: Existing RoW ...... 16

Table 2.2: Homogenous sections on project corridor ...... 16

Table 2.3: Projected Traffic ...... 16

Table 2.4: Summary of landuse ...... 17

Table 2.5: Urban Areas along the Project Corridor ...... 19

Table 2.6: Length of Widening Options Considered ...... 21

Table 2.7: Summary of Cross Drainage Structures ...... 26

Table 2.8: List of Bus stop along the Project Corridor ...... 27

Table 2.9: Tollplaza Locations ...... 28

Table 2.10: Proposed intersection Improvements ...... 28

Table 2.11: Details of Major Intersections ...... 29

Table 2.12: Details of Intersections of Minor Intersection ...... 30

Table 2.13: Details of Quarry Area for Aggregates ...... 31

Table 2.14: Details of Sand Quarry ...... 31

Table 2.15: Location details of Water Sample ...... 32

Table 2.16: Land Requirement ...... 34

Table 3.1: Summary of Relevant Legal Requirements considered for this Project and Institution responsible ...... 36

Table 3.2: Statutory Clearance Requirements ...... 40

Table 4.1: Temperature of the Project Region ...... 43

Table 4.2: Monthly Average Humidity of the Project Region (in %) ...... 44

Table 4.3: Rainfall in the Project Districts (in mm)] ...... 44

Table 4.4: Mean Wind Speed (Kmph) ...... 44

Table 4.5: Landuse in the Project RoW ...... 46

Table 4.6: Ambient Air Quality Results ...... 47

Table 4.7: Noise Quality Results ...... 49

Table 4.8: River Crossing the Project stretch ...... 51 Environmental Impact Assessment 5 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 4.9: Ponds along the alignment ...... 53

Table 4.10: Depth to ground water level along the corridor ...... 54

Table 4.11: Water Quality Results ...... 55

Table 4.12: Road Side Tree Species ...... 58

Table 4.13: Educational Institutes along the project road ...... 58

Table 4.14: Number of Settlements along the Project Corridor ...... 60

Table 4.15: Population Distribution in talukas along the Project Corridor, 2011 ...... 61

Table 4.16: Population Distribution and Density along Project Corridor, 2011 ...... 61

Table 4.17: Sex Ratio along Project Corridor, 2011 ...... 62

Table 4.18: Share of Vulnerable Groups along Project Corridor, 2001 ...... 62

Table 4.19: Literacy Rate along Project Corridor, 2011 ...... 63

Table 4.20: Type of Workers within the Project Influence Area, 2001 ...... 63

Table 4.21: Landuse along the Project Corridor ...... 63

Table 4.22: Protected and Conserved Monuments Located in the Project Districts ...... 64

Table 7.1: Probable Soil Borrow Pits ...... 98

Table 7.2: Details of Quarry Area for Aggregates ...... 98

Table 7.3: Details of Sand Quarry ...... 99

Table 7.4: Water Contaminants, sources & receptors ...... 100

Table 7.5: Roadside Schools along project corridor ...... 102

Table 7.6: Roadside Religious Properties along project corridor ...... 103

Table 8.1: Measures to minimize air pollution during the progress of work ...... 113

Table 8.2: Locations proposed for Vegetative Barriers ...... 115

Table 8.3: Locations of Underpasses ...... 117

Table 9.1: Environmental Management Measures ...... 125

Table 10.1: Performance Indicators for the Project ...... 141

Table 10.2: Environmental Monitoring Plan ...... 144

Table 10.3: Summary Details of Reporting Formats ...... 146

Table 11.1: Environmental Costs ...... 148

Environmental Impact Assessment 6 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

List of Figures

Figure 1.1: Project Corridor...... 10

Fig – 2.2: Typical cross section for 2-Lane Highway without Service Road ...... 22

Fig – 2.3: Typical Cross Section for 2-Lane Highway without Service Road ...... 22

Fig – 2.4: cross section of 4-lane with service road ...... 23

Fig – 2.5: Typical cross section of 4-lane Flyover/Underpass with slip road ...... 23

Fig – 2.6: Typical cross section of 6-Lane with service road ...... 24

Fig – 2.7: Typical cross section of 6-Lane Flyover / Underpass with Slip Road ...... 24

Fig 5.1: Adhewada Bypass ...... 68

Fig 5.2: Budhel Bypass Option ...... 68

Fig 5.3: kobadi Bypass ...... 69

Fig 5.4: Bhandaria Bypass Option ...... 70

Fig 5.5: Tansa Bypass Option ...... 70

Fig 5.6: Trapej Bypass Option ...... 71

Fig 5.7: Una Bypass Option ...... 72

Fig 5.8: Talaja Bypass Options ...... 73

Fig 5.9: Bhadrad Bypass Options ...... 74

Fig 5.10: Datardi Bypass Options ...... 75

Fig 5.11: Hemal Bypass Options ...... 76

Fig 5.12: Samter Bypass Options ...... 77

Fig 5.13 Dholasa Bypass Option ...... 77

Fig 5.14: Chorwad Bypass Option ...... 78

Fig 5.15: Prachi Bypass Options ...... 79

Fig 5.16: Kukasawada bypass Option ...... 80

Fig 5.17: Madhavpur Bypass Options...... 81

Fig 5.18: Porbandhar Bypass Options ...... 82

Figure 8.1 Stone Pitching ...... 108

Environmental Impact Assessment 7 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Figure 8.2 Oil Interceptor ...... 109

Figure 8.28.3: Channelised Embankment: Chute Drain ...... 110

Figure 8.4: Cross-section of Silt Fencing ...... 112

Figure 8.5: Layout Plan of Silt Fencing ...... 112

Environmental Impact Assessment 8 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

1. INTRODUCTION

This chapter describes the objectives and scope of Environmental and Social study.

1.1 PROJECT BACKGROUND

The National Highways Authority of (NHAI), Government of India, has decided to take up the development of various National Highway Corridors for augmentation of capacity and for safe and efficient movement of traffic by widening to four/six lanes. Accordingly NHAI has proposed to implement the development projects for few selected sections/corridors through Public – Private Partnership (PPP) under Design, Build, Finance, Operate & Transfer (DBFOT) Pattern.

The alignment starts at Bhavnagar (km 03.200) and extends up to Dwarka (km 473.000) for a length of approximately 470 km in the State of Gujarat. In discussions with NHAI officials, the project has been extended from Dwarka to Okha for a length of approximately 30 kms that is presently SH-25. The present study corridor is the existing National Highway – 8E passing through five districts of the state of Gujarat namely, Bhavnagar, Amreli, , Porbandar and . The project road is approximately 500 km long. It starts at Bhavnagar, runs almost parallel to the southern coast of Gujarat and ends at Okha. Initially, the highway was up to and continued northwards as NH8E from here. Later on, a link was made to Chorwad from NH8E and this link continues as NH8E up to Dwaraka. From Dwarka to Okha, the existing highway is SH-25.

The project road passes through many towns like Trapej, Pipavav, Una, Somnath, Veraval, Madhavpur and Porbander, Dwarka before it ends at Okha. It also passes through many villages enroute. The project corridor has been indicated in fig 1.1.

1.2 THE PROJECT

1.2.1 Project Description

The corridors selected for the project are indicated below

1. Bhavnagar (km 3.200) to Dwarka (km 473.000) section of NH – 8E.

2. Dwarka (km 231.000) to Okha (km 261.100) section of SH – 25.

The present report on EIA deals with the environment analysis of Bhavnagar to Okha section of NH-8E and SH-25.

Environmental Impact Assessment 9 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Figure 1.1: Project Corridor

Environmental Impact Assessment 10 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

1.2.2 Objectives of the Assignment

The main objective would be to alleviate the current unsafe conditions of the road network connecting the villages and towns by providing better quality and safe roads to the users in a sustainable and Environment friendly manner.

 Enhanced safety of the traffic, the road users and the people living close to the highway

 Enhanced operational efficiency of the highway

 Fulfilment of the access needs of the local population

 Minimal adverse impact on the road users and the local population due to construction

 Feasible and constructible options for the project with least cost option.

Government of India (GOI) through Ministry of Environment and Forest (MoEF) enforces Environment (Protection) Rules, 1986 towards Environment Protection of new projects/ expansion/ modernization and existing projects based on their Environmental Impacts.

The present report is prepared in accordance with MoEF/ MoRTH Guidelines on EA and to meet the statutory requirement of MoEF, GSPCB, state forestry department, etc.

The objectives of this study are stated below:

 To present to decision makers a clear assessment of potential impact associated with the proposed project intervention,

 To apply a methodology which assesses and predict potential impacts and provides a) the means for impact prevention and mitigation, b) the enhancement of project benfits, and c) the minimization of long-term impacts;

 To provide a specific forum in which consultation is systematically undertake in a manner that allows stakeholders to have direct input to the environmental management process.

 To assess the analysis of alternatives to bring environmental considerations into the upstream stages of development planning as well as the later stage of site selection, design and implementation, and

 To recommend the environment al management measure to reduce adverse impacts.

IN order to achieve these objectives, details surveys and other studies have been carried out along the project roads to identify Valued Ecosystem components (VEC) and corridor specific significant environmental issues (SEI). For investigation/monitoring purpose the study are has been defined as under

 Corridor of Impact, CoI: is the 20 m wide strip on either side, beyond Right of Way, RoW.

Environmental Impact Assessment 11 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

 Project Influence Area, PLA: is the 10 km area on either side along the alignment.

 Project District, PD is/are the district/districts through which project road is passing.

1.2.3 Scope of EIA

The key environmental issues with regards to physical and Biological Environment highlighted during screening includes

Tree felling in forest and non-forest stretches: Since roadside trees have to be felled for road widening, adequate compensatory plantation have to be carried out to mitigate the impacts.

Generation of Solid waste: Efforts have to be made to strike a balance between cutting and filling. The remaining solid waste will be disposed off to designated dumping site after permission from local statutory authority.

With regards to the social and cultural environment the following issues are of major concern in the proposed project:

Removal of Encroachments & Squatters: In stretches of dense developments along the roadside, removal of encroachments and squatters assume a critical issue. In addition to local resistance to shifting, identification of ways and means to rehabilitate the vulnerable communities becomes significant. Though preliminary consultations reveal acceptance of the proposed project a continuous interaction with the affected communities in the later stages of the project is of immense importance.

Land Acquisition: Along with the issue of structure removal, acquisition of land too is a critical issue in India primarily in case of high value residential, commercial and agricultural lands. In the subsequent stages of the project further attempts shall be made to minimize land acquisition primarily in stretches of high land values.

Impact on utilities: Impact on utilities cause disruption to the local public during the construction stage. Widening of the corridor shall also affect permanent utilities like taps, tube wells, wells, etc. It needs to be ensured that replacement of such utilities is in place before the existing ones are closed.

Impact on Religious properties: These are sensitive properties and relocation of some may generate local resistance. Consultations in such properties shall be initiated after horizontal designs are firmed up so that the extent of impact and likely mitigation measures can be discussed with the stakeholders.

1.3 METHODOLOGY FOR EIA

The methodology followed for the Environmental Impact Assessment consists of the following steps.

Environmental Impact Assessment 12 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

1.3.1 Review of Policy, Legal and Administrative Framework

This step discussed the policy, legal framework within which the Environmental Assessment (EA) is prepared and also reviewed the existing institutions and legislations relevant to the project corridor, at the, national level and at the state level.

1.3.2 Assessment of Baseline Environmental Status

Baseline conditions within the defined area were determined as per MoEF / WB requirements for EA of highway projects. The database for working out the baseline status was from both secondary and primary sources.

1.3.3 Assessment of Alternatives

Assessment of various environmental issues due to various cross sections alternatives has been carried out.

1.3.4 Assessment of Potential Impacts

Based on the baseline conditions, the significant impacts needing mitigation have been identified. The direct and indirect impacts likely to be induced due to the project have been adequately identified and addressed.

1.3.5 Integration of Environmental Assessments in the Design Process

The design and decision-making process integrated with environmental, resettlement and rehabilitation issues have been carried out. This has prompted the early identification of appropriate actions. Such actions included, for example, shifts in alignments based on awareness of the locations of cultural resources, and biological resources.

1.3.6 Conduct of Community Consultations

Public participation and community consultation has been taken up involving public understanding of the processes and mechanisms through which developmental problems and needs are investigated and solved.

1.3.7 Identified Mitigation & Environmental Enhancement Measures

Positive actions to not only avoid adverse impacts, but also to capitalize on opportunities to correct environmental degradation or improve environmental conditions have been determined.

1.3.8 Preparation of the Preliminary Environmental Management Plan (EMP)

Environmental Management Plan (EMP) has been prepared to specify the steps necessary to ensure that the mitigation measures have been suggested. It includes the monitoring plan and gives details of the resources budgeted and the implementation arrangements.

Environmental Impact Assessment 13 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

1.4 PROJECT BENEFITS

The widening/ upgradation of the project highway have direct benefits and are indicated below: a. Improved quality of living in the project area b. Economic benefits to the local population c. Provide Employment d. Easy accesses to Agricultural Marketing e. School, Health facilities f. Enhance Environmental measures for aesthetic impacts

1.5 STRUCTURE OF REPORT

The report has been organized under the following heading, which contains the details as described below.

Chapter 2 – Project Description: The existing features present along the project corridor have been discussed in this chapter

Chapter 3 – Legal and Institutional Framework: The Legal requirements applicable to the project have been discussed in this chapter along with the Institutions enforcing them.

Chapter 4 – Environmental and Social Baseline: The physical, biological, social and cultural environments have been assessed to establish a comprehensive picture of the existing environmental / socio-economic scenario along the project corridor and its area of influence.

Chapter 5 – Analysis of Alternatives: Alternative widening and alignment options adopted to minimize impacts on the environmental, social and cultural assets have been discussed in this chapter.

Chapter 6 – Community Consultation Public consultation carried out during the project preparation stage and people’s perceptions of the project benefits and the potential impacts.

Chapter 7 – Potential Impacts: Likely impacts on environmental, social and cultural features along the roadside have been analyzed.

Chapter 8 – Mitigation Measures presents an elaborate listing of the nature of impacts on each of the environmental components and the avoidance and mitigation measures.

Chapter 9 – Environment Management Plan presents an elaborate description of the various management measures to be taken during various stages of the project.

Chapter 10 – Environment Monitoring Plan presents a monitoring plan for all performance indicators, reporting formats and necessary budgetary provisions.

Chapter 11 – Environmental Budget presents the environmental budget for the various environmental management measures proposed in the EMP.

Environmental Impact Assessment 14 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

2. PROJECT DESCRIPTION

This chapter describes the project background and also discusses the methodology adopted and structure of the present report.

2.1 PROJECT BACKGROUND & OBJECTIVES

The National Highways Authority of India (NHAI), Government of India, has decided to take up the development of various National Highway Corridors for augmentation of capacity and for safe and efficient movement of traffic by widening to four/six lanes. Accordingly NHAI has proposed to implement the development projects for few selected sections/corridors through Public – Private Partnership (PPP) under Design, Build, Finance, Operate & Transfer (DBFOT) Pattern.

The alignment starts at Bhavnagar (km 03.200) and extends up to Dwarka (km 473.000) for a length of approximately 470 km in the State of Gujarat. In discussions with NHAI officials, the project has been extended from Dwarka to Okha for a length of approximately 30 kms that is presently SH-25. The present study corridor is the existing National Highway – 8E passing through five districts of the state of Gujarat namely, Bhavnagar, Amreli, Junagadh, Porbandar and Jamnagar. The project road is approximately 500 km long. It starts at Bhavnagar, runs almost parallel to the southern coast of Gujarat and ends at Okha. Initially, the highway was up to Veraval and continued northwards as NH8E from here. Later on, a link was made to Chorwad from NH8E and this link continues as NH8E up to Dwaraka. From Dwarka to Okha, the existing highway is SH-25.

The project road passes through many towns like Trapej, Pipavav, Una, Somnath, Veraval, Madhavpur and Porbander, Dwarka before it ends at Okha. It also passes through many villages enroute. The project corridor has been indicated in fig 1.1.

2.2 PROJECT CORRIDOR CHARACTERISTICS

2.2.1 Existing Right-of-Way (RoW)

The project corridor, in general, under present consideration falls under NH divisions of R&B Department of Govt. of Gujarat namely Divisions.

The existing RoW available in the project stretch is indicated below in table 2.1.

Environmental Impact Assessment 15 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 2.1: Existing RoW From (Km) To (Km) Width (m) Left (m) Right (m) 3.200 48.000 33.5 3.5 30.0 48.000 408.000 30.0 15.0 15.0 408.000 473.000 46.0 23.0 23.0 231.000 261.000 30.0 15.0 15.0

In the seven bypasses proposed by R&B, 45m RoW is available.

2.2.2 Traffic Scenario

Passenger traffic dominates project corridor, however, the review of the data provides the impression of having considerable percentage of commercial traffic movement. The volume/capacity ratio based on available traffic data come out to be greater than one, and calls for attention towards capacity augmentation. The average speed on project corridor is about 45 kmph, which is moderate.

Looking at the corridor specific and regional characteristics along the project corridor, the project corridor can be divided into three homogenous sections as given in the Table 2.2 below. Table 2.2: Homogenous sections on project corridor

Section Homogenous Sections Length of Section (km) 1 Bhavnagar (Km 3.200) to Mahuva (Km 89.000) 85.800 2 Mahuva (Km 89.000) to Kodinar (Km 226.700) 137.700 3 Kodinar (Km 226.700) to Veraval (Km 263.000) 36.300 4 Veraval (Km 263.000) to Urang (Km 443.000) 180.000 Urang (Km 443.000) to Dwarka (Km 473.000) 5 61.100 Dwarka (Km 231.000) to Okha (Km 261.100)

Projected Traffic Table 2.3: Projected Traffic (PCU)

Homogeneous Sections 2011 2015 2020 2025 2030 2036

Bhavnagar (Km 3.200) to 32000 38896 49643 63358 80862 108362 Mahuva (Km 89.000)

Mahuva (Km 89.000) to 20000 24310 31027 39599 50539 67729 Kodinar (Km 226.700)

Environmental Impact Assessment 16 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Homogeneous Sections 2011 2015 2020 2025 2030 2036

Kodinar (Km 226.700) to 31000 37681 48091 61378 78335 104979 Veraval (Km 263.000)

Veraval (Km 263.000) to 9000 10940 13962 17819 22743 30477 Urang (Km 443.000)

Urang (Km 443.000) to Dwarka (Km 473.000) 20000 24310 31027 39599 50539 71115 Dwarka (Km 231.000) to Okha (Km 261.100)

2.2.3 Land Use and Road side Environments

The project roads start from km 3.200 at Bhavnagar to Dwarka at km 473.000 and from Dwarka at km 231.000 and traverses till Okha at km 261.100. The land use plan has been indicated in table 2.1. The following table indicates the distribution of length of project road and percentage length in terms of landuse and roadside environments. The existing landuse with the project influence area is indicated in table 2.4.

Table 2.4: Summary of landuse

S. No. Land Use % of Total Length

1 Agriculture 51

2 Commercial 9.6

3 Residential 7.4

4 Barren 32

Total 100

Environmental Impact Assessment 17 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Project corridor Project

Landuse Plan of Landuse Plan the

: :

1

.

2 Fig Fig

Environmental Impact Assessment 18 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

2.2.4 Major Settlements Enroute

Agriculture is the predominant land use along the corridor. Several educational institutions, cement concrete blocks/bricks manufacturing units have also been observed along the corridor. The project corridor has already bypassed towns of Mahuva, Kodinar, and Veraval. Apart from these, there are many settlements and ribbon developments on the corridor. Generally commercial and residential land use is seen in most of them. Details of urban areas and settlements are given in Table 2.5. Table 2.5: Urban Areas along the Project Corridor Sr.No Km From Km to Length City/Town/Villege 1 3.200 4.000 0.800 Bhavnagar 2 4.000 6.000 2.000 Adhewada 3 9.400 10.500 1.100 Budhel 4 15.400 16.300 0.900 Kobadi 5 21.100 22.500 1.400 Bhandaria 6 29.300 30.500 1.200 Tansa 7 33.200 33.600 0.400 Rajpara 8 39.750 40.400 0.650 Trapaj 9 51.000 52.400 1.400 Talaja 10 54.100 54.300 0.200 Sobhavad 11 61.400 62.100 0.700 Pasvi 12 67.400 68.200 0.800 Borda 13 70.300 70.800 0.500 Jagdhar 14 74.300 75.100 0.800 Longadi 15 86.400 87.400 1.000 Bhadrod 16 90.000 99.300 9.300 Mahua/Mahua Bypass 17 101.700 102.000 0.300 Devadia 18 107.300 108.000 0.700 Madhiya 19 109.600 110.000 0.400 Vangar 20 114.200 114.600 0.400 Datardi 21 122.000 122.100 0.100 Pipavav Port Junction 22 132.900 133.100 0.200 Chatadiya 23 134.000 134.500 0.500 Dungar parada 24 149.000 149.500 0.500 Nagasari 25 157.700 159.000 1.300 Hemal 26 161.200 161.800 0.600 Chalana 27 170.300 170.700 0.400 Goingada 28 174.800 175.200 0.400 Samter 29 180.000 186.200 6.200 Una 30 192.000 193.000 1.000 Nadholi 31 195.900 196.400 0.500 Kesariya 32 201.300 202.200 0.900 Simasi 33 205.200 207.200 2.000 Dholasa

Environmental Impact Assessment 19 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Sr.No Km From Km to Length City/Town/Villege 34 211.700 211.800 0.100 Malgam 35 222.250 226.600 4.350 Kodinar/Kodinar Bypass 36 230.900 231.200 0.300 Bittawada 37 232.000 232.400 0.400 Mordiya 38 237.000 237.600 0.600 Parasli 39 240.500 242.500 2.000 Prachi 40 248.800 250.000 1.200 Gorakhmandhi 41 256.900 257.400 0.500 Athoda 42 258.300 258.700 0.400 Sutrapada phatak 43 261.000 261.400 0.400 Kajali 44 262.800 262.900 0.100 Gadu 45 269.200 271.100 1.900 Chorwad 46 274.000 274.800 0.800 Kukasawada 47 278.400 278.900 0.500 Arena 48 285.900 290.000 4.100 Mangrol 49 292.600 293.300 0.700 Rahej 50 295.100 295.300 0.200 Loej 51 298.100 299.000 0.900 Shil 52 304.300 304.800 0.500 Aadhroli 53 309.000 309.500 0.500 Goard Madhavpur 54 310.000 312.700 2.700 Madhavpur (Ghed) 55 322.000 322.400 0.400 Gorsur 56 322.600 322.800 0.200 Mucha 57 328.000 328.300 0.300 Balach 58 332.400 332.500 0.100 Ratia 59 347.600 348.000 0.400 Ghosa 60 351.250 351.800 0.550 Gurda 61 364.000 375.800 11.800 Porbandar 62 382.100 382.500 0.400 Kuchhadi 63 386.100 386.400 0.300 Kantela 64 390.300 390.500 0.200 Ratadi 65 393.400 393.700 0.300 Palkheda 66 397.100 397.500 0.400 Visawada 67 400.600 401.300 0.700 Tukada 68 404.000 404.500 0.500 Bhavpara 69 407.400 408.300 0.900 Milyani 70 430.900 431.400 0.500 Bhogat 71 465.000 465.100 0.100 Bordiya 471.000 473.000 2.000 Dwaraka 72 231.000 233.500 2.500 Dwaraka 73 237.200 238.000 0.800 Varvala 74 251.500 254.700 3.200 Mithapur 75 255.800 256.600 0.800 Arambada Environmental Impact Assessment 20 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Sr.No Km From Km to Length City/Town/Villege 76 245.700 245.950 0.250 Mojab

2.3 SCOPE OF ENVIRONMENTAL IMPACT ASSESSMENT

Environmental impact assessment of the project will include:  Collection of baseline information on various components of the environment.  Identification of areas and aspects that is environmentally or socially significant.  Conducting community consultations on various environmental and social aspects of the project and documenting the same.  Determining the magnitude of environmental impacts and formulation of mitigation measures for consideration and incorporation during planning/design, construction and operational phases of the project implementation.  Preparation of environmental management plans including a program for monitoring environmental impacts, implementation schedule and responsibilities. It also specifies requirements of Institutional strengthening, if any, supervision program and contracting procedures for execution of environmental mitigation works.

2.4 IMPROVEMENT PROPOSALS

2.4.1 Widening Scheme

A detailed evaluation of the information collected and options described in the preceding subsections has enabled formulation of widening scheme that best suits the different stretches of the Project Road. The tentative length of proposed individual widening options along the project corridor is given in table, 2.6, below: Table 2.6: Length of Widening Options Considered Total Length S.No Widening Option Code (Km) 1 Eccentric widening on LHS while moving towards Somnath EL 62.642 2 Eccentric widening on RHS while moving towards ER 144.799 Somnath 3 Concentric CON 151.740 4 Bypass, Realignments & Curve Improvement BYP/RE 100.133 5 Flyover/ VUP/ CUP/ PUP/ RoB 38.075

Environmental Impact Assessment 21 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

CL OF CARRIAGEWAY LEFT SIDE RIGHT SIDE RIGHT OF WAY 2000 2000 1500 7000 1500 2000 2000 PROPOSED

CARRIAGEWAY

CORRIDOR CORRIDOR

UTILITY UTILITY

SHOULDER SHOULDER

EARTHEN SHOULDER PAVED PAVED EARTHEN SHOULDER

3.0% 2.5% 2.5% 3.0% 2 2 1000 1 1 1000

G.L. G.L. 1000 1000 TYPICAL CROSS SECTIONFig – 2.2: Typical FOR cross 2-LANE section for HIGHWAY 2-Lane Highway WITHOUT without Service SERVICE Road ROAD (CONCENTRIC WIDENING)CL OF CARRIAGEWAY LEFT SIDE (TYPE-1) RIGHT SIDE RIGHT OF WAY 2000 2000 1500 7000 1500 2000 2000 PROPOSED

CARRIAGEWAY

CORRIDOR CORRIDOR

UTILITY UTILITY

SHOULDER SHOULDER

EARTHEN SHOULDER PAVED PAVED EARTHEN SHOULDER

3.0% 2.5% 2.5% 3.0% 2 2 1000 1 1 1000

G.L. G.L. 1000 1000 Fig – 2.3: Typical Cross Section for 2-Lane Highway without Service Road TYPICAL CROSS SECTION FOR 2-LANE HIGHWAY WITHOUT SERVICE ROAD Environmental Impact Assessment (NEW CONSTRUCTION) 22 Rev – R0 (TYPE-2) Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

CL OF CARRIAGEWAY LEFT SIDE RIGHT SIDE RIGHT OF WAY 2000 1500 7000 15001500 2000 1500 7000 250 4500 250 7000 1500 2000 15001500 7000 1500 2000 (SERVICE ROAD) PROPOSED MEDIAN PROPOSED (SERVICE ROAD)

CARRIAGEWAY CARRIAGEWAY

DRAIN DRAIN

CORRIDOR CORRIDOR

UTILITY UTILITY

EARTHEN SHOULDER

SHOULDER SHOULDER

EARTHEN SHOULDER EARTHEN SHOULDER PAVED PAVED EARTHEN SHOULDER EARTHEN SHOULDER EARTHEN SHOULDER

2.5% SLOPE 3.0% 2.5% SLOPE 2.5% SLOPE 3.0% 2.5% SLOPE G.L. G.L. FENCE EXISTING FENCE CARRIAGWAY

Fig – 2.4: cross section of 4-lane with service road TYPICAL CROSS SECTION FOR 4-LANE HIGHWAY WITH SERVICE ROAD (ECCENTRIC WIDENING IN RHS) (MIRROR IMAGE FOR ECCENTRIC WIDENING IN LHS) (TYPE-7)CL OF CARRIAGEWAY LEFT SIDE RIGHT SIDE 46800 23400 23400 10001750 9900 3500 9900 17501000

PROPOSED CARRIAGEWAY MEDIAN PROPOSED CARRIAGEWAY

DRAIN BLOCK PAVER BLOCK DRAIN 2000 7000 PAVER 7000 2000

SLIP ROAD 2.5% SLOPE 2.5% SLOPE SLIP ROAD

CORRIDOR CORRIDOR

UTILITY UTILITY 2.5% / 3% SLOPE 2.5% / 3% SLOPE 2 2 1 1

G.L. G.L.

1000 1000

Fig – 2.5: Typical cross section of 4-lane Flyover/Underpass with slip road TYPICAL CROSS SECTION FOR 4-LANE FLYOVER/UNDERPASS WITH SLIP ROAD Environmental Impact Assessment (TYPE-12) 23 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

CL OF CARRIAGEWAY LEFT SIDE RIGHT SIDE RIGHT OF WAY

2000 7000 15001500 2000 1500 10500 250 4500 250 10500 1500 2000 15001500 7000 1500 2000

(SERVICE ROAD) PROPOSED CARRIAGEWAY MEDIAN PROPOSED CARRIAGEWAY (SERVICE ROAD)

DRAIN DRAIN

CORRIDOR

UTILITY

CORRIDOR

UTILITY

EARTHEN SHOULDER

SHOULDER SHOULDER

EARTHEN SHOULDER PAVED PAVED EARTHEN SHOULDER EARTHEN SHOULDER EARTHEN SHOULDER FENCE 2.5% SLOPE 3.0% 2.5% SLOPE 2.5% SLOPE 3.0% 2.5% SLOPE G.L. G.L. FENCE EXISTING CARRIAGWAY

TYPICAL CROSS SECTIONFig – 2FOR.6: Typical6-LANE HIGHWAYcross section WITH SERVICEof 6-Lane ROAD with (ECCENTRIC service road WIDENING IN RHS) (EXISTING CARRIAGEWAY AS LHS SERVICE ROAD) (TYPE-21)CL OF CARRIAGEWAY LEFT SIDE RIGHT SIDE 53800 26900 26900 1000 1750 13400 3500 13400 1750 1000

PROPOSED CARRIAGEWAY MEDIAN PROPOSED CARRIAGEWAY

DRAIN PAVER BLOCK

PAVER BLOCK 2000 7000 DRAIN 7000 2000 SLIP ROAD SLIP ROAD

2.5% SLOPE 2.5% SLOPE

CORRIDOR CORRIDOR

UTILITY UTILITY 2.5% / 3% SLOPE 2.5% / 3% SLOPE 2 2 1

G.L. 1 G.L.

1000 1000

TYPICAL CROSS SECTION FOR 6-LANE FLYOVER/VEHICULAR/CATTLE/PEDESTRIAN UNDERPASS Fig – 2.7: Typical cross section of 6-Lane Flyover / Underpass with Slip Road WITH SLIP ROAD (TYPE-25)

Environmental Impact Assessment 24 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

2.4.2 Proposed Bypasses

Alternative options have been studied to identify the most suitable alignment for the proposed improvement of the project road.  Along existing alignment  Along the bypass alignment

The following eighteen locations have been considered for the study of bypass:  Adhewada, Km. 4.400 – Km. 7.000  Budhel, Km. 8.500 – Km 11.060  Kobadi, Km.14.540 – Km. 17.300  Bhandaria, Km. 20.080 – Km. 23.000  Tansa, Km. 28.650 – Km. 31.150  Trapej, Km. 39.200 – Km. 41.050  Talaja, Km. 49.600 – Km. 53.500  Bhadrad, Km. 85.610 – Km. 89.000  Datardi, Km. 113.240 – Km. 115.450  Hemal, Km. 157.200 – Km. 159.850  Samter, Km. 174.025 – Km. 176.400  Una, Km. 180.400 – Km. 188.000  Dholasa, Km. 204.950 – Km. 207.000  Prachi, Km. 240.080 to Km. 243.390  Chorwad, Km. 268.600 – Km. 271.400  Kukasawada, Km. 272.800 – Km. 276.550  Madhavpur, Km. 308.600 to Km. 312.650  Porbandar, Km. 356.860 – Km. 376.300

As indicated above, total 18 nos of bypasses have been considered for the study of detailed alternative alignment of the Project Road. Out of these 18 nos of bypasses, the following 7 nos of bypasses have already been proposed by R&B department.  Adhewada, Km. 4.400 – Km. 7.000  Budhel, Km. 8.500 – Km 11.060  Kobadi, Km.14.540 – Km. 17.300  Bhandaria, Km. 20.080 – Km. 23.000  Tansa, Km. 28.650 – Km. 31.150  Trapej, Km. 39.200 – Km. 41.050

Environmental Impact Assessment Report 25 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

 Una, Km. 180.400 – Km. 188.000

2.4.3 Proposed RoW Width

The proposed Right of Way is 60 m from Bhavanagar (km3.2+000) to Veraval (km263+000).

The proposed Right of Way is 30 m from Veraval (km 263+000) to Urang (km 443+000).

The proposed Right of Way is 60 m from Urang (km 443+000) to Okha (km 501+700).

2.4.4 Proposed Median Width

The proposed median width is 4.5m in rural areas and 2.0m in urban areas.

2.4.5 Proposed Road Features

Bridges and Culverts: There are 578 numbers of Bridges and CD structures found in the entire project corridor as per Bridge inventory and condition survey.

The condition of bridges is found to be in fair condition and in few cases the carriageway has been narrowed by providing a barrier wall in order to restrict the traffic on central portion only. All such bridges have been proposed for reconstruction. The remaining bridges are mostly in good condition and just need some repair work.

The culverts found on the stretch are overall in good condition. The culverts proposed to be reconstructed are mainly those which are below 900mm diameter or fully choked in case of pipe culverts or in very poor condition in case of slab or arch culverts. The existing culverts shall be widened based on improvement proposal. All retained culverts need minor repair work only. The rehabilitation of the pipe culverts mainly require repair of headwall, cleaning of siltation in pipes and cleaning of waterway. Bed protection is to be provided for the Slab/Slab and arch culverts.

Table 2.7: Summary of Cross Drainage Structures Summary of Bridges

Sr. No. Structure Type Numbers 1 Major Bridges 30 2 Minor Bridges 187

Summary of Culverts

Sr. No. Culvert Type Numbers 1 Slab 170 2 Pipe 191

Environmental Impact Assessment 26 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Bus Stops: The list of bus stops along the project corridor is given in Table 2.8. Table 2.8: List of Bus stop along the Project Corridor Sl.No Chainage Side 1 3.200 RHS 2 4.000 RHS 3 17.700 RHS 4 19.800 RHS 5 42.700 LHS 6 133.200 LHS 7 144.000 LHS 8 148.800 LHS 9 154.000 RHS 10 161.600 LHS 11 173.700 LHS 12 178.700 LHS 13 228.000 LHS 14 232.100 LHS 15 234.600 RHS 16 251.800 RHS 17 256.600 LHS 18 281.400 RHS 19 288.500 RHS 20 292.000 RHS 21 295.300 LHS 22 300.200 LHS 23 306.600 LHS 24 325.900 LHS 25 336.500 RHS 26 350.500 LHS 27 385.200 LHS 28 389.400 RHS 29 402.950 RHS 30 405.200 RHS 31 405.950 RHS 32 424.800 LHS 33 426.800 LHS 34 436.800 RHS

Environmental Impact Assessment 27 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Toll Plaza

It is proposed to provide seven toll plazas in the project stretch. The details are indicated below in table 2.9. Table 2.9: Tollplaza Locations Sl. No Existing Km No of lanes 1 11.600 10+2 2 78.000 10+2 3 168.800 10+2 4 245.400 10+2 5 294.000 4+2 6 356.200 4+2 7 445.300 6+2

2.5 INTERSECTIONS

There are more than 224 cross roads with various categories of roads all along the corridor. All of these intersections are at-grade. Apart from these intersections, there are some additional intersections that have come up at the start and end of proposed bypasses at various urban settlements. All these new intersections are considered as important ones. There is deletion of some intersections and there is change of intersection type from T-intersection to x-intersection due to introduction of bypasses.

Accordingly, total number of intersections is divided into different categories of varying importance and developments are proposed to each category as mentioned in Table 2.10.

Table 2.10: Proposed intersection Improvements

S.NO Type Proposed Improvement Type-I: Intersections of At-grade/Grade separated intersection with Acceleration 1 prime Importance /Deceleration lane /service road and median opening Type-2:Intersections of At- Grade channelised intersections with median opening. 2 secondary importance No Acc/Dec lanes

Typical intersection drawings indicating the various elements of intersections have been developed and presented in drawing volume of this report. A) Major Intersection:

These are intersections with major category of roads like NH, SH and MDR carrying good amount of cross road traffic. Details of these intersections are given below:

Environmental Impact Assessment 28 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 2.11: Details of Major Intersections

Type of Road Going to village Sr. Existing (SH/MDR/VR) No. Km Type Left Right Left Right

1 8.990 4 Leg Sidsar SH

2 95.800 Rotary Mahua Savarkundala

3 223.100 4 Leg Kodianar Amreli

4 262.800 Tee Veraval NH

5 262.800 Tee Jetpur NH

6 286.300 Tee Mangrol MDR

7 288.000 4 Leg Mangrol Keshod SH SH

8 367.100 Tee Porbandar MDR

9 369.400 Tee Rajkot NH

10 372.200 Tee Porbandar MDR

11 375.600 Tee Jamnagar MDR

12 407.800 Tee Harshad Bagvodar VR MDR

13 431.100 Tee Bhatia MDR

14 443.500 Tee Jamnagar SH

15 473.000 Tee Dwarka Khambaliya VR SH

16 251.920 Tee LHS Mithapur CR

17 260.100 Tee LHS Okha City CR b) Minor Intersection:

This type of improvement is proposed at junctions with cross-roads of villages and access roads carrying moderate to low traffic. There are 207 minor junctions along the project corridor. Details of type of minor intersections are indicated below:

Environmental Impact Assessment 29 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 2.12: Details of Intersections of Minor Intersection Sl. No. Type of Intersection Number of Intersections

1 T 137

2 + 39

3 Y 29

4 5 Legged 2

2.6 ROAD DRAINAGE

Presence of a good drainage system is essential. In the project alignment, the following types of drains have been proposed: i) Covered Drain below Footpath in Urban Areas ii) Road-side Drain in Rural Areas iii) Chute Drains at High Embankments

2.6.1 Covered Drain below Footpath in Urban Areas

These drains are provided in urban areas, wherever there is service road. A covered rectangular RCC drain, having width of 1.5 m, with varied depth has been proposed below footpath on both sides, to drain off water from main carriageway and service road.

2.6.2 Road-side Drain

In rural areas, open unlined trapezoidal drains with 0.6 m widths and 1V: 2H side slope have been proposed near ROW on both sides of the road as per guidelines given IRC SP-42

2.6.3 Chute Drains

When the height of the embankment is more than 3.0m, the possibility of erosion of embankment slopes and shoulders increases. In such cases longitudinal kerbed drains at edge of roadway are provided to channelise the flow and are led down by lined chute drains. And these chute drains are ultimately discharged into roadside drains.

2.6.4 Additional Culvert for Field Channel

On demand by the local people, additional culvert of 1.0m dia HP (NP-4) for field channel shall be provided at bypasses to allow the water to pass from one side to other side if the lands on both side of the road belong to the same owner.

2.6.5 Additional Culvert at Cross Road

Additional culvert of 1.0m dia HP is to be provided at the cross road joining Main Carriage Way (i.e. at intersections etc.) wherever drains are passing. This size shall be increased to fulfill the

Environmental Impact Assessment 30 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd. road drainage requirement. If there is existing culvert at the crossroad, the size of the culvert shall be the maximum of the existing size of the culvert and 1.2m dia HP.

2.7 SOURCE OF CONSTRUCTION MATERIALS

Quarry Areas:

Aggregates to be used for base, surface courses and concrete works have been collected from the crushers under operation in the existing quarries. The locations, estimated quantity and the approximate distance from each source to the nearest point on the project road are compiled in Table 2.13. Table 2.13: Details of Quarry Area for Aggregates

Sr.No Chainage Side Distance Location 1 9.000 Left 2 Km Bhikada 2 17.000 Left 3 Km Ukhalla 3 51.000 Right 10 Km Road 4 134.000 Right 20 Km Rajula 5 184.000 Left 17 Km Girgaradha 6 204.000 Right 5 Km Near Dolasa 7 223.000 Right 35 Km Dronaki 8 240.000 Right 15 Km Rampara 9 331.000 Left 2 km 10 408.000 Right 6 Km

2.7.1 Quarries for Sand

Sand samples have been collected from two sand sources and tested. Table 2.14 shows the location of these sand quarries. Locations of these quarries are provided in Table 2.14. Table 2.14: Details of Sand Quarry

Existing km Source of Sand

149.426 Nagasari 175.000 Datakdi

2.7.2 Source for Water

There are no perennial rivers in the vicinity of the project corridor. The discharges of the rivers are maximum during rainy with visible impurities such as clay and discharge reduces to minimum in dry season.

A total of nine water sources were identified and details are shown in Table 2.15.

Environmental Impact Assessment 31 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 2.15: Location details of Water Sample

Existing km Name of the source

49.565 Shetranji River 86.655 Bhadrodi River 88.937 Butiyo River 94.380 Malan River 134.593 Datakdi River 183.179 Machchundari River 223.215 Shingoda River 262.122 Hiranya River 339.223 Bhadar River

The suitability of these identified water sources is to be checked before incorporation of construction works as per IS 456-2000.

2.8 GEOTECHNICAL INVESTIGATIONS

Geotechnical Investigations have been carried at proposed bridge locations to explore subsurface conditions by drilling boreholes to different depths in order to identify the thickness and sequences of various strata and to ascertain the subsurface profile of soils and bed rock to determine the most suitable foundation level of structures.

2.9 HYDRAULIC AND HYDROLOGICAL INVESTIGATIONS

All the hydraulic data for bridges has been collected from the field and it has been analyzed and studies carried out to determine the adequacy of waterway of the existing bridges proposed to be retained and new bridges to be constructed as per provisions of IRC: 5-1998 and IRC: SP-13.

2.10 ROAD SAFETY MEASURES

2.10.1 Carriageway Markings

Carriageway markings have been designed primarily to delineate lane positions to encourage lane discipline and safety. The MOST details in "Type Design for Intersection on National Highways" provide good guidelines. Also IRC Code IRC: 35-1997 gives recommendations regarding carriageway markings.

Notable features of the provisions are: i) Traffic lane lines shall be single broken lines. Their width shall be 100 mm and the length of segments and gaps shall be as under.

 On straight reaches, 1.50 m segments and 3.0 m gaps.

Environmental Impact Assessment 32 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

 On curves and approaches to intersections 1.50 m segments and 1.50m gaps.

The colour of lane markings is white and it is visible in the dark under car/truck head lights. ii) Continuous white lines, 150 mm wide are used to show the extent of the travelled carriageway.

2.10.2 Traffic Signs

The traffic sign’s design is standardised for mandatory/regulatory types are as per standard IRC- 67 design.

Some of the signs will be in the verges mounted on steel posts in the usual manner. On the approaches to junctions, overhead signs mounted on gantries have been designed. This enables the signs to span the road and allow the driver on the moderately high speed road to easily read the sign and take appropriate action.

The signs are proposed to be bi-lingual, in English and .

The minimum letter size is 150mm and is in accordance with the guidelines.

Hectometer/Kilometer stones and Marker Posts, Marker Stones are proposed at each kilometer as is the practice on the Urban Roads.

2.10.3 Safety Barriers

Two types of safety barriers have been proposed: i) Rigid Barriers  Rigid barriers are proposed on bridges, the details of which are provided in the volume containing the design of standard drawings. ii) Flexible Barriers

Flexible metal beam crash barriers are proposed at high embankment locations & bridge/flyover approaches & the details are indicated in drawings volume.

2.11 LAND REQUIREMENT

For widening of project road land needs to be acquired. The total land required for the project is 1280.64 ha. Details are indicated in table 2.16.

Environmental Impact Assessment 33 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 2.16: Land Requirement S. No. Land Use Land (ha) 1 Agriculture 653.13 2 Commercial 122.94 3 Residential 94.77 4 Barren 409.80 Total 1280.64

Environmental Impact Assessment 34 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH- 35 8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

3. LEGAL AND INSTITUTIONAL FRAMEWORK

The present chapter discusses the legal framework of the present project and the stakeholder agencies that have to be duly consulted for its effective implementation.

3.1 LEGAL FRAMEWORK

The environmental regulations, legislation, policy guidelines and control that may apply to this project are the responsibility of a variety of government agencies. The following agencies would play an important role in this project.

Ministry of Environment and Forests (MoEF): The primary responsibility for administration and implementation of the Government of India’s (GoI) policy with respect to environmental management, conservation, ecologically sustainable development and pollution control rests with the Ministry of Environment and Forests (MoEF). Established in 1985, the MoEF is the agency primarily responsible for the review and approval of Environmental Impact Assessments (EIAs) pursuant to GoI legislation. The Ministry of Environment and Forests (MoEF) has set up regional offices, with each region having an office. The office for the present project is located at .

Gujarat State Forest Department: The Gujarat State Forest Department is responsible for the protection and managing the forest designated areas within the state. At the state level, the through Principal Chief Conservator of Forests (PCCF) is empowered to declare reserved and protected forests. It has also been given the authority to acquire land for extension and preservation of forests. The Forest Department works out Forest Working Plans for the various forest divisions to manage and protect the forest resources. These plans form the basis for managing the forest resources and for chalking out specific plans and policies with respect to the conservation, protection and development of the forest areas. The department is also responsible for granting clearances for projects as per the provisions of the Forest (Conservation) Act, 1980.

Legislation and Regulations: Environmental legislation, regulations and policy guidelines that may apply to this project and government agencies that administer them are summarized in Table 2.1.

3.2 THE LEGAL SETTING

The Government of India has laid out various policy guidelines, acts and regulations for protection of environment, which have been summarized in the table below:

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Table 3.1: Summary of Relevant Legal Requirements considered for this Project and Institution responsible

National Level Acts Responsible National Act Year Objective Institution Environment (Protection) Act. To protect and improve the overall 1986 MOEF, CPCB environment Notification on Environment Impact To provide environmental clearance Assessment of Development projects to new development activities (and amendments) (referred to as the 2006 following environmental impact MOEF, CPCB Notification on Environmental assessment. Clearance) Coastal Regulation Zone Regulations, To restrict the establishment or 1991 & and Notifications on Coastal Regulation expansion of industries, operation subsequent MOEF zone. or process between the High Tide amendments and Low Tide Lines. Wildlife Protection Act To protect wild animals and birds 1972 through the creation of National MoEF Parks and Sanctuaries Forest (Conservation) Act 1980 To protect and manage forests MoEF Water (Prevention and Control of To provide for the prevention and Pollution) Act (and subsequent control of water pollution and the 1974 CPCB amendments) maintaining or restoring of wholesomeness of water. Air (Prevention and Control of Pollution) To provide for the prevention, Act (and subsequent amendments) control and abatement of air CPCB and 1981 pollution, and for the establishment Transport of Boards to carry out these Department purposes. Central Motor Vehicle Act Central Motor To control vehicular air and noise Vehicle Rules 1988 pollution. To regulate development Motor Vehicle 1989 of the transport sector, check and Department control vehicular air and noise pollution. Ancient Monuments and Archaeological Conservation of Cultural and Archaeological sites and Remains Act historical remains found in India. Dept. GOI, Indian Heritage Society 1958 and Indian National Trust for Art and Culture Heritage (INTACH).

I. Summary of National Acts:

Water (Prevention and Control of Pollution) Act 1974 resulted in the establishment of the Central Pollution Control Board whose responsibilities include managing water quality and effluent standards, as well as monitoring water quality, processing offenders and issuing licenses for construction and operation of any facility. This includes the generation of liquid effluent during road construction, including from residential construction camps.

Air (Prevention and Control of Pollution) Act 1981 empowers Central Pollution Control Board to set air quality and emission standards, monitoring air quality, prosecute offenders and issuing licenses for the construction and operation of any facility. Air quality includes noise level standards. This act has notified National Ambient Air Quality Standards for different activities, e.g. Industrial, Residential and Sensitive.

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Environment Protection Act 1986: This act was passed as an overall comprehensive act for protection and improvement of the environment. The requirements for Environmental Clearance under this Act have been described above. Under this Act rules have been specified for discharge/emission of effluents and different standards for environment quality. These include standards for Ambient Noise, Emission from Motor Vehicles, Mass Emission Standards for Diesel and Petrol Driven vehicles, and General Effluent Standards. These standards are of direct relevance for road construction projects.

Coastal Regulation Zone (CRZ) Notification: Through the CRZ Notification dated 19th February 1991, the Ministry of Environment and Forests (MoEF), Government of India declared the coastal stretches of seas, bays, estuaries, creeks, rivers and backwaters which are influenced by tidal action (in the landward side) up to 500 metres from the High Tide Line (HTL) and the land between the Low Tide Line (LTL) and the High Tide Line (HTL) as Coastal Regulation Zone and imposed certain restrictions on the setting up and expansion of industries, operations or processes, etc in the said Coastal Regulation Zone (CRZ).

The CRZ areas are classified into four categories based on their environmental and ecological sensitivity and significance. Their permissible and prohibitory activities are also classified accordingly.

Protection of Cultural Places: With regard to the cultural aspects of the environment, the Indian constitution states that, ’it shall be the duty of every citizen of India to value and preserve the rich heritage in the nation, both government agencies and NGOs concerned with the preservation and conservation of this heritage have been established.

The Archaeological Survey of India (ASI) is the oldest organization concerned with conservation in India and continues to be an important organization, working on the protection and conservation of monuments and archaeological sites. It is supported in its endeavors by the State level Directorates of Archaeology and it administers the Ancient Monuments and Archaeological Sites and Remains Act 1958. There are numerous NGOs interest groups involved in the conservation of cultural property in India including the Indian Heritage Society (HIS). The Indian National Trust for Art and Cultural Heritage (INTACH) has regional chapters in most states and is the largest such NGO. It acts as a reference for government agencies on conservation issues. However, there are no such archaeological sites in this project area.

II. Summary of State Acts:

The Felling of Trees (Infliction of Punishment) Act 1951: This act is for taking the permission from Forest and Environment Department of Government of Gujarat for felling of tress of Limdo, Baval, Kanji, Khijdo, Ambo and Amli under Saurashtra Felling of Trees (Infliction of Punishment) Act, 1951 and this shall be required in case of above trees cut within the distance of 200 meters from the edge of the National Highways, State Highways and District Roads, Notified urban areas and notified ecosensitive areas and within 5 Kms of the boundary of Reserved Forest, Sanctuaries, National Parks, Sea coast and Desert. Environmental Impact Assessment 37 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Gujarat State Pollution Control Board: The Gujarat State Pollution Control Board has the mandate for environmental management at the state level, with emphasis on air and water quality. The board is responsible for:  Planning and executing state-level air and water initiatives;  Advising state government departments on air, water and industry issues;  Establishing standards based on National Minimum Standards;  Enforcing and monitoring of all the activities within the state under the Air Act, the  Water Act, the Water Cess Act and the Environment Protection Act; and  Issuing No-objection certificates (NOC) for the projects in accordance with the water  (Prevention and Control of Pollution) Act of 1974, the Water Cess Act of 1977 and the  Air (Prevention and Control of Pollution) Act of 1981.

Gujarat State Coastal Zone Management Authority: The Central Government constituted an authority to be known as the Gujarat State Coastal Zone Management Authority in supersession of the Notification of the Government of India in the Ministry of Environment and Forests Number 999 (E) dated, the 26th November, 1998. The Authority has the power to take the following measures for protecting and improving the quality of the coastal environment and preventing, abating and controlling environmental pollution in the coastal areas of the State of Gujarat and examine proposals for changes or modifications in classification of Coastal Regulation Zone areas and in the Coastal Zone Management Plan (CZMP) received from the Gujarat State Government and making specific recommendations to the National Coastal Zone Management Authority therefor . Authority has its headquarters at Gandhinagar, Gujarat. The Authority deals with environmental issues relating to Coastal Regulation Zone which may be referred to it by the Gujarat State Government, the National Coastal Zone Management Authority or the Central Government. The Authority identifies:

- Ecologically sensitive areas in the Coastal Regulation Zone and formulate area-specific management plans for such identified areas.

- Coastal areas highly vulnerable to erosion or degradation and formulate area specific management plans for such identified areas.

- Economically important stretches in Coastal Regulation Zone and prepares Integrated Coastal Zone Management Plans for the same.

Water (Prevention and Control of Pollution) Act 1974 resulted in the establishment of the State Level Pollution Control Board whose responsibilities include managing water quality and effluent standards, as well as monitoring water quality, processing offenders and issuing licenses for construction and operation of any facility. This includes the generation of liquid effluent during road construction, including from residential construction camps.

Air (Prevention and Control of Pollution) Act 1981 empowers State Pollution Control Board to set air quality and emission standards, monitoring air quality, prosecute offenders and issuing licenses for the construction and operation of any facility. Air quality includes noise level standards. This act has notified National Ambient Air Quality Standards for different activities, e.g. Industrial, Residential and Sensitive. Environmental Impact Assessment 38 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Quarrying and Other Materials Extraction: All rock, aggregates and sand for construction will be obtained from designated quarries and other sources such as river beds which are under the regulatory control of the Department of Land and Land Revenue of GOG. Mining projects (including quarries) with leases of more than 5 hectares fall into the Schedule I group of activities requiring Environmental Clearance from MOEF. Other quarrying activities require Environmental Clearance from DOE. Where quarries are located on forested lands, Forest Clearance is required from the MOEF or the GOG Forests Department.

3.3 CLEARANCE PROCEDURES

3.3.1 The EIA Notification

As per the provisions of the new amended EIA Notification dated 14th September 2006, the requirement for Environmental clearance has been quoted below: REQUIREMENT FOR SEEKING ENVIRONMENTAL CLEARANCE

“Categorization of projects and activities i) All projects and activities are broadly categorized into two categories-Category A and Category B….. ii) Category A: New National Highways and Expansion of National Highways greater than 30 km involving additional right of way greater than 20m involving land acquisition. iii). Category B: New State Highways and Expansion of State Highways greater than 30 km involving additional right of way greater than 20 m involving land acquisition.”

Procedure for Environmental Clearance: The application seeking prior environmental clearance is to be made in the prescribed Form I annexed to the notification and Supplementary Form IA, if applicable, as given in Appendix II of the notification, after the identification of prospective site for the project and /or activities to which the application relates, before commencing any construction activity, or preparation of land, at the site by the applicant. The environmental clearance process for new projects comprises of four steps, which are,

Screening ( only for Category B projects or activities) will entail the scrutiny of application (Form 1) by the concerned State Level Expert Appraisal Committee (SEAC) for determining whether or not the project requires further environmental studies and preparation of Environmental Impact Assessment Report for grant of environmental clearance. Projects requiring EIA Report are termed Category B1 and the remaining as Category B2.

In Scoping, the EAC (for Category A projects) and SEAC (for Category B projects) determine detailed comprehensive Terms of Reference (TOR) for the preparation of the EIA Report in relation to the project for which environmental clearance is sought. The TOR would be determined on the basis of information furnished in Form 1/1A.

Public Consultation: All Category A and B1 projects have to undertake Public Consultation (except expansion of Roads and Highways which do not involve any further acquisition of land). Public Hearing and Consultation shall be done by the SPCB.

Appraisal of the Final EIA.Report by EAC/ SEAC for grant of environmental clearance.

Environmental Impact Assessment 39 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

3.3.2 Categorisation and Clearance Requirement for the Present Project

The present project alignment is a National Highway greater than 30 km in length and involves additional right of way greater than 20 m, hence has been considered under Category A. Thus, environmental clearance is required for the project (as per MOEF Notification, September 2006). In view of this, a screening report along with Form 1 (duly filled in) and Draft Terms of Reference (TOR) has been submitted to the Ministry of Environment and Forests (MoEF) for their perusal and comment.

The existing legislation and policies relevant to the project at the National and State levels have been reviewed and identified. The clearance requirement for the project at various stages of the project is described below. Table 3.2: Statutory Clearance Requirements Sl Statute under which clearance is Clearance Required for Statutory Authority No required 1. Environmental Clearance EIA Notification, 2006 issued under Ministry of Environment and Forest, GOI, EP Act, 1986 New Delhi 2. Coastal Zone Clearance Coastal Zone Regulation,1991 Gujarat Coastal Management Authority, Ministry of Environment and Forest, GOI, New Delhi It is observed that about 63 kms of land is observed in the coastal regulatory zone and adequate clearances shall be obtained from the concerned Authority 3. Permission for felling of The Saurashtra Felling of Trees Forest Department, Gujarat. Roadside trees (Infliction of Punishment) Act 1951 Tree Enumeration along with Girth and Height parameters have been completed on the field and the same has been submitted to the concerned forest officials for verification. 4. No Objection Certificate EIA Notification, 2006 issued under Gujarat Pollution Control Board. EP Act, 1986 Water (P&CP) Act, 1974 & Air (P&CP) Act, 1981

Environmental Impact Assessment 40 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH- 41 8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

4. BASELINE ENVIRONMENTAL STATUS

The present chapter describes the physical, biological, social and cultural environment along the project corridor and its immediate influence area.

4.1 BACKGROUND

Previous chapters have highlighted scope of environment assessment, existing features of the road and proposed improvement, methodology and regulations applicable to environmental assessment. In this chapter an attempt has been made to prepare a baseline environmental setting so as applicability of Government of India (GoI) regulatory requirements could be envisioned. Based on the existing environmental scenario potential impacts of road improvement will be identified and accordingly management plan will be proposed in forthcoming sections. The baseline environmental conditions will help in comparing and to monitor the predicted negative and positive impacts, significant less adverse revised impact, resulting from the project during construction and operation phases.

Data was collected from secondary sources for the macro-environmental setting like climate, physiography (Geology and slope), biological and socio-economic environment. First hand information have been collected to record the micro-environmental features within and adjacent to the project corridor. Collection of first hand (Primary) information includes preparation of base maps, extrapolating environmental features on proposed road design, tree enumeration, location and measurement of socio-cultural features abutting project road.

Data was also recorded at sites used for extraction of materials for construction but generally outside the project corridor e.g. borrows areas and quarries. Ambient Air, Noise and water quality sample were collected at important locations in terms of environment quality to prepare a baseline database. Consultation was another source of information to explain local conditions like submergence, recent floods etc. However, these consultation results were largely base on short term memories like information on floods, submergence but still it was helpful in comparing secondary information.

Following section describes the nature, type and characteristics of the physical, biological, cultural and socioeconomic components along the project roads.

4.2 STUDY REGION DELINEATION

The study region has been divided into:

Corridor of Direct Impact: This includes the area adjacent to the existing road, roughly 60m on either side of the existing centerline. Minor alignment changes, widening, curve improvements, etc. is expected to directly affect the land and assets located in this region.

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Corridor of Indirect Impact: This includes the region within 15km offset of the road centerline on either side.

4.3 COLLECTION & COLLATION OF DATA ON ENVIRONMENTAL AND SOCIAL FEATURES

The data on the various environmental and social components relevant to decisions about project location, design and operation have been assembled from:  Primary Survey of the corridor, and  Secondary information collected from various organizations, institutes, publications, etc.

4.3.1 Primary Data Collection

The primary data collection along the project corridor has been carried out with respect to the following features:

Environmental Features: Environmental features that may be directly impacted are trees along the roadside, water bodies like ponds, wells and water crossings, agriculture lands, plantations, forest stretch etc. Apart from these, environmentally sensitive locations like educational institutions; hospitals etc have also been recorded.

Social Features: Social features that may be affected include loss of land and structures within the proposed RoW. The type of structures i.e. residential, commercial, mixed uses (residential cum commercial), public, educational institutions and health facilities have been recorded. The structures have been further classified as kutcha, semi-pucca and pucca. To ascertain the impact on land and structures, the RoW limits are being verified on the field.

Cultural Component: The cultural properties along the project corridor including shrines, temples, mosques, churches and graveyards have been listed.

4.3.2 Secondary Data Collection

Secondary data collection has been collected primarily on regional environmental and social features from various Government Agencies/Institutions and through literature reviews. Such information includes:

Hydrogeological Atlas of Gujarat, Central Ground Water Board,

Socio-economic profile of the influence area along the project corridor: The database for analysis has been taken from Census of India (1991 & 2001) and other secondary sources.

4.4 PHYSICAL ENVIRONMENT

The physical environment consists of environmental attributes such as meteorology, physiography, geology, soil quality, land use, water resources, air quality and noise levels. Each attribute has been detailed subject to the available data constraints. Environmental Baseline

Environmental Impact Assessment 42 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd. characteristics of the project area have been described for the region comprising of a 15 km offset on either side of the road centerline for the project corridor.

4.4.1 Climate and Meteorology The climate of both the districts is characterized by a hot summer and dryness in the non-rainy seasons. The cold season from December to February is followed by the hot season from March to May. The south-west monsoon season is from June to September and is followed by the post monsoon season from October to November.

Temperature: The mean maximum temperature in the region reaches 41C in the warmer months from March to June. During the winter season, in December-January, the minimum temperature dips to 12.2C and the maximum temperature remains around 29C. The lowest average monthly minimum temperature is around 21C. The average monthly maximum and minimum temperature of the project region as recorded during the period 2009 by the Indian Meteorological Department (IMD) is presented in Table 4.1 below. Table 4.1: Temperature of the Project Region

Months Jan Feb Mar April May June July Aug. Sept. Oct. Nov. Dec.

Bhavnagar Mean 12.2 16.9 18.8 22.9 25.9 27 25.6 24.5 24.2 21.7 19.2 14.1 Minimum Mean 28.9 32.1 35.6 41.1 41.2 38.1 33.3 31.6 33.2 35.8 34.4 29.7 Maximum Amreli Mean 12.3 16.2 18.2 22.7 25.9 27.1 24.8 25.4 24.8 22.3 18.2 15.2 Minimum Mean 29.3 32 35.5 38.6 36.6 37.6 34.6 32.4 34.2 34.9 33.4 27.4 Maximum Junagarh Mean 16.2 18.9 20.4 24 27 27.7 27.7 25.7 25.9 23.1 21.1 18 Minimum Mean 30 30.1 32.9 33.5 32.3 33.3 31.6 29.9 31.3 34.2 33.4 30.7 Maximum Porbander Mean 13.2 15.4 17.3 23.5 26.5 ------Minimum Mean 30.1 32.1 34.5 38.5 37.4 ------Maximum Jamnagar Mean 14.2 18.4 21.2 26 26.6 28.1 26.8 24.8 26.4 24.2 20.1 17.6 Minimum Mean 29 29.8 31.4 34.5 31.4 32.1 30.9 30.2 31.8 34.3 34.2 29.5 Maximum Based on IMD Observation from 2009

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Humidity: The maximum humidity is observed to be 92.00 percent (Amreli) during the month of August. The minimum humidity is recorded at Jamnagar (26 percent) during the month of January. The monthly variation of humidity in the project region is presented in Table 4.2 below. Table 4.2: Monthly Average Humidity of the Project Region (in %) Months Jan Feb Mar April May June July Aug. Sept. Oct. Nov. Dec. Bhavnagar 8.30 56 75 67 76 79 82 87 87 78 68 63 57 17.30 54 68 62 71 81 86 81 85 81 65 59 62 Amreli 8.30 54 73 60 73 82 84 88 92 86 65 67 58 17.30 51 64 67 72 74 80 85 88 80 65 68 54 Junagarh 8.30 55 76 67 74 78 79 85 83 79 82 79 82 Porbander 8.30 54 72 65 75 79 ------17.30 52 69 61 66 85 ------Jamnagar 8.30 55 79 62 76 76 80 88 91 89 72 74 66 17.30 26 36 22 19 32 56 69 76 65 35 36 36 Based on IMD Observation from 2009

Rainfall: Maximum rainfall occurs under the influence of the South West monsoons (June- September). The annual rainfall is around 1097mm. Table 4.3: Rainfall in the Project Districts (in mm)] Months Station Jan Feb Mar Apr May Jun July Aug Sept Oct Nov Dec Bhavanagar 0 0 0 0 0 262.3 124.2 101.2 96 1.4 - - Amreli 0 0.5 0 0 0 211.3 142.2 109.2 255.8 0 0 0 Junagarh 0 1.3 0 0 0 185.3 132.6 121.3 194.3 0 0.6 0 Porbander 0 0 1 0.2 0 184.2 156.2 141.2 185.2 1.2 0 0 Jamnagar 0 1 0 0.1 0 195.4 176.3 221.3 156.2 0 29.2 0 Based on IMD Observation from 2009

Wind Speed: The most predominant wind speed in the region is 1-19 Kmph. Wind speed above 62 kmph is not found to occur, those in the range of 20-61 kmph is also rare for Keshod. Calm (0 kmph) conditions also prevail in Veraval. Table 4.4: Mean Wind Speed (Kmph) Months Station Jan Feb Mar Apr May Jun July Aug Sept Oct Nov Dec Veraval 12.16 13.49 15.15 14.5 15.2 20.3 25.15 19.64 10.8 11.68 9.9 13.795 Based on IMD Observation from 2009

4.4.2 Physiography and Terrain The project region is located in Bhavnagar, Amreli, Junagadh, Porbandar and Jamnagar districts in Gujarat. Bhavnagar district is situated in the south-east corner of the peninsular region of

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Gujarat known as '' of Saurashtra''. It lies between the parallels of latitude 200.59' and 220.16' and the meridians of longitude 710.23' and 720.18'. The length from north to south of this territory is about 151.7 kms and from east to west about 108.6 kms. Bhavnagar district forms a part of Kathiawar Peninsula and is subdivided into four submicro regions, namely, Bhavnagar Coastal Plain, Palitana-Savarkundal Upland, Songadh Forested Plain and Keri, Kalubhar and Ghelo Plain on the basis of topography, climate, geology, soils and natural vegetation. It is bounded in the north by Surendranagar and Ahmadabad districts and in the west by Rajkot and Amreli districts and in the south by the east by the Gulf of Kambhat. The area covered by the district is 9,981 Sq. kms.Areawise rank of this district is 6th among the districts of the state.

Amreli is located near the in the Arabian Sea, in the western part of Gujarat. It lies between the parallels of latitude 70.30º and 71.75º and the meridians of longitude 20.45º to 22.25º. The district has 11 talukas, of which the major ones are Amreli, Babra, Bagasara, Jafrabad, Rajula, Savarkundla and Vadi

Junagadh district is situated at Saurashtra region and form part of the Kathiawar peninsula. It lies between the parallels of latitude 20°41’ and 21°41’ and the meridians of longitude 69°56’ and 71°13’. It is sub divided into four sub-micro regions namely, Junagadh coastal plain, Bhadar, Ojat and Harna river plain, hills and Junagadh Gir forested Region. The elevation of the region falling in Mangrol, Manavadar, Keshod, Malia and Patan-Veraval talukas varies between 5 metres and 52 metres above the M.S.L in the Junagadh Coastal Plain. Some parts of Mangrol, Manavadar, Keshod, Malia, Patan-Veraval, Vanthali, Junagadh talukas falls in the Bhadar, Ojat and Harna River Plain which elevates between 45 metres and 241 metres above M.S.L.

Porbandar forms a part of the erstwhile Kathiawar peninsula located in the western part of Gujarat. It lies between the parallels of latitude 69.550 and 70.25and the meridians of longitude 21.15 to 21.5. The district comprises of 3 talukas viz. Porbandar, Ranawav, and Kutiyana It is famous for the birthplace of Mahatma Gandhi – the Father of the Nation.

Jamnagar is located in Saurashtra region of western Gujarat. It lies between the parallels of latitude 68°57’ and 70°37’ and the meridians of longitude 21°42’ and 22°57’. The district has 10 talukas, of which the major ones are Jamnagar (District Headquarter), Jodiya, Okha, and Khambhaliya. The district is famous for its brass products, (bandhani) tie-dyed fabric, and handicrafts The proposed alignment traverses through fertile plain terrain along its entire length.

Soil Salty land which is mainly the type of land in Morbi and Maliya and Black, loamy soil which is mainly present in Bhavanagar, Amreli and Dwaraka, districts. The soils of the project region that falls in are formed partly from sedimentary rocks and partly from igneous rocks. They are calcareous in nature, rich in potassium content but deficient in nitrogen and humus. The main types of soils in the district are black, medium black, alluvial soil in the low-lying area, calcareous and brackish.. Most of the villages in Junagadh have medium black soil. The alluvial Environmental Impact Assessment 45 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd. soil in the low-lying area, known as ‘Ghed’, comprises parts of Keshod, Mangrol and remains inundated during monsoon. The brackish soils are mostly found near the coastal belt of Mangrol, Malia and Veraval talukas and represent the degeneration of coastal alluvial soil due to ingress of sea water.

Land Use The geographical area in the five districts can be divided into two major classes: arable land: that includes net sown area, fallow land and non-arable land: that includes forest, area not available for cultivation and other uncultivable land excluding current fallow. The proposed alignment runs through five districts, major portion being through Junagarh. The alignment mainly runs through agriculture land; water bodies in the form of ponds, rivers and canals also fall within the proposed Right of Way (ROW). At places, the alignment also runs through a few settlements and structures.

The land use on either side of the cross roads is mostly agricultural, only at certain locations structures are being affected. The locations where comparatively more number of structures are present along the alignment are – Talaja, Veraval, Somnath and Porbandar.

The total landuse of the project corridor within the RoW is broadly classified and presented in Table 4.5. Table 4.5: Landuse in the Project RoW S. No. Land Use % To Total 1 Agriculture 51 2 Commercial 9.6 3 Residential 7.4 4 Mixed 32 Total 100

Air Quality Ambient air quality in a region is characterized by concentrations of various pollutants in the atmosphere. The presence of air pollutants and their concentrations depends on the type of polluting sources, and other factors that influence their flow and dispersion. In most cases vehicular emissions are the predominant source of air pollution. Existing ambient air quality data on various sections of the project corridors was collected to establish a baseline database. The aim was to identify areas that already have high pollution levels or are expected to experience so, on account of the road project, and to design adequate mitigation measures, as applicable.

The activities, which generate modify atmospheric air quality, are transportation (i.e, motor vehicle emissions, which are addressed in this study); industry; domestic and construction. The principal sources of air pollution due to road projects are hot mix plants and machineries used during construction phase and the vehicles that ply over it during the operation phase. The parameter of significance to roadside air quality, on account of vehicular emissions, are suspended particulate matter (SPM), Respirable particulate matter (RPM), sulphur dioxide (SO2), nitrogen oxides (NOx), hydrocarbons (HC), carbon-monoxide (C). Environmental Impact Assessment 46 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Dispersal of pollutants depends upon factors like prevailing wind direction and other weather conditions, height of the source, and characteristics of roadside plantation along the project corridor.

The air polluting sources in the project region primarily consist of industries and the vehicles plying on the roads. A total of 15 ambient air monitoring stations were identified based on the different existing land use pattern to study the ambient air quality along the project corridor and are indicated in fig 4.1. The ambient air quality in the corridor was found to be in compliance with the ambient air quality norms stipulated by CPCB/GPCB. The results of ambient air quality monitoring are indicated in table – 4.6. Table 4.6: Ambient Air Quality Results Pollutant Concentration (µg/m3) Monitoring Chainage Station Area Category 24 hourly mean values Location (km) RSPM TSPM SO2 NO2 HC CO

AQ1 Junction 8.900 179.45 345.69 12.85 21.06 Nil 654 Residential, AQ2 School 52.300 Rural & other 164.59 290.45 13.06 22.25 Nil 598 Areas AQ3 School 92.375 149.56 282.5 12.56 19.45 Nil 1452

AQ4 School 116.900 150.55 234.55 10.09 14.42 Nil 1236 Residential, AQ5 School 148.600 Rural & other 160.89 389.29 11.56 26.54 Nil 1090 Areas AQ6 Industry 184.270 178.45 384.88 15.46 21.45 Nil 1450

AQ7 School 188.450 165.75 290.56 14.45 20.52 Nil 1260 Residential, AQ8 School 211.900 Rural & other 167.48 301.15 12.5 15.12 Nil 1350 Areas AQ9 School 237.200 170.84 315.64 12.56 17.56 Nil 1058

AQ10 Junction 262.800 145.89 298.54 14.5 16.87 Nil 1265 Residential, AQ11 School 288.700 Rural & other 147.26 294.52 13.56 17.45 Nil 1165 Areas AQ12 School 322.100 170.84 269.89 15.45 14.6 Nil 1452

AQ13 Industry 366.000 139.11 350.45 10.56 14.56 Nil 1235 Residential, AQ14 Junction 443.500 Rural & other 147.26 309.12 13.56 15.46 Nil 658 Areas AQ15 Junction 473.000 156.12 312.54 10.12 12.09 Nil 985

NAAQ Norms* (8/24 Hourly Mean) 100 200 80 80 2000

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ting Air Quality Monitoring Locations along Project corridor Project along Locations Monitoring Quality Air ting

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Environmental Impact Assessment 48 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Monitoring Results The TSPM range is 234.55 µg/Nm3 to 389.29 µg/Nm3. The total particulate concentration at 50% of location is less than 288 µg/Nm3. The higher concentrations of TSPM are attributed to anthropogenic activities, major settlements, unpaved road conditions, minor industrial areas, dryness, semi-arid conditions and loose dust particles along the project corridors.

In most of the samples, RSPM is 50% higher than the prescribed standard. All gaseous pollutants like SO2, NO2, HC and CO are well within the prescribed limits of statutory bodies.

Noise Quality

To assess background noise levels in the study area, ambient noise monitoring is conducted. A total of fifteen (15) locations were identified along the project road, based on different categories of area and are indicated in fig 4.2.

Ambient noise level or sound pressure levels (SPL) are measured by a portable sound level meter having built in facilities to read noise level directly in dB(A). From the SPL values, equivalent continuous sound pressure level values (Leq) are calculated. Noise measurement is conducted as per IS: 4954 as adopted by CPCB.

Ambient noise level monitoring has been carried out during Febraury 2011. At each location monitoring was conducted continuously over a period of twenty- four hours to obtain Leq values at uniform time intervals of 1 hour. From the hourly Leq values, day and night Leq values are calculated to compare with the national ambient noise standards. Description of the noise monitoring stations and the Leq values at each station are given in Table 4.7. Table 4.7: Noise Quality Results Noise Levels, dB(A) Day Time Night Time Overall Station Chainage Type Category (06:00-22:00 hrs.) (22:00-06:00 hrs.) Leqmin. Leqmax. Leqmin. Leqmax. Leqmin. Leqmax. NL1 8.900 Junction Commercial 37.1 62.56 34.0 58.6 34.0 62.56 NL2 52.300 School Commercial 40.5 65.33 33.4 57.6 33.4 65.33 NL3 92.375 School Commercial 44.7 67.86 36.8 61.9 36.8 67.86 NL4 116.900 School Commercial 43.2 66.78 36.8 63.2 36.8 66.78 NL5 148.600 School Commercial 41.2 64.23 36.1 57.2 36.1 64.23 NL6 184.270 Industry Commercial 39.1 61.87 30.4 61.3 30.4 61.87 NL7 188.450 School Commercial 40.5 65.23 33.4 60.8 33.4 65.23 NL8 211.900 School Commercial 38.7 66.23 34.0 55.1 34.0 66.23 NL9 237.200 School Commercial 34.0 61.28 33.2 57.2 33.2 61.28 NL10 262.800 Junction Commercial 40.3 66.83 37.6 58.4 37.6 66.83 NL11 288.700 School Commercial 40.5 68.56 34.0 55.1 34.0 68.56 NL12 322.100 School Commercial 34.8 60.88 34.2 54.8 34.2 60.88 NL13 366.000 Industry Commercial 37.2 64.46 34.9 58.5 34.9 64.46 NL14 443.500 Junction Commercial 34.4 62.43 33.8 58.3 33.8 62.43 NL15 473.000 Junction Commercial 36.5 61.48 34.6 55.4 34.6 61.48 Leq Norms for Residential Areas - 55 - 45 - - Leq Norms for Commercial Areas - 65 - 55 - - Environmental Impact Assessment 49 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Monitoring Locations along Project corridor Project along Locations Monitoring

Noise Level Noise

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Overall the Leq noise level range is 30.4 to 68.56 dB(A). During daytime, the noise level ranges from 34-68.56 dB(A). During the night time, the Leq range is 30.4 to 61.9 dB(A). The higher noise levels have been observed in commercial areas.

Water Resources

Surface Water: The project region Passes through five Districts i.e, Bhavnagar, Amerli, Jungadh, Poranbandar and Dwarka. The rivers that cross the project road are indicated in fig 4.3. All the rivers are non perennial, rainfed and are tributaries of the Arabian Sea which is the main Coastline of the project area. The rivers are used for washing, cleaning and cultivation. The list of rivers crossing the project highway is indicated in table 4.8.

Table 4.8: River Crossing the Project stretch Station Existing km Name of the source WQ1 49.565 Shetranji River WQ2 86.655 Bhadrodi River WQ3 88.937 Butiyo River WQ4 94.380 Malan River WQ5 134.593 Datakdi River WQ6 183.179 Machchundari River WQ7 223.215 Shingoda River WQ8 262.122 Hiranya River WQ9 339.223 Bhadar River

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onitoring Locations along Project corridor Project along Locations onitoring

er Quality m Quality er

Wat

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There are a number of ponds along the project road. Their locations have been indicated in table 4.9. Table 4.9: Ponds along the alignment Existing Km Side Existing Km Side 16.600 LHS 330.000 RHS 30.200 LHS 330.900 - 331.500 LHS 30.130 RHS 331.350 RHS 32.600 RHS 332.000 RHS 35.500 LHS 332.200 LHS 62.200 LHS 350.700 RHS 67.000 RHS 350.700 LHS 68.700 RHS 370.000 LHS 122.700 LHS 380.240 LHS 158.500 LHS 381.000 - 382.600 LHS & RHS 194.420 LHS 386.300 RHS 201.200 RHS 386.400 RHS 208.700 RHS 393.650 LHS 216.860 RHS 397.580 RHS 225.750 RHS 403.950 RHS 264.700 LHS 410.200 LHS 277.570 RHS 410.700 RHS 281.400 LHS 410.700 LHS 281.400 RHS 411.400 LHS 295.800 LHS 417.200 RHS 310.400 RHS 417.200 - 417.800 LHS 310.500 RHS 468.500 LHS & RHS 316.750 LHS

Ground Water: This categorization is attributed to the level of extraction of ground water against increased domestic, industrial and irrigation requirements. The extraction is higher in the region of Saurashtra.

The districts were categorised as Gray zone and the availability of the ground water along the corridor varied between from 5 to 20 m below ground level (bgl) during pre-monsoon (May 2002), while during post monsoon (November 2002) it has varied from less than 5 to 10 m bgl (Table 4.10). It is considerably depending on aquifer geology, geomorphology and rainfall. South-West monsoon is the main source of ground water recharge for the entire area of the corridor. Ground water is also a source of irrigation in the area. Drinking water is available through borewell.

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Table 4.10: Depth to ground water level along the corridor

Depth to Water level (mbgl) S.No. District Pre Monsoon Post Monsoon (May 2002) (November 2002) 1 Bhavnagar Greater than 20 m Greater than 20 m 2 Amerli 10 – 20 m 5 – 10 m 3 Junagadh 10 – 20 m 5 – 10 m 4 Poranbandar 5 – 20 m 5 – 10 m 5 Jamnagar 5 – 20 m 5 – 10 m

Source: Central Ground Water Board

Description / Km Km Km Km Km Km Sl. No. Location 15.115 90.865 174.900 248.150 340.150 467.100 1 pH 7.7 7.9 7.5 7.6 7.7 7.8 2 DO 4 6 5 3 2 4 3 BOD 1.8 1.6 1.2 1.4 1.7 1.9 4 COD 4 3 2 2 4 3 5 Chloride 208 293 280 217 229 262 6 Alkalinity 360 422 265 315 356 383 Total Coliform Count 7 Absent MPN/100 ml. 8 Total hardness 151 172 125 133 147 165

The ground water sources had agreeable colour, taste and odour. The pH value ranged between 7.5 to 7.9, generally above the neutral mark and within the permissible limits for dirinking water. Chloride values ranged from 208 mg/l to 293 mg/l thus, within ther permissible limits. BOD is also absent. There is no significant bacteriological contamination of these sources. Total alkalinity is found to be within permissible limits. Total hardness ranged between 125 – 172 mg/l. Heavy metals like iron, zinc, arsenic mercury, lead, cadmium, chromium and selenium are absent.

In general, the ground water quality in the project corridor is found to be in compliance with IS:10500 Standard for Drinking Water.

Surface Water Quality: The water quality of Setranji, Bhadrodi, Butiyo and Datakdi rivers were taken for monitoring the surface water quality. Borewells are the major source of water for drinking and other domestic purposes in villages and towns.

The results of the water quality tests are given in Table 4.11.

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Table 4.11: Water Quality Results RIVER Sl. IS:10500 Parameter No. WQ1 WQ2 WQ3 WQ4 WQ5 WQ6 WQ7 WQ8 WQ9 - 2001 Setranji Bhadrodi Butiyo Malan Datakdi Machchundari Shingoda Hiranya Bhadar

1 Colour Clear Colour Less - 2 Odour Odour Less - 3 Turbidity (NTU) 3 2 4 3 1 4 1 2 4 - 4 pH (Unit) 7.7 7.36 7.72 7.41 7.81 7.69 7.7 7.49 7.54 6.5-8.5 Temperature 5 28 31 33 29 32 30 31 29 31 - (Deg. C)

Total Dissolved 6 600 158 510 550 490 502 496 533 510 500 Solids (mg/l)

Ether Soluble 7 8 3 5 6 4 7 6 9 8 - (Oil & Greece)

Total Hardness 8 179 132 182 146 196 169 175 151 157 300 as CaCO3 (mg/l) 9 Chloride (mg/l) 131 210 180 173 165 202 217 184 192 250 10 Sulphate (mg/l) 78 65 58 52 60 55 69 49 65 200 11 Phosphate (mg/l) 1 1 2 1 1 2 1 2 1 -

Bio Chemical Oxygen Demand 12 5 8 3 16 7 5 8 11 13 - (3 Days at 27 C) (mg/l)

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RIVER Sl. IS:10500 Parameter No. WQ1 WQ2 WQ3 WQ4 WQ5 WQ6 WQ7 WQ8 WQ9 - 2001 Setranji Bhadrodi Butiyo Malan Datakdi Machchundari Shingoda Hiranya Bhadar

13 Lead (mg/l) NIL - 14 Arsenic (mg/l) NIL - 15 Iron (mg/l) NIL 0.3 Total Coliform 16 48 32 35 69 38 44 66 48 37 500 (MPN/100 ml)

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The pH value ranged between 7.36-7.81. TDS content ranged between 158-600 mg/l while Chloride values ranged from 131 to 210 mg/l respectively, well below the tolerance limits. Iron content is found to be nil. There is no significant presence of trace metals in the surface waters. There is no faecal contamination as the Oil and grease, toxic constituents like phenolic compounds and cyanides are found to be absent.

While comparing with the CPCB Norms for Surface Waters, all parameters are found to be within the standard limits.

Ecology

Forests

The forest areas of Gujarat are unevenly distributed. The major concentration of forests is found all along the eastern border of the state and the hilly portion of Saurashtra. Reserve forest for conservation of Neelgai has been identified on either side of the project stretch in Bhavnagar district. The forests are found mainly in the district Junagadh. Tropical Dry Deciduous Forests thrive in the region having the rainfall between 600 mm to 1200 mm. These forests are found in the central part of the state in parts of Saurashtra in the districts of Junagadh. Northern Tropical Thorn Forests occur in the region with less than 600 mm rainfall. These forests are found in Rajkot and Junagadh districts. These forests contain spare and stunted growth of species like Acacia and thorn bushes etc. Littoral and Swamp Forest, Mangrove forest are found in the coastal creeks in the districts of Junagadh. The main species found in these forests is Avicenia sp. Out of 207 subtypes of forests, recorded by Champion and Seth, 31 subtypes, (14.7%) have been identified in the state.

Sensitive Ecological Habitats/ Ecosystems

No sensitive ecological habitats or ecosystems are identified within the direct influence area of the project corridor. The details are discussed below.

Flora: Teak, dudhlo, khair, ber, desi baval, dhav, hermo, sadad, timru, ashitro, saledi, modad, khakhro etc.

Fauna: The Gir forests support a rich biodiversity comprising 32 species of mammals, 300 species of birds and 26 species of reptiles and thousands of species of insects.

Flora and Fauna in the Study Area

Flora: The flora in the project area comprises of roadside trees, fruit trees in certain villages besides the vegetables and crops grown in the agriculture lands.

Roadside Plantation: The common tree species found along the roadside are given in Table 4.12. Fruit trees are observed in certain locations along the corridor: Guava, mango, coconut, Sofeda and banana garden.

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Table 4.12: Road Side Tree Species Sl No Common Names Scientific Names 1. Amla Emblica officinalis 2. Arduso Ailanthus excelsa 3. Bor Zizyphus glabrata 4. Desibaval Acacia nilotica 5. Gando baval Prosopis juliflora 6. Gundo Cordia dichotoma 8. Jambu Syzygium cumini 9. Karanj Derris indica 10. Khair Acacia chundra 11. Khajuri Phoenix sylvestris 12. Khijdo Prosopis cineraria 13. Limdo Azaditachta indica 14. Mitosaragavo Moringa oleifera 15. Piplo Ficus religiosa 16 Rayan Manilkara hexandra 17. Sag Tectona grandis 18. Sisam Dalbergia latifolia 19. Vad Ficus benghalensis

Fauna: Local Fauna in the project area includes reptiles like crocodile, tortoise, gecko, garden lizard owing to the large number of water bodies and fruit gardens in the area. Common animals like dogs, cats and cattle are also present.

Institutional Facility

These include schools, colleges and hospitals along the project road. There are 55 institutions along the project road. There are primary schools upper primary high school and higher secondary schools. In most of the educational institutes, the boundary wall is located close to the existing road but the building is quite far from the road with a playground in front of the school building. They have been enlisted below.

Table 4.13: Educational Institutes along the project road

Sr.No Existing Km Side 1 9.460 Left 2 21.900 Left 3 30.085 Right 4 36.700 Left 5 39.570 Right 6 44.650 Right 7 52.300 Left 8 61.500 Left 9 86.776 Right

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Sr.No Existing Km Side 10 91.150 Left 11 92.375 Right 12 97.700 Right 13 98.630 Right 14 98.700 Left 15 99.600 Right 16 107.400 Left 17 116.900 Left 18 118.000 Left 19 148.600 Left 20 158.600 Right 21 160.500 Left 22 182.750 Right 23 174.950 Right 24 177.600 Left 25 182.800 Left 26 188.450 Right 27 192.850 Right 28 196.600 Right 29 201.500 Left 30 206.050 Left 31 211.900 Left 32 232.400 Left 33 237.200 Left 34 251.300 Left 35 256.400 Left 36 268.360 Right 37 274.400 Left 38 278.300 Right 39 278.850 Left 40 288.250 Right 41 288.700 Left 42 288.900 Left 43 295.200 Right 44 310.000 Right 45 322.100 Right 46 332.300 Right 47 344.000 Left

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Sr.No Existing Km Side 48 367.800 Right 49 369.400 Right 50 379.800 Left 51 385.500 Left 52 397.400 Right 53 404.250 Left 54 405.250 Right 55 427.200 Left

Coastal Regulation Zone The project corridor falls under CRZ –III as per Coastal Zone Regulation Notification, January, 2011 issued by MoEF, GOI. As per CRZ Notification, 2011, CRZ III includes areas that are relatively undisturbed and those which do not belong to either Category-I or II. These will include coastal zone in the rural areas (developed and undeveloped) and also areas within Municipal limits or in other legally designated urban areas which are not substantially built up. As per the guidelines of Gujarat Coastal Zone Management Authority for obtaining CRZ clearance, a map clearly demarcating HTL and LTL along with other proposed activities, landuse within 5 km radius, latitude and longitude has been prepared by an external agency authorized by MOEF and has been submitted with the State Department, Gandhinagar.

4.5 SOCIAL & CULTURAL ENVIRONMENT

4.5.1 Social Environment The project corridor passes through five Districts namely Bhavnagar, Amreli, Junagadh, Porbandar and Jamnagar. 119 villages and 11 urban areas would be directly impacted, 37 in Bhavanagar, 18 in Amreli, 27 in Junagadh, 29 in Porbandar and remaining in . Details of each of the districts are presented in Table 4.14. Table 4.14: Number of Settlements along the Project Corridor S. No District Urban Villages 1 Bhavanagar 4 37 2 Amreli 2 18 3 Junagarh 5 27 4 Porbandar 2 29 5 Jamnagar 1 12 Total 14 119

Therefore, in order to understand the socio-economic profile of the influence area of the project corridor, a micro-level analysis is essential. The aerial unit for analysis of the socio-economic profile of the influence area of the project corridor includes all traversed villages, urban and forest areas. Though the corridor passes through five administrative districts, for better appreciation, all socio-economic characteristics have been analyzed.

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4.6 SOCIO-ECONOMIC PROFILE The socio-economic profile along the project corridor takes into account the socio as well as the economic aspects:  Population Distribution;  Density of Population;  Gender Ratio;  Share of Vulnerable Groups and  Literacy Rate  Workforce Participation Ratio and  Sector-wise Distribution of Workers 4.6.1 Population Distribution The project influence area comprises of five districts namely, Bhavnagar, Amreli, Junagadh, Porbandar and Jamnagar. The growth rate of population in the project influence area is 3.17 % which is higher than the average growth rate of population in the state (2.06%). The highest population growth rate is 4.66% recorded in Veraval taluka of Junagadh district followed by 4.46% in Junagadh taluka. In rest of the talukas, growth ranges between 1% to 2%. Jetpur taluka of has registered the lowest growth rate of 0.77%. Talukawise demographic characteristics in project influence area are presented in Table 4.15. Table 4.15: Population Distribution in talukas along the Project Corridor, 2011 Population District AAGR (01-11) 2001 2011 Bhavanagar 2469630 2877961 0.87 Amreli 1,393,295 1513614 0.92 Junagarh 2448173 2742291 0.89 Porbander 536,854 586062 0.92 Jamnagar 1,913,685 2159130 0.89 Project Influence Area 8,761,637 9,879,058 0.89 Gujarat State 50671017 60383628 0.84 Source: Population Totals of Gujarat, Census of India, 2011 and 2001; Note: Figures are rounded of to first decimal place

4.6.2 Population Density The project influence area has population density of about 135 to 277 persons per sq.km in 2001 and 153 to 310 persons per sq.km in 2011. In 2011, the population density for Gujarat State is 382 persons per sq.km and 325 persons per sq.km in 2001 amongst all the districts (Table 4.16). Table 4.16: Population Distribution and Density along Project Corridor, 2011 Population Density(Persons/Sq km) District 2001 2011 Bhavanagar 247 288 Amreli 188 205 Junagarh 277 310 Porbander 234 255 Jamnagar 135 153 Gujarat state 325 382 Source: Census of India, 2011 Environmental Impact Assessment 61 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

4.6.3 Sex Ratio

As per the Census estimates (2011) number of Sex ratio (females/1000 male) of project influence area is about 931 to 964 The Sex ratio for the state of Gujarat is 940. All the districts have shown a decrease in sex ratio from 2001-2011 (Refer Table 4.17).Amongst all the districts, registered the highest sex ratio with an increase from 946 in 2001 to 947 in 2011. A decline in sex ratio is observed in four districts of project influence area during 2001- 2011 in accordance with the decline observed at state level. Table 4.17: Sex Ratio along Project Corridor, 2011 Sex Ratio (Number of Females per District 1000 Males) 2001 2011 Bhavanagar 937 931 Amreli 987 964 Junagarh 955 952 Porbander 946 947 Jamnagar 941 938 Gujarat state 933 940

Source: Population Totals of Gujarat, Census of India, 2011 Note: Figures are rounded of to first decimal place

4.6.4 Vulnerable Population

The percentage distribution of scheduled caste is higher than scheduled tribes in project influence area. Bhavnagar, Amreli, Junagarh and Jamnagar district has a higher percentage of SC population (percentage of SC population to total population in the state). Details indicated in Table 4.18. Table 4.18: Share of Vulnerable Groups along Project Corridor, 2001 Population 2001 % to Total Population District SC ST SC ST Bhavanagar 142198 7298 3.96 0.10 Amreli 115490 3256 3.21 0.04 Junagarh 235624 18832 6.56 0.25 Porbander 48233 6456 1.34 0.09 Jamnagar 154819 10459 4.31 0.14 Gujarat state 3592715 7481160 7.09 14.76 Source: Population Totals of Gujarat, Census of India, 2001 and 1991;

4.6.5 Literacy Rate

As per the Census estimates (2001), 69 percent of the population are literate in the State, where as the average literate rate is lower (67 percent) in the project influence area. Within the project influence area, Junagadh district has the highest literacy rate (76.88 percent) followed by Porbandar (75.63 percent) and Amreli (74.5 percent). The lowest literacy rate was observed in Bhavnagar (69.84 percent). Details indicated in Table 4.19.

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Table 4.19: Literacy Rate along Project Corridor, 2011 Literates Literacy Rate (%) District 2001 2011 2001 2011 Bhavanagar 1395205 1927573 66.98 69.84 Amreli 8141151 1001768 67.22 74.50 Junagarh 1432422 1876761 68.35 76.88 Porbander 320053 400196 69.09 75.63 Jamnagar 1048894 1417294 67.19 74.4 Gujarat State 29827750 41948677 69.97 79.31 Source: Census of India, 2011

4.6.6 Workforce Participation

As per the Census estimates (2001), has 33.72 percent of main workers among males and 15.04 percent among females. The details are indicated in Table 4.20. Table 4.20: Type of Workers within the Project Influence Area, 2001 Main Workers Marginal Workers Total Workers Non- Workers S.No District Among Among Among Among Persons Persons Persons Persons Females Females Females Females 1 Bhavnagar 31.63 11.18 6.62 10.87 38.25 22.05 61.75 77.95 2 Amreli 33.72 15.04 9.38 15.98 43.1 31.02 56.9 68.98 3 Junagadh 32.09 11.86 8.79 14.67 40.88 26.52 59.12 73.48 4 Porbandar 32.34 11.1 7.74 12.32 40.07 23.42 59.93 76.58 5 Jamnagar 32.77 12.25 5.79 9.18 38.56 21.43 61.44 78.57

Source: Director of census operations, Gujarat state.

4.6.7 Right of Way

The extent of Public Land adjacent to the project Corridor was collected from the Department of Land Revenue. Knowledge of extent of land was required to restrict development within the public land and thereby reducing private land acquisition. District and Block wise land use is presented in the Table 4.21 below. Table 4.21: Landuse along the Project Corridor

Permanent Area Under Barren & Pasture & Geographical Reporting Non- District Forest Unculturable Other Area Area Agriculture Land Grazing Use Land

Amreli 6760 6720 339 385 225 471 Bhavanager 11155 9789 315 724 1017 709 Jamnagar 14125 10152 425 640 1562 774 Junagadh 10607 10561 1976 525 310 1115 Porbandar 11203 11042 359 698 1025 868 Gujarat 196117 188118 18648 11414 26038 8491 State

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Area Sown Total Culturable Other Current Net Area More Then Cropped Wasteland Fallow Fallow Sown Once Area 96 22 201 4981 234 5215 307 12 417 6288 206 6494 331 15 655 5750 181 5931 120 0 592 5923 550 6473 130 2 678 7282 323 7605 19818 131 9109 94989 12028 107017 Source: Census of India, 1991

4.6.8 Cultural Environment

Baseline Information on Cultural Environment is presented for the project corridor. This includes heritage structures as well as those having local and regional significance.

4.6.8.1 Protected Sites & Monuments

There are three significant protected sites or monuments in the immediate vicinity of the project corridor. Within the 10 km offset of the corridor the following monuments are of State level significance. Table 4.22: Protected and Conserved Monuments Located in the Project Districts Places of Interest / Distance District Taluka Religious Importance (in KM) Bhavnagar Talaja Jain Temple 1.00 Junagadh Veraval Somnath Temple 1.00 Jamnagar Dwarka Temple 2.00

4.6.8.2 Cultural Properties of Local /Regional Significance

There are about 123 religious structures that exist along the project road; most of them are stiuated within 30m from the edge of the carriageway. The widening has been designed such that most of these structures remain unaffected or least affected due to the proposed project.

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5. ANALYSIS OF ALTERNATIVES

This chapter presents the various alternatives considered for minimizing the impacts on natural, social and cultural environments, at the preliminary design stage.

5.1 INTRODUCTION

This chapter presents a comparative analysis of various alternatives considered to avoid or minimize impacts that would be inevitable if technically (based on design speed and geometrics) best fit alignment is followed. Cross sections adopted for the upgradation component as presented in Chapter 1 are flexible in design to avoid most of the impacts within ROW. An analysis of various alternatives is attempted to arrive at the technically and environmentally best- fit alternative considering environmental and project attributes

There are large settlements as seen in the baseline environmental scenario along the corridors, where there is constricted ROW and traffic is higher leading to congestion, delay as well as various environmental impacts. Such locations are identified for bypassing the through traffic. Several alternatives are analyzed for avoiding localized environmental impacts & arriving at the best-fit alignment. Screening procedure for road links & alignments are presented in the following sections.

The project corridor passes through several urban & semi urban areas, which have series of developments with residential and commercial activities. There are few major urban sections along the project corridor namely Bhavanagar, Mahuva, Una, Kodinar, Veraval, Chorvad, Mangrol, Porbandar and Dwarka.

In the rest of the urban areas as mentioned above, continuous developments have come up on both sides almost in the entire length. The clear land width available between building lines at these urban settlements is much less than the minimum land required to accommodate 6/4 lanes plus service roads to segregate local traffic. Widening the project corridor through these urban settlements not only cause traffic safety hazards, congestion, delay, but also pose severe environmental and social concerns of resettlement and rehabilitation.

Thus the existing alignment of project corridor through these urban settlements experience insufficient land width, traffic congestion, high VOC and low Level of Service (Los) for through traffic, high potential for environmental degradation because of increase in noise and pollution levels due to frequent breaking and acceleration of traffic. Above all there will be severe threat to safety of pedestrians and road users. Hence, these urban areas qualify as potential candidates for bypasses and realignments. The bypasses to these settlements will not only provide a better level of service and economic benefits by way of reduced VOC's to through traffic, but will also improve the level of service and safety of local traffic on existing road and improve environmental conditions within the urban settlements.

Environmental Impact Assessment 65 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

The project corridor does not suffer from much of the commercial activity and local traffic at remaining minor settlements. The proposed improvements can be taken through all of the remaining minor settlements without any major concern.

Elaborate description of bypasses and re-alignments is presented in subsequent sections of this chapter.

5.2 WITH OR WITHOUT PROJECT SCENARIO

The with and without project scenarios are analysed with respect to the development of the state by the backdrop of requirement of reliable quality infrastructure of sustained growth economy and consequent well being of its citizens.

Providing better connectivity will ensure that goods and people from areas covered by the road can move in and out of the areas quicker and save time. Inceased trade and commerce activity are expected. Accounting just for the savings in the Vehicle Operation costs makes the project viable. The project roads have been designed to connect the important settlements with shorter & better road network. It provides greater impetus to religious and commercial establishments. It has a very good tourism potential due to famous religious and tourist places. The industrial activity will be getting a good boost due to this upgradation of the existing road to Gujarat Government plan of developing industrial region. The industrial activity will give rise to employment potential for people in and around the region. However, there would be an increase in the vehicular pollution air and noise, in the vicinity of the road. Some agricultural land will have to be diverted for road use to construct bypasses. In other settlements, some people will lose there properties close to the road to accommodated the proposed widening.

If the project is not implemented, there is every likehood that the project rods will deteriorate further. Only certain roads may be maintained regularly. There is every likehood of deterioration of the existing pavements. Increased air pollution, due to slow moving traffic and congestion, will follow. Noise levels will rise due to deterioration of the pavement as well as increased honking. Without the bypass, the traffic would continue passing through the built-up areas and continue to pose a safety risk for the residents in the already congested areas.

Therefore, the “with” project scenario, with its minor adverse impacts is more acceptable than the “without” project scenario which would mean an aggravation of the existing problems. Potential benefits of the proposed road improvements are substantial and far-reaching both in terms of the geographical spread and time. Hence, it is clear that the implementation of the project will be a definite advantage to project road in order to achieve all round development of its economy and progress for its people.

5.3 ALIGNMENT SELECTION

Alignment selection was carried out on the basis of evaluation of various alternative alignments for each bypass. The evaluation has been done both qualitatively and quantitatively for the various factors influencing the selection process. These factors can be broadly grouped under

Environmental Impact Assessment 66 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

main heads such as geometrics, cost, and social and environmental impacts. The qualitative evaluation rates the alternative as less desirable, desirable, and most desirable against each factor. The factors considered for qualitative comparison are:  Land availability  Effect on residential/commercial buildings  Ponds affected  Religious structures affected  Environmental Quality/ Ecology

Similarly quantitative evaluation was done for the following factors:

 Route length  Length of agricultural land affected  Length of barren land affected  Number of road crossings  Pucca / Kutcha - commercial / residential structures affected  Telephone/Electric poles to be shifted  Total Cost

The following sections describe the bypasses/ realignments considered on the project road

5.4 ALTERNATIVE PROPOSALS FOR BYPASSES

5.4.1 Bypasses Proposed by R&B

5.4.1.1 Comparative Studies for Bypass near Adhewada (Km. 4.400 – Km. 7.000)

Adhewada Existing Alignment Bypass Alt-1

Start/End Ch. Km. 4.400 – Km. 7.000 Km. 4.400 – Km. 7.000

Length along alignment 2.6 kms 2.62 kms

Encroachments Pucca – 85 Pucca – 5, Katcha – 3

Structures 1 Minor Bridge 1 Minor Bridge

Bypass alignment alternative – 1 has been proposed.

Environmental Impact Assessment 67 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.1: Adhewada Bypass 5.4.1.2 Comparative Studies for Bypass near Budhel (Km. 8.500 – Km. 11.060)

Budhel Existing Alignment Bypass Alt-1

Start/End Ch. Km. 8.500 – Km. 11.060 Km. 8.500 – Km. 11.060

Length along alignment 2.1 kms 2.32 kms

Encroachments Pucca – 200 Pucca – 5, Katcha – 10

Structures Flyover - 1 No. Flyover - 1 No.

Bypass alignment alternative – 1 has been proposed.

Fig 5.2: Budhel Bypass Option

Environmental Impact Assessment 68 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

5.4.1.3 Comparative Study for Bypass near Kobadi (Km. 14.540 to Km. 17.300)

Kobadi Existing Alignment Bypass Alt-1

Start/End Ch. Km. 14.540 – Km. 17.300 Km. 14.540 – Km. 17.300

Length along alignment 2.76 kms 2.99 kms

Encroachments Pucca – 140 Pucca – 5

Structures ------

Bypass alignment alternative – 1 has been proposed.

Fig 5.3: kobadi Bypass

5.4.1.4 Comparative Study for Bypass near Bhandaria (Km. 21.080 to Km. 23.000)

Bhandaria Existing Alignment Bypass Alt-1

Start/End Ch. Km. 21.080 – Km. 23.000 Km. 21.080 – Km. 23.000

Length along alignment 2.92 kms 3.68 kms

Encroachments Pucca – 135 Pucca – 5

Structures ------

Bypass alignment alternative – 1 has been proposed.

Environmental Impact Assessment 69 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.4: Bhandaria Bypass Option

5.4.1.5 Comparative Study for Bypass near Tansa (Km. 28.650 to Km. 31.150)

Tansa Existing Alignment Bypass Alt-1

Start/End Ch. Km. 28.650 – Km. 31.150 Km. 28.650 – Km. 31.150

Length along alignment 2.5 kms 2.65 kms

Encroachments Pucca – 240 Pucca – 1

Structures ------

Bypass alignment alternative – 1 has been proposed.

Fig 5.5: Tansa Bypass Option

Environmental Impact Assessment 70 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

5.4.1.6 Comparative Study for Bypass near Trapej (Km. 39.200 to Km. 41.050)

Trapej Existing Alignment Bypass Alt-1

Start/End Ch. Km. 39.200 – Km. 41.050 Km. 39.200 – Km. 41.050

Length along alignment 1.85 kms 1.73 kms

Encroachments Pucca – 210 Pucca – 3, Katcha – 3

Structures VUP – 1 No VUP – 2 Nos

Bypass alignment alternative – 1 has been proposed.

Fig 5.6: Trapej Bypass Option

5.4.1.7 Comparative Study for Bypass near Una (Km. 180.400 to Km. 188.000)

Option 1 Una Existing Alignment Bypass_Alt 1

Start/End Ch. Km. 180.400 – Km. 188.000 Km. 180.760 – Km. 187.750

Length along alignment 7.6 kms 8.9 kms

Encroachments Pucca – 500 Pucca – 15, Katcha – 10

Structures Major Bridge – 1 Major Bridge – 1

Environmental Impact Assessment 71 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Bypass alignment alternative – 1 has been proposed.

Fig 5.7: Una Bypass Option

5.4.2 Bypasses Proposed by STUP

5.4.2.1 Comparative Study for Bypass near Talaja (Km. 49.600 to Km. 53.500)

Option 1 Option 2

Talaja Existing Existing Bypass_Alt 1 Bypass_Alt 2 Alignment Alignment

Km. 49.600 – Km. 49.600 – Km. 48.200 – Km. 48.200 – Start/End Ch. Km. 53.500 Km. 53.500 Km. 54.500 Km. 54.500

Length along 3.9 kms 4.18 kms 6.3 kms 6.8 kms alignment

Pucca – 50 Pucca – 10 Pucca – 75 Pucca – 2 Encroachments Katcha – 10 Katcha – 1 Katcha – 10 Katcha – 10

Structures ---- Minor Bridge – 1No. ---- Major Bridge – 1 No.

Bypass alignment Alternative – 1 is recommended.

Environmental Impact Assessment 72 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.8: Talaja Bypass Options

5.4.2.2 Comparative Study for Bypass near Bhadrad (Km. 85.610 to Km. 89.000)

Option 1 Option 2

Bhadrad Existing Existing Bypass_Alt 1 Bypass_Alt 2 Alignment Alignment

Km. 85.610 – Km. 85.610 – Km. 85.500 – Km. 85.500 – Km. Start/End Ch. Km. 89.000 Km. 89.000 Km. 89.200 89.200

Length along 3.39 kms 3.43 kms 3.7 kms 4.3 kms alignment

Pucca – 2 Encroachments Pucca – 80 Pucca – 80 ---- Katcha – 2

Structures ---- Minor Bridge – 1No ---- Major Bridge – 1 No.

Bypass alignment Alternative – 1 is recommended.

Environmental Impact Assessment 73 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.9: Bhadrad Bypass Options

5.4.2.3 Comparative Study for Bypass near Datardi (Km. 113.240 – Km. 115.450)

Datardi Existing Alignment Bypass_Alt1 Bypass_Alt2

Km. 113.240 – Km. 113.240 – Km. 113.240 – Start/End Ch. Km. 115.450 Km. 115.450 Km. 115.450

Length along 2.21 kms 2.21 kms 2.41 kms alignment

Pucca – 3, Encroachments Pucca – 50 Katcha – 3 Katcha – 2

Structures Major Bridge – 1 No Minor Bridge – 1 No Minor Bridge – 1 No

Bypass alignment Alternative – 2 is recommended.

Environmental Impact Assessment 74 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.10: Datardi Bypass Options

5.4.2.4 Comparative Study for Bypass near Hemal (Km. 157.200 to Km. 159.850)

Option 1 Option 2

Hemal Existing Existing Bypass_Alt 1 Bypass_Alt 2 Alignment Alignment

Km. 157.200 – Km. 157.200 – Km. 157.300 – Km. 157.300 – Start/End Ch. Km. 159.850 Km. 159.850 Km. 159.900 Km. 159.900

Length along 2.65 kms 2.93 kms 2.65 kms 2.7 kms alignment

Encroachments Pucca – 90 ---- Pucca – 90 ----

Structures ------

Bypass alignment Alternative – 1 is recommended.

Environmental Impact Assessment 75 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.11: Hemal Bypass Options

5.4.2.5 Comparative Study for Bypass near Samter (Km. 174.025 – Km. 176.400)

Samter Existing Alignment Bypass_Alt1 Bypass_Alt2

Km. 174.025 – Km. 174.025 – Km. 173.900 – Start/End Ch. Km. 176.400 Km. 176.400 Km. 176.300

Length along 2.4 kms 2.4 kms 2.6 kms alignment

Pucca – 1, Pucca –1 Encroachments Pucca – 50 Katcha – 2 Katcha –2

Structures Major Bridge – 1 No Major Bridge – 1 No Major Bridge – 1 No

Bypass alignment Alternative – 2 is recommended.

Environmental Impact Assessment 76 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.12: Samter Bypass Options

5.4.2.6 Comparative Study for Bypass near Dholasa (Km. 204.950 to Km. 207.000)

Dholasa Existing Alignment Bypass Alt-1

Start/End Ch. Km. 204.950 – Km. 207.000 Km. 204.950 – Km. 207.000

Length along alignment 2.05 kms 2.3 kms

Encroachments Pucca – 300 Pucca – 6, Katcha – 4

Structures ---- Minor Bridge – 1 No.

Bypass alignment alternative – 1 has been proposed.

Fig 5.13 Dholasa Bypass Option Environmental Impact Assessment 77 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

5.4.2.7 Comparative Study for Bypass near Chorwad (Km. 268.600 to Km. 271.400)

Chorwad Existing Alignment Bypass Alt-1

Start/End Ch. Km. 268.600 – Km. 271.400 Km. 268.400 – Km. 271.200

Length along alignment 2.8 kms 2.25 kms

Encroachments Pucca – 170 Pucca – 5, Katcha – 4

Structures ------

Cost Will be incorporated later

Bypass alignment alternative – 1 has been proposed.

Fig 5.14: Chorwad Bypass Option

5.4.2.8 Comparative Study for Bypass near Prachi (Km. 240.080 to Km. 243.390)

Prachi Existing Alignment Bypass_Alt1 Bypass_Alt2

Km. 240.080 – Km. 240.080 – Km. 240.080 – Start/End Ch. Km. 243.390 Km. 243.390 Km. 243.390

Length along 3.31 kms 3.6 kms 4.5 kms alignment Pucca – 2, Encroachments Pucca – 70 Katcha –3 Katcha – 5

Minor Bridge – 1 No Minor Bridge – 1 No Minor Bridge – 1 No Structures PUP – 1 No

Environmental Impact Assessment 78 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Bypass alignment Alternative – 1 is recommended.

Fig 5.15: Prachi Bypass Options

5.4.2.9 Comparative Study for Bypass near Kukasawada (Km. 272.800 toKm. 276.550)

Kukasawada Existing Alignment Bypass Alt-1

Start/End Ch. Km. 272.800 – Km. 276.550 Km. 272.800 – Km. 276.550

Length along alignment 3.75 kms 3.5 kms

Encroachments Pucca – 180 Katcha – 5

Structures ------

Bypass alignment alternative – 1 has been proposed.

Environmental Impact Assessment 79 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.16: Kukasawada bypass Option

5.4.2.10 Comparative Study for Bypass near Madhavpur (Km. 308.600 to Km. 312.650)

Option 1 Option 2

Bhadrad Existing Existing Bypass_Alt 1 Bypass_Alt 2 Alignment Alignment

Km. 310.200 – Km. 310.200 – Km. 308.600 – Km. 308.600 – Start/End Ch. Km. 312.200 Km. 312.200 Km. 312.650 Km. 312.650

Length along 2.0 kms 2.1 kms 4.05 kms 3.6 kms alignment

Pucca – 5, Pucca – 250, Encroachments Pucca – 225 Pucca - 1 Katcha – 5 Katcha – 20

Structures ------

Bypass alignment alternative – 2 has been proposed.

Environmental Impact Assessment 80 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.17: Madhavpur Bypass Options

5.4.2.11 Comparative Study for Bypass near Porbandar (Km. 356.860 to Km. 376.300)

Porbandar Existing Alignment Bypass_Alt1 Bypass_Alt2

Km. 356.860 – Start/End Ch. Km. 356.860 – Km. 356.860 – Km. Km. 376.300 Km. 376.300 376.300

Length along 19.44 kms 21.3 kms 21.7 kms alignment

Pucca – 10, Encroachments Pucca – 1200 Katcha – 35 Katcha – 40 Major Bridge – 2 Nos Major Bridge – 3 Nos Major Bridge – 2 No Minor Bridge – 1 No Minor Bridge – 1 No Structures Flyover – 1 No Flyover – 1 No Flyover – 1 No VUP – 1 No VUP – 1 No

Bypass alignment alternative – 1 has been proposed.

Environmental Impact Assessment 81 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Fig 5.18: Porbandhar Bypass Options

Environmental Impact Assessment 82 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

6. STAKEHOLDER CONSULTATION

Community consultation has been taken up as an integral part of environmental assessment process throughout the project preparation stage of this project.

Introduction The public consultation is an important tool of information, dissemination and awareness creation during the planning stage of the project. It provides valuable inputs regarding successful implementation of the project besides ensuring public participation and involvement in the process.

As per the requirements of the project, public consultations were conducted at strategic locations in the month of April 2011. The purpose of conducting public consultations was to inform and explain the features of the project including operational and safety requirements to local people and to understand their concerns and perceptions with regard to adverse impact on their property and assets, livelihood, social relations, access to various facilities and resources, etc. Before conducting the public consultations, a reconnaissance survey of the project road was undertaken to identify strategic locations for public consultations.

The project road as NH-8E starts from km 3.200 and ends at km 473.000 and as SH-25 starts at km 231.000 and ends at km 261.100 and is approximately 500 kms. The project road is in the state of Gujarat extending from Bhavnagar to Dwarka.

Public Consultation has been conducted in 11 villages on NH-8E from Bhavnagar to Dwarka in the state of Gujarat between April 07, 2011 and April 13, 2011. The villages in which Public consultation is conducted are indicated below:  Talaja  Bhadrod  Datardi  Hemal  Samter  Dolasa  Prachi  Chorwad  Kukaswada  Madhavpur  Porbandar Environmental Impact Assessment 83 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Selection of Stakeholders

Various categories of stakeholders ranging from Project Affected Persons to government officials to other opinion leaders were selected in order to discuss social and environmental impacts, including the issue of resettlement and rehabilitation. The participants from several categories were present during discussion and expressed their views  Elected representatives  PAPs  Government Official

Other stakeholders: businessmen, educationists, agriculturist, shopkeepers

Objective of Public Consultation Meetings

The purpose of the public consultation meetings was to promote public awareness and understanding and purpose of the proposed project. The main objective of conducting meetings was to disseminate information about the project and to notify stakeholders and provide opportunities to participate in consultation and assessment process. The objectives of the public consultation meetings were as follows 1) Disseminate the information about the proposed project to the general public 2) Create awareness about the project among the PAPs (Project Affected Persons) 3) Dispel the appearance of PAPs regarding the positive/adverse impact of the project. 4) Seek the suggestion of Gram Panchayat, PAPs and other stakeholders on the various involved including those related to compensation, resettlement and rehabilitation, social and environmental impacts. 5) To resolve the issues that has affect on common property.

Method of Information Dissemination

The team including social experts and meeting facilitator team had visited nearly all the affected villages and requested primary and secondary Stakeholders to attend the meeting

Following were the methods used for notifying the meeting to the Participants 1. Face to face meetings were organized to disseminate the information. 2. Discussion at individual and group level 3. The stakeholders were also reminded to attend the meeting through personal phone calls wherever possible.

Environmental Impact Assessment 84 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Public consultations were organized at a pre-fixed place and time. Keeping the public needs in view, several consultations were conducted on the project road, details of which are as under:

Talaja

Public consultation has been conducted in Talaja on April 07, 2011. Two bypass alternatives have been proposed for this town, Alternative-1 on RHS and Alternative-2 on LHS.

The public demands are as follows: 1. Alignment alternative – 1 has been unanimously agreed by the villagers. 2. The alternative – 1 shall be modified so that the heavy structures shall not be required to be demolished. 3. Alternative – 1 shall be suitably modified so that it shall pass behind the existing market yard.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 85 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Bhadrod

Public consultation has been conducted in Bhadrod village on April 08, 2011. Two bypass alternatives have been proposed for this village, Alternative-1 on LHS and Alternative-2 on RHS.

The public demands are as follows: 1. Bypass Alternative – 1 has been unanimously agreed by the villagers. 2. The bypass alternative shall be modified so that the alignment passes through government land so as reduce the land acquisition. 3. Alternative – 1 passes through water-logging area. Hence, adequate cross-drainage structures shall be provided based on hydrological studies to drain out the water into the sea. 4. Adequate facility shall be provided at the start and end of bypass for entry to village and exit from village to highway.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 86 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Datardi

Public consultation has been conducted in Datardi village on April 08, 2011. Two bypass alternatives have been proposed for this village, Alternative-1 on LHS and Alternative-2 on RHS.

The public demands are as follows: 1. Bypass Alternative – 1 has been unanimously agreed by the villagers. 2. The bypass alternative shall be modified so that the alignment passes through government land available in LHS. 3. Alternative – 1 passes through water-logging area. Hence, adequate cross-drainage structures shall be provided based on hydrological studies to drain out the water into the sea. 4. Adequate facility shall be provided at the start and end of bypass for entry to village and exit from village to highway.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 87 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Hemal

Public consultation has been conducted in Hemal village on April 09, 2011. Two bypass alternatives have been proposed for this village, Alternative-1 on RHS and Alternative-2 on LHS.

The public demands are as follows: 1. The alternative of widening of existing highway though the village has been agreed by the villagers. 2. An underpass with slip road shall be provided in the village for separation of through traffic. 3. Adequate safety facilities required such as signs, street-lighting and road markings shall be provided.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 88 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Samter

Public consultation has been conducted in Samter village on April 09, 2011. Two bypass alternatives have been proposed for this village, Alternative-1 on RHS and Alternative-2 on LHS.

The public demands are as follows: 1. The villagers have agreed for a bypass of Samter village. 2. The alternatives proposed shall be studied in detail and final alternative proposal shall have less land acquisition. 3. Adequate facility shall be provided at the start and end of bypass for entry to village and exit from village to highway.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 89 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Dolasa

Public consultation has been conducted in Dolasa village on April 10, 2011. One bypass alternative have been proposed for this village, Alternative-1 on LHS.

The public demands are as follows: 1. The bypass alternative has been unanimously agreed by the villagers 2. Adequate facility on the bypass shall be provided for movement of vehicles to and from the village on access roads. 3. The alternative shall be passing thorough water-logging area. Hence, adequate cross- drainage structures shall be provided based on hydrological studies to drain out the water into the sea. 4. A comparative bypass alternative on RHS shall be studied and the most feasible among both shall be proposed.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 90 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Prachi

Public consultation has been conducted in Prachi village on April 10, 2011. One bypass alternative have been proposed for this village, Alternative-1 on LHS and Alternative-2 on RHS.

The public demands are as follows: 1. Bypass Alternative-1 has been unanimously agreed by the villagers. 2. Access road leading to Alidra village shall have a CD structure of adequate height so that the structure shall be used as underpass during summer season.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 91 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Chorwad

Public consultation has been conducted in Chorwad village on April 11, 2011. One bypass alternative have been proposed for this village, Alternative-1 on RHS.

The public demands are as follows: 1. Bypass Alternative has been unanimously agreed by the villagers. 2. The ROW to be acquired shall be minimum as the bypass alignment passes though well established coconut plantation. 3. The income generated per vigha (1624 sqm) is Rs. 1 lakh per annum and the market value per vigha is ranging between 5 to 7 lakhs.

The photographs of Public Consultation are indicated below:

Environmental Impact Assessment 92 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Kukaswada

Public consultation has been conducted in Kukaswada village on April 11, 2011. One bypass alternative have been proposed for this village, Alternative-1 on LHS as.

The public demands are as follows: 1. The alternative of widening of existing highway though the village has been agreed by the villagers. 2. Utility ducts of 1.0m diameter with a spacing of 250m to be provided. 3. Adequate safety requirements have to be followed at School, bus stops, etc by providing traffic signs, road markings and street lighting.

The photographs of Public Consultation are indicated below:

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Madhavpur

Public consultation has been conducted in Madhavpur village on April 11, 2011. Two bypass alternatives have been proposed for this village, Alternative-1 & 2 on RHS.

The public demands are as follows: 1. The alternative of widening of existing highway though the village has been agreed by the villagers. 2. Existing geometry shall be maintained with no further curve improvement as existing structures have already been dismantled for four laning of highway. 3. Adequate safety requirements have to be followed at School, bus stops, etc by providing traffic signs, road markings and street lighting.

The photographs of Public Consultation are indicated below:

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Porbandhar

Public consultation has been conducted in Porbandhar village on April 13, 2011. Two bypass alternatives have been proposed for this village, Alternative-1 & 2 on RHS.

The public demands are as follows: 1. Bypass Alternative – 1 has been unanimously agreed by the villagers. 2. The proposed alignment shall cross the existing NH – 8B beside the ITI campus. 3. The existing highway needs to be rehabilitated before handover. 4. The alignment passes through water-logging areas. Hence, adequate cross drainage structures shall be provided based on hydrological studies. 5. Grade separation as an underpass or flyover shall be provided at the crossings of national and state highways.

The photographs of Public Consultation are indicated below:

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Main Findings and Observations

Through active participations of the stakeholders, key issues relating to social and environmental impacts, compensation, resettlement and rehabilitation were identified and discussed during the public consultation. Certain observations as they emerged from various public consultations may be summarized as follows:  Majority of the participants likely to get affected were not opposed to the widening of the road and are convinced with the advantages that accrue with the 6/4/2 laning of the road like distribution of the presently high traffic load, reduction in number of accidents, lesser fuel consumption and time saving.  Majority of participants from various villages have agreed for the bypass proposal.  There is a common demand of construction of underpasses and elevated roads / flyovers in major built up areas and provision of bus shelters. Appropriate measures for controlling the accidents were also demanded, like signboards, road markings and street lighting before the built-up areas etc.

With regards to R&R and environmental issues, the following concerns were raised by the participants  The mode of compensation for land acquisition  Provision of employment in project construction works to Project Affected Persons (PAPs)  Environment protection and pollution control

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7. ASSESSMENT OF IMPACTS

This chapter assesses the nature, type and magnitude of the potential impacts likely on the various physical, biological and cultural environmental components along the project corridor.

7.1 INTRODUCTION

Road widening projects have typical potential impacts though these vary in accordance with the intensity of construction works involved, future scenario envisaged during the operation stage and the importance attached to the impacted environmental attributes. Since the project involves widening of the existing NH-8E from existing two lane to 6/4/2 lane with paved shoulder, most of the impacts will be confined to the proposed RoW. Subsequent sections detail out the likely impacts on various environmental components.

7.2 NATURAL ENVIRONMENT

Meteorology: By and large, no significant change is expected in the macro-climatic setting (precipitation, temperature and wind) of the corridor due to the project. However, the microclimate is likely to be modified due to removal of roadside trees and addition of increased pavement surface. In addition, temporary loss of shade giving roadside trees will cause discomfort to the slow moving traffic and pedestrians.

Physiography & Terrain: The project corridor traverses through plain to rolling terrain. A large stretch of the road passes through agricultural and barren lands. Widening to 6/4 lane will involve large quantities of earthwork as fill materials. Such modifications in the topography may lead to drainage problems both along the project corridor and at the borrow area sites.

Soil: The widening of the road to 6/4 lane would require acquisition of agriculture lands at places where the presently available RoW is inadequate to accommodate the proposed improvements. Establishment of labour camps, hot mix plants and movement of construction machinery shall avoid ecologically sensitive locations and Construction and allied activities such as setting up of construction camps and movement of vehicle along haul roads would result in compaction of soil. Disposal of oil wastes from vehicle and construction equipment maintenance yards shall also lead to contamination of productive soil.

Borrow Areas: The investigation was aimed at locating the potential borrow areas for sub-grade/ embankment fill and granular sub-base along the project corridors within economic hauling distance. To obtain this information regarding probable borrow pits along the corridor and to obtain this objective, field surveys have been carried out. Based on the information received and field surveys, the consultants identified the borrow areas which are new ones /existing ones belonging to the government or public. This material has been explored for construction of embankment and subgrade.

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7.2.1 Borrow Pits for Construction of Embankment and Sub-grade

The sources identified as potential borrow sources are shown in Table 7.1 and include certain useful information such as, distance from the project road, location, village name etc. Borrowing soil from these areas would require prior approval of the local authorities, negotiations with private people. Soil samples from these borrow sources were collected in bulk quantities by excavating test pits down up to 1.0 m depth from the existing ground surface. The Top organic soil layer of approximately 100 mm thickness was removed before sampling. Table 7.1: Probable Soil Borrow Pits

Lead Distance to the Sr. No. Name of Borrow Area Location Project Road in km 1 Sanodar at km 24. 400 Sanodar 1.000 Km 2 At km 25.700 Kachha 300 m 3 Bapasara at km 45.800 Bapasara 300 m 4 Vavadi at km 26.240 Vavadi 500 m

The probable impacts of soil borrow pits are indicated below: 1. The borrow areas located in agriculture lands deprives the cultivation of the area and disturbs top soil containing high nutrients. 2. The soil erosion for borrow areas leads to sedimentation / silt flowing along the adjacent cultivated lands. 3. The borrow areas also triggers impact on safety of animals / cattle even if it si fenced before the redevelopment of borrow area (either leveling of monts/ storing of water for agriculture/ water for irrigation). 4. During excavation, the excavator emanates dust with a fine organic silt content between 2 to 10 microns which affects nearby communities. 5. Borrow area also triggers impacts on natural drains and subsequent irrigation meandering channels.

7.2.2 Quarries for Aggregates

Aggregates to be used for base, surface courses and concrete works have been collected from the crushers under operation in the existing quarries. The locations and the approximate distance from each source to the nearest point on the Project Road are compiled in Table 7.2. Table 7.2: Details of Quarry Area for Aggregates Sr.No Chainage Side Distance Location 1 9.000 Left 2 Km Bhikada 2 Kobadi Left 3 Km Ukhalla 3 51.000 Right 10 Km Palitana Road

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Sr.No Chainage Side Distance Location 4 189.000 Left 1 Km near Una 5 204.000 Right 5 Km Near Dolasa 6 242.000 Right 5 Km Rampara 7 331.000 Left 2 km 8 408.000 Right 6 Km

The impacts of Quarry sites are indicated below: 1. Quarry operation triggers impacts mainly on air and noise pollution besides blasting of rocks endangers the community / grazing cattles in and around 3 kms (fly rock distance) 2. Impacts are due to irregular shape of quarrying operations affecting natural drainage. The secondary impacts are due to transportation of aggregates through haulage roads. 3. The flora and fauna of the quarry area operations are significantly impacted.

7.2.3 Quarries for Sand

Sand samples have been collected from three sand sources and tested. Table 7.3 indicates the location of these sand quarries along with the lead to Project Road. Table 7.3: Details of Sand Quarry

Existing km Source of Sand

51.000 Shetranji 134.200 Datakdi

7.2.4 Water Resources

Impacts envisaged on water resources due to proposed improvements are:

 Loss of existing water sources  Loss of water storage capacity  Increased pressure over available resources  Deterioration of water quality and  Drainage impact

Loss of water sources: Widening of the road width may result in partial and full filling of roadside water bodies like ponds and ditches. Most of the ditches and ponds that are likely to be impacted are non-perennial. The ditches along the project road are borrow areas from which soil had been taken while constructing the existing road. Some of these lie within the proposed ROW and are to be filled up. The ponds are mainly privately owned and are quite big in size. Both the ponds and ditches are used for domestic purposes like washing, cleaning etc.

Efforts have been made to minimize the impacts on these surface water bodies. Reduction of the area of these surface water bodies will be a moderate long-term negative impact during the

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construction and operation stage of the project. There are also loss of other water extraction sources like hand pumps and bore wells due to widening of road.

Increased pressure on available resources: Seven surface water rivers have been identified as likely water sources for construction. The suitability of these identified water sources and availability of water during extraction is to be checked before incorporation of construction works as per IS 456-2000. In addition water may also be sourced from new bore wells. During lean season competitive uses of water from these sources may be adversely affected.

Deterioration of water quality: Pollution of water resources can result from the following highway related sources. However, the impacts are dependent on the scale of pollution and the nature of receptors. The likely pollutants, sources and receptors are presented in Table-7.4.

Table 7.4: Water Contaminants, sources & receptors Sl. No. Contaminants Highway related Sources Receiving water bodies Erosion from exposed land surfaces 1. Sediment Surface water bodies during and after construction. Primarily from parked vehicles, fueling 2. Oils and Grease Surface water bodies and repair stations 3. Heavy metals Vehicle exhaust Surface & Ground water 4. Debris Litter Surface water bodies Fertilizers, Pesticides, Fertilizers applied for establishment of 5. Surface water bodies and Herbicides turf on embankments

Drainage Impacts: As per the bridge condition survey there are 550 cross drainage structures in the project corridor. Out of these, 30 Major Bridges (Total length > 60.0 m), 204 are Minor Bridges (6.0 m <= Total Length <= 60.0m) and the remaining 316 structures are culverts. Improvement measures include rehabilitation of existing structures as well construction of new structure to house the proposed additional lanes.

During the construction of the new structures, there are chances of the waterways getting blocked due to the haphazard dumping of the construction materials and wastes.

7.2.5 Air Quality

Construction Stage: Potential impacts on the air quality during the construction stage will be due to the fugitive dust and the exhaust gases generated in and around the construction equipments and ground related activities such as crushing sites, hot-mix and asphalt plants, etc. The ambient Air quality is likely to be impacted due to activities such as site clearance, stone crushing, dumping of fill materials, earthwork etc which will create dust in the construction area and its vicinity. This will affect the health of the construction workers and dwellers with in the near by vicinity of the construction activities. The impacts anticipated on the air quality during the construction stage, though significant, will be short-term impacts.

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Operation Stage: The improved road quality will lead to induced traffic on the corridor. This additional increase in the number of vehicles will result in a slow but steady increase in the air pollution levels and pollutant concentrations.

Mitigation Measures

The mitigation/management measures proposed as a part of the project are likely to improve the air quality scenario along the corridor during the operation stage. Tree plantation as per the proposed road landscape strategy will help to attenuate the air pollution levels. The tree species suggested include broad-leaved tree species, which can help settle particulates with their higher surface areas and thick foliage and reduce the distance for which particulates are carried from the road itself. This measure is of specific importance in context of the high SPM concentrations as predicted in some of the receptor locations.

Other measures such as the reduction of vehicular emissions, ensuring vehicular maintenance and up-keep, educating drivers about driving behavior / methods that will reduce emissions are beyond the scope of the project but will be far more effective in reducing the pollutant levels.

Apart from provision of the mitigation measures, their effectiveness and further improvement in designs to reduce the pollutant levels with increase in traffic shall be monitored. A monitoring plan to this affect will be prepared as a part of the Environmental Management Plan (EMP).

7.2.6 Noise Levels

Construction Stage: Due to the various construction activities, there will be temporary noise impacts in the immediate vicinity of the project corridor. The construction activities will include the excavation for foundations and grading of the site and the construction of structures and facilities. However construction noise is generally intermittent and depends on the type of operation, location and function of the equipment.

Operation Stage: During the operation stage the noise generated by vehicles will have adverse impact on residents of settlements located close to the corridor. Apart from the dwelling areas the sensitive receptors consisting of occupants at educational institutions and hospitals will also be impacted.

Mitigation Measures

The mitigation/management measures proposed as a part of the project are likely to reduce the noise levels along the corridor during the operation stage. Vegetative noise barriers have been proposed in front of the schools and hospitals depending on the space available. 3 rows of trees have been proposed with each row comprising of 10-15 trees. The predicted noise levels are marginally above the norms in most cases, so provisions of separate noise barrier for receptors is not called for. The green cover recommended will be sufficient to attenuate ambient noise levels to comply with relevant standards.

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Roadside Trees

Roadside trees within the existing RoW in certain stretches of the project road have been notified as Protected forest.

The roadside plantations consist of mature trees on either side of the project corridor. Predominant roadside tree species include Babool, Neem, Peepal and Banyan.

For roadside trees that are demarcated as Notified Protected forests, an application is to be submitted to the State Forest Department for tree cutting (as per Forest Conservation Act 1980). A joint verification of trees will be carried out in presence of concerned Forest officials before tree cutting.

7.2.7 Fauna

Only commonly found fauna are present in the area. The project road does not contain any endangered or threatened species close to the project highway and does not pass through any sensitive wildlife / protected areas. No animal crossings have been reported or observed along the stretch. Thus, there will be no major impact on the fauna of the area.

7.3 SOCIAL & CULTURAL ENVIRONMENT

The social environment consists of the lands, buildings, and other community owned assets including utilities. The proposed widening along the existing corridor will include one or more of the following impacts:

 Removal of encroachments and squatters and

 Acquisition of land and structures – residential, commercial, institutional, agricultural, etc.

This would lead to affecting livelihood and community access to the roadside communities. However, the options for the proposed widening will be finalized with a thrust to minimize the impact on structures and other properties.

The likely social impacts have been analyzed based on the number of assets impacted and area to be acquired under various land uses. This has been discussed in the RAP Report.

7.3.1 Impact on Educational Institutes and Hospitals

The details of educational institutes getting affected due to widening of existing highway are indicated in table 7.5. Table 7.5: Roadside Schools along project corridor Sr. No Existing Km Side Extent of Impact 1 36.700 Left Affected 2 44.650 Right Affected

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Sr. No Existing Km Side Extent of Impact 3 61.500 Left Affected 4 92.375 Right Affected 5 97.700 Right Affected 6 98.630 Right Affected 7 98.700 Left Affected 8 99.600 Right Affected 9 107.400 Left Affected 10 116.900 Left Affected 11 118.000 Left Affected 12 148.600 Left Affected 13 160.500 Left Affected 14 182.750 Right Affected 15 177.600 Left Affected 16 188.450 Right Affected 17 196.600 Right Affected 18 211.900 Left Affected 19 232.400 Left Affected 20 237.200 Left Affected 21 251.300 Left Affected 22 256.400 Left Affected

7.3.2 Impact on Cultural Environment

52 religious structures are being affected due to widening of the project road. Apart from these, many shrines are found to be present within the proposed ROW. The affected temples are to be relocated. The details are presented in Table 7.6. Table 7.6: Roadside Religious Properties along project corridor

Temples / Dargas Sl.No Chainage LHS RHS 1 4.000 1 2 8.000 1 3 8.100 1

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Temples / Dargas Sl.No Chainage LHS RHS 4 11.800 1 5 32.000 1 6 35.400 1 7 36.700 1 8 43.400 1 9 47.950 1 10 49.500 1 11 54.100 1 12 55.700 1 13 61.900 2 14 64.700 1 15 85.100 1 16 93.050 1 17 95.700 1 18 101.900 1 19 103.100 1 20 104.100 1 21 112.200 1 22 113.600 1 1 23 120.800 1 24 144.000 1 25 148.700 1 26 149.300 1 27 149.600 1 28 153.800 1 29 167.400 1 30 170.400 1 31 172.300 1 32 178.700 1 33 207.000 1 34 213.700 1

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Temples / Dargas Sl.No Chainage LHS RHS 35 216.100 1 36 221.000 1 37 225.200 1 38 226.950 1 39 228.000 1 40 243.300 1 41 247.600 1 42 252.800 1 43 255.800 1 44 448.200 1 45 463.500 1 46 472.200 1 47 234.100 1 48 225.500 2 1 49 256.500 1

These impacts are assessed for each environmental component and environmental mitigation measures / avoidance of negative impacts is proposed. The environmental management plans, itemwise / sequentially prepared is to be followed by the Concessionaire during preconstruction and construction phases.

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8. MITIGATION MEASURES

This chapter presents mitigation and management measures to address likely impacts on identified environmental components due to the proposed project development. The description is an overview of the specific measures provided in the EMP. The Chapter finally presents the environmental costs for mitigating adverse impacts.

The following subsections details the mitigation measures that need to be undertaken during different project stages. They are required to minimize the negative impacts and enhance the positive impacts of the project on the surrounding environment. The mitigation measures revolve around various alternatives during the design phase, pre-construction, construction and operation phase of the road project; incorporating the following:

The “standard design” of various road sections is arrived at detailed deliberation between highway design and social-environmental team.

“General measures” to mitigate negative impacts on the natural, socio-economic and cultural environment, based on the characteristic features (existing environmental settings and assessment of probable impacts) of the project corridor.

Specific design solutions in the section that is found to be sensitive including formulation of special provisions to ensure sensitive construction methods that take place in critical sections or areas.

8.1 MITIGATION OF IMPACTS

8.1.1 Land Resources

No major changes in the topography are envisaged along the project corridor. However, requirement of materials shall necessitate creation of new borrow and quarry pits. Rehabilitation of such sites after use, by smoothening the steep slopes and covering them with vegetation or converting them into water body shall form a part of this project. Similarly, fresh embankments created at the site shall be covered with dredged earth for turfing of the slopes, in order to prevent erosion of the murram casing, for minimizing the runoff and stabilizing the embankment.

8.1.2 Soil Resources

Due to widening of the project corridor, adverse impacts on the soil include: loss of topsoil, increase in soil erosion, soil instability, tipping of spoils generated from construction work and contamination of soil. Following are the measures needed to minimize the adverse impacts:

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1). Conservation of Topsoil:

The topsoil shall be stripped upto a depth of 15 Locate stockpiles in … cm at all locations opened up for construction. The A secure area away from stripped topsoil should be carefully stockpiled at - Grade, Subsoil & Overburden materials; suitable accessible locations approved by the PIU. - Pit activities; and At least 10% of the temporarily acquired area shall - Day-to-day operations. be earmarked for storing topsoil Areas that do not interfere with future pit expansion

The stockpiles for storing the topsoil shall be Areas away from drainage paths and uphill of designed such that the slope does not exceed 1:2 sediment barriers. (vertical to horizontal), and the height of the pile is restricted to 2m. A minimum distance of 1m is required between stockpiles of different materials

In the cases where the topsoil has to be preserved Vegetative material for stockpile stabilisation… for more than a month, the stockpile is to be Must consist of grasses, legumes, herbaceous, or stabilized within 7 days of forming. The woody plants or a mixture thereof stabilization shall be carried out through Selection & use of vegetative cover to take into temporary seeding. It consists of planting rapid- account soil and site characteristics such as growing annual grasses or small grains, to provide drainage, pH, nutrient availability, and climate to initial, temporary cover for erosion control. ensure permanent growth

After spreading the topsoil on disturbed areas, topsoil must be seeded, and mulched within 30 days of final grading.

During construction, if erosion occurs from stockpiles due to their location in small drainage paths, the sediment-laden runoff should be prevented from entering nearby watercourses.

Preservation of Stockpiles: The contractor shall Preserving stockpiles – Precautions preserve the stockpile material for later use on slopes or shoulders as instructed by the engineer. Stockpiles will not be surcharged or otherwise loaded and multiple handing will be kept to a minimum to Spreading back of topsoil: The area to be ensure that no compaction will occur. covered with vegetation shall be prepared to the Divert runoff around stockpiles unavoidably located required levels and slope. The stockpile material in drainage paths using a perimeter bank uphill. shall be spread evenly to a depth of 5-15cm to the The stockpiles shall be covered with gunny bags or designed slopes and watering the same as tarpaulin immediately in case they are not stored for periods longer than 1 month required. The growth of the vegetation shall be monitored at frequent intervals.

All temporary arrangements made for stockpile preservation and erosion control are to be removed after reusing the stockpile material.

2). Erosion Control Protection

Stabilization of High Embankment Slopes:

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Slope of the road embankment shall be 1:2, which will reduce the possibilities of slope failure. Further to stabilize the slope, vegetative cover as per box 8.1 shall be done. Box-8.1: Detailed specifications for Vegetative cover

Description:

The vegetative cover should be planted in the region where the soil has capacity to support the plantation and at locations where meteorological conditions favours vegetative growth.

Site Preparation:

To prevent the seeds from washing away subsequent to sowing, area should be protected with surface roughening and diversions.

Soil samples should be taken from the site and analysed for fertiliser and lime requirements.

Seed Application:

The seed should be sown uniformly as soon as preparation of the seedbed has been completed.

No seed should be sown during windy weather, or when the ground surface is wet, or when not tillable.

Maintenance:

During first six weeks, the planting should inspected by the PIU, to check if the growth is uniform and dense. Appropriate moisture levels shall be maintained. There may be requirement of watering the plantings regularly during the dry seasons. Fertiliser and pest control applications may also be needed from time to time.

In case slope is steeper than 1:2, stone pitching (Figure 8.2) will be done. Stones will be fixed on slopes by gentle hammering. A P.C.C. anchor will be provided at the base, which will prevent sliding of stones on slope. The gaps between adjacent stones allow grass to grow which will hold the soil firmly together.

To check the slope stabilisation of Figure 8.1 Stone Pitching borrow pits adjacent to the embankment, the depth of the pit will be so regulated that the bottom edge of pit shall not intersect the imaginary line of slope 1:4 drawn from the top edge of the nearest embankment. To avoid embankment slippage and erosion, borrow pits shall not be dug continuously.

3). Measures to minimize Soil Contamination

Reduction and management of spoil

Construction activities will generate a lot of spoil as the cut and fill quantities will not be balanced. The solid waste generated will be used in road construction to the extent possible. The top soil will be used in median for turfing and also in embankments for slope stabilization. Also extra waste will be used to level the site of construction camp in the hilly section.

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Construction Stage

Cut and fill works will be carried out strictly in accordance with the design drawings.

Contamination of soil from fuel and lubricants

With an increase in the traffic volume, the contamination of the soil adjacent to the highway is likely, even though the effect will be very localized.

Construction Stage

At the various construction sites, the vehicles and equipment will be maintained and refueled in such a fashion that oil/diesel spillage does not contaminate the soil. It will be ensured that the fuel storage and refueling sites are kept at least 300m away from drainage channels and important water bodies. In all fuel storage and refueling areas located on agricultural lands or productive lands, the topsoil preservation shall be carried out. At the wash down and refueling areas, “oil interceptors” as shown in Figure 8.2, shall be provided. The oil interceptor works on the principle: the grease and oil being Figure 8.2 Oil Interceptor lighter in weight float on the top surface of the wastewater. Hence, oil and grease can be scum and be disposed in environmentally sound fashion.

Operation Stage

Probability of contamination of soil being only from the road runoff, which is regulated by well- designed drains, no impact on the soil during operation stage except in case of accidents, is anticipated.

Contamination of soil from Construction wastes and quarry materials

Pre-construction Stage

The generation of spoil materials has been minimized. For the disposal of spoils, low-lying areas or quarries with extra storage capacity have been proposed for storage.

Construction Stage

It will be required that the cut and fill works are carried out strictly in accordance to the design drawings. Earth, if required, will be dumped in selected area approved by the PIU. All spoils will be disposed off as desired and the site will be fully cleaned before handing over. Non-bituminous wastes from construction activities will be dumped in borrow pits and covered with a layer of the conserved topsoil. Bituminous wastes will be disposed off in an identified dumping site approved by the PIU.

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8.1.3 Water Resources

Surface Water Body

A number of ponds and ditches will be affected due to the proposed alignment. Mitigation measures as suggested below are to be undertaken at the locations.  The ditches are situated within the existing RoW, thus they are to be filled up.  For the loss of private ponds, compensation is to be provided to the owners.  In case of partially filled ponds, reconstruction of earthen embankment is to be undertaken to protect the embankment from erosion with turfing/pitching or construction of retaining wall.

While working around or near the water body following measures shall be undertaken:  Silt fencing and/or brush barrier shall be installed near all the ponds for collecting the sediments before letting them into the water body.  Silt/sediment should be collected and stockpiled for possible reuse as surfacing of slopes where they have to be revegetated.  Alternate drain inlets and outlets shall be provided in the event of closure of existing drainage channels of the water body.  Movement of machinery, workforce shall be restricted around the water body and no waste from construction camps or sites shall be disposed into it.

Run off Control / Drainage

To ensure efficient drainage system and to prevent water logging along the sides, adequate size and number P L A N O F SIDE VIEW OF DISSIPATIONE N E R G Y BASIN of cross-drainage structures have BASIN SECTION ON C - C been provided. All cross-drainage structures have been designed to SECTION ON DB R- B A IN A G E handle a 50-year peak flood level as CHUTE F R O N T VIEW STONE PITCHING ON per IRC: 5 – 1998 (Standard S ID E S L O P E Specifications and Code of Practice for Road Bridges Section I), IRC: SP- F R O N T ELEVATION PLA N 13 – 1973 (Guidelines for the Design ENERGY DISSIPATION BASINTO CHUTE AT TOE W HER E EMBANKMENTH E IG H T O F IS MORE of Small Bridges and Culverts), IRC: TH A N 3 .0 m

S E C TIO N 78-2000, (Standard Specifications DETAILSA T OFA - A BELL MOUTH OPENING and Code of Practice for Road Bridges Section VII). Figure 8.28.3: Channelised Embankment: Chute Drain

At the location high embankment or bridge approaches, Chute Drains shall be provided to drain the surface runoff and prevent erosion from the slopes. Detailed specifications are mentioned in Figure 8.28.3. (Refer IRC SP: 50 – 1999, Guidelines on Urban Drainage; IRC SP: 42 – 1994, Guidelines on Road Drainage for detailed drainage design)

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During the progress of work, the contractor will remove obstructions that may cause any temporary flooding of local drainage channels during construction. No spoil or construction material will be stored outside the proposed RoW or at places obstructing the natural drainage system.

In project corridor along watercourses, and locations close to cross-drainage channels, the contractor will ensure that earth; stone or any other construction material shall be disposed off immediately at the designated landfill site so as to avoid blocking the flow of water along those channels. Silt fencing (Box 8.2) shall be provided at construction sites in proximity of water bodies. Warning posts for notice of public against entry into the stream channels while construction shall be erected.

During the operation phase following measures need to be undertaken:

Inspection (as per IRC SP: 18-1978, Manual for Highway Bridge Maintenance Inspection) and cleaning of drains / culverts shall be done they gets choked with silt/debris and growth of vegetative cover over the accumulated debris. Box – 8.2: Detailed Specifications For Silt Fencing

Description:

Silt fencing is as temporary sediment barrier made of woven, synthetic filtration fabric supported by steel or wood post. The purpose of the silt fence is to prevent sediment carried by sheet flow from leaving the site and entering to natural drainage or any other water body located near the construction site. Silt fencing encourages the sheet flow and reduces the potential for development of rills and gullies. Care should be taken that silt fences are not installed across streams, ditches, waterways or other concentrated flow areas. All silt fencing should be installed along the contour, never up or down a slope. Where all the sheet flow run off is to be stored behind the silt fence, maximum slope length should not exceed as shown in the table 2

Criteria For Silt Fence Placement Land Slope (%) Maximum Slope Length (Above the fence in m) < 2 30.0 2 to 5 22.5 5 to 10 15.0 10 to 20 7.5 > 20* 4.5 * In areas where slope is greater than 20 %, a flat area length of 3.0 m between the toe of the slope and the fence should be provided

Construction Specification:

Silt fencing (Refer Figure 8.4 for Cross-section) consists of 1.0 m wide filter fabric and should be placed on the contour. Incase runoff flow or velocities are very high or where slope exceed vertical height of 3.0 m, silt fencing should be wire reinforced. The contractor should purchase silt fencing in a continuous role to the length of the barrier to avoid the use of joint. Incase of joints, filter cloth should be spliced together only at supporting post, with minimum 15 cm overlap and securely sealed. The pile is drive to the depth of 300 mm into the ground by pressing from the top. The frame will be installed at the edge of stockpiles and at the water bodies along which construction is in progress.

Inspection:

The PIU will inspect location as well as efficiency of silt fencing. The inspection should be done after every 15 days

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and incase of storm water, within 24 hours after the end of rain.

Maintenance:

The contractor should remove sediments, once it has accumulated to one-half the original height of the fence. Filter fabric should be replaced whenever it has deteriorated to such an extent that the effective of the fabric is reduced. Silt fence should remain in place until disturb areas have been permanently stabilized. All the sediments accumulated and properly disposed of before the fence is removed. The operation of removing and disposing have to be monitored by the PIU or Engineer In-charge.

Fabric (Woven Wire Fence Baking)

Side View Front View

Figure 8.4: Cross-section of Silt Fencing

Figure 8.5: Layout Plan of Silt Fencing

Prevention of Water Quality Degradation

Following are the measures that need to be undertaken to prevent contamination of water body during the progress of work and also during the operation phase of the project corridor:  To prevent the entry of the surface run-off from fuel and other contaminants into the wells and other surface water bodies along the corridor, settling ponds and oil receptors shall be constructed.  All the diversion and bunds shall be removed such that there should be minimum amount of sediment generation.

Environmental Impact Assessment 112 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

 All wastes arising from the project shall be disposed off at identified disposal sites in environmentally sound manner.  No vehicles or equipment shall be parked or refueled near the water-body, so as to avoid contamination from fuel and lubricants.  At the construction camps, the sewage system shall be properly designed and built so that no water pollution takes place close to any water body or watercourse.

8.1.4 Air Pollution Control Measures

During the progress of work, construction equipments and plants always have an impact on the environment. The impact can be due to the emissions, dust, noise and oil spills that concern the safety and health of the workers, surrounding settlements and environment as a whole. Following measures need to be undertaken to address the air pollution during the progress of work:

Construction Stage

Selecting the site for plant area and parking lot for equipments and vehicles as per Box 8.3. Box 8.3: Siting of Plant Area / Parking Lot

Avoid the following … Prefer the following …

Lands within 500m of habitations Waste lands

Irrigated agricultural lands Community lands not used for beneficial purposes

Lands within 100m of community water bodies and Lands with an existing access road water sources as rivers

Lands within 100m of watercourses

Grazing lands and lands with tenure rights  Acquiring “No Objection Certificate (NoC)” from the Gujarat State Pollution Control Board before setting up crusher, hot-mix plant and generator.  Ensuring all vehicles must possess Pollution under Control (PUC) Certificate and shall be renewed accordingly.  During the progress of work to minimize -the dust generation, emissions and noise measures as per Table 8.1 shall be undertaken. Table 8.1: Measures to minimize air pollution during the progress of work Concern Causes Measures Water sprinkling Vehicle Fine Materials shall be Transported in Bags or Covered by Tarpaulin during Movement Transportation Dust Tail board shall be properly closed & sealed Generation Crushers Water Sprinkling Concrete-mix Educate the workers for following good practices while material handling Plant Site Selection as per Clause 6.5.2, Section 6.5, IRC Manual for Construction & Hot-Mix Plant Supervision of Bitumen Work Emissions Regular maintenance of Dust Collector as per manufacture schedule Vehicles Regular maintenance as per manufacture schedule Generators Exhaust vent of long length

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Concern Causes Measures Heavy load Exhaust silencer, Regular maintenance as per manufacture schedule vehicles Noise Crushers Siting as per Box 78-3 Shall be kept in closed room and regular maintenance as per manufacture Generators schedule

Operational Stage During the operation stage to control emission due to vehicle movement, following measures need to be undertaken:  By enhancing tree plantation along the project corridor.  Vehicles traveling on the highway should conform to vehicular emission norms.

 Vehicular emissions of critical pollutants (SPM, RSPM, CO, SO2, NOx) will be monitored with regular maintenance of roadside tree plantation.  A monitoring of the effectiveness of the pollution attenuating barriers will be taken up after 5 years from the planting of roadside trees. Based on the results, recommendation for any changes in the mitigation measures or suggestion of additional measures shall be made.

8.1.5 Noise Control Measures

Construction Stage

The plants and equipment used for construction shall strictly conform to existing noise norms. Vehicles and equipments used shall be fitted with exhaust silencers. During routine servicing operations (as per manufacture schedule), the effectiveness of exhaust silencers shall be checked and incase of any defective shall be replaced. The noise level from any item of plants (measured at one meter from the edge of the equipment in free field) such as compactors, rollers, front loaders, concrete mixers, cranes, vibrators and saws shall not exceed 75 dB (A), as specified in the Environmental Protection Rules, 1986.

In construction sites within 150m of the nearest habitation, noisy construction work such as crushing, concrete mixing, batching will be stopped during the night time between 9:00 p.m. and 6:00 a.m. No noisy construction activities will be permitted around the silence zones, a distance of 100m from the sensitive receptors as hospitals, educational institutions etc. Blasting will be carried out as per The Explosives Rules, 1983. Prior intimation of operational hours of the blasting will be given to the people living near such blasting sites. Blasting will not be undertaken in night hours.

To protect construction workers from severe noise impacts, noise standards of industrial enterprises will be strictly enforced, and workers shall be provided with protective devices such as earplugs.

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Operational Stage

Noise Barriers:

Noise barriers have been proposed at specific receptor locations along the corridor based on the receptor, number of users, availability of space for the barrier and predicted noise levels. The following types of noise barriers have been considered for noise attenuation.

 Physical barriers in the form of walls  Rearrangement of the sensitive locations, through changes in the internal planning where possible  Vegetative barriers in the form of thick screen of vegetation

An evaluation of the various types of noise barriers have been made and based on their suitability and extent of noise attenuation, feasible noise barriers have been proposed for the project.

Physical Barriers: attenuate noise level up to a maximum of 20 dB(A). As they do not require any large space, they can be easily constructed. However, there are a few drawbacks.

 High cost involved in the construction of the barriers  Such barriers cause severence on either side of the highway  Such barrier facilitates opportunistic encroachment for urban squatters.

Vegetative Barriers: attenuate noise level up to a maximum of 10dB(A). These barriers require a considerable area and for attenuation of 10 dB(A) they require a depth of 40m.

Other measures for noise level reduction like structural modifications or change in the internal layout of these locations calls for consultation with the community.

During the operation stage, to minimize the impacts due to the noise generated by the vehicles, for institutional areas and hospitals located along the road side institutional plantations have been recommended. Also since the volume of projected traffic being not that significant, structural barriers have not been recommended. The details of locations where vegetative noise barriers have been proposed are presented in Table 8.2. Table 8.2: Locations proposed for Vegetative Barriers Sr. No Existing Km Side 1 9.460 Left 2 21.900 Left 3 29.700 Right 4 30.085 Right 5 39.570 Right 6 52.300 Left 7 86.776 Right

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Sr. No Existing Km Side 8 91.000 Left 9 91.150 Left 10 158.600 Right 11 174.950 Right 12 182.700 Left 13 182.800 Left 14 185.000 LHS 15 192.850 Right 16 201.500 Left 17 206.050 Left 18 268.360 Right 19 274.400 Left 20 278.300 Right 21 278.800 RHS 22 278.850 Left 23 288.250 Right 24 288.700 Left 25 288.900 Left 26 295.200 Right 27 300.480 LHS 28 310.000 Right 29 322.100 Right 30 332.300 Right 31 344.000 Left 32 367.800 Right 33 369.400 Right 34 379.800 Left 35 385.500 Left 36 397.400 Right 37 404.250 Left 38 405.250 Right 39 427.200 Left

Educate the workers regarding… Personal safety measures (such as helmet, footwear, noise mask, ear plug, etc.) and location of safety devices.

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8.1.6 Safety Measures during Interaction with host community Protection of environment with respect to: 8.1.7 Construction: - Trampling of vegetation and cutting of trees for cooking The contractor must educate the workers to - Water body protection undertake the health and safety precautions. The - Storage and handling of materials contractor shall prepare traffic control plan and - Disposal of construction waste drawings containing detailed specifications for diversion, signages as well as location specific traffic detour plan. Other safety requirements that need to be undertaken are as follows: - Adequate lighting arrangement - Adequate drainage system to avoid any stagnation of water - Lined surface with slope 1:40 and provision of lined pit at the bottom end, at the storage and handling of bitumen and oil as well as at the location of generator. - Facilities for provision of first aid

Measures for Road User Safety  Clearing of vegetation at inner curves having access roads so that adequate sight distances are available to the driver. Depending on the speed at that section a sight distance corresponding to 8 seconds reaction time shall be provided.  All major junctions shall be designed adhering to the standards of adequate sight distances and facilities for the local traffic, parking areas, service roads, pedestrian sidewalks and zebra crossings.  Trees that have been saved and are very close to the pavement shall be marked in white paint or have reflective hazard signage on them to alert the driver.  Guardrails shall be provided close to religious structures adjacent to the corridor so that there is no spillage of activities on the carriageway.  Cattle under passes are usually introduced at places where there is substantial movement of people and cattle across the road with no cross drainage structures. The existing road does not have any animal underpasses, but there is significant number of animal crossing the road at some sections. The locations proposed for underpasses along the project alignment are indicated from table 8.3 to 8.6 below. Table 8.3: Locations of Underpasses

Existing Proposed Sr.No Location Chainage Chainage 1 1.100 Budhel Bypass 2 13.620 13.620 Industries 3 17.400 17.575 Industrial location 4 1.800 Bhandariya Bypass 5 1.150 Tansa Bypass 6 33.290 Rajpara Realignment 7 1.455 Trapaj Bypass End 8 48.440 48.440 Industries 9 1.250 Talaja Bypass 10 55.000 55.000 Industries

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Existing Proposed Sr.No Location Chainage Chainage 11 61.000 61.000 Industries 12 1.530 Bhadrad Bypass 13 91.395 Mahuva Bypass Start 14 95.750 95.700 Mahuva-Savarkundla 15 99.260 Mahuva Bypass End 16 108.950 108.720 Nirma Cement Industry 17 1.400 Datardi Bypass 18 127.620 127.600 Pipavav 19 134.320 134.400 Dungar Parada 20 153.332 153.450 Jaffarabad 21 1.100 Hemal Bypass 22 164.423 164.400 Bhada-Timbi 23 0.350 Samter Bypass 24 0.300 Una bypass start 25 8.600 Una bypass End 26 196.175 195.900 Diu-Bhulga 27 199.825 199.825 Revadh 28 0.275 Dholasa Bypass 29 214.000 214.000 Industries 30 223.098 222.400 Kodinar-Amreli 31 225.017 224.300 Kodinar-Kantela 32 228.425 227.660 Ambuja Cement 33 232.258 231.325 Moradia 34 0.400 Prachi Bypass 35 3.400 Prachi Bypass 36 248.825 Gorakhmandi Realignment 37 250.325 Gorakhmandi Realignment 38 257.113 257.300 Athoda 39 17.610 Porbandar Bypass 40 20.785 Table 8.4: Locations of Flyover Existing Proposed Sr.No Location Chainage Chainage 1 24.367 24.400 Port 2 0.000 Trapaj Bypass Start 3 137.526 137.900 Voola-Jaffarabad 4 222.143 221.400 Kodinar 5 11.400 Porbandar Bypass 6 443.700 443.100 Jamnagar

Environmental Impact Assessment 118 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 8.5: Locations of Cattle Underpass Existing Proposed Sr.No Location Chainage Chainage 1 1.900 Adhewada Bypass 2 44.153 44.140 Piprala 3 67.390 Borda Realignment 4 70.850 70.780 Moti Jagdar 5 74.960 Longdi Realignment 6 80.350 80.320 Unchakotta-Bagdhana 7 101.835 101.680 Devadiya 8 107.424 107.200 Billadi 9 116.500 116.500 10 121.989 122.000 Shasbantar-Dungar 11 142.275 142.550 Bharmuthala 12 148.706 148.800 Khamba 13 161.500 161.500 Sheyana 14 169.973 170.200 15 191.900 Nadholi Realignment 16 198.679 198.300 Chokkada 17 210.658 210.400 Velava 18 237.020 235.850 20 261.400 Kajali Realignment

Table 8.6: Locations of Pedestrian Underpass Existing Sr.No Proposed Ch. Location Kilometer 1 36.700 36.800 School 2 61.500 61.500 School 3 92.375 92.375 School 4 97.700 97.635 School 5 98.600 98.530 School 6 116.900 116.900 School 7 118.000 118.000 School 8 177.500 177.500 School 9 256.470 256.600 School

Accidents Involving Hazardous Materials

Accidents involving hazardous chemicals will generally be catastrophic to the environment, though the probability of occurrence is low. 'The Hazardous Wastes (Management and Handling) rules, 2000 shall be compiled to minimize the risk of accident involving transportation of hazardous material. For delivery of hazardous substances, three certificates issued by transportation department, viz., permit license, driving license and guarding license shall be

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required. These shall be issued and checked thoroughly. Vehicles delivering hazardous substances will be printed with appropriate signs.

In case of spillage, the report to relevant departments will be made and instructions followed in taking up the contingency measures immediately. Hazardous landfill site with line system will be designed at various campsites as per MoEF guidelines.

8.1.8 Bus Stop

There are several existing bus stops along the project corridor. Generally these stops are associated with a settlement area or an intersection with a crossroad. A number of bus stops have been proposed. The details of bus stop locations along the project corridor are given in Table 8.7. Table 8.7: Location of Bus Stops SL.No Chainage Side 1 3.200 RHS 2 4.000 RHS 3 17.700 RHS 4 19.800 RHS 5 42.700 LHS 6 133.200 LHS 7 144.000 LHS 8 148.800 LHS 9 154.000 RHS 10 161.600 LHS 11 173.700 LHS 12 178.700 LHS 13 228.000 LHS 14 232.100 LHS 15 234.600 RHS 16 251.800 RHS 17 256.600 LHS 18 281.400 RHS 19 288.500 RHS 20 292.000 RHS 21 295.300 LHS 22 300.200 LHS 23 306.600 LHS 24 325.900 LHS 25 336.500 RHS

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SL.No Chainage Side 26 350.500 LHS 27 385.200 LHS 28 389.400 RHS 29 402.950 RHS 30 405.200 RHS 31 405.950 RHS 32 424.800 LHS 33 426.800 LHS 34 436.800 RHS

8.1.9 Avoidance / Enhancement Measures for Cultural Properties

53 religious structures are being affected due to widening of the project road. Apart from these, many shrines are found to be present within the proposed ROW. The affected temples are to be relocated. The relocation cost has been provided in the RAP budget in VolumeV. The details of the temple to be relocated are as follows:

Sl No Number of Temples Description Side Falling within the 1. 53 proposed ROW i.e. 53 RHS & LHS religious structures

8.1.10 Highway Landscaping

Roadside plantation along the project corridor has to cut. Of the trees to be cut, three times the number is to be planted as compensatory plantation. Common plants generally recommended for stretches passing through rural areas are Amla (Emblica officinalis) alternating with shaded trees like, Ailanthus excelsa. Medium trees like Sapindus emarginta, Derris indica, are ideal for screening.

Near market places and congested areas, trees known for behaving as ‘pollution sink’ are proposed. Thus, trees which absorb pollutants, filter the air from pollutants, and act as noise barrier would be planted. Near sensitive areas like schools and hospitals, tall trees with thick canopies can create a wind screen through which the air can be filtered and the noise levels be considerably reduced. In addition tall shrubs would be planted to act as screens against noise and air pollution. Species recommended include Adhatoda vasica, Hibiscus hirtus, Withania somnifera.

Plantation in Medians

Careful consideration should be given to the cross section to ensure driver recovery, mowing access, and drainage. Vegetated medians offer excellent contrast to the travel lanes, making

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their edges more clearly evident. Additionally, turf areas offer visual relief and glare reduction in large expanses of pavement in multilane highways.

Turfing and median plantation has been proposed along the entire stretch.The shrubs planted in the median (Table 8.8) should be of low or medium height for prevention of the headlight glare. One to two rows of flowering shrubs have been provided according to the varying width of the median in different sections. In sections where the median width is less than 1.5m, only grass turfing is proposed. Medians with turf also hide small litter objects better than bare pavement, helping to keep the roadway neater in appearance.

At locations where a drain runs through the median woody plants are recommended so that drainage in the median will not be obstructed. Where space and drainage patterns allow, berms may reduce or prevent median crossings and reduce headlight glare. The species to be selected are mentioned in the section on Plantation. Table 8.8: Recommended Shrubs /Ground Cover for medians Suitable Shrubs/small Trees for Median Suitable Ground cover-Creepers and grasses for Median S. Species Species S.No No Botanical Name Common Name Botanical Name Common Name 1 Adhatoda vasica Ardusi 1 Coccinia grandis ( climber) Giloda 2 Apluda mutica Bhangoru 2 Leffery echinata (climber) Kakarpada 3 Daturo innoxia Daturo 3 Cucumis setosus(twinner) Tidho 4 Kaneri 4 Cyclea peltata (twinner) Kalipat 5 Bogemville 5 Ipomoea quamoclit Kamani 6 Ipomoea aquatic ( creeper) Nadinibhaji 7 Ipomoea penitigridis ( creeper) Rota belari

Environmental Impact Assessment 122 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH- 123 8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

9. ENVIRONMENT MANAGEMENT PLAN

The Environment Management measures shall be implemented during the various stages of the project – Pre-construction stage, Construction Stage and Operation Stage. The EMP is described below:

9.1 PRE-CONSTRUCTION STAGE

9.1.1 Pre-construction activities by PIU

Prior to the contractor mobilization, the PIU/Concessionaire will ensure that an encumbrance free CoI is handed over to enable the start of construction. The RoW clearance involves the following activities:  Acquisition of land and structures,  Clearance of the RoW including removal of trees, and  Relocation of common property resources impacted, including cultural properties as temples and community assets as hand pumps and other utilities.

9.1.2 Pre-construction activities by BOT Concessionaire/Independent Engineer

The pre-construction stage involves mobilization of the BOT Concessionaire, the activities undertaken by the concessionaire pertaining to the planning of logistics and site preparation necessary for commencing construction activities. The activities include:  Joint field verification of EMP by the Independent Engineer and Concessionaire  Modification (if any) of the contract documents by the Independent Engineer.  Procurement of construction equipment / machinery such as crushers, hot mix plants, batching plants and other construction equipment and machinery.  Identification and selection of material sources (quarry and borrow material, water, sand etc).  Selection, design and layout of construction areas, hot mix and batching plants, labour camps etc  Planning traffic diversions and detours, including arrangements for temporary land acquisition.  Apply for and obtain all the necessary clearances /NOC’s/ consents from agencies concerned.

9.2 CONSTRUCTION STAGE

9.2.1 Construction Stage activities by BOT Concessionaire

Construction stage is the most crucial stage in terms of activities that require careful management to avoid environmental impacts. Activities that trigger the need for environmental measures to be followed include:

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 Imbibing environmental principles at all stages of construction as good engineering practices.  Implementation of site-specific mitigation/management measures suggested  Monitoring the quality of environment along the construction sites (as air, noise, water, soil) and  Enhancement designs at specific locations suggested.  Tree plantation along the corridors and bypasses and landscaping along junctions by the Forest Department.  Monitoring of environmental conditions through approved monitoring agency

There are several other environmental issues that have been addressed as part of good engineering practices, the costs for which have been accounted for in the Engineering Costs. They include improvement of roadside drainage, provision of additional cross drainage structures or rising of road height in flood prone stretches, provision of cattle crossings and reconstruction and improvement of bunds of the affected water bodies.

9.2.2 Construction Stage Activities by PIU

The PIU/Independent Cosnultant shall be involved in the smooth execution of the project and assessing the BOT Concessionaire during this phase. Their work shall include but not be limited to:  Monitoring and guiding the BOt Concessionaire on adopting good environmental and engineering practices.  Arrangement of plantation through the Forest Department.  Arranging training to the BOT Concessionaire and other stakeholders according to the needs arising.

9.3 OPERATION STAGE

Operation stage activities that are to be carried out by the BOT Concessionaire and supervised by PIU are:  Monitoring operational performance of the various mitigation/enhancement measures carried out as part of the project.  Monitoring of Environmental conditions through approved monitoring agency

9.4 OTHER ACTIVITIES Training of Implementation agency staff towards project specific issues of EMP implementation

Environmental Impact Assessment 124 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Table 9.1: Environmental Management Measures Sl. No Activities Management Measure Location Reference 1.0 PRE-CONSTRUCTION STAGE 1.1 Pre-construction activities by PIU 1.1.1 Land Acquisition, The acquisition of land and private Corridor of Impact Land R&R properties will be carried out in Acquisition accordance with the RAP and Act of NHAI entitlement Framework for the project. It will be ensured that all R&R activities are to be completed before the construction activity starts, on any sub- section of project roads. It will be ensured by the PIU that the resettlement sites required for the sections to be taken up for construction in the first year are to be completed prior to the contractor mobilization at site. The PIU will identify suitable locations for resettlement sites in consultation with the PAPs to be relocated. Resettlement sites will be in line with the requirements of generic EMP for resettlement sites. 1.1.2 Tree Cutting Trees will be removed from the Corridor of Impact Design Corridor of Impact and construction MoRTH 201.6 sites before commencement of Forest Construction with prior intimation to the Conservation Forest Department. Forest Clearance Act, 1980 will be obtained For cutting of roadside trees notified as protected forest. Three times the trees to be cut will be planted. Forest department will maintain the plantation and NHAI will deposit the money for tree plantation. 1.1.3 Utility Relocation All utilities lost due to the project will be Corridor of Impact As in RAP relocated with prior approval of the concerned agencies before construction starts, on any sub-section of the project road. 1.1.4 Relocation of All cultural properties within the CoI, Corridor of Impact. Cultural Properties whose structure is getting affected, will be relocated at suitable locations, as desired by the community before construction starts. Local community meetings (facilitated by NGOs entrusted with the responsibility of R&R implementation) will be held to discuss relocation aspects, siting of structures. 1.1.5 Replacement of All common property resources such as Corridor of Impact. Common Property community sources of water will be Resources replaced. The replacement will be complete before construction starts. 1.2 Pre-construction activities by the Concessionaire / Contractor / Independent Engineer Field Verification and Modification of 1.2.1 the Contract Documents

Environmental Impact Assessment 125 125 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference Joint Field The Engineer and the Contractor will All locations along the Project Verification carry out joint field verification of the project corridor where Requirements 1.2.1.1 EMP. The efficacy of the mitigation/enhancement/ mitigation/enhancement measures monitoring measures suggested in the EMP will be checked. are proposed Modification of the If required, the Engineer will modify the All locations along the Contract Documents EMP and Contract documents project corridor where (particularly the BOQs) changes in 1.2.1.2 mitigation/enhancement/ monitoring measures are felt necessary Procurement of 1.2.2 Machinery 1.2.2.1 Crushers, Hot-mix Specifications of crushers, hot mix Contract, Plants & Batching plants and batching plants will comply MoRTH: Plants with the requirements of the relevant 111.1, GoI Air current emission control legislations. & Noise Standards, OSHA Standards 1.2.2.2 Other Construction The discharge standards promulgated Contract, Vehicles, Equipment under the Environment Protection Act, Environment and Machinery 1986 will be strictly adhered to. Protection All vehicles, equipment and machinery Act, 1986 & to be procured for construction will MoRTH: conform to the relevant Bureau of 111.1 Indian Standard (BIS) norms. Noise limits for construction equipments to be procured such as compactors, rollers, front loaders, concrete mixers, cranes (moveable), vibrators and saws will not exceed 75 dB (A), measured at one meter from the edge of the equipment in free field, as specified in the Environment (Protection) Rules, 1986. 1.2.3 Identification & Selection of Material Sources 1.2.3.1 Borrow Areas Arrangement for locating the source of At all borrow area MoRTH: supply of material for embankment and locations suggested for 305.2.2.2 sub-grade as well as compliance to the project. environmental requirements, as Annexure 8.1, applicable, will be the sole Annexure 8.2 responsibility of the contractor. (location of Siting of borrow areas to be as per the recommended Guidelines presented in Annexure 8.1. borrow The contractor will not use any of the locations) and locations described here for borrowing Annexure 8.3 (within and upto 1000m either side of Reserve Forest/ Ecologically sensitive areas). Locations identified by the contractor shall be reported to the Engineer. Format for reporting shall be as per Form EM3, Annexure 9.1 Planning of haul roads for accessing borrow materials will be undertaken

Environmental Impact Assessment 126 126 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference during this stage. The haul roads should be routed to avoid agricultural areas. In addition to testing for the quality of borrow materials by the SC, the environmental personnel of the SC will be required to inspect every borrow area location prior to approval. 1.2.3.2 Quarries The Contractor will identify materials All quarries MoRTH: from existing licensed quarries with the recommended to be 111.3 suitable materials for construction. used in the project Apart from approval of the quality of the quarry materials, the Engineer’s Annexure 8.4 representative will verify the legal status of the quarry operation, as to whether approval under statutory is obtained. Some of the locations identified during this stage is presented in Annexure 8.4. 1.2.3.3 Water The contractor will source the All rivers / surface water Contract requirement of water preferentially from bodies that can be used surface water bodies, as rivers and in the project tanks in the project area. To avoid disruption/disturbance to other water users, the contractor will extract water from fixed locations. The contractor shall consult the local people before finalizing the locations. Only at locations where surface water sources are not available, the contractor can contemplate extraction of ground water. Consent from the Engineer that no surface water resource is available in the immediate area for the project is a pre-requisite prior to extraction of ground water. The contractor will need to comply with the requirements of the state Ground water department and seek their approval for doing so. 1.2.3.4 Sand The contractor will identify sand quarries with requisite approvals for the extraction of sand for use in the project 1.2.4 Labour The contractor will use unskilled labour Along project corridor at Contract Requirements drawn from local communities to avoid construction sites any additional stress on the existing facilities (medical services, power, water supply, etc.) 1.2.5 Setting up construction sites 1.2.5.1 Construction Camp Siting of construction camps is to be as All Construction Contract Locations – per the guidelines presented in Workers Camps Annexure 8.5 Selection, Design & Annexure 8.5 of EMP. Locations including areas in Section Layout identified by the contractor shall be immediate vicinity. 1.2.3.1 reported as per format EM2, Annexure 9.1. Annexure 9.1 Construction camps will not be proposed: (i)Within 1000m of locations as

Environmental Impact Assessment 127 127 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference described in Section 1.2.3.1 (Reserve Forest /Ecologically sensitive areas). (ii)Within 1000m from the nearest habitation to avoid conflicts and stress over the infrastructure facilities, with the local community. (iii) Layout of construction camps will be as per the conceptual design presented in Drawing 3.5.1 of Annexure 8.5. (iv) Locations for stockyards for construction materials will be identified at least 1000 m from watercourses. (v) The waste disposal and sewage system for the camp will be designed, built and operated such that no odour is generated. (vi) Unless otherwise arranged by the local sanitary authority, arrangements for disposal of excreta suitably approved by the local medical health or municipal authorities or as directed by Engineer will need to be provided by the contractor. 1.2.5.2 Hot Mix Plants & Hot mix plants and batching plants will Contract Batching Plant be sited sufficiently away from reserve MoRTH Location forest, habitation, agricultural clause 111.5 operations or industrial establishments. Such plants will be located at least 1000m away from the nearest habitation, preferably in the downwind direction. 1.2.6 Arrangements for The contractor as per prevalent rules Areas temporarily Temporary Land will carry out negotiations with the land acquired for Requirement owners for obtaining their consent for construction sites/ hot temporary use of lands for construction mix plants / borrow sites/ hot mix plants /traffic detours areas / diversions/ /borrow areas etc. detours. The Engineer will be required to ensure that the clearing up of the site prior to handing over to the owner (after construction or completion of the activity) is included in the contract. 2.0 CONSTRUCTION STAGE 2.1 Construction Stage Activities by Contractor 2.1.1 Site Clearance 2.1.1.1 Clearing and Vegetation will be removed from the Corridor of Impact Design Grubbing CoI before the commencement of MoRTH 201 Construction. 111.15.1, Sub All works will be carried out such that clause the damage or disruption to flora is 111.15.4 minimum. Only ground cover / shrubs that impinge directly on the permanent works or necessary temporary works will be removed with prior approval from the Engineer. The contractor, under any circumstances will not

Environmental Impact Assessment 128 128 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference damage trees (in addition to those already felled with prior permission from the forest department). Vegetation only with girth of over 30 cm will be considered as trees and shall be removed as per Activity 1.1.2. 2.1.1.2 Dismantling of The culverts will be dismantled At locations were bridge MoRTH 202.2 Bridgework / carefully and the resulting materials so works and culverts are Culverts removed as not to cause damage to proposed. the part of the structure retained and other properties and structures nearby. All necessary measures will be taken while working close to cross drainage channels to prevent earthwork, stonework, materials and appendage as well as the method of operation from impeding cross-drainage at rivers, streams, water canals and existing irrigation and drainage systems. 2.1.1.3 Generation of Debris Debris generated due to the Throughout Project MoRTH 202.5 from dismantling of dismantling of the existing pavement Corridor MoRTH 517 pavement structures structure shall be suitably reused in the proposed construction, subject to the Annexure 8.7 suitability of the material and the Annexure 9.1 approval of the Engineer Unutilized debris material shall be suitably disposed off by the contractor, either through filling up of borrow areas created for the project or at pre- designated dump locations, subject to the approval of the Engineer. Debris generated from pile driving or other construction activities shall be disposed such that it does not flow into the surface water bodies or form mud puddles in the area. Disposal sites shall be identified by the contractor as per guidelines provided in Annexure 3.6. The identified locations will be reported to the Engineer as per format EM1, Annexure 9.1 2.1.1.4 Non-bituminons As far as possible construction waste Dump site locations Contract construction waste will be utilized in road construction. MoRTH: disposal Location of disposal sites will be 201.4 & 202.5 finalized prior to completion of the Section earthworks on any particular section of 1.2.3.1 the road. As local villagers requested Annexure 8.6 for preparing play ground in the hill section during consultation, rest of the solid waste will be utilized for preparation of playgrounds. Solid waste will also be utilized for preparation of construction camps. After providing these facilities, if disposal of waste required, contarctor will identify the site as the guidelines for siting of disposal sites (Annexure 8.6). 2.1.1.5 Bituminous wastes The disposal of residual bituminous Throughout Project Contract & disposal wastes will be done by the contractor at Corridor Annexure 8.6

Environmental Impact Assessment 129 129 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference secure landfill sites, with the requisite MoRTH: approvals for the same from the 201.4 concerned government agencies. 2.1.2 Planning Traffic Temporary diversions will be All along the Project MoRTH: Diversions & constructed with the approval of the Corridor. 112.1 Detours Engineer. Detailed Traffic Control Plans will be MoRTH: prepared and submitted to the 112.4 Engineer for approval, 5 days prior to commencement of works on any section of road. The traffic control plans MoRTH:112.2 shall contain details of temporary MoRTH: diversions, details of arrangements for 112.5 construction under traffic, details of traffic arrangement after cessation of work each day, safety measures for transport of hazardous material and arrangement of flagmen. Environmental personnel of the Engineer will assess the environmental impacts associated as the loss of vegetation, productive lands and the arrangement for temporary diversion of the land prior to the finalisation of diversions and detours. Special consideration will be given to the preparation of the traffic control plan for safety of pedestrians and workers at night. The Contractor will ensure that the diversion/detour is always maintained in running condition, particularly during the monsoon to avoid disruption to traffic flow. He shall inform local community of changes to traffic routes, conditions and pedestrian access arrangements. The temporary traffic detours will be kept free of dust by frequent application of water. 2.1.3 Procurement of Construction Materials 2.1.3.1 Borrow Areas No borrow area will be opened without All along the project MoRTH: permission of the Engineer corridor, all access 305.2.2.2 Borrow pits will not be dug continuously roads, sites temporarily IRC 10 1961 in a stretch. The location, shape and acquired & all borrow size of the designated borrow areas will areas be as approved by the Engineer and in Annexure 8.1 accordance to the IRC recommended practice for borrow pits for road MoRTH: embankments (IRC 10: 1961) 111.2, Sub The borrowing operations will be clause carried out as specified in the 111.15.2 guidelines for siting and operation of borrow areas (Annexure 8.1) The unpaved surfaces used for the haulage of borrow materials will be maintained dust free by the contractor.

Environmental Impact Assessment 130 130 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference Since dust raising is the only impact along the haul roads sprinkling of water will be carried out twice a day along such roads during their period of use. 2.1.3.2 Stripping, stocking The topsoil from borrow areas, areas of Throughout Project MoRTH: and preservation of cutting and areas to be permanently Corridor, where 301.3.2 & top soil covered will be stripped to a depth of productive land is MoRTH: 150mm and stored in stockpiles. At acquired. 305.3.3 least 10% of the temporarily acquired MoRTH: area will be earmarked for storing 301.7 & topsoil. MoRTH: The stockpile will be designed such 305.3.9 that the slope does not exceed 1:2 (vertical to horizontal), and the height of Annexure 9.1 the pile is to be restricted to 2m. Stockpiles will not be surcharged or otherwise loaded and multiple handling will be kept to a minimum to ensure that no compaction will occur. The stockpiles will be covered with gunny bags or tarpaulin. It will be ensured by the contractor that the topsoil will not be unnecessarily trafficked either before stripping or when in stockpiles. Such stockpiled topsoil will be returned to cover the disturbed area and cut slopes. The management of topsoil shall be reported regularly to the Engineer as per format EM6, Annexure 9.1 2.1.3.3 Quarries The quarry operations will be All along the project MoRTH: undertaken within the rules and corridor and all haul 111.3 regulations in force. roads 2.1.3.4 Blasting Except as may be provided in the All blasting and Pre- MoRTH: contract or ordered or authorized by the splitting Sites. 302.4 Engineer, the Contractor will not use explosives. Where the use of explosives is so provided or ordered or authorized, the Contractor will comply with the requirements of the following Sub- Clauses of MoRTH 302 besides the law of the land as applicable. The Contractor will at all times take every possible precaution and will comply with appropriate laws and regulations relating to the import, handling, transportation, storage and use of explosives. The contractor will at all times when engaged in blasting operations, post sufficient warning flagmen, to the full satisfaction of the Engineer. The Contractor will at all times make full liaison with and inform well in advance and obtain such permission as is required from all Government Authorities, public bodies and private parties whomsoever concerned or

Environmental Impact Assessment 131 131 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference affected or likely to be concerned or affected by blasting operations. Blasting will be carried out only with permission of the Engineer. All the statutory laws, regulations, rules etc., pertaining to acquisition, transport, storage, handling and use of explosives will be strictly followed. Blasting will be carried out during fixed hours (preferably during mid-day) or as permitted by the Engineer. The timing should be made known to all the people within 1000m (200m for pre- splitting) from the blasting site in all directions. 2.1.3.5 Transporting All vehicles delivering materials to the All along the Project MoRTH: Construction site will be covered to avoid spillage of corridor and all haul 111.9 Materials materials. roads All existing highways and roads used by vehicles of the contractor, or any of his sub-contractor or suppliers of materials and similarly roads which are part of the works will be kept clean and clear of all dust/mud or other extraneous materials dropped by such vehicles The unloading of materials at construction sites close to settlements will be restricted to daytime only. 2.1.3.6 Water Extraction Procurement of water is to be carried All water bodies Section out as per Section 1.2.3.3 The recommended to be 1.2.3.3 contractor will minimize wastage of used in the project water during construction. 2.1.4 Infrastructure The Contractor during the progress of Construction camps Contract provisions at work will provide, erect and maintain construction camps necessary (temporary) living accommodation and ancillary facilities for labour to standards and scales approved by the resident Engineer. There shall be provided within the precincts of every workplace, latrines and urinals in an accessible place, and the accommodation, separately for each for these, as per standards set by the Building and other Construction Workers (regulation of Employment and Conditions of Service) Act, 1996. Except in workplaces provided with water-flushed latrines connected with a water borne sewage system, all latrines shall be provided with dry-earth system (receptacles) which shall be cleaned at least four times daily and at least twice during working hours and kept in a strict sanitary condition. Receptacles shall be tarred inside and outside at least once a year. If women are employed, separate latrines and urinals, screened from those for men

Environmental Impact Assessment 132 132 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference (and marked in the vernacular) shall provided. There shall be adequate supply of water, close to latrines and urinals. All temporary accommodation must be constructed and maintained in such a fashion that uncontaminated water is available for drinking, cooking and washing. The sewage system for the camp must be designed, built and operated so that no health hazard occurs and no pollution to the air, ground or adjacent watercourses takes place. Compliance with the relevant legislation must be strictly adhered to. Garbage bins must be provided in the camp shall be regularly emptied and the garbage disposed off in a hygienic manner. Construction camps are to be sited at least 1000m away from the nearest habitation and adequate health care is to be provided for the work force. Unless otherwise arranged for by the local sanitary authority, arrangement for disposal of excreta by putting a layer of night soils at the bottom of a permanent tank prepared for the purpose shall be taken up by the contractor. It should be covered with 15 cm layer of waste or refuse and then with a layer of earth for a fortnight (by then it will turn into manure).

Environmental Impact Assessment 133 133 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference 2.1.5 Operation of All vehicles and equipment used for All construction Environment construction construction will be fitted with exhaust equipments and (Protection) equipments and silencers. During routine servicing vehicles Rules, 1986 vehicles operations, the effectiveness of exhaust silencers will be checked and if Monitoring found to be defective will be replaced. Plan Noise limits for construction equipment Table 9.1 & used in this project (measured at one Table 9.2 metre from the edge of the equipment in free field) such as compactors, rollers, front loaders, concrete mixers, cranes (moveable), vibrators and saws will not exceed 75 dB(A), as specified in the Environment (Protection) Rules, 1986 Notwithstanding any other conditions of contract, noise level from any item of plant(s) must comply with the relevant legislation for levels of noise emission. The contractor will ensure that the AAQ concentrations at these construction sites are within the acceptable limits of industrial uses in case of hot mix plants and crushers and residential uses around construction camps. Dust screening vegetation will be planted on the edge of the RoW for screening dust crusher. Monitoring of the exhaust gases and noise levels will be carried out by the agency identified for Environmental Monitoring for the project. 2.1.6 Material Handling at All workers employed on mixing All construction sites MoRTH: Site asphaltic material, cement, lime 111.6 mortars, concrete etc., will be provided MoRTH: 105 with protective footwear and protective goggles. MoRTH: Workers, who are engaged in welding 111.4, Sub works, would be provided with welder’s clause protective eye-shields. 111.15.3 Workers, engaged in stone breaking IS: 6994 (Part activities will be provided with I) – 1973, protective goggles and clothing and will IS: 14352 – be seated at sufficiently safe intervals. 1996, The use of any herbicide or other toxic IS: 2925 - chemical will be strictly in accordance 1984 with the manufacturer’s instructions. The Engineer will be given at least 6 working days notice of the proposed use of any herbicide or toxic chemical. A register of all herbicides and other toxic chemicals delivered to the site will be kept and maintained up to date by the Contractor. The register will include the trade name, physical properties and characteristics, chemical ingredients, health and safety hazard information, safe handling and storage procedures, and emergency and first aid

Environmental Impact Assessment 134 134 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference procedures for the product. No man below the age of 14 years and no woman will be employed on the work of painting with products containing lead in any form. No paint containing lead or lead products will be used except in the form of paste or readymade paint. Face masks will be supplied for use by the workers when paint is applied in the form of spray or a surface having lead paint dry rubbed and scrapped. 2.1.7 Precautionary/Safety All relevant provisions of the Factories All construction sites Factories Act, Measures During Act, 1948 and the Building and other 1948 and the Construction Construction Workers (regulation of Building and Employment and Conditions of Service) other Act, 1996 will be adhered to. Construction Adequate safety measures for workers Workers during handling of materials at site (regulation of (Section 2.1.6) will be taken up. Employment The contractor has to comply with all and regulations regarding safe scaffolding, Conditions of ladders, working platforms, gangway, Service) Act, stairwells, excavations, trenches and 1996 safe means of entry and egress. Section 2.1.6 MoRTH 105 Sub clause 111.11 2.1.8 Protection of All necessary and adequate care shall All construction sites MoRTH: Religious Structures be taken to minimize impact on cultural 111.15.9 properties (which includes cultural sites and remains, places of worship including temples, mosques, churches and shrines, etc., graveyards, monuments and any other important structures as identified during design and all properties/sites/remains notified under the Ancient Sites and Remains Act). No work shall spillover to these properties, premises and precincts. Access to such properties from the road shall be maintained clear and clean. 2.1.9 Chance found All fossils, coins, articles of value of All construction sites Archaeological antiquity, structures and other remains property or things of geological or archaeological interest discovered on the site shall be the property of the Government, and shall be dealt with as per provisions of the relevant legislation. The contractor shall take reasonable precaution to prevent his workmen or any other persons from removing and damaging any such article or thing. He shall, immediately upon discovery thereof and before removal acquaint the Engineer of such discovery and carry out the Engineer’s instructions for

Environmental Impact Assessment 135 135 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference dealing with the same, awaiting which all work shall be stopped. The Engineer shall seek direction from the Archaeological Society of India (ASI) before instructing the Contractor to recommence work on the site. 2.1.10 Earthworks 2.1.10.1 Excavations All excavations will be done in such a All along the project MoRTH manner that the suitable materials corridor 301.3.3 available from excavation are MoRTH satisfactorily utilized as decided upon 304.3.6 beforehand. IS:3764 The excavations shall conform to the lines, grades, side slopes and levels shown in the drawings or as directed by the engineer. While planning or executing excavation the contractor shall take all adequate precautions against soil erosion, water pollution etc (clause 306) and take appropriate drainage measures to keep the site free of water (clause 311), through use of mulches, grasses, slope drains and other devices. The contractor shall take adequate protective measures to see that excavation operations do not affect or damage adjoining structures and water bodies. For safety precautions guidance may be taken from IS: 3764. Earth fill Embankment and other fill areas, Along earth fill areas MoRTH unless other wise permitted by the 305.3.5.3 Engineer, be constructed evenly over their full width and the contractor will control and direct movement of construction vehicles and machinery over them 2.1.10.2 Stripping, stocking Stock piling of top soil as per Section All along the project Section and preservation of 2.1.3.2 corridor 2.1.3.2 top soil The stockpiles will be located at least 100m from watercourses. 2.1.10.3 Drainage In addition to the design requirements, All along the project requirements at the contractor will take all desired corridor construction sites measures as directed by the Engineer to prevent temporary or permanent flooding of the site or any adjacent area. 2.1.10.4 Dust All earthwork will be protected in a All along the project MoRTH 111.8 manner acceptable to the Engineer to corridor minimise generation of dust. The contractor will take every precaution to reduce the level of dust along construction sites involving earthworks, by frequent application of water. 2.1.10.5 Contamination of Vehicle/machinery and equipment All along the project MoRTH 306 & soil operation, maintenance and refueling corridor MoRTH 311 will be carried out in such a fashion that Section

Environmental Impact Assessment 136 136 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference spillage of fuels and lubricants does not 2.1.3.2. contaminate the ground. Oil interceptor will be provided for vehicle parking, wash down and refueling areas within the construction camps. Fuel storage will be in proper bunded areas. All spills and collected petroleum products will be disposed off in accordance with MoEF and SPCB guidelines. Fuel storage and refilling areas will be located at least 1000m from rivers and irrigation ponds or as directed by the Engineer. In all fuel storage and refueling areas, if located on agricultural land or areas supporting vegetation, the topsoil will be stripped, stockpiled and returned after cessation of such storage and refueling activities as per Section 2.1.3.2 2.1.10.6 Compaction of soil To minimize soil compaction, All along the project Annexure ‘A’ construction vehicle, machinery and corridor to MoRTH equipment will move or be stationed in 501 designated area (RoW or CoI, haul roads as applicable) only. The haul roads for construction materials should be routed to avoid agricultural areas 2.1.10.7 Silting, Silt fencing will be provided around Water bodies falling Environmental Contamination of stockpiles at the construction sites along the project Protection Water bodies close to water bodies. The fencing corridor. Act, 1986 needs to be provided prior to commencement of earthworks and continue till the stabilization of the embankment slopes, on the particular sub-section of the road. Construction materials containing fine particles will be stored in an enclosure such that sediment-laden water does not drain into nearby watercourses. All discharge standards promulgated under Environmental Protection Act, 1986, will be adhered to. All liquid wastes generated from the site will be disposed off as acceptable to the Engineer. 2.1.10.8 Cutting/Filling of Earth works shall be undertaken such Surface Water bodies Contract Surface water that the existing embankments of water whose water storage bodies bodies are not disturbed. In case of capacity is affected by cutting of embankments, the same the project and whose shall be reconstructed with appropriate embankments are being slope protection measures and cut adequate erosion control measures. Filling of surface water bodies will be compensated by digging an equal volume of soil for water storage. Such dug-up soil will be used for spreading as topsoil. Wherever digging is undertaken, the banks will be protected as designed or

Environmental Impact Assessment 137 137 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference as approved by the Engineer. The excavation will be carried out in a manner so that the side slopes are no steeper than 1 vertical to 4 horizontal, otherwise slope protection work, as approved by the Engineer will be provided. As far as practicable, and as approved by the Engineer, excavation for replacement of water bodies will be at the closest possible place/location, with respect to the original water body or part thereof consumed by filling. 2.1.10.9 Sub-Base & Base The contractor will take all necessary All along the project Annexure A to measures/ precautions to ensure that corridor MoRTH 501 the execution of works and all associated operations are carried out in conformity with statutory and regulatory environmental requirements including those prescribed in Annexure A to MoRTH 501. Section 2.1.6 The contractor will plan and provide for remedial measures to be implemented Section in event of occurrence of emergencies 2.1.10.5 such as spillage of oil or bitumen or chemicals. The contractor will provide Section 2.1.5. the Engineer with a statement of

measures that he intends to implement

in event of such an emergency, which Section will include a statement of how he 2.1.3.5 intends to adequately train personnel to Section 2.1.7 implement such measures. Adequate safety measures for workers during handling of materials at site (Section 2.1.6) will be taken up. The contractor will take every precaution to reduce the level of dust along construction sites by frequent application of water as per Section 2.1.10.5 Noise levels from all vehicles and equipment used for construction will conform to standards as specified in Section 2.1.5. Construction activities involving equipments with high noise levels will be restricted to the daytime. Transport of materials for construction will be as per Section 2.1.3.5 The contractor will provide for all safety measures during construction as per Section 2.1.7 2.1.11 Surfacing The contractor will take all necessary All along the project Annexure A to means to ensure that works and all corridor MoRTH 501 associated operations are carried out in conformity with Annexure A to MoRTH Section 2.1.6 501. All workers employed on mixing Section 2.1.5 asphaltic material etc. will be provided

Environmental Impact Assessment 138 138 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference with protective footwear as specified in Section 2.1.6. Section Noise levels from all vehicles and 2.1.3.5 equipment used for surfacing will Section 2.1.7 conform to standards as specified in Section 2.1.5. Construction activities involving equipments with high noise levels will be restricted to the daytime. Transport of materials for construction will be as per Section 2.1.3.5 The contractor will provide for all safety measures during construction as per Section 2.1.7 2.1.12 Bridge Works & While working across or close to the At locations where MoRTH 2500 Culverts rivers, the Contractor will not disrupt bridge works and the flow of water. If for any bridgework, culverts are proposed. etc., closure of flow is required, the Contractor apart from obtaining the requisite clearances from the PWD (irrigation department) will seek approval of the Engineer. The Engineer will have the right to ask the Contractor to serve notice on the downstream users of water sufficiently in advance. Construction over and close to the non- perennial streams will be undertaken in the dry session. Construction work expected to disrupt users and impacting community water bodies will be taken up after serving notice on the local community. Dry stone pitching for apron and revetment will be provided for bridges and cross drainage structures. 2.1.13 Mitigation Measures Provision is made for vegetative noise Annexure 8.8 Noise Rule for Noise Sensitive barrier at locations exceeding operation 2002 Receptors stage noise levels. Other noise mitigation options shall be explored based on site conditions. Details of noise barrier at the identified sensitive receptors are presented in Annexure 3.8. The measures shall be taken during construction stage only in case of excessive noise causing disturbance to the sensitive receptors otherwise the measures shall be implemented in operation stage. 2.1.14 Road Furniture Road furniture including footpaths, All along the project MoRTH 801 railings, storm water drains, crash corridor barrier, traffic signs, speed zone signs, pavement markers and any other such items will be provided as per design 2.1.15 Enhancements Enhancement of all cultural properties, water bodies, incidental spaces has been detailed out. (Refer drawing volume of the Design report). 2.1.16 Monitoring The contractor will undertake seasonal Monitoring Locations as Table 9.2 Environmental monitoring of air, water, noise and soil specified in Table 9.3 Table 9.3

Environmental Impact Assessment 139 139 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of STUP Consultants P. Ltd. NH-8E in the State of Gujarat (approx length 445 km)

Sl. No Activities Management Measure Location Reference Conditions quality through an approved monitoring agency. The parameters to be monitored, frequency and duration of monitoring as well as the locations to be monitored will be as per the Monitoring Plan prepared (Table 9.2). 2.1.17 Contractor Demobilization 2.1.17.1 Clearing of Contractor to prepare site restoration All Construction Construction of plans for approval by the Engineer. The Workers’ Camps Camps & plan is to be implemented by the Restoration contractor prior to demobilization. On completion of the works, all temporary structures will be cleared away, all rubbish burnt, excreta or other disposal pits or trenches filled in and effectively sealed off and the site left clean and tidy, at the Contractor’s expense, to the entire satisfaction of the Engineer. Residual topsoil will be distributed on adjoining/proximate barren/rocky areas as identified by the Engineer in a layer of thickness of 75mm - 150mm. 2.1.17.2 Redevelopment of Redevelopment of borrow areas will be At all borrow area Annexure 8.9 Borrow Areas taken up in accordance with the plans locations suggested for MoRTH: approved by the Engineer. Guidelines the project. 111.2 for redevelopment of borrow areas are presented in Annexure 8.9 2.2 CONSTRUCTION ACTIVITIES BY PIU-ENVIRONMENTAL CELL 2.2.1 Tree Plantation and Tree plantation and landscaping shall Entire Project Corridor Landscaping be implemented through the BOT Concessionaire. Trees felled will be replaced in accordance with the Forest (Conservation) Act, 1980. 3.0 OPERATION STAGE ACTIVITIES BY PIU-ENVIRONMENTAL CELL 3.1 Monitoring The PIU will monitor the operational Refer Table 9.1 Table 9.1 Operational performance of the various Table 9.4 Performance mitigation/enhancement measures carried out as a part of the project. The indicators selected for monitoring include the survival rate of trees, utility of enhancement provisions for cultural properties, water bodies, status of rehabilitation of borrow areas and utility noise barrier at sensitive receptors. 4.0 OTHER ACTIVITIES 4.1 Training of The PIU shall organize training implementing sessions during all stages of the agency and project. The orientation session shall contractors involve field level EMP implementation staff of PIU, Independent Engineer and BOT Concessionaire.

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10. ENVIRONMENT MONITORING PLAN

The monitoring programme is devised to ensure that the envisaged purpose of the project is achieved and results in desired benefit to the target population. To ensure effective implementation of the EMP, it is essential that an effective monitoring programme be designed and carried out. Broad objectives of the monitoring programme are:

1. To evaluate the performance of mitigation measures proposed in the EMP 2. T suggest improvements in the management plans, if required 3. To satisfy the statutory and community obligations 4. To provide feedback on adequacy of Environmental Impact Assessment

The monitoring programme contains monitoring plan for all performance indicators, reporting formats and necessary budgetary provisions. Monitoring plan for performance indicators and reporting system is presented in the following sections. Budgetary provisions for the envisaged programme is presented in Chapter – 10: Environment Budget.

10.1 PERFORMANCE INDICATORS

Physical, biological and environmental management components identified as of particular significance in affecting the environment at critical locations have been suggested as Performance Indicators (PIs). The Performance Indicators shall be evaluated under three heads as:  Environmental condition indicators to determine efficacy of environmental management measures in control of air, noise, water and soil pollution;  Environmental management indicators to determine compliance with the suggested environmental management measures  Operational performance indicators have also been devised to determine efficacy and utility of the mitigation/enhancement designs proposed.

The Performance Indicators and monitoring plans prepared for the project are presented in Table 10.1. Table 10.1: Performance Indicators for the Project

MONITORING Sl. Indicator Details Stage Responsibility No A Environmental Condition Indicators and Monitoring Plan The parameters to be monitored, BOT Concessionaire through Construction frequency and duration of monitoring as approved monitoring agency 1 Air Quality well as the locations to be monitored will BOT Concessionaire through Operation be as per the Monitoring Plan prepared approved monitoring agency (Refer Table 5.2) BOT Concessionaire through Construction approved monitoring agency 2 Noise Levels BOT Concessionaire through Operation approved monitoring agency

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Sl. Indicator Details Stage Responsibility No BOT Concessionaire through 3 Water Quality Construction approved monitoring agency BOT Concessionaire through approved monitoring agency 4 Soil Quality Construction through approved monitoring agency B Environmental Management Indicators and Monitoring Plan Locations for dumping have to be Pre- Dumping identified and parameters indicative of 1 Construction BOT Concessionaire Locations environment in the area has to be Stage reported Location of construction camps have to Construction be identified and parameters indicative of Pre- 2 BOT Concessionaire Camps environment in the area has to be construction reported Location of borrow areas have to be identified and parameters indicative of Pre- 3 Borrow Areas BOT Concessionaire environment in the area has to be construction reported Progress of enhancement measures suggested for cultural properties, water 4 Enhancements Construction BOT Concessionaire bodies and incidental spaces is to be reported Progress of measures suggested as part Tree Plantation 5 of the Landscaping Strategy is to be Construction BOT Concessionaire and Landscaping reported Implementation of the measures 6 Top Soil suggested for top soil preservation shall Construction BOT Concessionaire be reported by Contractor to Engineer C Management & Operational Performance Indicators The number of trees surviving during Operation The Concessionaire will be each visit will be compared with the responsible for monitoring Survival Rate of 1 number of saplings planted upto BOT contract period (20 Trees years after construction of road). The PIU will visit each of the Operation The Concessionaire will be Utility of enhancement locations (for cultural responsible for monitoring Enhancement properties, water bodies and incidental upto BOT contract period (20 2 Provisions spaces) to determine the efficacy of the years after construction of enhancements carried out and the road). community utilization of such areas. The PIU will undertake site visits to Operation The BOT Concessionaire will Status Regarding determine how many borrow areas have be responsible for monitoring 3 Rehabilitation of been rehabilitated in line with the upto 3 years after Borrow Areas landowners request and to their full construction of road. satisfaction. The PIU will visit such sensitive locations Operation The Concessionaire will be along with the environmental monitoring responsible for monitoring Utility of Noise 4 agency (responsible for monitoring of upto BOT contract period (20 Barrier noise levels during operation stage) to years after construction of check for the efficacy of noise barrier. road).

10.2 PLAN FOR ENVIRONMENTAL CONDITIONS

For each of the environmental condition indicator, the monitoring plan specifies the parameters to be monitored; location of the monitoring sites; frequency and duration of monitoring. The

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monitoring plan also specifies the applicable standards, implementation and supervising responsibilities. The monitoring plan for environmental condition indicators of the project in construction and operation stages is presented in Table 10.2.

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Table 10.2: Environmental Monitoring Plan Project Institutional Responsibility Attribute Parameter Special Guidance Standards Frequency Duration Location Measures Stage Impl’ion Super’ ion SPM, RPM, High volume Air (prevention and Once every Continuous (i) Wherever Wherever air BOT Independent SO2, NOX, sampler to be Control of Pollution) season for 24 hours/ or the contractor pollution Concessionaire Engineer / CO & Pb. located 50 m from Rules, CPCB, 1994 three seasons for 1 full decides to parameters through approved PIU the plant in the (except working day locate the Hot increase above monitoring downwind direction. monsoons) mix plant specified agency Construction Use method per year for (ii) At critical standards, specified by CPCB each year of stretches as additional for analysis Construction indicated in measures as Table 9.3 decided by the Engineer shall be adopted Air SPM, RPM, Respirable Dust Air (prevention and Once every Continuous i) At critical Wherever air BOT PIU SO2, NOx, Sampler / High Control of Pollution) year for winter 24 hours stretches as pollution Concessionaire CO & HC. volume sampler to Rules, CPCB, 1994 season for five indicated in parameters through approved be located 50 m years after Table 9.3 increase above monitoring from the plant in the completion of specified agency Operation downwind direction. construction standards, Use method activity. additional specified by CPCB measures as for analysis decided by the Engineer shall be adopted (i) pH, Grab sample Indian Standards for Twice a year Grab At all locations At locations of BOT Independent BOD,COD, collected from Inland Surface (Pre monsoon Sampling as indicated in increase in Concessionaire Engineer / TDS, Pb, Oil source and analyse Waters (IS: 2296, and Post Table 9.3 water pollution, through approved PIU & Grease as per Standard 1982) and for monsoon all inflow monitoring and Methods for Drinking Water (IS: seasons) for channels shall agency Detergents Examination of 10500, 1991) each year be checked for for Surface Water and during the pollution loads (ii) Water Wastewater Construction and channel pH, TDS, Period delivering Water Construction Total higher pollution Hardness, load shall be Sulphate, terminated Chloride, from disposal Fe, Pb for into the water Ground source and Water other methods of disposal shall be adopted

Environmental Impact Assessment 144 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav- Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Project Institutional Responsibility Attribute Parameter Special Guidance Standards Frequency Duration Location Measures Stage Impl’ion Super’ ion Noise levels Free field at 1 m MoEF Noise Rules, Once every Readings to Wherever the Incase of noise BOT Independent on dB (A) from the equipment 2000 season (except be taken at contractor levels causing Concessionaire Engineer / scale whose noise levels monsoons) for 15 seconds decides to disturbance to through approved PIU are being each year of interval for locate the the sensitive monitoring determined. Construction 15 minutes Equipment receptors, agency every hour yard double-glazing and then of openings of averaged. the receptor Construction Noise levels Equivalent noise MoEF Noise Rules, Once every Readings to At critical walls shall be BOT Independent on dB (A) levels using an 2000 season (except be taken at stretches as provided. Concessionaire Engineer / scale integrated noise monsoons) for 15 seconds indicated in through approved PIU level meter kept at a each year of interval for Table 9.3 monitoring distance of 15 from Construction 15 minutes agency Noise edge of pavement every hour and then averaged. Noise levels Equivalent noise MoEF Noise Rules, Once every Readings to At all the Incase of noise BOT PIU on dB (A) levels using an 2000 seasons be taken at critical levels causing Concessionaire, scale integrated noise (except 15 seconds receptors as disturbance to through an level meter kept at a monsoons) for interval for mentioned in the sensitive approved distance of 15 from five year after 15 minutes Table 5.3 receptors, monitoring Operation edge of pavement completion of every hour (ii) Additional double-glazing agency construction and then sites will be of openings of activity. averaged. monitored. The the receptor location will be shall be decided by the provided. PIU (EC). Monitoring Sample of soil Threshold for each During the Pre Grab At productive At locations of BOT Independent of Pb, SAR collected to contaminant set by monsoon & Sampling agricultural increase in Concessionaire Engineer / and Oil & beacidified and IRIS database of Post monsoon lands abutting pollution levels, through approved PIU Grease analysed using USEPA until season each traffic detours source shall be monitoring absorption national standards year for the and traffic identified and agency spectrophotometer are promulgated entire diversions and shall be construction major diverted from Soil Construction period intersections, further disposal

as indicated in Table 9.3 BOT Independent Concessionaire Engineer / Monitoring after any major accidents / spillage during bulk transport of hazardous material. Depending on the type of through approved PIU spillage/accident the parameters to be monitored will be decided by the Engineer apart from those mentioned above. monitoring agency

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REPORTING SYSTEM

Reporting system for the suggested monitoring program operates at two levels as: a.) Reporting for environmental condition indicators and environmental management indicators (except tree cutting indicator) b.) Reporting for operational performance indicators at the PIU level.

BOT Concessionnaire and Independent Engineer operate the reporting system for environmental condition and environmental management indicators (except tree cutting). PIU will operate the reporting system for environmental management tree cutting indicator and operation performance indicators. The PIU will set the targets for each activity envisaged in the EMP beforehand and all reports will be against these targets.

Concessionaire will report to the Independent Engineer, on the progress of the implementation of environmental conditions and management measures as per the monitoring plans. The Independent Engineer will in turn report to the PIU on a quarterly basis. The PIU will send compliance report to the MoEF every six months as per the conditions of clearance granted for the project after receiving the report from the contractor and duly verified by the Engineer. The reports submitted to the MoEF will also be forwarded to the NHAI Head Office. Reporting formats for contractors have been prepared, which will form the basis of monitoring, by the Engineer. The details of reporting formats prepared for the project is presented in Table 10.3. Table 10.3: Summary Details of Reporting Formats BOT Concessionaire Independent Engineer (IE) Format Item Stage Implementation & No. Supervision Reporting to PIU Reporting to IE EM1 Identification of Pre-Construction One Time One Time One Time Dumping Locations EM2 Setting up of Pre-Construction One Time One Time One Time Construction Camp EM3 Borrow Area Pre-Construction One Time One Time One Time Identification EM4 Enhancement Construction Measures for Cultural Properties, Water Monthly Monthly Monthly bodies & Incidental Spaces EM5 Tree Plantation and Construction Monthly Monthly Landscaping EM6 Top Soil Monitoring Construction Quarterly Continuous Quarterly EC 1 Pollution Monitoring Construction As Per Monitoring Quarterly Quarterly Plan EC 2 Pollution Monitoring Operation - - - OP 1 Survival Rate of Trees Operation - - - OP 2 Utility of Enhancement Operation Measures for Cultural Properties, Water - - - bodies and Incidental Spaces

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BOT Concessionaire Independent Engineer (IE) Format Item Stage Implementation & No. Supervision Reporting to PIU Reporting to IE OP 3 Status Regarding Operation Rehabilitation of - - - Borrow Areas OP 4 Utility of Noise Barrier Operation - - -

In addition to these formats, to ensure that the environmental provisions are included at every activity of the implementation by the contractor, it is suggested that the approval of the environmental personnel of the engineer is required in the Request for application to proceed or other similar reporting formats used by the contractor. These will not only ensure that the environmental provisions are addressed but also link the satisfactory compliance to environmental procedures prior to approval of the Interim Payment Certificate (IPC) by the Engineer. The activities by the contractor that can impact the environment will be identified based on discussions between the PIU, team leader of the Engineer and the Environmental personnel of the Engineer. The decisions will be communicated to the contractor prior to the start of the construction activities.

10.3 IMPLEMENTATION ARRANGEMENTS

The NHAI is responsible for implementation of all the mitigation and management measure suggested in the EMP. The NHAI already has certain organizational and institutional capacity to be able to satisfactorily complete the implementation of the EMP. The capacity was mainly created due to the requirements of implementing of this project corridor of the NHDP.

10.4 TRAINING

The Environmental Unit at the NHAI headquarters and the PIUs, who would be responsible for the implementation of the EMP, need to be trained on the effective implementation of the environmental issues. To ensure the success of the implementation set up proposed, there is a high requirement of training and skill up-gradation at the field level also. The requirements of training will be in line with the existing modules being adopted by NHAI for training of the implementing agency. Additional training if required will be identified by the PIU during/prior to implementation and accordingly included in the Scope of Services of the Engineer employed for supervision of the project with necessary budgetary provisions.

Environmental Impact Assessment 147 Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

11. ENVIRONMENTAL BUDGET

11.1 ENVIRONMENTAL MANAGEMENT

Budgetary estimates for environmental management include all items envisaged as part of the Environmental Management Plans. These costs have been worked out based on the estimates for the mitigation measures. A substantial portion of the works costs will form a part of contractors’ costs. The environment budget includes provisions for the various environmental management measures (other than measures considered under good engineering practices). It also includes the environmental monitoring and training costs. The environmental budget for the various environmental management measures proposed in the EMP is detailed in Table 11.1.

There are several other environmental issues that have been addressed as part of good engineering practices, the costs for which has been accounted for in the Engineering Cost. Various environmental aspects covered under engineering costs are listed below:  Turfing and Pitching of slopes  Construction of slope protection works  Construction of roadside amenities as bus stops

The total environmental mitigation costs for the project road is Rs 254.95 million. The detailed cost is given in Table 11.1. Table 11.1: Environmental Costs Sl No Activity Unit Cost (Rs) Quantity Amount (Rs.) A. Construction Phase 1 Air Quality Monitoring 8000/sample 113 904000 Monitoring of Air Quality 2 8000/sample 30 240000 near hot mix plants 3 Noise Monitoring 4000/sample 113 452000 Noise Monitoring at 4000/sample for Equipment yards (at 5 4 5 equipment 188 752000 locations within equipment yards yards) 5 Water Quality Monitoring 8000/sample 68 544000 6 Soil Quality Monitoring 6000/sample 93 558000 7 Median Plantation 250/plant 213180 53295000 8 Oil Intercepter 60000 4 240000 9 Silt Fencing 370/sqm 960 355200 10 Noise Barrier (a) Noise Barrier (Vegetative with trees 4000 39 156000 Guard) (b) Noise Barrier (Wall) 15000 39 585000

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Sl No Activity Unit Cost (Rs) Quantity Amount (Rs.) Compensatory Plantation 11 1500 106956 160434000 (three times tree cutting) 12 Temple Enhancement 150000 74 11100000 Total 229615200 B. Operation Phase Monitoring of Environmental Attributes during Operation Stage Monitoring of Air Quality at 1 critical Locations upto 8000/sample 15*1*12 1440000 25yrs, once in every 2 yrs Monitoring of Noise level at 2 critical Locations upto 25 4000/sample 15*1*12 720000 yrs, once in every 2 yrs Total 2160000 Total (A+B) 231775200 Contingency (10%) 23177520 Total 254952720

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Table of Contents Executive Summary 1. INTRODUCTION ...... 1

1.1 PROJECT BACKGROUND ...... 9 1.2 THE PROJECT ...... 9 1.2.1 Project Description ...... 9 1.2.2 Objectives of the Assignment ...... 11 1.2.3 Scope of EIA ...... 12 1.3 METHODOLOGY FOR EIA ...... 12 1.3.1 Review of Policy, Legal and Administrative Framework ...... 13 1.3.2 Assessment of Baseline Environmental Status ...... 13 1.3.3 Assessment of Alternatives ...... 13 1.3.4 Assessment of Potential Impacts ...... 13 1.3.5 Integration of Environmental Assessments in the Design Process ...... 13 1.3.6 Conduct of Community Consultations ...... 13 1.3.7 Identified Mitigation & Environmental Enhancement Measures ...... 13 1.3.8 Preparation of the Preliminary Environmental Management Plan (EMP) ...... 13 1.4 PROJECT BENEFITS ...... 14 1.5 STRUCTURE OF REPORT ...... 14 2. PROJECT DESCRIPTION ...... 15

2.1 PROJECT BACKGROUND & OBJECTIVES ...... 15 2.2 PROJECT CORRIDOR CHARACTERISTICS ...... 15 2.2.1 Existing Right-of-Way (RoW) ...... 15 2.2.2 Traffic Scenario ...... 16 2.2.3 Land Use and Road side Environments ...... 17 2.2.4 Major Settlements Enroute ...... 19 2.3 SCOPE OF ENVIRONMENTAL IMPACT ASSESSMENT ...... 21 2.4 IMPROVEMENT PROPOSALS ...... 21 2.4.1 Widening Scheme ...... 21 2.4.2 Proposed Bypasses ...... 25 2.4.3 Proposed RoW Width ...... 26 2.4.4 Proposed Median Width ...... 26 2.4.5 Proposed Road Features ...... 26 TOLL PLAZA ...... 28 2.5 INTERSECTIONS ...... 28 2.6 ROAD DRAINAGE ...... 30 2.6.1 Covered Drain below Footpath in Urban Areas...... 30 2.6.2 Road-side Drain ...... 30 2.6.3 Chute Drains ...... 30 2.6.4 Additional Culvert for Field Channel ...... 30 2.6.5 Additional Culvert at Cross Road ...... 30 2.7 SOURCE OF CONSTRUCTION MATERIALS ...... 31 2.7.1 Quarries for Sand ...... 31 2.7.2 Source for Water ...... 31 2.8 GEOTECHNICAL INVESTIGATIONS ...... 32

Environmental Impact Assessment I Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

2.9 HYDRAULIC AND HYDROLOGICAL INVESTIGATIONS ...... 32 2.10 ROAD SAFETY MEASURES ...... 32 2.10.1 Carriageway Markings ...... 32 2.10.2 Traffic Signs ...... 33 2.10.3 Safety Barriers ...... 33 2.11 LAND REQUIREMENT ...... 33 3. LEGAL AND INSTITUTIONAL FRAMEWORK ...... 35

3.1 LEGAL FRAMEWORK ...... 35 Legislation and Regulations: Environmental legislation, regulations and policy guidelines that may apply to this project and government agencies that administer them are summarized in Table 2.1...... 35 3.2 THE LEGAL SETTING ...... 35 3.3 CLEARANCE PROCEDURES ...... 39 3.3.1 The EIA Notification ...... 39 3.3.2 Categorisation and Clearance Requirement for the Present Project ...... 40 4. BASELINE ENVIRONMENTAL STATUS ...... 41

4.1 BACKGROUND...... 41 4.2 STUDY REGION DELINEATION...... 41 4.3 COLLECTION & COLLATION OF DATA ON ENVIRONMENTAL AND SOCIAL FEATURES ...... 42 4.3.1 Primary Data Collection ...... 42 4.3.2 Secondary Data Collection ...... 42 4.4 PHYSICAL ENVIRONMENT ...... 42 4.4.1 Climate and Meteorology ...... 43 4.4.2 Physiography and Terrain ...... 44 Soil ...... 45 Land Use ...... 46 Noise Quality ...... 49 Ecology ...... 57 Institutional Facility...... 58 Coastal Regulation Zone ...... 60 4.5 SOCIAL & CULTURAL ENVIRONMENT ...... 60 4.5.1 Social Environment ...... 60 4.6 SOCIO-ECONOMIC PROFILE ...... 61 4.6.1 Population Distribution ...... 61 4.6.2 Population Density ...... 61 4.6.3 Sex Ratio ...... 62 4.6.4 Vulnerable Population ...... 62 4.6.5 Literacy Rate ...... 62 4.6.6 Workforce Participation ...... 63 4.6.7 Right of Way ...... 63 4.6.8 Cultural Environment ...... 64 5. ANALYSIS OF ALTERNATIVES ...... 65 5.1 INTRODUCTION ...... 65 5.2 WITH OR WITHOUT PROJECT SCENARIO...... 66 5.3 ALIGNMENT SELECTION ...... 66 5.4 ALTERNATIVE PROPOSALS FOR BYPASSES ...... 67

Environmental Impact Assessment II Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

5.4.1 Bypasses Proposed by R&B ...... 67 5.4.2 Bypasses Proposed by STUP ...... 72 6. STAKEHOLDER CONSULTATION ...... 83 7. ASSESSMENT OF IMPACTS ...... 97

7.1 INTRODUCTION ...... 97 7.2 NATURAL ENVIRONMENT ...... 97 7.2.1 Borrow Pits for Construction of Embankment and Sub-grade ...... 98 7.2.2 Quarries for Aggregates ...... 98 7.2.3 Quarries for Sand ...... 99 7.2.4 Water Resources ...... 99 7.2.5 Air Quality ...... 100 7.2.6 Noise Levels ...... 101 Roadside Trees ...... 102 7.2.7 Fauna ...... 102 7.3 SOCIAL & CULTURAL ENVIRONMENT ...... 102 7.3.1 Impact on Educational Institutes and Hospitals ...... 102 7.3.2 Impact on Cultural Environment ...... 103 8. MITIGATION MEASURES ...... 106

8.1 MITIGATION OF IMPACTS ...... 106 8.1.1 Land Resources ...... 106 8.1.2 Soil Resources ...... 106 8.1.3 Water Resources ...... 110 8.1.4 Air Pollution Control Measures ...... 113 8.1.5 Noise Control Measures ...... 114 8.1.6 Safety Measures during ...... 117 8.1.7 Construction: ...... 117 8.1.8 Bus Stop ...... 120 8.1.9 Avoidance / Enhancement Measures for Cultural Properties ...... 121 8.1.10 Highway Landscaping ...... 121 9. ENVIRONMENT MANAGEMENT PLAN ...... 123

9.1 PRE-CONSTRUCTION STAGE ...... 123 9.1.1 Pre-construction activities by PIU ...... 123 9.1.2 Pre-construction activities by BOT Concessionaire/Independent Engineer ...... 123 9.2 CONSTRUCTION STAGE ...... 123 9.2.1 Construction Stage activities by BOT Concessionaire ...... 123 9.2.2 Construction Stage Activities by PIU...... 124 9.3 OPERATION STAGE ...... 124 9.4 OTHER ACTIVITIES ...... 124 10. ENVIRONMENT MONITORING PLAN ...... 141

10.1 PERFORMANCE INDICATORS ...... 141 10.2 PLAN FOR ENVIRONMENTAL CONDITIONS ...... 142 REPORTING SYSTEM ...... 146 10.3 IMPLEMENTATION ARRANGEMENTS ...... 147 10.4 TRAINING ...... 147

Environmental Impact Assessment III Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

11. ENVIRONMENTAL BUDGET ...... 148

11.1 ENVIRONMENTAL MANAGEMENT ...... 148

Environmental Impact Assessment IV Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

List of Tables

Table 2.1: Existing RoW ...... 16

Table 2.2: Homogenous sections on project corridor ...... 16

Table 2.3: Projected Traffic ...... 16

Table 2.4: Summary of landuse ...... 17

Table 2.5: Urban Areas along the Project Corridor ...... 19

Table 2.6: Length of Widening Options Considered ...... 21

Table 2.7: Summary of Cross Drainage Structures ...... 26

Table 2.8: List of Bus stop along the Project Corridor ...... 27

Table 2.9: Tollplaza Locations ...... 28

Table 2.10: Proposed intersection Improvements ...... 28

Table 2.11: Details of Major Intersections ...... 29

Table 2.12: Details of Intersections of Minor Intersection ...... 30

Table 2.13: Details of Quarry Area for Aggregates ...... 31

Table 2.14: Details of Sand Quarry ...... 31

Table 2.15: Location details of Water Sample ...... 32

Table 2.16: Land Requirement ...... 34

Table 3.1: Summary of Relevant Legal Requirements considered for this Project and Institution responsible ...... 36

Table 3.2: Statutory Clearance Requirements ...... 40

Table 4.1: Temperature of the Project Region ...... 43

Table 4.2: Monthly Average Humidity of the Project Region (in %) ...... 44

Table 4.3: Rainfall in the Project Districts (in mm)] ...... 44

Table 4.4: Mean Wind Speed (Kmph) ...... 44

Table 4.5: Landuse in the Project RoW ...... 46

Table 4.6: Ambient Air Quality Results ...... 47

Table 4.7: Noise Quality Results ...... 49

Table 4.8: River Crossing the Project stretch ...... 51

Environmental Impact Assessment V Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Table 4.9: Ponds along the alignment ...... 53

Table 4.10: Depth to ground water level along the corridor ...... 54

Table 4.11: Water Quality Results ...... 55

Table 4.12: Road Side Tree Species ...... 58

Table 4.13: Educational Institutes along the project road ...... 58

Table 4.14: Number of Settlements along the Project Corridor ...... 60

Table 4.15: Population Distribution in talukas along the Project Corridor, 2011 ...... 61

Table 4.16: Population Distribution and Density along Project Corridor, 2011 ...... 61

Table 4.17: Sex Ratio along Project Corridor, 2011 ...... 62

Table 4.18: Share of Vulnerable Groups along Project Corridor, 2001 ...... 62

Table 4.19: Literacy Rate along Project Corridor, 2011 ...... 63

Table 4.20: Type of Workers within the Project Influence Area, 2001 ...... 63

Table 4.21: Landuse along the Project Corridor ...... 63

Table 4.22: Protected and Conserved Monuments Located in the Project Districts ...... 64

Table 7.1: Probable Soil Borrow Pits ...... 98

Table 7.2: Details of Quarry Area for Aggregates ...... 98

Table 7.3: Details of Sand Quarry ...... 99

Table 7.4: Water Contaminants, sources & receptors ...... 100

Table 7.5: Roadside Schools along project corridor ...... 102

Table 7.6: Roadside Religious Properties along project corridor ...... 103

Table 8.1: Measures to minimize air pollution during the progress of work ...... 113

Table 8.2: Locations proposed for Vegetative Barriers ...... 115

Table 8.3: Locations of Underpasses ...... 117

Table 9.1: Environmental Management Measures ...... 125

Table 10.1: Performance Indicators for the Project ...... 141

Table 10.2: Environmental Monitoring Plan ...... 144

Table 10.3: Summary Details of Reporting Formats ...... 146

Table 11.1: Environmental Costs ...... 148

Environmental Impact Assessment VI Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

List of Figures

Figure 1.1: Project Corridor...... 10

Fig – 2.2: Typical cross section for 2-Lane Highway without Service Road ...... 22

Fig – 2.3: Typical Cross Section for 2-Lane Highway without Service Road ...... 22

Fig – 2.4: cross section of 4-lane with service road ...... 23

Fig – 2.5: Typical cross section of 4-lane Flyover/Underpass with slip road ...... 23

Fig – 2.6: Typical cross section of 6-Lane with service road ...... 24

Fig – 2.7: Typical cross section of 6-Lane Flyover / Underpass with Slip Road ...... 24

Fig 5.1: Adhewada Bypass ...... 68

Fig 5.2: Budhel Bypass Option ...... 68

Fig 5.3: kobadi Bypass ...... 69

Fig 5.4: Bhandaria Bypass Option ...... 70

Fig 5.5: Tansa Bypass Option ...... 70

Fig 5.6: Trapej Bypass Option ...... 71

Fig 5.7: Una Bypass Option ...... 72

Fig 5.8: Talaja Bypass Options ...... 73

Fig 5.9: Bhadrad Bypass Options ...... 74

Fig 5.10: Datardi Bypass Options ...... 75

Fig 5.11: Hemal Bypass Options ...... 76

Fig 5.12: Samter Bypass Options ...... 77

Fig 5.13 Dholasa Bypass Option ...... 77

Fig 5.14: Chorwad Bypass Option ...... 78

Fig 5.15: Prachi Bypass Options ...... 79

Fig 5.16: Kukasawada bypass Option ...... 80

Fig 5.17: Madhavpur Bypass Options...... 81

Fig 5.18: Porbandhar Bypass Options ...... 82

Figure 8.1 Stone Pitching ...... 108

Figure 8.2 Oil Interceptor ...... 109

Environmental Impact Assessment VII Rev – R0 Preparation of Feasibility study forSix/Four/2 lane with paved shoulder of Bhavnagar-Pipavav-Porbandar-Dwarka section of NH-8E in the State of Gujarat (approx length 445 km) STUP Consultants P. Ltd.

Figure 8.28.3: Channelised Embankment: Chute Drain ...... 110

Figure 8.4: Cross-section of Silt Fencing ...... 112

Figure 8.5: Layout Plan of Silt Fencing ...... 112

Environmental Impact Assessment VIII Rev – R0