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T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic Chemical Manufacturing Unit Survey No. 922/P2, Village: Mota Dahisara, Navlakhi Highway, Taluka: Maliya, District: Morbi, Gujarat. Category: 5 (f) PROJECT PROPONENT Baseline Monitoring Period: October-2016 to December-2016 PREPARED BY T. R. Associates Ganesh Meridian, Block No.: C, Office No. 605-A, Opp. Kargil Petrol Pump, Nr. Sola Over Bridge, S. G. Highway, Ahmedabad-380060. Email: [email protected] Contact No.: 09825371099 NABET Accreditation No.: NABET/EIA/1619/RA0033 July, Year 2017
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Page 1: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TABLE OF CONTENTS 1

DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR

Proposed Synthetic Organic Chemical Manufacturing Unit

Survey No. 922/P2, Village: Mota Dahisara, Navlakhi

Highway, Taluka: Maliya, District: Morbi, Gujarat.

Category: 5 (f)

PROJECT PROPONENT

Baseline Monitoring Period: October-2016 to December-2016

PREPARED BY

T. R. Associates Ganesh Meridian, Block No.: C, Office No. 605-A,

Opp. Kargil Petrol Pump, Nr. Sola Over Bridge, S. G. Highway, Ahmedabad-380060.

Email: [email protected]

Contact No.: 09825371099

NABET Accreditation No.: NABET/EIA/1619/RA0033

July, Year 2017

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TABLE OF CONTENTS 2

TABLE OF CONTENTS

TOR COMPLIANCE ......................................................................................17

EXECUTIVE SUMMARY-ENGLISH ..................................................................25

સકં્ષીપ્ત અહવેાલ-ગજુરાતી ..................................................................................31

1 INTRODUCTION ....................................................................................39

1.1 PREAMBLE .......................................................................................... 39

1.2 PURPOSE OF THE EIA REPORT ..................................................................... 39

1.3 PROMOTERS AND THEIR BACK GROUND ............................................................ 39

1.4 NEED OF THE PROJECT AND ITS IMPORTANCE TO THE COUNTRY .................................. 40

1.5 LOCATION OF THE PROPOSED PROJECT AND SITING CRITERIA .................................... 41

1.6 SCOPE OF EIA STUDY .............................................................................. 42

1.7 REGULATORY FRAME WORK ........................................................................ 44

2 PROJECT DESCRIPTION .........................................................................46

2.1 INTRODUCTION ..................................................................................... 46

2.2 PROJECT LOCATION ................................................................................ 46

2.3 JUSTIFICATION OF SITE SELECTION AND SALIENT FEATURES OF SITE ............................. 49

2.4 LIST OF MAJOR INDUSTRIES WITHIN 10 KM STUDY AREA .......................................... 54

2.5 PROPOSED PROJECT LAND & PLANT LAY-OUT ..................................................... 54

2.6 CAPITAL COST OF THE PROPOSED PROJECT ........................................................ 56

2.7 MAGNITUDE OF PROJECT ........................................................................... 57

2.8 MANUFACTURING PROCESS ......................................................................... 58

2.8.1 Unsaturated Polyester Resin ............................................................. 58

2.9 WATER CONSUMPTION AND CONSUMPTION OF EACH RAW MATERIAL PER MT OF EACH PRODUCT. . 63

2.10 RAW MATERIALS DETAILS .......................................................................... 64

2.11 REQUIREMENT OF RESOURCES ..................................................................... 65

2.11.1 Electricity / Power .......................................................................... 65

2.11.2 Manpower ................................................................................... 65

2.11.3 Water ........................................................................................ 65

2.11.4 Fuel ........................................................................................... 65

2.11.5 Plant, Machineries & Utilities ............................................................. 66

2.12 ENERGY BALANCE .................................................................................. 66

2.13 POLLUTION POTENTIAL AND MITIGATION MEASURES .............................................. 67

2.13.1 Water Pollution ............................................................................. 67

2.13.2 Air Pollution ................................................................................. 70

2.13.3 Solid / Hazardous Waste .................................................................. 72

2.13.4 Noise & Vibration .......................................................................... 72

3 DESCRIPTION OF THE ENVIRONMENT .....................................................73

3.1 INTRODUCTION ..................................................................................... 73

3.1.1 EIA Methodology for Data Collection ................................................... 73

3.1.2 Objectives of Baseline Monitoring ....................................................... 73

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TABLE OF CONTENTS 3

3.1.3 Study Area .................................................................................. 73

3.1.4 Methodology of Baseline Study .......................................................... 74

3.2 AIR ENVIRONMENT ................................................................................. 74

3.2.1 Climate of the Study Area ................................................................ 74

3.2.2 Site Specific Meteorology (October 2016 to January 2017) ......................... 76

3.2.3 Sampling Methodology and Analysis .................................................... 78

3.2.4 Selection of Monitoring Locations and Results ........................................ 78

3.2.5 Discussion of Ambient Air Quality ....................................................... 82

3.3 NOISE .............................................................................................. 83

3.3.1 Sampling Methodology .................................................................... 83

3.3.2 Selection of Monitoring Locations and Results ........................................ 83

3.3.3 Discussion of Noise Levels ................................................................ 86

3.4 WATER ENVIRONMENT ............................................................................. 87

3.4.1 Sampling Methodology and Analysis .................................................... 87

3.4.2 Ground Water Quality ..................................................................... 87

3.4.3 Surface Water Quality ..................................................................... 93

3.5 SOIL ................................................................................................ 97

3.5.1 Sampling Methodology and Analysis .................................................... 97

3.5.2 Sampling Locations and Results ......................................................... 97

3.5.3 Discussion-Soil Environment ........................................................... 100

3.6 HYDROLOGY, GROUND WATER & WATER CONSERVATION ....................................... 101

3.6.1 Geological Features ...................................................................... 101

3.6.2 Geo-Hydrological Status ................................................................ 102

3.6.3 Drainage Pattern of the surrounding Region ........................................ 103

3.7 LAND USE ........................................................................................ 106

3.7.1 Introduction ............................................................................... 106

3.7.2 Land Use & Land Cover Classification ................................................ 106

3.7.3 Topography ............................................................................... 114

3.8 ECOLOGY STATUS ................................................................................ 116

3.8.1 Macro Level Approach: Secondary data collection .................................. 116

3.8.2 Micro Level Approach- Field Data Collection ......................................... 116

3.8.3 Biodiversity Status ....................................................................... 117

3.8.4 Threatened Plants and Animals ........................................................ 124

3.9 SOCIO ECONOMIC ENVIRONMENT ................................................................ 137

3.9.1 Introduction ............................................................................... 137

3.9.2 Population and Growth Rate of Study Area .......................................... 137

3.9.3 Sex-ratio in Study Area ................................................................. 139

3.9.4 Economic Attributes ..................................................................... 140

3.9.5 Infrastructure Resource Base .......................................................... 140

3.10 TRAFFIC SURVEY ................................................................................. 147

4 ANTICIPATED ENVIRONMENTAL IMPACTS AND MITIGATION MEASURES ... 149

4.1 INTRODUCTION ................................................................................... 149

4.1.1 Objective .................................................................................. 149

4.1.2 Environmental Aspects .................................................................. 149

4.1.3 Environmental Impacts ................................................................. 149

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TABLE OF CONTENTS 4

4.1.4 Environmental Indices................................................................... 149

4.1.5 Environmental Impact Assessment Study ............................................ 150

4.2 IMPACT IDENTIFICATION AND ASSESSMENT ...................................................... 150

4.2.1 Identification Matrix ..................................................................... 150

4.2.2 Assessment of Impacts ................................................................. 152

4.3 MITIGATION MEASURES FOR IMPACTS IDENTIFIED .............................................. 154

4.3.1 Land Environment ....................................................................... 154

4.3.2 Water Environment ...................................................................... 155

4.3.3 Noise ....................................................................................... 156

4.3.4 Ecology .................................................................................... 156

4.3.5 Socio-economic Environment .......................................................... 157

4.3.6 Existing Traffic & Vehicular Pollution ................................................. 158

4.3.7 Air Environment .......................................................................... 159

5 ANALYSIS OF ALTERNATIVES (TECHNOLOGY AND SITE) .......................... 165

5.1 PROJECT ALTERNATIVE ........................................................................... 165

5.2 SITE ALTERNATIVE ............................................................................... 165

5.3 FUEL ALTERNATIVE ............................................................................... 165

5.4 WATER SUPPLY ALTERNATIVE .................................................................... 165

5.5 PROCESS TECHNOLOGY ALTERNATIVE ............................................................ 165

5.6 WASTEWATER TREATMENT AND USE ALTERNATIVE .............................................. 165

6 ENVIRONMENTAL MONITORING PROGRAM ............................................ 166

6.1 INTRODUCTION ................................................................................... 166

6.2 MONITORING AND REPORTING PROCEDURE ...................................................... 166

7 ADDITIONAL STUDIES ......................................................................... 170

7.1 PUBLIC CONSULTATION .......................................................................... 170

7.2 SOCIAL IMPACT ASSESSMENT AND R & R ACTION PLAN ......................................... 170

7.3 RISK ASSESSMENT ................................................................................ 170

7.3.1 Objective, Philosophy & Methodology of Risk Assessment ........................ 170

7.3.2 Hazard Identification and Risk Analysis .............................................. 170

7.3.3 Storage Details of Raw material and Products ...................................... 171

7.3.4 Details of Hazardous Chemicals to be handled ...................................... 172

7.3.5 Hazard Identification and Preventive Measures ..................................... 173

7.3.6 Risk Assessment and Consequence Analysis ........................................ 177

Figure 7.2 Pool Fire Threat zone Styrene(40 MT tank) ...................................... 181

7.3.7 Occupational Health Surveillance Programme ....................................... 184

7.3.8 Chemicals which are exposed to Workers Directly or Indirectly .................. 185

7.3.9 Treatment of Workers Affected by Accidental Spillage of Chemicals ............ 185

7.3.10 Risk Reduction Measurement & Recommendation in View of Safety Consideration

186

7.4 ON SITE EMERGENCY PLAN ...................................................................... 188

7.5 OFFSITE EMERGENCY PREPAREDNESS PLAN ...................................................... 192

7.5.1 Do’s and Don’ts .......................................................................... 197

8 PROJECT BENEFITS ............................................................................. 200

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TABLE OF CONTENTS 5

8.1 EMPLOYMENT POTENTIAL ........................................................................ 200

8.2 IMPROVEMENT IN PHYSICAL & SOCIAL INFRASTRUCTURE ........................................ 200

8.3 OTHER TANGIBLE BENEFITS ...................................................................... 200

9 ENVIRONMENTAL COST BENEFIT ANALYSIS ........................................... 202

10 ENVIRONMENTAL MANAGEMENT PLAN (EMP) INTRODUCTION............... 203

10.1.1 Objectives of EMP ........................................................................ 203

10.1.2 Components of EMP ..................................................................... 203

10.1.3 Reuse/recycle and Cleaner Production Technologies .............................. 203

10.2 ENVIRONMENTAL MANAGEMENT PLAN FOR THE PROPOSED PROJECT ............................ 204

10.2.1 Environmental Management Plan for Land Environment .......................... 204

10.2.2 Air Environment .......................................................................... 205

10.2.3 Water and Soil Environment ........................................................... 207

10.2.4 Noise Environment ....................................................................... 210

10.2.5 Traffic Management Plan ............................................................... 211

10.2.6 Ecology and Biodiversity ................................................................ 212

10.2.7 Occupational Health Management Plan .............................................. 213

10.2.8 Enterprise Social Commitment (ESC) ................................................. 214

10.3 INSTITUTIONAL ARRANGEMENTS FOR ENVIRONMENT PROTECTION AND CONSERVATION ........ 215

10.3.1 Environmental Management Cell (EMC) .............................................. 215

10.3.2 Record Keeping and Reporting ........................................................ 216

10.4 BUDGET FOR ENVIRONMENT PROTECTION ....................................................... 217

11 SUMMARY & CONCLUSION ................................................................ 218

11.1 JUSTIFICATION FOR IMPLEMENTATION OF THE PROJECT ......................................... 218

11.2 ANTICIPATED ADVERSE ENVIRONMENTAL IMPACTS AND MITIGATION MEASURES ............... 218

11.3 CONCLUSIONS .................................................................................... 220

12 DISCLOSURE OF CONSULTANTS ENGAGED ........................................... 222

12.1 DECLARATION FOR INVOLVEMENT IN EIA STUDY ................................................ 222

12.2 COMPANY PROFILE ............................................................................... 225

12.2.1 Services .................................................................................... 225

12.2.2 Infrastructural facilities.................................................................. 225

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT LIST OF ANNEXURE 6

LIST OF ANNEXURES

Annexure 1: Terms of Reference .................................................................................... 228

Annexure 2: Primary Meteorology Data taken at Project Site ........................................... 232

Annexure 3: Raw data of all AAQ measurement for 12 weeks of all stations as per frequency

.................................................................................................................................... 291

Annexure 4: Letter from Tanker Water Supplier .............................................................. 296

Annexure 5: Land Documents ........................................................................................ 297

Annexure 6: Material Safety Data Sheet ......................................................................... 316

Annexure 7: Legal Undertaking stating that unit is complying the three conditions [i.e. water

consumption less than 25 m3/day; Fuel consumption less than 25 TPD; and not covered in

the category of MAH units as per the Management, Storage, Import of Hazardous Chemical

Rules (MSIHC Rules), 1989] as per the amendment to EIA Notification, 2006 vide SO 1599

(E) dated 25.06.2014. ................................................................................................... 382

Annexure 8: Undertaking to carry out tree Plantation Activities outside the Premises ........ 384

Annexure 9: An undertaking by the Project Proponent on the ownership of the EIA report as

per the MoEF&CC OM dated 05/10/2011 ........................................................................ 386

Annexure 10: An undertaking by the Consultant regarding the prescribed TORs have been

complied with and the data submitted is factually correct as per the MoEF&CC OM dated

04/08/2009. ................................................................................................................. 387

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT LIST OF TABLES 7

LIST OF TABLES

Table 1-1: Details of Product ........................................................................................... 39

Table 1-2: General Siting Criteria ..................................................................................... 41

Table 1-3: Scope of the Study ......................................................................................... 43

Table 2-1: Salient Features of the Proposed Project Site .................................................... 50

Table 2-2: Area Break-up of Proposed Project Site ............................................................ 54

Table 2-3: Break-up of Capital Cost for Proposed Project ................................................... 56

Table 2-4: Details of Products for Proposed Project ........................................................... 57

Table 2-5: Consumption of each raw material per MT of each product ............................... 63

Table 2-6: Details of Proposed Raw Materials ................................................................... 64

Table 2-7: Manpower Requirement .................................................................................. 65

Table 2-8: Fuel Requirement ........................................................................................... 66

Table 2-9: List of Plant, Machineries and Utilities .............................................................. 66

Table 2-10: List of Process Vessels ................................................................................... 66

Table 2-11: Energy Balance ............................................................................................. 66

Table 2-12: Stream-wise Water Requirement & Wastewater Generation ............................. 67

Table 2-13: Quality of Untreated and Treated Effluent ...................................................... 69

Table 2-14: Details of Effluent Treatment Plant Units ........................................................ 70

Table 2-15: Technical details of TFH Based Evaporator ..................................................... 70

Table 2-16: Details of Flue Gas Emissions ......................................................................... 71

Table 2-17: Details of Hazardous waste Management........................................................ 72

Table 3-1: Predominant Wind Direction (Blowing From) .................................................... 75

Table 3-2: Air – Parameters analysed and sampling duration ............................................. 78

Table 3-3: Ambient Air Quality - Methodology ................................................................... 78

Table 3-4: Ambient Air Monitoring Locations ..................................................................... 79

Table 3-5: Ambient Air Monitoring Results ........................................................................ 81

Table 3-6: Noise Monitoring Methodology ......................................................................... 83

Table 3-7: Ambient Noise Quality Standards for Different Areas/Zones ............................... 83

Table 3-8: Noise Monitoring Locations .............................................................................. 84

Table 3-9: Noise Levels ................................................................................................... 86

Table 3-10: Sample Collection and Analysis of Water Sample ............................................. 87

Table 3-11: Ground Water Monitoring Locations ............................................................... 89

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT LIST OF TABLES 8

Table 3-12: Water Quality – Physico-chemical Analysis of Ground Water ............................ 91

Table 3-13: Surface Water Monitoring Locations ............................................................... 93

Table 3-14: Water Quality – Physico-chemical Analysis of Surface Water ............................ 96

Table 3-15: Soil Sampling Location .................................................................................. 98

Table 3-16: Physicochemical Parameters of the Soil ........................................................ 100

Table 3-17: Feasibility of Ground Water.......................................................................... 102

Table 3-18: Land Use Land Cover- (Based on GIS Studies) .............................................. 108

Table 3-19: Land use data within study area (As per census 2011) .................................. 110

Table 3-20: Taxonomic Status of plant species ............................................................... 117

Table 3-21: Life form Status of Plant Species .................................................................. 117

Table 3-22: Common Tree species ................................................................................. 118

Table 3-23: Wild/Forest Tree species ............................................................................. 118

Table 3-24: List of Agriculture and Commercial Crop Species Recorded ............................ 119

Table 3-25: Taxonomical Status of Herpetofauna ............................................................ 119

Table 3-26: Overall Status of Terrestrial and Aquatic Birds .............................................. 120

Table 3-27: Overall Status of Mammals .......................................................................... 124

Table 3-28: Habitat-wise checklist of Plant Species recorded in and around the Project Site

.................................................................................................................................... 126

Table 3-29: Population in Study Area (Nos.) ................................................................... 137

Table 3-30: Growth Rate ............................................................................................... 138

Table 3-31: SC/ST Population (Nos.) .............................................................................. 138

Table 3-32: Sex-ratio in Study Area ................................................................................ 139

Table 3-33: Occupational Status of Study Area ............................................................... 140

Table 3-34: Nos. of Educational Facilities in Study Area ................................................... 140

Table 3-35: Literacy Rate of Study Area ......................................................................... 141

Table 3-36: Nos. of Medical Facilities in Study Area ......................................................... 141

Table 3-37: Nos. of Villages having Drinking Water Facility in Study Area ......................... 142

Table 3-38: Nos. of Villages having Sanitation Facility in Study Area................................. 143

Table 3-39: Nos. of Villages having Communication Facility in Study Area ........................ 144

Table 3-40: Nos. of Roads Available in Study Area .......................................................... 145

Table 3-41: Nos. of Villages having Transportation Facility .............................................. 145

Table 3-42: Nos. of Villages having Other Facility ............................................................ 146

Table 3-43: Traffic Volume on SH-24 ............................................................................. 147

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT LIST OF TABLES 9

Table 4-1: Impact Identification ..................................................................................... 151

Table 4-2: Impact Assessment ....................................................................................... 153

Table 4-3: Assessment of Proposed Expansion in Traffic Load.......................................... 159

Table 4-4: Details of Stacks ........................................................................................... 160

Table 4-5: Pollutant Emissions Rate ............................................................................... 160

Table 4-6: Predicted 24 hourly short term incremental Concentrations ............................. 164

Table 6-1: Environmental Monitoring Program ................................................................ 166

Table 6-2: Budget for Implementation of Environmental Monitoring Plan .......................... 168

Table 7-1: Raw Materials and Product Storage Details: .................................................... 171

Table 7-2: Chemical Properties of Hazardous Chemicals .................................................. 172

Table 7-3: Consequence Analysis and damage distances ................................................. 180

Table 10-1: Environment Management Plan for Land Environment ................................... 204

Table 10-2: Environment Management Plan for Air Environment ...................................... 205

Table 10-3: Environment Management Plan for Water and Soil Environment .................... 207

Table 10-4: Details of Rain Water Harvesting .................................................................. 209

Table 10-5: Environment Management Plan for Noise Environment .................................. 210

Table 10-6: Environment Management Plan for Traffic .................................................... 211

Table 10-7: Details of Plant Species in Greenbelt ............................................................ 212

Table 10-8: Roles and Responsibility of EMC Cell ............................................................ 215

Table 10-9: Record Keeping Requirement ....................................................................... 216

Table 10-10: Recurring & Capital Cost for Environmental Management............................. 217

Table 11-1: Anticipated Adverse Environmental Impacts and Mitigation Measures ............. 218

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT LIST OF FIGURES 10

LIST OF FIGURES

Figure 1-1: Latitude Longitude of All Corners of Project Site .............................................. 41

Figure 2-1: Index Map ..................................................................................................... 47

Figure 2-2: TOPO Map showing Proposed Project Site ....................................................... 48

Figure 2-3: 5 km Radius Study Area of Project Site ........................................................... 51

Figure 2-4: 10 km Radius Study Area of Project Site ......................................................... 52

Figure 2-5 Goggle Image Showing Distance of Wildlife Sanctuary from Project Site ............. 53

Figure 2-6: Plant Lay-out ................................................................................................. 55

Figure 2-7: Water Balance Diagram .................................................................................. 68

Figure 2-8: Schematic Diagram of Effluent Treatment Plant ............................................... 70

Figure 3-1: Meteorological Wind Rose Diagram for October 2016 to January 2017 on Google

Earth (Primary data) ....................................................................................................... 77

Figure 3-2: Google Image Showing Ambient Air Quality Locations ...................................... 80

Figure 3-3: Google Image Showing Noise Sampling Locations ............................................ 85

Figure 3-4: Google Image Showing Ground Water Sampling Locations ............................... 90

Figure 3-5: Google Image Showing Surface Water Sampling Locations ............................... 95

Figure 3-6: Google Image Showing Soil Sampling Locations............................................... 99

Figure 3-7: Ground Water Prospect Map ......................................................................... 105

Figure 3-8: Land use of Study Area (as per Census 2011) ............................................... 109

Figure 3-9: Land use and Land Cover Map of the 10 km Radius of the Study Area ............ 111

Figure 3-10: Satellite Image of the 10 km Radius of the Study Area ................................. 112

Figure 3-11: Infrastructure Map of the 10 km Radius of the Study Area............................ 113

Figure 3-12: Topography Map of the 10 km Radius of the Study Area .............................. 115

Figure 3-13: Chart Showing Status of Educational Facilities in Study Area ......................... 141

Figure 3-14: Chart Showing Status of Medical Facilities in Study Area ............................... 142

Figure 3-15: Chart Showing Status of Drinking Water Facilities in Study Area ................... 142

Figure 3-16: Chart Showing Status of Sanitation Facilities in Study Area ........................... 143

Figure 3-17: Chart Showing Status of Communication Facilities in Study Area ................... 144

Figure 3-18: Chart Showing Status of Availability of Roads in Study Area.......................... 145

Figure 3-19: Chart Showing Status of Transportation Facilities in Study Area .................... 146

Figure 3-20: Chart Showing Status of Other Facilities in Study Area ................................. 146

Figure 3-21: Image showing Traffic Surveying Location ................................................... 148

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT LIST OF FIGURES 11

Figure 4-1: Ground Level Concentration of PM10 .............................................................. 162

Figure 4-2: Ground Level Concentration of SO2 ............................................................... 163

Figure 7-1: Styrene BLEVE ............................................................................................. 181

Figure 7-2: Pool Fire Threat zone Styrene(40 MT tank).................................................... 182

Figure 7-3: Toxic dispersion threat zone styrene (40 MT tank) ......................................... 183

Figure 7-4: Off-Site Disaster Management Plan ............................................................... 193

Figure 10-1: Environmental Management Cell ................................................................. 216

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT LIST OF PHOTOGRAPHS 12

LIST OF PHOTOGRAPHS

Photograph 2-1: Project site ............................................................................................ 49

Photograph 3-1: Ambient Air Quality Monitoring ............................................................... 79

Photograph 3-2: Noise Monitoring .................................................................................... 84

Photograph 3-3: Ground Water Sampling ......................................................................... 89

Photograph 3-4: Photographs of Surface Water Sampling .................................................. 94

Photograph 3-5: Soil Sampling Photograph ....................................................................... 98

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT ABBREVIATIONS 13

ABBREVIATIONS

AAQ : Ambient Air Quality

ACGIH : American Conference of Governmental Industrial Hygienists

AEGL : Acute Exposure Guideline Level

AERB : Atomic Energy Regulatory Board

AERMOD : Atmospheric Dispersion Modeling System

ALOHA : Areal Locations Of Hazardous Atmospheres

APCM : Air Pollution Control Measures

APHA : American Public Health Association

B.D.L : Below Detection Limit

BLEVE : Boiling Liquid Expanding Vapour Explosion

BOD : Biochemical Oxygen Demand

BP : Boiling Point

CC : Close Cup

CCA : Consolidated Consent of Authorization

CCG : Central Crisis Group

CCOE : Chief Controller Of Explosives

CEES : Committee on Earth and Environmental Sciences

CGWA : Central Ground Water Authority

CO : Carbon Oxide

COD : Chemical Oxygen Demand

CPCB : Central Pollution Control Board

CS : Certifying Surgeon

CSR : Corporate Social Responsibility

D.G. : Diesel Generator

DCC : District Control Committee

DCG : District Crisis Group

DEM : Digital Elevation Map

DGFASLI : Directorate General, Factory Advice Service and Labor Institutes

DGFT : Directorate General of foreign Trade

DL : Detection Limit

DMP : Disaster Management Plan

DRDO : Defense Research and Development Organization

DTM : Digital Terrain Model

EAC : Expert Appraisal Committee

EC : Environmental Clearance

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT ABBREVIATIONS 14

ECG : Electrocardiogram

ECO : Emergency Coordinating Officer

EHS : Environment Health & Safety

EIA : Environmental Impact Assessment

EMP : Environmental Management Plan

EMS : Environmental Management System

EPA : Environment Protection Act

EPO : Emergency Planning Office

EPRG : Emergency Response Planning Guidelines

ERDAS : Earth Resources Data Analysis System

ESC : Enterprise Social Commitment

ESRI : Environmental Systems Research Institute

ETP : Effluent Treatment Plant

FAA : Functional Area Associate

FCC : False Color Composite

FP : Flash Point

GIDC : Gujarat Industrial Development Corporation

GIS : Geographic Information System

GoI : Government of India

GPCB : Gujarat Pollution Control Board

GPS : Global Positioning System

HDPE : High Density Poly Ethylene

HP : Horse Power

IDLH : Immediate Danger to Life or Health

IMD : Indian Meteorological Department

IRS : Indian Remote Sensing

IS : Indian Standard

IUCN : International Union for Conservation of Nature

KL/d : Kilo Liter per Day

LCG : Local Crisis Group

LEL : Lower Explosive Limit

LISS : Linear Imaging Self-Scanning Sensor

LOC : Level of Concern

LULC : Land Use Land Cover

MAH : Major Accident Hazards

MCA : Maximum Credible Accident

MLSS : Mixed Liquor Suspended Solids

Page 15: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT ABBREVIATIONS 15

MOC : Mode of Construction

MoEF&CC : Ministry of Environment and Forest & Climate Change

MS : Mild Steel

MSDS : Material Safety Data Sheet

MSIHC : Manufacture, Storage and Import of Hazardous Chemical

MSME : Micro, Small and Medium Enterprises

MT : Metric Tonnes

NA : Non-Agricultural

NABET : National Accreditation Board for Education and Training

NABL : National Accreditation Board for Testing and Calibration Laboratories

NFPA : National Fire Protection Association

NOC : No Objection Certificate

NOx : Oxides of Nitrogen

NRSC : National Remote Sensing Centre

NS : Not Specified

OC : Open Cup

OEP : Occupant Emergency Plan

OSHA : Occupational Safety and Health Administration

PCU : Passenger Car Unit

PEL : Permissible Exposure Limit

DGVCL : Dakshin Gujarat Vij Company Limited

PHC : Personal and Home Care

PM : Particulate Matter

PPE : Personnel Protective Equipment

ppm : parts per million

PRM : Rotation per Minute

PUC : Pollution Under Control

QRA : Quantitative Risk Assessment

R&R : Rehabilitation & Resettlement

RA : Risk Assessment

RM : Resident Migratory

SC : Schedule Cast

SCBA : Self-Contained Breathing Apparatus

SCG : State Crisis Group

SEAC : State Expert Appraisal Committee

SEIAA : State Level Environmental Impact Assessment Authority

SEZ : Special Economic Zone

Page 16: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT ABBREVIATIONS 16

SMF : Stack Monitoring Facility

SOP : Standard Operating Procedure

SOx : Oxides of Sulphur

SPCB : State Pollution Control Board

SPM : Suspended Particulate Matter

SRTM : Shuttle Radar Topographic Mission

SS : Stainless Steel

ST : Schedule Tribe

STEL : Short Term Exposure Limit

TDS : Total Dissolved Solids

TFH : Thermic Fluid Heater

TLV : Threshold Limit Value

ToR : Terms of References

TR : Tonne of Refrigeration

TREM : Transport Emergency

TSDF : Treatment Storage and Disposal Facility

TWA : Time Weighted Average

UEL : Upper Explosive Limit

UTM : Universal Transverse Mercator

UTPCC : Union territory Pollution Control Committee

VOC : Volatile Organic Compound

WHO : World Health Organization

ZLD : Zero Liquid Discharge

Page 17: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 17

TOR COMPLIANCE

Compliance statement is prepared for Terms of Reference received wide letter no.: SEIAA/GUJ/TOR/5(f)/270/2017 dated 24th April 2017 attached wide

Annexure 1.

TOR.

No. TOR Condition Compliance status

Page

No.

1. Land possession document with copy of 7/12, 8A, 6A and certified copy of

distance certificate of the nearest human habitation from the concerned

authority.

NA permission is received by industry and is enclosed as

Annexure 5.

297

2. Details of surrounding industrial with details like Name and address of the unit,

type and nature of industrial activity etc.

Refer section 2.4 of chapter no.: 2 54

3. Legal Undertaking stating that unit is complying the three conditions [i.e. water

consumption less than 25 M3/day; Fuel consumption less than 25 TPD;

and not covered in the category of MAH units as per the Management,

Storage, Import of Hazardous Chemical Rules (MSIHC Rules), 1989] as per

the amendment to EIA Notification, 2006 vide SO 1599 (E) dated

25.06.2014.

Legal undertaking as required is attached as Annexure 7 382

4. Demarcation of proposed activities in lay out plan. Exact details about

infrastructural facilities, plant machineries etc. required for the proposed

project.

Plant layout is enclosed as Figure 2-6. 55

5. Detailed manufacturing process along with chemical reactions and mass

balance (including reuse recycle, if any) for each product to be

manufactured. Details on end use of each product. Give full name and

chemical formula of all the raw materials and products.

Detailed manufacturing process, chemical reaction and

material balance is given in Section 2.8 of chapter 2

End use of product is mentioned in Section 2.7

58

57

6. Copy of permission obtained from concern authority for water supply. Source of water is road tanker and letter from supplier stating

he will supply required quantity of water is enclosed as

Annexure 4

296

Page 18: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 18

TOR.

No. TOR Condition Compliance status

Page

No.

7. Water consumption and consumption of each raw material per MT of each

product.

consumption of each raw material per MT of each product is

given in Section 2.9

63

8. Water balance diagram (including reuse-recycle, if any) along with qualitative

and quantitative analysis of the each waste stream to be generated. A

detailed treatability study vis-à-vis the adequacy and efficacy of the

treatment facilities proposed for the wastewater to be generated.

Water balance is enclosed as Figure 2-7

Quality of effluent stream wise is given in Table 2-13

68

69

9. Treated effluent management plan during monsoon season when utilization of

treated effluent for gardening & plantation purpose is not feasible.

Detailed study report considering Percolation rate of the land available for

gardening & plantation. Ensure that land is suitable for utilization of

treated waste water for plantation & gardening.

Note applicable as final mode of disposal is evaporation in

TFH based evaporator.

-

10. Technical details of the ETP/Evaporator including size of each unit, retention

time etc.

Technical details of evaporator are given in Table 2-15

Size and retention time of each ETP unit is given in Table

2-14.

70

11. Action plan for ‘Zero’ discharge of effluent shall be included. Give qualitative

and quantitative data with feasibility report for reuse of Mother Liquor in

process again. Submit an undertaking in this regard.

Action plan for zero liquid discharge is given in section

2.13.1.

Styrene is being used but it is consumed in process hence

there is no possibility of generation of mother liquor.

67

12. Plan for management and disposal of waste streams to be generated from

spillage, leakages, occasional reactor washing and exhausted media from

Scrubber etc.

Refer section 10.2.3 207

13. Explore the possibility of reuse / recycle and other cleaner production options

for reduction of wastes. Details of methods to be adopted for the water

conservation.

For reuse/recycle and cleaner production options refer

section 10.1.3.

Details of methods to be adopted for the water

conservation are given in section 10.2.3

203

207

Page 19: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 19

TOR.

No. TOR Condition Compliance status

Page

No.

14. AAQ data (except monsoon) to be given along with the dates of monitoring.

The parameters to be covered shall include PM10, PM2.5, SO2, and NOx.

The location of the monitoring stations should be so decided so as to take

into consideration the pre-dominant downwind direction, population zone

and sensitive receptors including reserved forests. There should be at least

one monitoring station in the upwind direction. There should be at least

one monitoring station in the pre dominant downwind direction at a

location where maximum ground level concentration is likely to occur.

One complete season base line ambient air quality data

(except monsoon) along with the dates of monitoring is

given in Annexure 3

Locations of monitoring given in Table 3-4.

291

79

15. One season Site-specific micro-meteorological data using temperature, relative

humidity, hourly wind speed and direction and rainfall should be

incorporated.

One season Site-specific micro-meteorological data is given as

Annexure 4

232

16. Anticipated environmental impacts due to the proposed project/production

may be evaluated for significance and based on corresponding likely

impacts VECs (Valued Environmental Components) may be identified.

Baseline studies may be conducted within the study area of 5 km for all

the concerned/identified VECs and likely impacts will have to be assessed

for their magnitude in order to identify mitigation measures.

Anticipated environmental impacts and its mitigation

measures due to the proposed project/production is given

in Chapter-4.

Baseline study for 5 km Radius is given in Chapter-3.1

149

73

17. One complete season base line ambient air quality data (except monsoon) to

be given along with the dates of monitoring. The parameters to be

covered shall be in accordance with the revised National Ambient Air

Quality Standards as well as project specific parameters. Locations of the

monitoring stations should be so decided so as to take into consideration

the pre-dominant downwind direction, population zone and sensitive

receptors. There should be at least one monitoring station in the upwind

direction. There should be at least one monitoring station in the pre

dominant downwind direction at a

location where maximum ground level concentration is likely to occur.

One complete season base line ambient air quality data

(except monsoon) along with the dates of monitoring is

given in annexure 3.

Locations of monitoring given in Table 3-4.

291

79

Page 20: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 20

TOR.

No. TOR Condition Compliance status

Page

No.

18. Modelling indicating the likely impact on ambient air quality due to proposed

activities. The details of model used and input parameters used for

modelling should be provided. The air quality contours may be shown on

location map clearly indicating the location of sensitive receptors, if any,

and the habitation. The wind rose showing pre-dominant wind direction

should also be indicated on the map.

Impact due to vehicular movement shall also be included into the prediction

using suitable model. Results of Air dispersion modelling should be

superimposed on satellite Image / geographical area map.

Details of model used are given in section 4.3.7-B-2.

Input parameters are given in Table 4-4 & Table 4-5.

Air quality contours on location map are shown in Figure

4-1 & Figure 4-2 .

Wind rose diagram showing pre-dominant wind direction

is given as Table 3-1.

The predicted concentration of pollutants is given in Table

4-6 . These values are including impact due to vehicular

movement.

161

160 &

160

162, 163

77

164

19. Base line status of the noise environment, impact of noise on present

environment due to the project and proposed measures for noise

reduction including engineering controls.

Baseline status of noise environment is given in section

3.3.1

Impact and mitigation measures proposed for noise

environment is given in section 4.3.3.

83

156

20. Specific details of (i) Process gas emission from each unit process with its

quantification, (ii) Air pollution Control Measures proposed for process gas

emission, (iii) Adequacy of the air pollution control measures for process

gas emission measures to achieve the GPCB norms (iv) Details of the

utilities required (v) Type and quantity of fuel to be used for each utility

(vi) Flue gas emission rate emission from each utility (vii) Air Pollution

Control Measures proposed to each of the utility along with its adequacy

(viii) List the sources of fugitive emission along with its quantification and

proposed measures to control it.

There is no process gas emission from production activities.

Details of the utilities required is given in Table 2-9.

Type and quantity of fuel to be used for each utility is

given in Table 2-8.

Flue gas emission rate emission from each utility is given

in Table 4-5.

As fuel used in TFH is diesel there is no requirement of Air

Pollution Control Measures, only adequate stack height is

sufficient. The details of stacks is given in Table 2-16.

List the sources of fugitive emission along with its

quantification and proposed measures to control it is

given in Section- 2.13.2-C

66

66

160

71

71

Page 21: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 21

TOR.

No. TOR Condition Compliance status

Page

No.

21. Details on management of the hazardous wastes to be generated from the

project stating detail of storage area for each type of waste, its handling,

its utilization and disposal etc. How the manual handling of the hazardous

wastes will be minimized. Explore the possibilities for co-processing of the

Hazardous waste/Solid waste prior to disposal into TSDF/CHWIF.

Methodology of de-contamination and disposal of discarded containers and

its record keeping.

Details on management of the hazardous wastes to be

generated from the project is given in Section-2.13.3.

Adequate storage area for hazardous waste will be

provided within the premises.

Membership of TSDF site will be taken after

commencement of plant.

Manual Handling will be minimized by using wheel

trolley or other equipment for the transportation.

72

22. Membership of Common Environmental Infrastructure including TSDF,

Common Hazardous Waste Incineration Facility (CHWIF) along with an

assessment to accommodate the additional quantity of wastes to be

generated.

Industry will take permission from TSDF after getting

Environmental clearance. Hazardous waste storage room

will be provided to store the waste generation

-

23. Complete Management plan for By-products/spent acid to be generated, (if

any) from the project including their quantity, quality, characteristics, end

use etc. along with the name and address of end consumers to whom the

by-product will be sold. Copies of agreement / MoU / letter of intent from

them, showing their willingness to purchase said by-products/spent acids

from the proposed project.

Not applicable as there is no by-product/spent acid

generation.

-

24. Name and quantity of each type of solvents to be used for proposed

production. Details of solvent recovery system including mass balance,

solvent loss, recovery efficiency feasibility of reusing the recovered

solvents etc. for each type of solvent. Leak detection and repairing

programme (LDAR) for VOC

The solvent used styrene which is being consumed in

process as it is used for resin dilution. The quantity of

styrene is given in Table 2-6.

64

25. Data on air emissions, wastewater generation and solid / hazardous waste

generation and management for the existing plant should also be

Not applicable as this is proposed project. -

Page 22: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 22

TOR.

No. TOR Condition Compliance status

Page

No.

incorporated. (Comparative data in tabular format).

26. Details of measures proposed for the noise pollution abatement and its

monitoring.

Refer section 10.2.4 210

27. A detailed EMP including the protection and mitigation measures for impact on

human health and environment as well as detailed monitoring plan and

environmental management cell proposed for implementation and

monitoring of EMP. The EMP should also include the concept of waste

minimization, recycle/reuse/recover techniques, energy conservation, and

natural resource conservation. Total capital cost and recurring cost/annum

earmarked for environment pollution control measures.

Detailed EMP including the protection and mitigation

measures for impact on human health and environment is

given in Section 10.2.

Detailed monitoring plan is given in section Table 6-1.

Details of environmental management cell proposed for

implementation and monitoring of EMP is given in section

10.3.1.

Total capital cost and recurring cost/annum earmarked

for environment pollution control measures is given in

section 10.4.

204-214

166

215

217

28. Occupational health impacts on the workers and mitigation measures proposed

to avoid the human health hazards along with the personal protective

equipment (PPE) to be provided to the workers. Provision of industrial

hygienist and monitoring of the occupational injury to workers as well as

impact on the workers. Plan for periodic medical check-up of the workers

exposed. Details of work place ambient air quality monitoring plan as per

Gujarat Factories Rules.

Refer section 10.2.7 213

29. Details of hazardous characteristics and toxicity of raw materials and products

to be handled and the control measures proposed to ensure safety and

avoid the human health impact. MSDS of all the products and raw

materials to be used. Permission from PESO, Nagpur for storage of

solvents, other toxic chemicals, if any.

Details of hazardous characteristics and toxicity of raw

materials and products to be handled are given in section

7.3.4 . Table 7-2: Chemical Properties of Hazardous

Chemicals

Hazard identification and control measures are given in

section 7.3.5.

172

173

Page 23: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 23

TOR.

No. TOR Condition Compliance status

Page

No.

MSDS are enclosed as Annexure 6.

Permission from PESO, Nagpur for storage of solvents,

other toxic chemicals will be taken after receipt of EC.

320

30. Details of quantity of each hazardous chemical to be stored, material of

construction of major hazardous chemical storage tanks, threshold storage

quantity as per schedules of Manufacture, Storage & Import of Hazardous

Chemicals (MSIHC) Rules of major hazardous chemicals.

Refer section 7.3.3 171

31. Details of the separate isolated storage area for flammable chemicals. Details

of flame proof electrical fittings, DCP extinguishers and other safety

measures proposed. Detailed fire control plan for flammable substances

and processes showing hydrant pipeline network, provision of D.G. Sets,

fire pumps, jockey pump, toxic gas detectors etc.

Refer Section 7.3.10 186

32. Risk assessment including prediction of the worst-case scenario and maximum

credible accident scenarios should be carried out. The worst-case scenario

should take into account the maximum inventory of storage at site at any

point of time. The risk contours should be plotted on the map clearly

showing which of the facilities and surrounding units would be affected in

case of an accident taking place. Based on the same, proposed safeguard

measures including On-Site / Off-Site Emergency Plan should be provided.

Risk assessment including prediction of the worst-case

scenario and maximum credible accident scenarios is

given in section 7.3.6. & Table 7-3: Consequence Analysis

and damage distances

Risk contours are given as Figure no. 7.1 to 7.3

On-Site / Off-Site Emergency Plan is given in section 7.4

& 7.5

177 &

180

181 &

183

188 &

192

33. Details of fire fighting system including provision for flame detectors,

temperature actuated heat detectors with alarms, automatic sprinkler

system, location of fire water tanks & capacity, separate power system for

fire fighting, details of qualified and trained fire personnel & their job

specifications, nearest fire station & time required to reach the proposed

site. Submit line diagram of the fire hydrant network.

Refer Section 7.3.10 1867

Page 24: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT TOR COMPLIANCE 24

TOR.

No. TOR Condition Compliance status

Page

No.

34. Submit checklist in the form of Do’s & Don’ts of preventive maintenance,

strengthening of HSE, manufacturing utility staff for safety related

measures.

Refer Section 7.5.1 197

35. A tabular chart for the issues raised and addressed during public

hearing/consultation and commitment of the project proponent on the

same should be provided. An action plan to address the issues raised

during public hearing and the necessary allocation of funds for the same

should be provided.

Will be given after public hearing. -

36. Detailed five year greenbelt development program including annual budget,

types & number of trees to be planted, area under green belt development

[with map], budgetary outlay; along with commitment of the management

to carry out the tree plantation activities outside the premises at

appropriate places in the nearby areas and elsewhere.

Detailed five year greenbelt development program

including, types & number of trees to be planted is given

in Table 10-7.

Area under greenbelt development is shown in Figure

2-6.1

Budget for greenbelt development is given in Table 10-10.

Commitment by management to carry out the tree

plantation activities outside the premises is enclosed as

Annexure 8.

212

55

217

384

37. Certificate of accreditation issued by the NABET, QCI to the environmental

consultant should be incorporated in the EIA Report.

Refer Section-12.1 224

38. An undertaking by the Project Proponent on the ownership of the EIA report as

per the MoEF&CC OM dated 05/10/2011 and an undertaking by the

Consultant regarding the prescribed TORs have been complied with and

the data submitted is factually correct as per the MoEF&CC OM dated

04/08/2009.

Undertaking by Project Proponent on the ownership of

the EIA report is enclosed as Annexure 9.

Undertaking by the Consultant for the data submitted

Annexure 10

386

388

39. A tabular chart with index for point-wise compliance of above. As above

Page 25: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT EXECUTIVE SUMMARY-ENGLISH 25

EXECUTIVE SUMMARY-ENGLISH

1. Introduction

Roman Petrochemical is proposing to manufacture Resin at Survey No. 922/P2, Village:

Mota Dahisara, Navlakhi Highway, Taluka: Maliya, District: Morbi, Gujarat for sell purpose.

Production details are given below:

Details of Products

Sr. No. Name of Product Capacity (MT/Month)

1. Unsaturated Polyester Resin 500

Total available land area of premises is 12,950 m2, out of which 4270 m2 (32.97%) area will

be developed for greenbelt. The estimated cost of the project is 300 lacs. Total budget

allocation towards Environmental Management Facilities will be Rs. 60 lacs and recurring cost

will be 18 Lacs.

M/s. T. R. Associates (NABET Accreditation No.: NABET/EIA/1619/RA0033) was

appointed by Roman Petrochemical to carry out the Environmental Impact Assessment

study for their proposed project.

Production of resin falls under clause No.5 (f) of category “B1” as stated in Environment

Impact Assessment Notification published on 14th September 2006 and hence the project

proponent has to obtain the Environmental Clearance from SEIAA, Gujarat. As a part of this

procedure, Public Hearing is required to be carried out as per the notification as well as the

ToR granted to the unit by the Expert Appraisal Committee (Industry-2).

This study of Rapid Environment Impact assessment (EIA) is based on studies carried out

during the month October-2016 to December -2016. The environmental parameters (ambient

air, water, soil, noise, flora and fauna, socio economy) selected for study are those, which are

likely to be most affected by the project. The study area is defined as an area within 10 km

radius from center of the site.

Salient Features within 10 km radius surroundings area as follows:

Sr.

No. Important Features Description

1. Location Survey No. 922/P2, Village: Mota Dahisara, Taluka:

Maliya, District: Morbi, Gujarat.

2. GPS Coordinates 22°57'2.67"N

70° 35'9.15"E

3. Mean Sea Level 8 m

4. Temperature range 180 C to 400 C

5. Annual Rain fall 709 mm

6. Nearest Road NH 947 @ 8.3 km, ESE

SH 24 @ 0.17 km, N

7. Nearest Railway station Maliya @ 24.2 km NE

Page 26: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT EXECUTIVE SUMMARY-ENGLISH 26

Sr.

No. Important Features Description

8. Nearest city Morbi @ 27.2 km, SE

9. Nearest village Khirasara @ 0.92 km, ESE

10. National Highway NH 947 @ 8.3 km, ESE

11. Nearest River/water body Phulku Nadi @ 1.13 km, NE

Jhinjhoda River @ 3.6 km, SSW

12. Seismic Zone Zone-V (Highest risk zone)

13. National Parks / Sanctuary None within 10 km radius.

2. Impact and Mitigation Measures

2.1 Air Environment

The main source of flue gas emission is TFH (6 lac kCal/h), D. G. Set (150 kVA) as a stand-

by source to the main power supply. Fuel used in TFH & D.G. is Diesel. There is no process

gas emission. Due to raw material handling and transportation and manufacturing activity,

there will be chances of fugitive emissions.

The base line Ambient Air Quality (AAQ) status within 10 km study area has been assessed

through a monitoring network of 5 AAQ sampling stations during October-2016 to December

-2016 Ambient Air Quality monitoring locations were decided on meteorology & available

infrastructure facilities. The base-line Ambient Air Quality of the study area was monitored for

Particulate Matter (PM10 & PM2.5), Sulphur Dioxide (SO2), Nitrogen Dioxide (NO2), VOC, & CO.

The result for the same is given as below:

Name of the villages for baseline monitoring:

Location

Distance

(km) &

Direction

98th Percentile (µg/m3)

PM2.5 PM10 SO2 NO2

Project Site - 33.4 79.8 21.7 27.7

Bodki 3.8

SSW 31.8 81.5 22.5 28.8

Vavniya* 6.7

NNE 31.5 81.4 23.5 26.8

Vavaniya Reserve Forest 8.6

N 30.5 82.8 23.5 25.7

Mangroves Swamp 12.4

W 35.8 83.0 23.0 28.9

Permissible limit [NAAQS -2009] 60 100 80 80

*: Indicates predominant downwind direction

CO: Not Detected; VOC: Not Detected

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT EXECUTIVE SUMMARY-ENGLISH 27

Analysis of ambient air samples revealed that the Air quality is found well within the

prescribed limits of National Ambient Air Quality standards.

There is no requirement Air Pollution Control Measure for TFH as Diesel will be used as fuel.

D.G. set is standby hence adequate stack height will be provided for proper dispersion of

pollutants.

Unit will take all the necessary precautions and control measures to take care of the fugitive

emissions, such as all the raw materials will be stored in isolated storage area; entire

manufacturing activity will be carried out in closed reactors / vessels and regular checking

and maintenance of the same will be carried out to avoid any leakages.

2.2 Water Environment

In proposed unit 16.9 KL/d fresh water is required for domestic activities, greenbelt

development, and utility operations. Source of fresh water is tanker.

Total 0.15 KL/d sewage (domestic wastewater) will be generated. Total industrial wastewater

generation will be 1.9 KL/d.

Stream-wise Water Requirement

Sr. No. Particular

Water

Requirement

(KL/d)

1 Domestic activities 3.2

2 Greenbelt development 7.5

3

Industrial activities 6.2

Cooling Tower 6.0

Washings 0.2

Process -

Total industrial 6.2

Total (domestic + industrial + Greenbelt development) 16.9

Stream-wise Wastewater Generation

Sr. No. Particular

Wastewater

Generation

(KL/d)

Remark

1 Domestic activities 0.15 To soak pit via

septic tank

2

Industrial activities 1.9

ETP followed

by Evaporator

Cooling Tower 0.3

Washings 0.2

Process 1.4

Total industrial 1.9

Total (domestic + industrial) 2.05

Sewage will be taken to soak pit. For industrial effluent following treatment scheme is

suggested:

Page 28: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT EXECUTIVE SUMMARY-ENGLISH 28

Total 1.9 KLD of waste water generated from floor washing water, process effluent and

cooling tower blow down will be collected in Collection cum neutralization Tank. Effluent will

be then neutralized using Lime & Alum and then taken to Nutch Filter for sludge separation.

Separated dried sludge will be collected, stored and disposed of at approved TSDF site.

Filtrate water from Nutch Filter will be taken to holding tank then it will be evaporated in

steam based Evaporator, thus unit will maintain zero liquid discharge.

Analysis of Ground Water & Surface Water samples revealed that the both ground water

quality & surface water quality is satisfactory to serve for domestic purposes as per drinking

water quality standards IS: 10500.

2.3 Solid and Hazardous Waste Management

The main hazardous waste generation will be ETP waste & evaporation residue. The other

hazardous wastes shall be used oil & Discarded Plastic Bags.

ETP sludge + evaporation residue will be disposed off at approved TSDF site. Used oil will be

reused within premises as a lubricant or sold to registered recycler. Discarded plastic

bags/drums will be sold to authorized vendor.

Unit will provide storage area for hazardous wastes having roof, pucca flooring with leachate

collection system to avoid land/soil contamination. Leachate, if any will be collected and

treated in effluent treatment plant.

2.4 Land Environment

During operation activity the impact of air, water and solid & hazardous waste pollution on

soil causes direct / indirect effect on soil.

As all necessary air pollution control steps are proposed to avoid adverse impact of air

pollution on soil. Proposed greenbelt inside the unit consists of tree cover which is tolerant to

major air pollutants.

Rain water harvesting system is proposed for recharging ground water. The effluent

treatment plant is ZLD hence there will be no disposal of untreated effluent on land. Soak-pit

will be cleaned periodically. So there will be no adverse effect on land / soil due to water.

All necessary control steps will be provided for handling, storage and disposal of

solid/hazardous waste generated from the plant. Thus, there will not be any significant

impact of solid/hazardous waste on the soil environment.

2.5 Noise Environment

In proposed project main source of noise will be D.G. set, pump, TFH & evaporator.

Noise level was recorded at 5 locations within the study area to provide the baseline data to

describe the existing situations.

Sampling Location Category

Leq (dB(A))

Limit Recorded

Day Time Night Time Day Time Night Time

Project Site Industrial 75.0 70.0 69.0 62.4

Page 29: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT EXECUTIVE SUMMARY-ENGLISH 29

Sampling Location Category

Leq (dB(A))

Limit Recorded

Day Time Night Time Day Time Night Time

Mota Dahisara Residential 55.0 45.0 52.3 43.1

Bodki Residential 55.0 45.0 47.8 41.0

Vavaniya Residential 55.0 45.0 46.6 39.2

Virparda Residential 55.0 45.0 45.2 37.5

Recorded Noise levels are found to be within the standard limits.

To control noise level in operation phase low noise D.G. set with acoustic enclosures will be

installed. Proper and timely lubrication, oiling and maintenance will be carried out for all plant

and machineries.

2.6 Ecology & Biodiversity

The area is predominated by open land. This study reported a total of 154 plant species, 10

Herpetofauna, 58 birds and 12 species of mammals from the buffer zone of unit. However,

no threatened biodiversity reported with highest density or richness from the core and buffer

zones of the study area.

Agricultural tree species found in the study area are Papaiyu, Chiku, Khajuri and Ambo. Major

crops in the study area are Bajra, and Jowar.

Common tree species found in study area are Deshi Bavar, Limbdo/ Neem, Goras Amali,

Khijado.

The most commonly spotted bird species of this area were Grey Francolin, Indian Peafowl,

Comb Duck, Common Hoopoe, Rock Pigeon, Laughing Dove, Blackwinged Stilt, House Crow.

The wild mammals found other than domesticated ones from study area were Nilgai, Golden

Jackal/ Indian Fox, Chinkara, Grey Mongoose, Wild Boar, and Jungle Cat.

2.7 Risk Assessment

Risk analysis and study have been carried out for identification of hazards, selection of

maximum credible scenarios, risk mitigation measures etc. All the hazardous chemicals will be

stored and handled as per MSDS guidelines.

2.8 Occupational Health and Safety

Based on risk assessment preventive measures are identified to ensure good health and

safety of workers. Such measures include:

Provision PPEs like ear plug, ear muff etc. where noise levels in excess of 80 dB (A) are

regularly generated. Regular medical checkup of workers. Provision of basic infrastructure i.e.

like drinking water, sanitation, first aid etc. to workers. Use of proper PPE’s during ETP

operation, hazardous waste handling, chemical handling etc.

2.9 Greenbelt Development

Total greenbelt area of 4270 m2 (32.97%)has been allotted for greenbelt development. This

will contains common tree species found in study area which is tolerant to pollutants, acts as

Page 30: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT EXECUTIVE SUMMARY-ENGLISH 30

noise absorbers. This will not only mitigate the ecological problem but also enhance the

beauty of project area that will attract avifauna, small mammals & insect species, and by this

way ecological balance can be maintained to great extent.

3. Environmental Management Plan

An Environmental Management Plan has been prepared to identify mitigation measures of

adverse impacts. It describes objective, responsibility, resources, monitoring related to

mitigations measures for identified impact. It also includes details of greenbelt development,

rain water harvesting, CSR activities etc.

4. Environment Monitoring Program

Environment monitoring program prepared to check efficiency of mitigation measures and

changes in environment over period of time at various stages of project development.

5. Project Benefits

Demographic & other socio-economic data was collected from District Census Handbook to

assess socio-economic status of the study area.

For proposed project activity, total 30 Nos. of skilled and unskilled employees/ workers will be

required. The indirect employment will be generated by way of transportation, shops and

other casual employment for many people.

Local people will be given preference wherever found suitable for all the jobs in the plant.

Economic status of the local people will improve due to the increased business opportunities,

thereby, making a positive impact. Unit will spend annually minimum 2.5% of its net profit for

carrying out various CSR activities every year.

6. Conclusion

Negligible impacts will occur on air quality. However, all the necessary air pollution

control measures will be provided.

No ecological damage will occur.

No adverse impacts will occur on water environment.

Local employment opportunities will increase.

Various other environment parameters like Forest/ National Park/ Sanctuary and

Religious / Historical Places will not be affected.

Environment Management Plan has been formulated to control all the pollutant

parameters and Environment Management Cell has been set-up to ensure that these parameters do not exceed the norms set out by the concerned authorities.

After commissioning of the proposed project the Environmental Management Cell will

take care of all the pollution control measures.

It can be concluded that positive implementation of mitigation measures and environmental

management plan during the construction & operational phase, there will be negligible impact

on the environment.

Page 31: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 31

સકં્ષીપ્ત અ વેાલ-ગજુરાતી

૦૧. પ્રસ્તાવના

મેસસા રોમન પેટ્રોકેમીકલ એ પ્રસ્તામવત એકમ છે. આ પ્રસ્તામવત એકમે અનસેચ્યરેુટેડ પોલીએસ્ટર રેઝીન કરવા માટેની દરખાસ્ત કરેલ છે તથા એકમ સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, નવલખી ાઈવે , તાલકુા :- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજર્મા ંઆવેલો છે.

ઉત્પાદન વવગતો ક્રમાકં પ્રોડક્ટનુ ંનામ ક્ષમતા (મેટ્રીક ટન/ માસ)

૧ અનસેચ્યરેુટેડ પોલીએસ્ટર રેઝીન ૫૦૦

પ્રસ્તામવત એકમનો કુલ મવસ્તાર આશરે ૧૨,૯૫૦ ચો. મીટર છે. જેમાથંી ૪૨૭૦ ચો.મી. (આશરે કુલ મવસ્તારના ૩૨.૯૭%) જમીન ગ્રીન બેલ્ટ માટે ફાળવવામા ં આવશે. પ્રસ્તામવત એકમને પ્રસ્થામપત કરવાની હકિંમત રૂમપર્ા ૩૦૦ લાખ થશે, જેમાથંી પર્ાાવરણીર્ વ્ર્વસ્થાપન પધ્ધમત માટે આશરે ૬૦ લાખ ફાળવવામા ંઆવશે અને તેનો આવતાક ખચા ૧૮ લાખ થશે.

મેસસા ટી. આર. એસોસીએટ્સની મેસસા રોમન પેટ્રોકેમમકલ દ્વારા પ્રસ્તામવત એકમનો પર્ાાવરણીર્ પથૃ્થકરણ અસર અભ્ર્ાસ (EIA) કરવા માટે મનમણ કં કરવામા ંઆવેલ છે.

અતે્ર નોંધનીર્ છે કે રેઝીન ઉત્પાદન EIA નોટીફીકેશન-૨૦૦૬ ના ૫(એફ) મવભાર્ગની બી ૧ કેટેર્ગરીમા ંઆવે છે. તદ્ઉપરાતં એકમની જગ્ર્ા સ ચચત ઓદ્યોચર્ગક મવસ્તારની બ ાર છે અને સ ચચત પરીર્ોજના ૨૫ જ ન ૨૦૧૪ના નોટીફીકેશન પ્રમાણે નાના પાર્ાના ઓદ્યોચર્ગક એકમ અંતર્ગાત આવે છે. તેથી SEIAA, Gujarat પાસેથી પર્ાાવરણીર્ મજં રી (ENVIRONMENTAL CLEARANCE) મેળવવાની જરૂરીર્ાત ર લે છે. આ પ્રકીર્ાના ભાર્ગ રૂપે લોકસનુાવણી એ જા રેનામા પ્રમાણે તથા એક્ષ્પટા એપ્રાઈઝલ કમીટી એ યમુનટને આપેલા TOR પ્રમાણે કરવામા ંઆવશે.

પર્ાાવરણ પ્રથૃ્થકરણ અસર અભ્ર્ાસ (ENVIRONMENTAL IMPACT ASSESSMENT STUDY) ઓક્ટૉબર ૨૦૧૬ થી હડસેમ્બર ૨૦૧૬ દરમમર્ાન ૫ સ્થળે કરવામા ંઆવેલ તા. પર્ાાવરણીર્ ઘટકો જેવા કે (આસપાસ ની વા, પાણી, જમીન,ધ્વમન, વનસ્પમતઓ અને પ્રાણીઓ) જે પ્રસ્તામવત એકમથી અસર પામી શકે તેમ છે., તેનો અભ્ર્ાસ કરવામા ંઆવ્ર્ો છે. પ્રસ્તામવત એકમને કેન્રમા ંલઈને ૧૦ હકમી. મત્રજ્ર્ાના વર્ુાળાકાર મવસ્તારને અભ્ર્ામસત ક્ષેત્ર તરીકે નક્કી કરવામા ંઅવેલ છે.

Page 32: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 32

આસપાસના ૧૦ કકમી વિજ્યાના વવસ્તારની મખુ્ય લાક્ષણિકતાઓ ક્રમાકં મખુ્ય લાક્ષણિક્તાઓ વિણન ૧ પ્રસ્તામવત એકમનુ ંસ્થાન સવે ન:ં- ૯૨૨/પી૨ , ર્ગામ:- મોટા દહ િંસરા,

તાલકુા:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્

૨ અક્ષાશં – રેખાશં

અક્ષાશં:- ૨૨⁰ ૫૭’ ૨.૬૭ ” N

રેખાશં:- ૭૦0 ૩૫ ’ ૦૯.૧૫ ” E

૩ સમરુી સ્તરના સરેરાશ ૮ મીટર

૪ તાપમાન ૧૮°સે. થી ૪૦°સે.

૫ વામષિક વરસાદ ૭૦૯ મી.મી ૬ નજીક નો રોડ સ્ટેટ ાઈવે ૨૪ (૦.૧૭ હકમી) ESE

નેશનલ ાઈવે ૯૪૭(૮.૩ હકમી) N ૭ નજીક નુ ંરેલ્વ ેસ્ટેશન માળીર્ા રેલ્વ ેસ્ટેશન ૨૪.૨ હકમી NE

૮ નજીક નુ ંશ રે મોરબી (૨૭.૦૨ હકમી) SE

૯ નજીક નુ ંર્ગામ ખીરસરા (૦.૯૨ હકમી) ESE ૧૧ નજીક જમીન પરના પાણીના સ્ત્રોત ફુલ્કુ નહદ- ૧.૧૩ હકમી NE

ઝીંઝુડા નહદ- ૩.૬ હકમી SSW ૧૨ ભ કંપ ઝોન ઝોન ૫ (સૌથી વધારે જોખમી મવસ્તાર)

૧૩ રાષ્ટ્ટ્રીર્ ઉપવન- જરં્ગલી પ્રાણીઓ માટેનુ ંઅભ્ર્ારણ્ર્

વાવાનીર્ા હરઝવા ફોરેસ્ટ પ્રસ્તામવત એકમ થી આશરે ૪ હકલોમીટર દ ર આવેલ છે.

૦૨ પયાણવરિીય અસરો અને તેના શમન( મીટીગેશન) માટેના પગલા:-

૨.૧ વાનુ ંપર્ાાવરણ (AIR ENVIRONMENT)

બળતણના વપરાશથી મનકળતા પ્રદ ષણનો મખુ્ર્ સ્ત્રોત થમમિક ફ્લલ્યડુ હ ટર ( ૬ લાખ હકલો કેલરી/કલાક) ડી.જી. સેટ ( પાવર ફેલર્ર વખતે વાપરવામા ં આવશે. થમમિક ફ્લલ્યડુ હ ટર અને ડી.જી.સેટમા ં હડઝલ બળતણ તરીકે વાપરવામા ંઆવશે. ઉત્પાદન દરમ્ર્ાન પ્રદ ષકોનુ ંઉત્સર્જન થવાની શક્યતાઓ નથી પરંર્ ુ રો-મટીરીર્લ ને્ડલીંર્ગ અને ટ્રાન્સપોરટેશન તથા ઉત્પાદન પ્રહકર્ા દરમ્ર્ાન પ્રદ ષકો ઉત્સજીત થવાની શક્યતા છે.

પ્રવતામાન આસપાસની વાની (Ambient Air) ગણુવત્તા જાણવા માટે પ્રસ્તામવત એકમ સ્થળથી ૧૦ હકમી મત્રજ્ર્ાના વર્ુાળાકાર મવસ્તારમા ં૫ અલર્ગ અલર્ગ સ્થળેથી ઓક્ટોબર ૨૦૧૬ થી હડસેમ્બર ૨૦૧૬ દરમમર્ાન નમ ના લઈને તેની ચકાસણી કરવામા ં આવી તી. વાની ગણુવત્તા નક્કી કરવા માટેના સ્થળની પસદંર્ગી વાયશુાસ્ત્ર અને મસમપમસબી ના ધારાધોરણ મજુબ નજીકની પ્રાપ્ત સમુવધાઓના આધારે નક્કી કરેલી તા. વાની ગણુવત્તા નક્કી કરવા માટે પટીક્યલુેટ મેટર(PM10& PM2.5), સલ્ફર

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નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 33

ડાર્ોકસાઈડ (SO2), નાઈટ્રોજન ઓક્સાઈડ (NO2), CO અને VOC ની ચકાસણી કરવામા ંઆવી તી. જેના પહરણામો નીચેના ટેબલમા ંદશાાવ્ર્ા મજુબ છે.

બેઝલાઈન મોનીટરીંગ માટે ગામો ના નામ અને પકરિામો

સ્થળ અંતર (કકમી) અને કદશા

૯૮ પેસણનટાયેલ (µg/m3) PM2.5 PM10 SO2 NO2

પ્રો. સાઈટ - ૩૧.૮૦ ૭૯.૮૦ ૨૨.૫૨ ૨૮.૬૫

બોડકી ૩.૮ SSW ૩૧.૧૭ ૮૧.૪૭ ૨૨.૫૨ ૨૮.૮૩

વવાણીર્ા* ૬.૭ (NNE) ૩૧.૨૦ ૮૧.૩૯ ૨૨.૫૨ ૨૯.૩૩

વવાણીર્ા જરં્ગલ ૮.૬ (N) ૩૧.૧૪ ૮૨.૦૮ ૨૩.૭૨ ૨૯.૩૯

મેન્રવુ જરં્ગલ ૧૨.૪ (W) ૩૧.૦૩ ૭૯.૫૦ ૨૨.૨૨ ૨૮.૩૪

સ્વીકૃત મયાણદા [નેશનલ એમ્બીયટં એર ક્વોલીટી – ૨૦૦૯]

૬૦ ૧૦૦ ૮૦ ૮૦

નોધ: * ડાઉનવીન્ડ ડીરેક્શન બતાવે છે.

CO: - Not Detected, VOC: - Not Detected

એમ્બીર્ટં એરના પહરણામ પરથી તારણ કાઢી શકાર્ કે વાની ગણુવતા નેશનલ એમ્બીર્ટં એર ક્વોલીટીના ધારાધોરણ મજુબ છે.

વા પ્રદ ષણ મનર્તં્રકની જરૂર ર તેી નથી. ડી.જી. સેટના પ્રદ ષકો માટે ચીમની ની પર્ાાપ્ત ઉંચાઈ રાખવામા ંઆવશે. જ્ર્ારે કે જે પાવર ફેઈલર વખતે વપરાશે.

સ ચચત એકમ દ્વારા ઉત્સજીત પ્રદ ષકો ને મનર્તં્રણમા ંરાખવા માટે જરૂરી પર્ગલા લેવામા ંઆવશે જેવાકે, રો-મટીરીર્લ ની જગ્ર્ા અલર્ગ ફાળવવામા ંઆવશે, ઉત્પાદન પ્રહકર્ા બધં રીએક્ટરમા ંકરવામા ંઆવશે અને લીકેજ અ ટકાવવા તેનુ ંમનર્મીત ચેકીંર્ગ અને મેઈન્ટેનશશ કરવામા ંઆવશે.

૨.૨ જળ પર્ાાવરણ (Water Environment)

પ્રસ્તામવત એકમ દ્વારા ૧૬.૯ હકલોલીટર/ હદવસ જેટલુ ં પાણી ઘરર્ગથ્થ ુ વપરાશ, ગ્રીન બેલ્ટ ડેવલોપમેન્ટ, યટુીલીટી પ્રોસેસમા ંવપરાશે.પાણીની જરૂરીર્ાત ટેંકર દ્વારા સતંોષવામા ંઆવશે.

એકમ દ્વારા ૦.૧૫ હકલોલીટર/હદવસ સએુજ (ઘરર્ગથ્થ)ુ પાણી અને ૧.૯ હકલોલીટર ઓદ્યોર્ગીક ર્ગદું પાણી ઉદભવશે.

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નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 34

પાિીની જરૂકરયાત ક્રમ વપરાશની જગ્યા પાિીની જરૂકરયાત (કક.લી./ કદવસ) ૧ ઘરગથ્થ ુવપરાશ ૩.૨ ૨ ગ્રીન બેલ્ટ ડેવલપમેન્ટ ૭.૫

ઓદ્યોગીક વપરાશ ૬.૨ કુલીંર્ગ ટાવર ૬.૦ વોશીંર્ગ ૦.૨

પ્રોસેસ -- કુલ ઓદ્યોણગક વપરાશ ૬.૨ કુલ (ઘરગથ્થ ુ+ ઓદ્યોણગક+ગ્રીનબેલ્ટ ડેવલોપમેન્ટ) ૧૬.૯

ગદંા પાિીનો ઉદભવ અને વનકાલ

ક્રમ ગદંા પાિીના ઉદભવન ુસ્થાન ગદું પાિી

(કક.લી./ કદવસ) વનકાલ

૧ સએુજ (ઘરગથ્થ)ુ પાિી ૦.૧૫ સોક્પીટ દ્વારા સેપ્ટીંક ટાકંીમા ં

૩ ઓદ્યોણગક ગદું પાિી ૧.૯ ઈટીપી અને ત્ર્ારબાદ ઈવોપરેટરમા ં

કુલીંર્ગ ટાવર ૦.૩ વોશીંર્ગ ૦.૨

પ્રોસેસ ૧.૪ કુલ ઓદ્યોણગક ૧.૯ કુલ ( ઘરગથ્થ ુ+ ઓદ્યોણગક) ૨.૦૫

ઘરર્ગથ્થ ુર્ગદંા પાણીનો મનકાલ સેપ્ટીંક ટેંક/ સોક્પીટ સીસ્ટમ દ્વારા કરવામા ંઆવશે. ઓદ્યોચર્ગક ર્ગદંાપાણીને

મનચે મજુબ શધુ્ધ્ધકરણ અને મનકાલ કરવામા ંઆવશે.

૧.૯ હકલોલીટર /હદવસ ફ્લલોર વોશીંર્ગ વાળુ ર્ગદું પાણી, પ્રોસેસ વોટર અને કુલીંર્ગ ટાવર બ્લોડાઉન વાળા પાણીને ઈટીપીમા ંકલેકશન કમ ન્યટુ્રલાઈઝેશન ટેંકમા ંલાવવામા ંઆવશે અને

લાઈમ અને એલમ દ્વારા તેની pH મનર્તં્રીત કરવામા ંઆવશે. ત્ર્ારબાદ તેને નચ હફલ્ટરમાથંી પસાર કરવામા ંઆવશે અને સ્લજ અલર્ગ કરવામા ંઆવશે .આ સ્લજને ડ્રાર્ કરીને એક અલર્ગ જગ્ર્ામા ં સગં્ર કરવામા ં આવશે. ત્ર્ારબાદ હફલ્ટર થરે્લા પાણીને ોલ્ડીંર્ગ ટેંકમા ં રાખવામા ંઆવશે અને આ પાણીને ઈવોપરેટરમા ંબાષ્ટ્પીભવન કરવામા ંઆવશે જેથી એકમ ઝીરો હડસ્ચાર્જ ર શેે.

ભ ર્ગભા જળ તેમજ જમીન પરના પાણીના નમ નાઓના ગણુવત્તા પરીક્ષણ પરથી તારણ કાઢી શકાર્

કે ભ ર્ગભા જળ તમેજ જમીન પરનુ ંપાણી IS: 10500 ર્ગાઈડલાઈન મા ંબ ાર પાડવામા ંઆવલે

પીવાલાર્ક પાણીના ધારાધોરણ મજુબ ઘરર્ગથ્થ ુવપરાશ માટે ર્ોગ્ર્ છે.

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નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 35

૨.૩ ઘન અને જોખમી કચરાનુ ંવ્ર્વસ્થાપન

મખુ્ર્ ઝેાડાસ વેસ્ટમા ંઈટીપી કચરો તથા ઈવેપોરેશન રેસીડય ુ છે. બીજા મખુ્ર્ વેસ્ટમા ંવપરારે્લુ ંઓઈલ

અને નકામી થેલીઓ અને સ્પેન્ટ કેટાલીસ્ટ અને સ્પેન્ટ કાબાન નો સમાવેશ થાર્ છે.

ઈટીપી કચરાનો તથા ઈવેપોરેશન રેસીડય ુ નો મજુંર થરે્લ TSDF Site મા ં મનકાલ કરવામા ં આવશે.

વપરારે્લુ ંઓઈલ લ્યબુ્રીકેન્ટ તરીકે પનુઃ વપરાશે અથવા રીસાઈકલરને વેચાશે, નકામી થેલીઓ અને ડ્રમ

મજં ર થરે્લ વેન્ડર ને વેચાશે.

એકમ ઝેાડાસ વેસ્ટના સગં્ર માટે અલર્ગથી જગ્ર્ા ફાળવશે જેમા લીચેટથી થતા જમીનના પ્રદ ષણને

અટકાવવા માટે પક્કા ફ્લલોરીંર્ગ કરવામા આવશે, આ લીચેટને કલેક્ટ કરી તેના શધુ્ધ્ધકરણ માટે ઈટીપીમા ંમોકલવામા ંઆવશે.

૨.૪ જમીન પર્ાાવરણ

કામર્ગીરી તબક્કા દરમ્ર્ાન વા, પાણી, ઘનકચરાના પ્રદ ષણથી જમીન પર સીધી અથવા આડકતરી અસરો થાર્ છે.

વાના પ્રદ ષણને રોકવા માટે જરૂરી બધાજ પર્ગલા લેવામા ંઆવશે જેથી જમીન પર કોઈ જ આડઅસર થશે

નહ િં. ગ્રીન બેલ્ટમા ંમોટાભાર્ગની વનસ્પમત વા પ્રદ ષકો સ ન કરવામા ંસક્ષમ શે

વરસાદી પાણીને ટાકંીમા ં સગં્ર કરવામા ંઆવશે. અતે્ર નોંધનીર્ છે કે ર્ગદું પાણી જમીન પર છોડવામા ંઆવર્ુ ં નથી જેથી જમીન પર કોઈ આડઅસર થશે નહ િં. ખાળકુવાને પણ સમર્ાતંરે સાફ કરવામા ંઆવશે.જેથી પાણીના કારણે જમીન ઉપર કોઈપણ આડઅસર નહ િં થાર્.

ઘન કચરાને સભંાળવા, સગં્ર કરવા અને તેના મનકાલ માટેના દરેક મનર્તં્રીત પર્ગલાઓ લેવામા ંઆવશે જેથી ઘન કચરાને કારણે જમીન પર કોઈ આડઅસર થશે નહ િં.

૨.૫ ધ્વમન પર્ાાવરણ

પ્રસ્તામવત એકમમા ં ધ્વમનના મખુ્ર્ સ્ત્રોત ડી.જી. સેટ, પપં, થમમિક ફ્લલ્યડુ હ ટર, ઈવોપરેટર અને એકમમા ંઆવતા વા નો ર શેે.

અભ્ર્ામસત ક્ષેત્રમા ંપ્રવતામાન ધ્વમનનુ ંમાપદંડ કાઢવા માટે ૫ અલર્ગ- અલર્ગ સ્થળે ઘોંઘાટની ચકાસણી કરવામા ંઆવી તી. જેના પરીણામો નીચે પ્રમાણે છે.

ક્રમાકં સ્થળ કેટેગરી Leq (dB(A))

મયાણદા પકરિામ કદવસ રાત કદવસ રાત

૧ પ્રોજેક્ટ સાઈટ

ઓદ્યોચર્ગક ૭૫.૦ ૭૦.૦ ૬૯.૦ ૬૨.૪

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નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 36

ક્રમાકં સ્થળ કેટેગરી Leq (dB(A))

મયાણદા પકરિામ કદવસ રાત કદવસ રાત

વસા તી ૫૫.૦ ૪૫.૦ ૫૨.૩ ૪૩.૧

૩ બોડકી વસા તી ૫૫.૦ ૪૫.૦ ૪૭.૮ ૪૧.૦

૪ વવાણીર્ા વસા તી ૫૫.૦ ૪૫.૦ ૪૬.૬ ૩૯.૨

૫ વસા તી ૫૫.૦ ૪૫.૦ ૪૫.૨ ૩૭.૫

ધ્વમનના પહરણામો મનર્ત માત્રામા ંછે.

તેમ છતા ંધ્વમન પ્રદ ષણ અટકાવવા જેવા કે ડી.જી.સેટ સાથે એકોસ્ટીક એંક્લોઝર લર્ગાડવામા ંઆવશે. દરેક

મશીનરીમા ંમનર્મીર્ લ્યબુ્રીકેશન, ઓઈલીંર્ગ અને મરામત કરવામા ંઆવશે.

૨.૬ જૈવ પહરસ્સ્થતી અને જૈવ મવમવધતા શાસ્ત્ર

જૈવ પહરસ્સ્થતી અને જૈવ મવમવધતાના મલુ્ર્ાકંનની માહ તીનો અભ્ર્ાસ અભ્ર્ામસત ક્ષેત્રમા ંકરવામા ંઆવ્ર્ો છે

તેના આધાર પર ૧૫૪ વનસ્પતી, ૧૦ પ્રાણીસષૃ્ટ્ટી, ૫૮ પક્ષી અને ૧૨ સસ્તન પ્રાણીનો સમાવેશ થાર્ છે.

આ અભ્ર્ાસીત મવસ્તારમા ંકોઈ જોખમી વન્ર્જીવ કે વનસ્પતી જોવા મળેલ નથી.

અભ્ર્ામસત ક્ષેત્રમા ંખેતીલાર્ક વનસ્પમત પ્રજામતઓ જેવીકે પપૈય,ુ ચીકુ, ખજ રી, આંબો, જોવા મળેલ છે.

બાજરી, જુવાર વરે્ગરે અભ્ર્ામસત ક્ષેત્રના મખુ્ર્ ખેતીલાર્ક પાકો છે.

અભ્ર્ામસત ક્ષેત્રમા ં સ્થામનક વનસ્પમત પ્રજામતઓ જેવીકે બાવળ, લીમડો, હ િંર્ગોળ, ગલુમ ોર, કરંજ, વડ,

ર્ગોરસ આંબલી, ખીજડો, જોવા મળેલ છે.

અભ્ર્ામસત ક્ષેત્રમા ંસામાન્ર્ રીતે દેખાતા પક્ષીઓમા ંઘળુીર્ો તેતર, મોર, નકટો, ઘટંી ટાકંણો, કબ તર, ોલો, ર્ગજ્પાવં, કાર્ગડો જોવા મળે છે. અભ્ર્ામસત મવસ્તારમા ંપાલર્ુ ંપ્રાણીઓ ઉપરાતં જે જરં્ગલી સસ્તન પ્રાણીઓ

જોવા મળેલ તા તેમા ં મનલર્ગાર્, મશર્ાળ, નોળીર્ો, જરં્ગલી સવુર, જરં્ગલી ચબલાડી, ચચિંકારા નો સમાવેશ

થાર્ છે.

૨.૭ જોખમની આકારણી

જોખમી રસાર્ણો રાખવા માટે કરવામા ંઆવતી જોખમ આકરણીમા ંપરીબળો જેવાકે, જોખમનો સ્ત્રોત, જોખમ

થવાની મ ત્તમ સભંાવના અને જોખમ નાથવા માટેના પર્ગલા ં આવરી લેવાર્ા છે. બધા જ જોખમી રસાર્ણોનો સગં્ર ણ અને મનર્તં્રણ MSDS ની માર્ગાદમશિકા ઠેળ કરવામા ંઆવશે.

૨.૮ વ્ર્વસાર્ આરોગ્ર્ અને સલામતી

જોખમ આકારણી નો અભ્ર્ાસ દ્વારા એકમમા ંકામ કરતા લોકો માટે નીચે મજુબના સરુક્ષાત્મક પર્ગલા ંલેવામા ંઆવશે.

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નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 37

વ્ર્સ્ક્તર્ગત રક્ષાત્મક સાધનો (પસાનલ પ્રોટેક્ટીવ ઈક્વીપમેન્ટ) જેવાકે ઈઅર પ્લર્ગ જ્ર્ા ંધ્વની પ્રદ ષણ ૮૦

dB(A) થી વધ ુ ોર્, કારીર્ગરો માટે મનર્મીત સ્વાસ્થ્ર્ ચેક-અપ, પાર્ાની જરૂરીર્ાતો જેમકે પીવાનુ ંપાણી, શૌચાલર્, પ્રાથમમક સારવાર આપવામા ં આવશે. પસાનલ પ્રોટેક્ટીવ ઈક્વીપમેન્ટનો ઉપર્ોર્ગ ઈટીપી ,

જોખમી કચરાના મનકાલ તથા કેમીકલ ેંડ્લીંર્ગમા ંકરાવવામા ંઆવશે.

૨.૯ ગ્રીન બેલ્ટ ડેવલપમેન્ટ

આશરે કુલ ૪૨૭૦ ચો.મી.(૩૨.૯૭ %) જેટલો ગ્રીન બેલ્ટ મવસ્તાર પ્રોજેક્ટ સાઈટની અંદર ડેવલોપ કરવામા ં આવશે. આ ગ્રીન બેલ્ટમા ં અભ્ર્ાસીત ક્ષેત્ર મા ં મળી આવતી સ્થામનક વનસ્પમત પ્રજાતીઓ ઉર્ગાડવામા ંઆવશે કે જે વા પ્રદ ષણ પ્રત્રે્ સહ ષ્ટ્ણ ુ શે અને ધ્વમન પ્રદ ષણ ને શોષી શકશે. ગ્રીન બેલ્ટ જૈવ પહરસ્સ્થતને લર્ગતી સમસ્ર્ાનુ ંશમન કરવાની સાથે એકમની સુદંરતામા ંવધારો કરશે તથા પક્ષીઓ, નાના સસ્તનપ્રાણી, જરં્ઓુ વરે્ગરેને આકષીત કરીને જૈવ પહરસ્સ્થતીનુ ંસરં્લુન જાળવવામાપંણ મદદરૂપ થશે.

૩. પર્ાાવરણીર્ વ્ર્વસ્થાપન ર્ોજના

પર્ાાવરણ પર થતી આડઅસરોને રોકવા/નાથવા માટે પર્ાાવરણીર્ વ્ર્વસ્થાપન ર્ોજના બનાવવામા ંઆવેલ છે. આ ર્ોજના ઉદેશ્ર્ જવાબદારી, સાધન સપંમત અને પથૃ્થકરણ દરમ્ર્ાન જોરે્લી અસરના શમન સાથે સકંળારે્લ પર્ગલાઓનુ ંવણાન કરે છે આ પર્ાાવરણીર્ વ્ર્વસ્થાપન ર્ોજનામા ંજરૂરી મવર્ગતો જેવીકે ગ્રીન બેલ્ટ ડેવલપમેન્ટ, વરસાદી પાણીનો સગં્ર , સી.એસ.આર એક્ટીમવટી, વરે્ગરેનો સમાવેશ થાર્ છે.

૪. પર્ાાવરણીર્ ચકાસણી ર્ોજના

પર્ાાવરણીર્ ચકાસણી ર્ોજનાને શમનના પર્ગલાનંી કાર્ાદક્ષતા અને એકમના મવકાસના મવમવધ તબક્કાઓમા ંપર્ાાવરણમા ંઆવતા બદલાવને જાણવા માટે તૈર્ાર કરવામા ંઆવેલ છે.

૫. પ્રોજેક્ટ થી થતા લાભો

અભ્ર્ામસત ક્ષેત્રનુ ં સામાજીક અને આમથિક માળખુ ં જાણવા માટે વસ્તી મવષર્ક અને બીજી સબંમધત સામાજીક-આમથિક માહ તી જીલ્લા વસ્સ્ત ર્ગણતરી પસુ્સ્તકામાથંી લેવામા ંઆવી તી.

પ્રસ્તામવત એકમ માટે કુલ ૩૦ જેટલા કુશળ અને ચબન કુશળ કારીર્ગરોની જરૂર પડશે. પરોક્ષ રીતે પહરવ ન, દુકાનો અને બીજી છુટક રોજર્ગારી ઉભી થશે.

એકમમા ં સ્થામનક લોકોને રોજર્ગારી માટે પ્રાથમમકતા આપવામા ંઆવશે. વેપારની તકોમા ંથતો વધારો સ્થામનક લોકોનુ ંઆમથિક સ્તર ઉંચ ુલાવશે જે એક કારાત્મક અસર છે. એકમ કુલ નફાના ૨૫ % જેટલી રકમનો ઉપર્ોર્ગ સામાજીક તેમજ આમથિક મવકાસ માટે કરશે.

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નવો સીન્થેટીક ઓર્ગેનીક કેમીકલ ઉત્પાદન એકમનો પર્ાાવરણીર્

પથૃ્થકરણ અસર અભ્ર્ાસ

રોમન પેટ્રોકેમમકલ

સવે ન-ં ૯૨૨/પી૨, ર્ગામ:- મોટા દહ િંસરા, તાલકુો:- માળીર્ા, જીલ્લો:- મોરબી, ગજુરાત રાજ્ર્.

ટી.આર.એસોમસએટ્સ અમદાવાદ, ગજુરાત.

સકં્ષીપ્ત અ વેાલ-ગજુરાતી 38

૬. ઉપસ ંાર

વાની ગણુવત્તા પર નજીવી અસર થાર્ છે .જો કે વા પ્રદ ષણ મનર્તં્રણ માટેના તમામ પર્ગલા લેવામા ંઆવશે .

કોઈ ઈકોલોજીકલ નકુશાન થશે નહ .

જળ પર્ાાવરણ પર કોઈ પ્રમતક ળ અસર થશે નહ .

સ્થામનક રોજર્ગારીની તકો વધશે .

મવમવધ પર્ાાવરણીર્ પહરમાણો જેવા કે જરં્ગલ, રાષ્ટ્ટ્રીર્ બર્ગીચા, અભ્ર્ારણ્ર્ અને ધામીક તથા ઐતી ામસક સ્થળો પર કોઈ અસર થશે નહ .

પર્ાાવરણીર્ મેનેજમેન્ટ ર્ોજના બધા પ્રદ ષણ પહરમાણોને મનર્મંત્રત કરવા માટે ઘડવામા ંઆવી છે .

અને આ પહરણામો સબંમધત સત્તામધકારો દ્વારા સ્થપારે્લ ધોરણ કરતા વધી ના જાર્ એ માટે

પર્ાાવરણ મેનેજમેન્ટ એકમ દ્વારા ખાતરી કરવામા ંઆવે છે .

પર્ાાવરણ મેનેજમેન્ટ સેલ સ ચચત પ્રોજેકટની શરૂઆત પછી પ્રદ ષણ મનર્તં્રણના ંપર્ગલા ંલેશે.

આથી અનમુાન કરી શકાર્ કે બાધંકામ અને કામર્ગીરી તબક્કા દરમમર્ાન મ કવામા ં આવેલ

પર્ાાવરણીર્ સચંાલન ર્ોજના અને શમનના પર્ગલાનંા કારાત્મક અમલીકરણ થી પર્ાાવરણ પર થતી અસરોને ઘટાડી શકાશે.

Page 39: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-1: INTRODUCTION 39

1 INTRODUCTION

1.1 Preamble

Roman Petrochemical is proposing to manufacture Resin at Survey No. 922/P2, Village:

Mota Dahisara, Navlakhi Highway, Taluka: Maliya, District: Morbi, Gujarat for sell purpose.

Production details are given below:

Table 1-1: Details of Product

Sr. No. Name of Product Capacity (MT/Month)

1. Unsaturated Polyester Resin 500

1.2 Purpose of the EIA Report

Production of resin falls under clause No.5 (f) of category “B1” as stated in Environment

Impact Assessment Notification published on 14th September 2006 and hence the project

proponent has to obtain the Environmental Clearance from SEIAA, Gujarat. As a part of this

procedure, Public Hearing is required to be carried out as per the notification dated 25th June

2014. Hence, project proponent has to obtain the Environmental Clearance from the State

Environment Impact Assessment Authority, Gujarat. As per requirements of the

notification, an application was submitted on 16th December 2015 along with Form-1, pre-

feasibility report and draft Terms of Reference (ToR). The proposal was considered by SEIAA

on 24th February 2016. Subsequently the Committee has issued the ToR wide letter No.

SEIAA/GUJ/TOR/5(f)/270/2017 dated 24th April 2017. Based on the ToR points issued by

SEIAA, a Draft Environmental Impact Assessment (EIA) report has been prepared covering all

aspects of the ToR.

The purpose of the preparation of Environment Impact Assessment (EIA) report is not only to

obtain Environment Clearance from SEIAA, but also to understand the likely impacts and to

take Environment Protection measures during and after commissioning of the project.

1.3 Promoters and their Back Ground

S.

No. Name of Partner Residential Address Age Experience

1 Rohit Govindbhai

kavar

Kubernagar 3, bhagvati park,

vavdi road, morbi-363641.

26 4 year ceramic

industry experience.

2 Govindbhai veljibhai

Kavar

Kubernagar 3, bhagvati park,

vavdi road, morbi-363641.

52 12 year ceramic

industry Experience.

3 Harkhjibhai veljibhai

Kavar

Kubernagar 3, bhagvati park,

vavdi road, morbi-363641.

48 9 year cotton and

ceramic industrial

Experience.

4 Rakesh Anilbhai

Adroja

Akshar residensy, Avadh

apartment, opp om party plot,

26 5 year ceramic

industry experience.

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-1: INTRODUCTION 40

S.

No. Name of Partner Residential Address Age Experience

Ravapar road. Morbi.

5 Lalitaben Anilbhai

Adroja

Akshar residensy, Avadh

apartment, opp om party plot,

Ravapar road. Morbi.

48 --

6 Rahul anantray

bavarva

At barvala. District morbi. 25 2 year plywood

industry experience.

7 Hardik samjibhai

Thoriya

At Bagathra, Taluka & District :

morbi.

27 3 year Computer

hardware experience.

8 Ravikumar

Rameshbhai

Vasdadiya

At Bagathra, Taluka & District :

morbi

25 2 year job experience

in chemical industry.

1.4 Need of the Project and its Importance to the Country

This is a small scale new proposed unit having approximately cost of Rs. 3 crore for Resin

plant. Proposed unit will manufacture unsaturated polyester resin (total production of 500

MT/Month) which will be utilized for sell purposes.

Unsaturated Polyester Resins are used predominantly in making trays, shower stalls, boats,

swimming pool, water tanks, etc. it is an individual Industry having no direct dependency on

others.

In India, good quality raw materials are available at cheap rates, enabling the manufacturing

at low cost. This increases the profit margin as compared to other players in the world. To

meet the current and future market demand, the project proponent intends to start a new

unit. Looking to the market demand, the proposed project is feasible at stated location.

Indian market is open and big that is why every kind of import is booming. Indian industrialist

must understand the fact that it’s no more a regional shift, it is a global shift. Indian

technology should be upgraded an updated at par with international standards.

The working environment in India has changed tremendously. Earlier the trade fairs were

hardly participated by foreign chemical manufacturing companies where as now it is flooded

with global suppliers.

There is good possibility for export. But currently we are focused on local sell market for

distribution.

The proposed project will contribute revenue to the Central & State exchequer. Indirect

contribution to the Central & State exchequer. Thus, the proposed project will help the

Government by paying different taxes from time to time, which is a part of revenue and thus,

will help in developing the area. Demand of the products in foreign market is also significant,

which will boost the export potential of the company as well as country. Export oriented units

plays vital role in development of economy as well as local physical infrastructure for further

boosting of industrial development with sustainable approach as the industries need to

maintain good environment & safety condition to get better foreign market.

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-1: INTRODUCTION 41

1.5 Location of the Proposed Project and Siting Criteria

Figure 1-1: Latitude Longitude of All Corners of Project Site

The project site is in proximity of Morbi District of Gujarat State and Project proponent is very

well familiar with the surrounding environment & resin production; therefore, it becomes easy

for the unit to set up the project on the above said location. The proposed unit, apart from

generating direct and indirect employment and various business opportunities, it will bring

overall up-liftmen of the area and will ultimately result in complete socio-economic and

infrastructure development. The other features are briefly summarized hereunder:

Availability of all basic facilities like infrastructure, communication, transportation,

medical facilities, fuel, water, power, unskilled & skilled manpower, raw materials,

road network etc. Proximity of market.

No R & R will be required;

No national park or wildlife Habitats falls within 5 km radial distance from project site.

The siting criteria as per the guidelines are given in the following table;

Table 1-2: General Siting Criteria

Details Requirement Compliance

Forest No forest land shall be converted

into non-forest activity for the

sustenance of the industry.

No forest land is involved in the

proposed project site

Agricultural land No prime agricultural land shall

be converted into industrial site.

NA permission is obtained for this

project. NA permission is attached

as Annexure 5.

Layout Enough space should be provided

for storage area, plant area,

greenbelt area, Utilities, Raw

material storage, Fly ash, other

storage like solid wastes so that

these could be available for

possible reuse.

The total acquired land is 12,950

m2. Enough space will be

provided according to the

requirement. This can be verified

from the Lay-out given in the

Figure 2-6.

Major settlements

(3,00,000 population):

At the time of siting of the

industry, if the notified limit of

any major settlement is found to

Nearest major habitation is Morbi

city which is about 27.2 km far

from the project site in SE

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-1: INTRODUCTION 42

Details Requirement Compliance

be within 50 km from the project

boundary, the spatial direction of

growth of the settlement for at

least a decade must be assessed.

direction.

Ecologically and/or

otherwise Sensitive areas

Preferably 5 km depending on

the geo-climatic conditions the

requisite distance may be

decided appropriately by the

Environmental agency.

High water line is 5.03 Km from

the project site: source: survey of

India topomap no.: F42K9.

Transport /

Communication system

Preferably ½ km. away from

highway and railway line.

Nearest National Highway 947

is at 8.3 km distance in ESE

direction.

Nearest State Highway 24 is at

0.17 km distance in N

direction.

Nearest railway line is between

Wakaner & Navlakhi which is

0.42 km N from the project

site.

Coastal areas Preferably ½ km away from high

tide line (HTL)

High water line is 5.03 Km

from the project site: source:

survey of India topomap no.:

F42K9.

Flood plain of the river

line system

Preferably ½ km away from flood

plain or modified flood plain

affected by dam in upstream or

flood control system.

Phulku Nadi is approx. 1.13 km

from the project site in NE

direction.

Jhinjhoda River is approx. 3.6

km from the project site in

SSW direction.

1.6 Scope of EIA Study

The EIA study includes determination of baseline conditions, assessment of the Impacts on

the environment due to the construction and operation of the project and making

recommendations on the preventive measures to be taken, to minimize the impact on the

environment to acceptable levels. The scope of the study broadly includes:

Field sampling of environmental attributes at various representative locations in the

study area to establish the baseline status.

Collect & compile secondary data.

Identification, assessment and evaluation of the beneficial and adverse impacts on

surrounding environment due to proposed project activities considering the existing

baseline status and secondary data, by using scientifically developed and widely

accepted models.

Identification and assessment of risks associated with the proposed project and their

appropriate management through proper Risk Assessment (RA) and Disaster

Management Plan (DMP).

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-1: INTRODUCTION 43

Prepare an Environmental Management Plan (EMP) to mitigate the predicted impacts.

Identify critical environmental attributes required to be monitored during the project

execution and to suggest post project monitoring.

As per the guidelines, the Generic structure of EIA is given in EIA notification dated 14th

September, 2006 is maintained. The scope of study based on MoEF&CC / CPCB guidelines is

tabulated below;

Table 1-3: Scope of the Study

Environmental

Attributes

No. of

Locations Observations

Meteorology 1 One season site specific meteorological status of the study

was carried out for prediction of ground level

concentration in downwind direction.

Ambient Air

Quality

5 The prevailing ambient air quality status was established

through a network of stations monitored during the period

of October to December 2016. The ambient air quality

monitoring as per the parameters prescribed in ToR was

carried out within the study area of 10 km. Prediction of

impacts on air quality due to proposed operations were

carried out through application of air quality models.

Water 7 (5 Ground

water and 2

Surface

water)

The water quality data with respect to Physico-chemical,

biological parameters and heavy metals were analyzed to

established baseline water quality of study area of 10 km.

The wastewater generation, its characterization and

management were carried out which was used in

assessing the impact of the project on water environment.

Noise 5 Noise level measurements were carried out around the

project site, data were also analyzed for establishing

baseline status of noise and it was used in assessing the

impact of the project on noise & vibration environment.

Soil 5 Soil samples were collected and have been analyzed to

understand nutrient status as well as assessing the impact

of the project on soil environment.

Ecology --

Flora and fauna species was listed based on the available

secondary information. Study of flora and fauna was

carried out within 5 km radius around the proposed

project.

Geology & Geo-

hydrology

-- Geological and geo-hydrological investigation work has

been carried out in and around the study area to know the

status of the study area.

Risk and Hazard

Analysis

-- Risk Assessment study has been carried out to evaluate

risk, assess its impact associated to the proposed project

activity and plan the appropriate action to control risk by

the most economical means.

Socio-economic

data

- Existing baseline status of the socio-economic profile of

the study area with reference to demographic structure,

provision of basic amenities, health status incorporating

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-1: INTRODUCTION 44

Environmental

Attributes

No. of

Locations Observations

economic pattern in the nearby rural areas (10 km radius)

were undertaken, it was used in assessing the impact of

the project on socio-economic environment.

1.7 Regulatory Frame Work

The proposed project is of resin manufacturing unit; hence the regulatory framework related

with the hazardous or toxic chemicals as well as regulatory provision of risk, emergency &

safety management are applicable to the proposed project. The regulatory provision related

with hazardous material handling, manufacturing, storage & transportation are also applicable

to the proposed project. The unit will have potential of pollution and also attracts the

provisions of EIA notifications 2006- SO 1533 (as amended). Thus, the proposed project may

be required to comply with many regulatory provisions.

The proponent shall follow the regulatory frame work as listed below and additional

applicable provision shall also be referred timely as cited as mandatory provision for proposed

project. In any case, proponent shall comply with the regulatory provision as directed through

particular regulatory provision. The major regulatory provisions applicable to the proposed

project are tabulated as under.

S.

No.

Legal Instrument (Type, Ref., Year) Concern Authority or Bodies

1 Air (Prevention and Control of Pollution)

Act, 1981 and its subsequent

amendments

CPCB and SPCB/UTPCC

2 Water (Prevention and Control of

Pollution) Act, 1974 and its subsequent

amendments

CPCB and SPCB/UTPCC

3 Water (Prevention and Control of

Pollution) Rules, 1975 and its subsequent

amendments

CPCB and SPCB/UTPCC

4 The Environment (Protection) Act, 1986

and their subsequent amendments

Ministry of Environment and Forests, &

Climate Change (MoEF&CC), CPCB and

SPCB/UTPCC.

5 Hazardous and Other Wastes

(Management and Transboundary

Movement) Rules, 2016

MoEF&CC, CPCB, SPCB/UTPCC, DGFT, Port

Authority and Customs Authority

6 Manufacture Storage and Import of

Hazardous Chemicals Rules, 1989

amended 2000

MoEF&CC, Chief Controller of Imports and

Exports, CPCB, SPCB/UTPCC, Chief Inspector

of Factories, Chief Inspector of Dock Safety,

Chief Inspector of Mines, AERB, Chief

Controller of Explosives, District Collector or

District Emergency Authority, CEES under

DRDO

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-1: INTRODUCTION 45

S.

No.

Legal Instrument (Type, Ref., Year) Concern Authority or Bodies

7 Chemical Accidents (Emergency

Planning, Preparedness and Response)

Rules, 1996

CCG, SCG, DCG, LCG and MAH Units

8 EIA Notification, 2006 and its subsequent

amendments

MoEF&CC, SPCB/UTPCC

9 Public Liability Insurance Act, 1991

amended 1992 & Public Liability

Insurance Rules, 1991 and its

subsequent amendments

MoEF&CC, District Collector

10 The Factories Act, 1948 Ministry of Labour, DGFASLI and Directorate

of Industrial Safety and Health/Factories

Inspectorate

11 The Explosive Act ,1884 Ministry of Commerce and Industry

(Department of Explosives)

12 Chemical Accident (Emergency Planning,

Preparedness and Response) Rules, 1996

Ministry of Environment & Forests & Climate

Change, Chief Controller of Imports and

Exports, CPCB, SPCB/UTPCC, Chief Inspector

of Factories, Chief Inspector of Dock Safety,

Chief Inspector of Mines, AERB, Chief

Controller of Explosives, District Collector or

District Emergency Authority, CEES under

DRDO.

13 Noise Pollution (Regulation and Control)

Rules, 2000 and its amendments

CPCB and SPCB/UTPCC

M/s. T. R. Associates (NABET Accredited EIA Consultant) was appointed by Roman

Petrochemical to carry out the Environmental Impact Assessment study for their proposed

project of manufacturing of Resin.

Page 46: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 46

2 PROJECT DESCRIPTION

2.1 Introduction

Roman Petrochemical is to be located at Survey No. 922/P2, Mota Dahisara Village in

Maliya Taluka of Morbi District in state of Gujarat for manufacturing of various resins for sell

purpose. Proposed production of resin will be to the tune of 500 MT/Month. The proposed

project is a green field project where unit proposes to manufacture products covered under

Category 5(f) ‘B1’ as per new EIA Notification of Ministry of Environment & Forest and

Climate Change (MoEF&CC) dated 14/09/2006 and subsequate amendments.

2.2 Project Location

The proposed site is located at Survey No.922/P2, Village: Mota Dahisara, Navlakhi highway,

Taluka: Maliya, District: Morbi, Gujarat. GPS coordinates of the site is situated at Latitude:

22° 57' 2.67" N and Longitude: 70° 35' 9.15" E. Nearest major city is Morbi which is about

27.2 km far from the project site in SE direction. National Highway 947 is about 8.3 km

distance in ESE direction. State Highway 24 is about 0.17 km distance in N direction.

The index map is given in Figure 2-1. Topo map showing surrounding area in 10 km radius

from project site is given as Figure 2-2.

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 47

Figure 2-1: Index Map

Page 48: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 48

Figure 2-2: TOPO Map showing Proposed Project Site

Page 49: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 49

2.3 Justification of Site Selection and Salient Features of Site

The unit is to be located at Mota Dahisara Village in Maliya Taluka.

Site selection was guided by many factors like infrastructure, availability of land, water

sources, fuel, transportation, power availability etc. Specific site selection criteria for the

proposed project are given below;

The project site is highly developed with all basic infrastructure facilities such as

proximity to man power, electricity, water supply, transportation, telecommunication systems etc.

Proposed project site is only 8.3 km away from National Highway no 947 which is

well connected to Maliya, Morbi and rest of India.

The project site is intended for the industrial purpose and thus no displacement of

population will take place.

There is no protected area notified under the Wild Life (Protection) Act (1972) & Eco-

sensitive area notified under Section 3 of the Environment (Protection) Act- 1986

exists within 5 km radius areas from the project site.

Availability of trained and skilled manpower nearby area.

Photograph 2-1: Project site

Page 50: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 50

Salient features in the surroundings area of the proposed site as well as infrastructure

availability with approximate aerial distance and direction are as given below:

Table 2-1: Salient Features of the Proposed Project Site

Sr.

No. Important Features Description

1. Location Survey No. 922/P2, Village: Mota Dahisara, Taluka:

Maliya, District: Morbi, Gujarat.

2. GPS Coordinates 22°57'2.67"N

70° 35'9.15"E

3. Mean Sea Level 8 m

4. Nearest power station PGVCL (Paschim Gujarat Vij Company Ltd.)

5. Temperature range 180 C to 400 C

6. Annual Rain fall 509 mm

7. Nearest Road NH 947 @ 8.3 km, ESE

SH 24 @ 0.17 km, N

8. Nearest Railway station Maliya @ 24.2 km NE

9. Nearest city Morbi @ 27.2 km, SE

10. Nearest village Khirasara @ 0.92 km, ESE

11. National Highway NH 947 @ 8.3 km, ESE

12. Nearest River/water body Phulku Nadi @ 1.13 km, NE

Jhinjhoda River @ 3.6 km, SSW

13. Seismic Zone Zone-V (Highest risk zone)

14. National Parks / Sanctuary None within 10 km radius.

Satellite image of 5 km and 10 km Radius from Project site showing nearest residential area,

Water Body, national highway, state highway, railway line is given as Figure 2-3 & Figure

2-4 respectively.

There is no national park and sanctuary in 10 km radius study area; Figure 2-5 is Google

image showing Distance of Wild Ass Sanctuary from the Proposed Project Site.

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ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 51

Figure 2-3: 5 km Radius Study Area of Project Site

Page 52: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 52

Figure 2-4: 10 km Radius Study Area of Project Site

Page 53: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 53

Figure 2-5 Goggle Image Showing Distance of Wildlife Sanctuary from Project Site

Page 54: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 54

2.4 List of Major Industries within 10 km study area

There is no industry in 10km study area.

2.5 Proposed Project Land & Plant Lay-Out

Proposed project land has already converted in non-agriculture. Land possession document

and non-agricultural (NA) land certificate is enclosed as Annexure 5. Total available land

area of premises is 12,950 m2, out of which 4270 m2 (32.97%) area will be developed for

greenbelt. Plant Lay-out is shown in Figure 2-6.

Table 2-2: Area Break-up of Proposed Project Site

Sr. No. Particular Area (m2) % of Total Land

1 Built-up area 2,497 19.28 2 Greenbelt area 4,270 32.97 3 Open area 6,183 47.75

Total 12,950 100

Page 55: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 55

Figure 2-6: Plant Lay-out

Page 56: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 56

2.6 Capital Cost of the Proposed Project

Proposed Resin unit is a Small Scale Unit having total investment of about Rs. 300 lacs. The

break-up of the capital cost is given in Table 2-3.

Table 2-3: Break-up of Capital Cost for Proposed Project

Sr.

No. Particular Cost (INR in Lac)

1 Land & site development 8.5

2 Building 116

3 Plant & Machineries 115

4 Environment Protection Measures 60

5 Miscellaneous 0.5

Total 300

Page 57: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 57

2.7 Magnitude of Project

Looking to the market demand, unit proposes to manufacture resin. Manufacturing resin does require obtaining Environmental Clearance. It will be used for

sell purposes. Product will be sold in domestic market. Details of proposed products are given below in Table 2-4.

Table 2-4: Details of Products for Proposed Project

S.

No. Name of Product

Capacity

per

(MT/Month)

Capacity

per

(MT/d)

Physical

Form

Mode of

Storage

No. of

Units

Capacity

of

storage

(MT)

Total

Storage

Capacity

(MT)

Storage

Inventory

(d)

Transportation

1. Unsaturated Polyester

Resin 500 20

Semi

solid

40 KL MS/SS

Tank 3 45 135 7 Road

Page 58: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 58

2.8 Manufacturing Process

Manufacturing process including chemical reaction, mass balance and process flow diagram is

described here below;

2.8.1 Unsaturated Polyester Resin

A. Using Poly Ethylene Terephthalate as main raw material

1. Process

A mixture of 1 mole Poly Ethylene Terephthalate (PET), 1.5 moles Glycol (Di/ Mono

Ethylene Glycol or Propylene Glycol) is fed to a reactor equipped with stirrer,

thermometer, Nitrogen gas introducing tube and with condenser.

The mixture is mechanically stirred and heated to 150 oC to 170 oC under nitrogen

gas stream. When reaction mass become a clear, it is allowed to cool at room temperature and then add 0.6 mole Maleic Anhydride (MA) and continuous heated up

to 200 oC – 210 oC until an acid number reaches below 10.

During esterification reaction water formed as a part of reaction, which is

continuously removed from the reaction mass as it inhibit the reaction rate.

Then the produced unsaturated polyester resin is cooled to 160 oC. Then add 50 mg

of Hydroquinone as inhibitor. When resin temperature dropped below the boiling point of reactive diluent (i.e. Styrene), the polyester resins were mixed with Styrene

by 35 weight plastic resin. This mixture is ready for packing.

A mixture of 1 mole Poly Ethylene Terephthalate (PET), 1.5 moles Glycol (Di/ Mono

Ethylene Glycol or Propylene Glycol) is fed to a reactor equipped with stirrer, thermometer, Nitrogen gas introducing tube and with condenser.

The mixture is mechanically stirred and heated to 150 oC to 170 oC under nitrogen

gas stream. When reaction mass become a clear, it is allowed to cool at room temperature and then add 0.6 mole Maleic Anhydride (MA) and continuous heated up

to 200 oC – 210 oC until an acid number reaches below 10.

During esterification reaction water formed as a part of reaction, which is

continuously removed from the reaction mass as it inhibit the reaction rate.

Then the produced unsaturated polyester resin is cooled to 160 oC. Then add 50 mg

of Hydroquinone as inhibitor. When resin temperature dropped below the boiling

point of reactive diluent (i.e. Styrene), the polyester resins were mixed with Styrene by 35 weight plastic resin. This mixture is ready for packing.

Page 59: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 59

2. Chemical Reaction

3. Mass Balance

Raw Material Input (kg) Product Output (kg)

Poly Ethylene Terephthalate 4468 Unsaturated Polyester

Resin 10236

Mono Ethylene Glycol 2164 Aqueous 417

Maleic Anhydride 1368

Styrene 2653

Total 10653 Total 10653

or Raw Material Input (kg) Product Output (kg)

Poly Ethylene Terephthalate 4210 Unsaturated Polyester

Resin 10268

Di Ethylene Glycol 2500 Aqueous 393

Maleic Anhydride 1289

Styrene 2662

Total 10661 Total 10661

or

Raw Material Input (kg) Product Output (kg)

Poly Ethylene Terephthalate 3748 Unsaturated Polyester

Resin 10327

Propylene Glycol 3104 Aqueous 350

Maleic Anhydride 1148

Styrene 2677

Total 10677 Total 10677

Page 60: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 60

4. Process Diagram

B. Using Phthalic Anhydride/Iso phthalic acid as main raw material

1. Manufacturing Process

A mixture of 2 mole Mono ethylene Glycol (MEG), 1.0 mole Phthalic Anhydride (PA)

will be fed to a reactor equipped with stirrer, thermometer, nitrogen gas indtroducing

tube and water condenser.

The mixture will be mechanically stirred and heated to 150 oC under nitrogen gas

stream. When reactor mass become clear, it will be allowed to cool below 60 oC or

room temperature and then 0.9 mole Maleic Anhydride (MA) will be fed and continuously heated to 200 oC – 210 oC until an acid number reaches below 10.

During esterification reaction, water formed as a part of reaction and is continuously

removed from the reaction mass as it inhibits the reaction rate.

Then the produced unsaturated polyester resin is cooled to 160 oC. Then add 150 mg

of Hydroquinone as inhibitor. When resin temperature dropped below the boiling point of reactive diluent (i.e. Styrene), the polyester resins were mixed with Styrene

by 30 to 35 weight percent of resin. This mixture is ready for packing.

Poly Ethylene Tere-phthalate Monoethylene or

Di Ethylene or Propylene Glycol

Reaction Vessel

Stirring and heating up to 150 C

When mixture become clear Cool up to room temperature

Reaction Mass

Stirring and heating up to 200 C – 210 C until Acid number

reaches below 10

Unsaturated Polyester Resin cooled to 160 C

Maleic Anhydride

Aqueous water

Viscous Unsaturated Polyester Resin

Aqueous water Viscous Unsaturated

Polyester Resin

Product: UnsaturaMaleic AnhyUnsaturated Polyester

Resin cooled to 160 C dride

in

Page 61: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 61

2. Chemical Reaction

Or

3. Mass Balance

Raw Material Input (kg) Product Output (kg)

Phthalic Anhydride 3287

Unsaturated Polyester

Resin 10716

Mono Ethylene Glycol 2754 Aqueous 760

Maleic Anhydride 1960

Styrene (as diluent solvent) 3476

Total 11476 Total 11476

Page 62: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 62

or

Raw Material Input (kg) Product Output (kg)

Iso Phthalic Acid 3269

Unsaturated Polyester

Resin 10843

Propylene Glycol 2993 Aqueous 673

Maleic Anhydride 1738

Styrene (as diluent solvent) 3516

Total 11516 Total 11516

4. Process Diagram

Product: Unsaturated Polyester

Resin

Phthalic Anhdride Monoethylene Glycol or

Iso Phthalic acid Propylene Glycol Reaction Vessel

Stirring and heating up to 150 C

Reaction Mass

Stirring and heating up to 200 C –210 C until Acid number

reaches 16

Unsaturated Polyester Resin cooled to 160 C

Maleic Anhydride

Aqueous water

Viscous Unsaturated Polyester Resin

Styrene as solvent by 35 % of resin for dilution

When mixture become clear cool up to 60 C

Page 63: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 63

2.9 Water consumption and consumption of each raw material per MT of each

product.

Table 2-5: Consumption of each raw material per MT of each product

Sr. No. Name of The Raw Material Quantity MT/MT of product

(If we use Polyethylene Terephthalate as main raw material)

1 Polyethylene Terephthalate 0.436

2 Mono Ethylene Glycol 0.211

3 Maleic Ahydride 0.134

4 Styrene(for resin dilution) 0.259

OR

1 Polyethylene Terephthalate 0.410

2 Di Ethylene Glycol 0.243

3 Maleic Anhydride 0.126

4 Styrene(for resin dilution) 0.259

OR

1 Polyethylene Terephthalate 0.363

2 Propylene Glycol 0.301

3 Maleic Anhydride 0.111

4 Styrene(for resin dilution) 0.259

If we use Iso Phthalic Acid/ Phthalic Anhydride as main raw material)

1 Phthalic Anhydride 0.307

2 Mono Ethylene Glycol 0.257

3 Maleic Anhydride 0.183

4 Styrene (for resin dilution) 0.324

OR

1 Iso Phthalic Acid 0.301

2 Propylene Glycol 0.276

3 Maleic Anhydride 0.160

4 Styrene (for resin dilution) 0.324

Page 64: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 64

2.10 Raw Materials Details

For manufacturing of proposed products various raw materials will be required which are listed below in Table 2-6. Mostly all raw materials are available in

market so will be purchased from local market. The convenient transportation medium will be used for the transportation of raw materials.

Table 2-6: Details of Proposed Raw Materials

S.

No.

Name of

Product

Capacity

per

(MT/Month)

Capacity

per (MT/d)

Physical

Form

Mode of

Storage

No. of

Units

Capacity

of

storage

(MT)

Total

Storage

Capacity

(MT)

Storage

Inventory

(d)

Transportation

1 Polyethylene

Terephthalate 218.2 8.728 Solid 40 kg PP bag 655 0.04 26.2 4 Road

2 Phthalic

Anhydride 153.4 6.136 Crystal solids 50 kg PP bag 369 0.05 18.45 4 Road

3 Iso Phthalic Acid 150.7 6.028

Lustrous,

crystalline

solid plates

50 kg PP bag 362 0.05 18.1 4 Road

4 Mono Ethylene

Glycol 128.5 5.14 Liquid

30 MT M.S/S.S

Tank 1 30 30 6 Road

5 Di Ethylene

Glycol 121.7 4.868 Liquid

30 MT M.S/S.S

Tank 1 30 30 7 Road

6 Propylene Glycol 150.3 6.012 Liquid 40 MT M.S/S.S

Tank 1 30 30 6 Road

7 Maleic

Anhydride 80.1 3.204 Crystal solids 25 kg Paper bags 440 0.025 11 4 Road

8 Styrene(for

resin dilution) 162.2 6.488 Liquid

40 MT S.S. 316

Tank 1 30 30 6 Road

Page 65: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI

HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 65

2.11 Requirement of Resources

There will be requirement of resources like water, power, fuel, manpower, plant &

machineries, utilities etc. Details of requirement of such resources for proposed project are

described in subsequent sections under respective headings.

2.11.1 Electricity / Power

Total power requirement for the proposed project will be about 200 HP which will be

procured from Pashchim Gujarat Vij Company Ltd. (PGVCL). In addition to this, unit will install

one D. G. Set of 150 kVA as stand-by to the main source and the same will be utilized only in

case of non-availability of power from PGVCL.

2.11.2 Manpower

There will be requirement of about 30 persons, skilled & unskilled, for the operation and

maintenance of the proposed project in efficient way. Out of 30 persons, 10 will be female

employees. During construction also, there will be requirement of workers. However, the

same will be of contractor’s persons and utilized according to the requirements and type of

construction activities. Details of proposed manpower are given in Table 2-7.

Table 2-7: Manpower Requirement

S. No. Particular Permanent Local Total

Male Female Male Female Male Female

1 Skilled Workers - - 10 - 10 -

2 Unskilled Workers 10 10 - - 10 10

Total 20 10 30

2.11.3 Water

For the proposed project, water will be required for domestic activities, greenbelt

development, and utility operations. Total water requirement will be 16.9 KL/d which will be

fulfilled by road tanker. There is no other source of water is envisaged in nearby area.

The letter from tanker supplier stating that he will be able to supply said quantity (16.9 KL/d)

is enclosed as Annexure 4.

The Industrial water consumption for proposed resin unit will be 6.2 KL/d which will be used

for cooling (make-up) & washing purpose. Domestic water consumption for proposed unit will

be 3.2 KL/d. The unit will develop Green Belt Area within the industrial premises hence the

water requirement for gardening purpose will be 7.5 KL/d.

2.11.4 Fuel

Fuel will be required for Thermic Fluid Heater (TFH) and D. G. Set (Stand-by). Diesel will be

used in TFH & D. G. Set. Fuel will be purchased from the nearby trader. Details of fuel

requirement are given in Table 2-8.

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 66

Table 2-8: Fuel Requirement

S. No. Particular Type of fuel Fuel Requirement

1 Thermic Fluid Heater (6 lac kCal/h) Diesel 100 L/d

2 D. G. Set (150 kVA) Diesel 32 L/h

2.11.5 Plant, Machineries & Utilities

List of plant machineries required for the proposed project is given in Table 2-9 & Table

2-10. The actual requirements of utilities and machineries & equipment are not limited to the

list given below as some additional minor requirements can also be cited depending up on

necessity noticed during installation & operations.

Table 2-9: List of Plant, Machineries and Utilities

S. No. Particular Quantity Size / Capacity

1 Thermic Fluid Heater 1 6 lac kCal/h

2 Cooling tower 1 100 TR

3 D. G. Set (Stand-by) 1 150 kVA

Table 2-10: List of Process Vessels

Sr.

No. Equipment Qty. (Nos.) Capacity MOC

1 Reactor 1 10 KL SS316

2 Blender 1 12 KL M.S.

2.12 Energy Balance

Major equipment to be utilized in proposed unit for thermal energy requirement is Thermic

Fluid Heater. Thus, energy balance of boiler presented below in Table 2-11.

Table 2-11: Energy Balance

Particular Unit Thermic Fluid Heater

Installed Capacity Kcal/hr 600000

Density of Diesel kg/L 0.832

Fuel Required L/d 100

kg/d 83.2

Gross Calorfic Value per kg of Fuel kJ 44800

kCal 10707.47

Efficiency on Gross Calorfic Value % 75

Energy Produced Kcal/day 668146

Losses through Flue gas 0.4% Kcal/day 2673

Net Energy output Kcal/day 665473

Production TPD 20

Energy consumption per MT production Kcal/MT 33274

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 67

2.13 Pollution Potential and Mitigation Measures

There will be possibility of pollution from the proposed project due to domestic & industrial

wastewater generation & disposal; flue gas emission from utilities, fugitive emission, noise &

vibration and hazardous waste generation & disposal. The said probable pollutions are

described below under respective heading with necessary details and mitigation measures.

2.13.1 Water Pollution

Total fresh water requirement for the proposed project will be 16.9 KL/d which will be fulfilled

by road tanker. For domestic activities be 3.2 KL/d, for utilities & washing activities 6.2 KL/d

and for greenbelt development 7.5 KL/d water will be required.

Total 0.15 KL/d sewage (domestic wastewater) will be generated. Total industrial wastewater

generation will be 1.9 KL/d.

Stream-wise water requirement and wastewater generation is given in Table 2-12 and

detailed water balance is given in Figure 2-7.

Table 2-12: Stream-wise Water Requirement & Wastewater Generation

Sr. No. Particular

Water

Requirement

(KL/d)

Wastewater

Generation

(KL/d)

1 Domestic activities 3.2 0.15

2 Greenbelt development 7.5 Nil

3

Industrial activities 6.2 1.9

Cooling Tower 6.0 0.3

Washings 0.2 0.2

Process - 1.4

Total industrial 6.2 1.9

Total (domestic + industrial + Greenbelt development) 16.9 2.05

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 68

Figure 2-7: Water Balance Diagram

Fresh water through road tanker

Gardening Domestic Industrial

To soak pit through septic

tank Washing Cooling Tower

ETP followed by Evaporator (Zero Discharge)

Process

Sludge to TSDF Site

16.9

3.2

0.15

7.5 6.2

6.0 0.2

6.2

0.3 0.2 1.4

Blo

w d

ow

n

1.9

Raw water

Waste water

Note: All values are in KLD

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 69

A. Domestic wastewater (Sewage) Treatment and Disposal

Total 0.15 KL/d sewage will be generated from the domestic activities of the proposed project

which will be taken to soak pit.

B. Industrial wastewater Treatment and Disposal

Total 1.9 KLD of waste water generated from floor washing water, process effluent and

cooling tower blow down will be collected in Collection cum neutralization Tank.

Effluent will be then neutralized using Lime & Alum and then taken to Nutch Filter for sludge

separation. Separated dried sludge will be collected, stored and disposed of at approved

TSDF site.

Filtrate water from Nutch Filter will be taken to holding tank then it will be evaporated in

steam based Evaporator, thus unit will maintain zero liquid discharge.

Quantity of effluent is very less, hence simple evaporator will be used. Heat Will be given by

TFH based evaporator. The capacity of evaporator will be around 190 L/Hr considering worst

scenario of effluent quantity

Schematic flow diagram of ETP is given in Figure 2-8 and Stream-wise effluent quality is

given in Table 2-13.

Table 2-13: Quality of Untreated and Treated Effluent

S.

No.

Stream

Particular Process Washing

Cooling

Tower Blow

Down

Composite

to ETP

Mode of

Disposal

1 Flow (KLD) 1.25 0.2 0.3 1.75

Neutralization &

Complete

Evaporation

2 pH 3.0-5.0 6.0-7.0 6.5-7.5 3.0-6.0

3 TSS (mg/L) 50-60 50-60 70-80 65-70

4 TDS (mg/L) 6000-7000 5000-6000 2000-2500 5500-6500

5 COD (mg/L) 3000-3500 1000-1200 40-50 2000-2500

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

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Table 2-14: Details of Effluent Treatment Plant Units

S. No. Unit Size/ Capacity Retention

Time

Quantity

(Nos.)

1. Collection cum Neutralization

Tank

1900 L 24 h 2

2. Nutch Filter 500 L - 1

3. Holding Tank 1900 L 24 h 2

4. Evaporator 190 L/h 1 h working 1

Table 2-15: Technical details of TFH Based Evaporator

Particulars Details

Capacity : 190 L/h

Quantity of Effluent to be evaporated : 190 L/d

Working hours per day : 1.0 h

Cost of operating ETP and evaporator : Rs. 500 /day

Rs.12500 /Month

Estimated profit by unit at full capacity

utilization

: Rs. 2 Lacs /Month

2.13.2 Air Pollution

In this proposed unit, flue gas emission will be the main source of air pollution. There is no

process gas emission from proposed project. There will be chances of fugitive emission due

to raw material handling and transportation and manufacturing activity. Various potential of

air pollution are described below under respective heading:

Collection Tank cum Neutralization Tank

Nutch Filter

/Filter Press

Holding Tank

TFH based Evaporation

system

ETP Sludge to be sent

to TSDF site

Figure 2-8: Schematic Diagram of Effluent Treatment Plant

Waste water from floor washing, process and

cooling tower blow down

Waste water from floor washing, process and

cooling tower blow down

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 71

A. Flue Gas Emission

In the proposed project, flue gas emission will occur from stack attached to Thermic Fluid

Heater (6 lac kCal/h), in which Diesel will be utilized as fuel. There will also a provision of D.

G. Set (150 kVA) as a stand-by source to the main power supply. Diesel will be used as fuel

in D.G. Set. The details of flue gas stack are given hereunder in Table 2-16 .

Table 2-16: Details of Flue Gas Emissions

S.

No. Stack attached to

Stack

Height

(m)

Fuel

Requirement

APC

System

Expected

Pollutant

1

Thermic Fluid

Heater

(6 lac kCal/h)

30 Diesel 100 L/d Adequate stack

height

SPM 150

mg/Nm3

SO2 100

ppm

NO2 50

ppm

2 D.G. set

(150 kVA) 6.0

HSD

6 L/h

Adequate stack

height

B. Process Gas Emission

There is no process gas emission from proposed unit.

C. Fugitive Emission

There will be chances of fugitive emissions due to manufacturing activity and storage & handling of raw materials:

The entire manufacturing activity will be carried out in closed reactors/vessels

and regular checking and maintenance of the same is carried out to avoid any leakages.

All the motors of pumps for the handling of hazardous chemicals will be flame proof

and provided with suitable mechanical seal with stand-by arrangement.

Control of all parameters on a continuous basis will be done by adequate control

valves, pressure release valves and safety valves etc.

All the flange joints of the pipe lines will be covered with flange guards.

A regular preventive maintenance will be planned and performed to replace or

rectify all damage gaskets, joints etc.

All raw materials will be stored in tanks/drums in isolated/designated storage area

and will be kept tightly closed.

All precautionary measures will be taken while handling various hazardous

chemicals.

There will also provision of adequate ventilation system in process plant and

hazardous chemical storage area.

Gas detectors will be provided in work area.

Workers will be provided with appropriate personal protective equipments.

Unit will also develop green belt area within the factory premises to control the

fugitive emissions from spreading into surrounding environment.

Unit will carry out work area monitoring twice in a year as per GFR

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-2: PROJECT DESCRIPTION 72

2.13.3 Solid / Hazardous Waste

The main hazardous waste generation will be ETP waste & evaporation residue. The other

hazardous wastes shall be used oil & Discarded Plastic Bags. The details of hazardous waste

generation and handling / Management are given in Table 2-17. Unit will provide storage

area for hazardous wastes having roof, pucca flooring with leachate collection system.

Leachate, if any will be collected and treated in effluent treatment plant. Unit will take

membership of TSDF site after commencement of proposed project.

Table 2-17: Details of Hazardous waste Management

Sr.

No. Description Category

Quantity

(MT/Annum) Management

1

Used oil/ Spent

Oil

5.1 0.55 Collection, storage and Use within

premises as a lubricant/ sell to

registered recycler.

2

Discarded Plastic

Bags/ Drums

33.1 1.7 Collection, storage and reuse within

premises/ sell to approve scrap

vendor.

3

ETP Sludge and

evaporation

residue

35.3 11.5 Collection, storage and disposal at

authorized TSDF site.

2.13.4 Noise & Vibration

The source of noise generation will be plant machineries and utilities. The adequate

precautions will be taken for abatement of noise pollutions as follows;

D.G. Set will be provided with acoustic enclosure.

Proper and timely oiling, lubrication and preventive maintenance will be carried out

for the machineries and equipments to reduce noise generation.

All the vibrating parts will be checked periodically and serviced to reduce the noise

generation. The equipment, which generates excessive noise, will be provided with enclosures etc.

To minimize the adverse effect on the health, ear muffs/ earplugs will be provided to

the working under high noise area.

To reduce the noise generation during the transportation activities; the vehicle will be

kept periodically serviced and maintain as per the requirement of latest trend in automobile industry. Only those vehicles with PUC’s are allowed for the

transportation.

Green belt area will be developed to prevent the noise pollution outside the factory

premises.

Noise monitoring will be carried out regularly at prominent places in the plant

through NABL approved laboratory.

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 73

3 DESCRIPTION OF THE ENVIRONMENT

3.1 Introduction

As per EIA Notification 2006, baseline monitoring is required to evaluate prevailing

environment to workout direct and indirect impacts on various components of environment

(viz. water, air, noise, soil, socio) due to proposed project and their interrelationships. Based

on the identified impacts required and adequate mitigation measures will be proposed.

3.1.1 EIA Methodology for Data Collection

An effective methodology is important for baseline data collection and impact prediction to

develop an efficient environment management plan. In this regards it is important to

understand the ground realities of the site and surrounding by the experts involved in

preparation of EIA. Accordingly a team of expert visited the proposed site to understand the

site surroundings and possible impacts from the activities of the proposed project. The

environment co-ordinates in consultation with the respective functional area experts selected

the sampling locations as per the ToRs prescribed by the SEAC & SEIAA. Subsequently the

field monitoring was undertaken for ambient air monitoring during October 2016 to December

2016 while for water, noise, socio economics, soil in May-2017 by laboratory staff of T. R.

Associates along with functional areas of respective fields. The collected data were analyzed

and interpreted.

3.1.2 Objectives of Baseline Monitoring

The term ‘baseline’ refers to conditions exiting before development against which subsequent

changes can be referenced. Baseline monitoring studies are carried out to:

Measure environmental parameters during a pre-project period for the purpose of

determining the range of variation of the system and establishing reference points

against which changes can be measured.

Identify environmental conditions which might influence project design decisions

(e.g., site layout, structural or operational characteristics);

Identify sensitive issues or areas requiring mitigation or compensation;

Collect input data for analytical models and predict effects due to proposed project;

Provide proposed environmental monitoring programs.

At this stage of EIA process, baseline monitoring is primarily discussed in the context of first

purpose wherein feedback from baseline monitoring programs may be used to:

Determine available assimilative capacity of different environmental components

within the designated impact zone and whether more or less stringent mitigation

measures are needed.

Improve predictive capability of EIAs.

3.1.3 Study Area

To carry out Environment Baseline Monitoring and to generate baseline environmental data

study area of 10 km radial distance from proposed project site has been selected. Base line

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 74

data of Ambient air quality, water sampling, land use, land cover, topography, ecology study

as well as socio economic study was collected for study area of 10 km.

3.1.4 Methodology of Baseline Study

For the generation of baseline data guideline proposed by MoEF&CC as well as generic ToRs

issued by SEAC & SEIAA has been taken into consideration. Relevant secondary data

available for different environmental components were collected and analyzed.

The land-use & land cover map of the 10 km radius study area from the project site

was prepared using IRS P6 LISS-III satellite image procured from NRSC (National

Remote sensing Centre), Hyderabad (Figure 3-9).

Survey of India Toposheet (Figure 2-2)

Secondary macro-metrological data from Indian Meteorological Department

(Section-3.2.1).

The details of the study period, frequency of sampling & method of environmental sampling

& analysis are given below in succeeding sections under respective titles.

3.2 Air Environment

Dispersion of different air pollutants released into the atmosphere has significant impacts on

the neighborhood air environment of project and forms an important part of impact

assessment studies. Meteorological conditions of the site regulates the transport and diffusion

of air-pollutants released into the atmosphere.

Ambient temperature, wind speed, wind direction and atmospheric stability are called primary

or basic Meteorological Parameters because the dispersion and diffusion of pollutants depend

mainly on these Parameters. Humidity, precipitation, pressure and visibility are secondary

Meteorological Parameters as this control the dispersion of the pollutants indirectly by

affecting primary Parameters. This data is useful for proper interpretation of the baseline

information as well as serves as an input, to predictive models for air quality impacts.

The ambient air quality status with respect to the study zone of 10 km radial distance from

the plant site will form the base line information over which the predicted impacts due to the

proposed plant can be super imposed to find out the net (Final) impacts on air environment.

From the final impacts a viable Environmental Management Plan (EMP) can be prepared

based on the impact statement for the air environment. .

3.2.1 Climate of the Study Area

The general agro-climatic zone of the study area is Arid to Semi-Arid. Information presented

in subsequent paragraphs is from the most recently published Long Term Climatologically

Tables for the nearest observatory, Rajkot by the Indian Meteorological Department (IMD)1.

1

1 Climatological Normals 1981-2010, issued by office of the additional director general of meteorology (Research)

Indian Meteorological Department, Pune-5

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 75

Month

Mean daily

Temperature (°C)

Humidity

(%) Rainfall

(mm)

Mean Wind

Speed

(km/h) Max. Min. Max. Min.

January 28.4 12.8 58 27 0.8 8.8

February 30.9 15 62 24 0.3 10.1

March 35.5 19.2 68 21 0.1 12.7

April 39.1 22.6 71 21 1.4 16.5

May 40.5 25.4 75 30 5.4 20.8

June 37.8 26.5 79 51 108.4 20.3

July 33 25.4 87 70 253.4 19

August 31.6 24.4 89 71 165.3 16.7

September 33.6 23.8 86 58 115.1 13.5

October 35.9 22.4 71 32 19.3 9

November 33.2 18.4 54 29 6.3 7.2

December 29.9 14.4 56 29 0.3 7.9

Annual Mean 34.12 20.86 71.33 38.58 52.01 12.5

D. Wind Direction

Details of predominant wind direction (blowing from) of month wise are as under:

Table 3-1: Predominant Wind Direction (Blowing From)

Season

Predominant

Month

First Second Third

Morning Evening Morning Evening Morning Evening

Winter

December E N NE NE N NW

January NE N E NW N NE

February NE NW NW N E NE

Summer

March W NW NW W SW N

April W NW NW W SW N

May W W SW NW NW SW

Monsoon

June SW W W SW S NW

July SW SW W W S S

August SW SW W W S NW

September W W SW NW NW SW

Post-

monsoon

October W NW NW N N NE

November E NE NE N N E

Source: Climatological Normals 1981-2010, issued by office of the additional director general of meteorology (Research) Indian Meteorological Department, Pune-5

Seasonal predominant downwind lies between:

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 76

1. Monsoon: NE to SE

2. Post monsoon: S to W

3. Winter: SE to SW

4. Summer: NE to SE

Predominant downwind of the study area lies between NE to SE.

3.2.2 Site Specific Meteorology (October 2016 to January 2017)

Weather station was installed near the proposed project site for the October 2016 to

December 2016 and recorded hourly observations for the parameters like Maximum and

minimum Temperatures (o C), Relative Humidity (%), Wind Speed (m/s), Wind direction and Rainfall (mm). These parameters are used in computing percentage frequencies and are

depicted in the form of ‘wind roses’ in Figure 3-1. Primary meteorological data are shown in Annexure 2.

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 77

Figure 3-1: Meteorological Wind Rose Diagram for October 2016 to January 2017 on Google Earth (Primary data)

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 78

3.2.3 Sampling Methodology and Analysis

Ambient levels of pollutants such as PM10, PM2.5, SO2, NO2, CO and VOC are selected for the

sampling. The methodology of sampling and analysis in detail is given in Table 3-2 & Table

3-3.

Table 3-2: Air – Parameters analysed and sampling duration

Attribute Parameter Frequency of Monitoring during

Study period

AAQ2

PM10, PM2.5, SO2, NO2, 24 hr. sampling - 2 d/week.

CO & VOC 24 hr. sampling – once in a study

period

Meteorological

Data

Wind speed, wind Direction,

Temperature, Relative humidity and

rainfall at one center location

Hourly data collected at site using AWS

Table 3-3: Ambient Air Quality - Methodology

Pollutant Method of analysis

Va

ria

ble

s

Du

st

PM10 Particulate Matter 10 IS 5182 (Part 23)

PM2.5 Respirable Suspended Particulate

Matter

STP No. TRA/STP/AA/02 Based on

manual instrument manufactures.

Ga

se

s SO2 Sulfur dioxide IS 5182 (Part 2)

NO2 Nitrous dioxide IS 5182 (Part 6)

VOC Volatile Organic Carbon IS 5182 (Part 11)

CO Carbon Monoxide NDIR spectroscopy

Various statistical parameters like standard deviation, geometric mean, minimum; maximum

concentrations and different percentiles have been computed from the data generated during

sampling in all sampling stations.

3.2.4 Selection of Monitoring Locations and Results

The baseline status of the ambient air quality can be assessed thorough scientifically

designed ambient air quality monitoring network. The design of monitoring network in the air

quality surveillance program was designed based on the following considerations:

Meteorological conditions on synoptic scale.

Topography of the study area.

Representation of regional background levels.

Representation of plant site.

Representation of cross sectional distribution in the downward direction.

Influence of the existing sources if any, are to be kept at minimum.

Inclusion of major distinct villages to collect the baseline status.

1

2 Sampling height as per standard method.

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T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 79

Minimum one location in within 0-3 km radius of study area was fixed. 5 monitoring locations

were identified and the sites are depicted in the Table 3-4 & Figure 3-2 recorded pollution

levels are given in Table 3-5.

Table 3-4: Ambient Air Monitoring Locations

Location

Code Location

Distance

(km) Direction Located in GPS Coordinates

A1 Project Site - - - 22°57'2.00"N

70°35'9.00"E

A2 Bodki 3.8 SSW Upwind 22°55'18.00"N

70°33'55.00"E

A3 Vavniya 6.7 NNE Downwind 23° 0'22.86"N

70°36'34.26"E

A4

Vavaniya

Reserve

Forest

8.6 N Crosswind 23° 1'39.00"N

70°34'35.00"E

A5 Mangroves

Swamp 12.4 W Upwind

22°56'56.22"N

70°27'54.84"E

Bodki

Vavaniya Reserve Forest

Photograph 3-1: Ambient Air Quality Monitoring

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Figure 3-2: Google Image Showing Ambient Air Quality Locations

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Table 3-5: Ambient Air Monitoring Results

Pollutant Particular

LOATION

Permissible Limits

(µg/m3) Project Site

(A1) Bodki (A2) Vavaniya (A3)

Vavniya Reserve

Forest (A4)

Mangroves

Swamp (A5)

PM 2.5

Min 24.25 22.68 23.40 21.13 20.78

60 Max. 33.84 32.47 31.75 30.87 35.84

Mean 28.15 26.72 27.95 25.97 29.11

98 % 33.4 31.8 31.5 30.5 35.8

PM 10

Min 64.31 61.30 63.73 60.36 62.54

100 Max. 80.00 82.35 81.45 83.77 84.88

Mean 73.49 71.85 74.92 72.83 75.05

98 % 79.8 81.5 81.4 82.8 83.0

SO2

Min 8.23 11.22 10.12 9.27 12.78

80 Max. 21.77 22.78 24.53 25.00 23.69

Mean 14.89 17.27 18.10 15.78 16.80

98 % 21.7 22.5 23.5 23.5 23.0

NO2

Min 15.47 17.43 16.28 19.38 18.12

80 Max. 27.71 29.04 26.89 25.85 28.93

Mean 23.86 24.67 22.97 21.92 25.14

98 % 27.7 28.8 26.8 25.7 28.9

Note: CO & VOC not detected

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3.2.5 Discussion of Ambient Air Quality

The maximum concentrations are recorded at Mangroves Swamp with PM10 of 84.88 g/m3.

The maximum concentrations are recorded at Mangroves Swamp with PM2.5 of 35.84 g/m3.

The maximum concentrations of SO2 found at Vavaniya Reserve Forest with 25.00 g/m3.

Similarly the maximum concentration of NO2 found at Bodki village with 29.04 g/m3.

All the above results are found well within the prescribed limits of National Ambient Air

Quality standards. CO and VOCs were found below detectable limits or not detected. All the

above results are found well within the prescribed limits of National Ambient Air Quality

standards.

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3.3 Noise

3.3.1 Sampling Methodology

Monitoring of noise is done by identifying suitable number of noise quality monitoring

locations. Background noise quality is monitored in dB(A) Leq (d) and dB(A) Leq (n) at the

selected locations.

Table 3-6: Noise Monitoring Methodology

Environment

Component

Sampling

frequency Methodology

Sample collection Sampling

Parameter Sampling

equipment Range Resolution

Ambient

Noise

Once during

the study

(Hourly

reading for

24

hours at each

location)

IS: 9989-1991

Sound level

meter (Model-

SL-4033SD)

30

dB(A)

to 130

dB(A)

0.1 dB Decibels –

dB(A)

Table 3-7: Ambient Noise Quality Standards for Different Areas/Zones

Ambient Air Quality

Standards

in Respect of Noise

Area

Code Category

Limits in dB(A) Leq3

Day Time Night Time

The Noise Pollution

(Regulation and Control)

Rules, 2000 and its

subsequent amendments

A Industrial 75.0 70.0

B Commercial 65.0 55.0

C Residential 55.0 45.0

D Silence4 50.0 45.0

3.3.2 Selection of Monitoring Locations and Results

As this is proposed site ambient noise monitoring was carried out. To study noise in 10 km

study area sensitive locations were identified and ambient monitoring was done at a distance

more than 100 m from the identified location.

Keeping in view of various local activities such as residential and Industrial activities 5 noise

level measurement locations were identified and the sites are depicted in the Figure 3-3 &

Table 3-8 recorded sound levels are given in Table 3-9.

1

3 dB (A) Leq*: denotes the time weighted average of the level of sound in decibels on scale A which is

relatable to human hearing. Day Time: 6:00 AM to 10:00 PM and Night Time: 10:00 PM to 6:00 AM 4 Area comprising not less than 100 mt around Hospitals, educational institutions, courts, religious places or any

other area which is declared as such by the competent authority.

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Table 3-8: Noise Monitoring Locations

Code Sampling Location Category Latitude

Longitude

N1 Project Site Industrial 22°57'5.13"N

70°35'6.92"E

N2 Mota Dahisara Residential 22°57'40.20"N

70°36'37.45"E

N3 Bodki Residential 22°55'16.52"N

70°33'54.10"E

N4 Vavaniya Residential 23° 0'17.70"N

70°36'42.58"E

N5 Virparda Residential 22°54'32.88"N

70°38'57.32"E

Project Site

Mota Dahisara

Photograph 3-2: Noise Monitoring

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Figure 3-3: Google Image Showing Noise Sampling Locations

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Table 3-9: Noise Levels

Code Sampling

Location Date Category

Day Time

Recorded level in

dB(A) Limits in

dB(A) Leq Min Max Leq

N1 Project Site 18.05.17 to

19.05.17 Industrial 65.0 73.1 69.0 75

N2 Mota Dahisara 19.05.17 to

20.05.17 Residential 48.8 54.9 52.3 55

N3 Bodki 20.05.17 to

21.05.17 Residential 44.8 51.1 47.8 55

N4 Vavaniya 21.05.17 to

22.05.17 Residential 43.0 49.1 46.6 55

N5 Virparda 22.05.17 to

23.05.17 Residential 42.5 47.8 45.2 55

Code Sampling

Location Date Category

Night Time

Recorded level in

dB(A)

Limits in

dB(A) Leq

Min Max Leq

N1 Project Site 18.05.17 to

19.05.17 Industrial 59.7 64.4 62.4 70

N2 Mota Dahisara 19.05.17 to

20.05.17 Residential 39.8 45.1 43.1 45

N3 Bodki 20.05.17 to

21.05.17 Residential 38.3 43.1 41.0 45

N4 Vavaniya 21.05.17 to

22.05.17 Residential 36.4 41.0 39.2 45

N5 Virparda 22.05.17 to

23.05.17 Residential 35.2 39.6 37.5 45

3.3.3 Discussion of Noise Levels

Out of all the 5 locations measured for noise levels, the sound levels recorded at project site

area is found to be 69.0 (A). Recorded Noise levels are found to be within the standard limits.

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3.4 Water Environment

Water of high quality is essential to human life, and water of acceptable quality is essential

for Agricultural, industrial, domestic and commercial uses; in addition, most recreation is

water based. Therefore, water quality studies have been carried out in the study area to

understand the availability of water resources, possibility of water contamination and existing

water quality.

3.4.1 Sampling Methodology and Analysis

The water resources in the study area may be classified into two major categories like

Surface and Ground water sources.

Water samples were collected at 7 locations, out of which 2 samples from surface Sources

and 5 samples from ground water sources for Physico-chemical and biological parameters.

Parameters were selected based on Guidelines for Water Quality Monitoring by Central

Pollution Control Board, Parivesh Bhawan, East Arjun Nagar, Delhi-32 published in December

2007.

Table 3-10: Sample Collection and Analysis of Water Sample

Parameter Frequency Sampling

methodology

Preservation

method

Analysis

Method

Prescribed

standard

pH and

Temperature

Once in a

baseline

period

IS: 3025 (part

I)

Not applicable Onsite

measurement

IS: 10500

specifications

Other

Physico-

chemical and

biological

parameters

IS: 3025 (part

I)

‘Standard

Methods for

Examination of

Water and

Wastewater’

Published by

American Public

Health

Association

(APHA) / IS

3025

3.4.2 Ground Water Quality

A. Monitoring Locations and Results

To identify drainage pattern and prevailing ground water conditions ground water prospects

map prepared by National Remote sensing Agency, Dept. of space, GoI was used (Figure

3-7). Samples were collected at 5 locations as mentioned in

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Table 3-11. Sampling locations are shown in Figure 3-4 while analysis results are given in

Table 3-12.

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Table 3-11: Ground Water Monitoring Locations

Code

Water

Sample

Location

Source Distance

(km) Direction GPS Coordinates

GW1 Project Site

Tanker water from

bore located at other

location

- - 22°57'2.00"N

70°35'10.00"E

GW2 Mota Dahisara Uncovered open well 3.2 E 22°57'18.00"N

70°37'2.00"E

GW3 Bodki Well 4.0 SSW 22°55'13.00"N

70°33'58.00"E

GW4 Vavaniya Uncovered open well

near pond 6.5 NNE

23° 0'15.00"N

70°36'34.00"E

GW5 Virparda Hand pump 7.8 SW 22°54'33.00"N

70°38'52.00"E

Bodki

Photograph 3-3: Ground Water Sampling

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Figure 3-4: Google Image Showing Ground Water Sampling Locations

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Table 3-12: Water Quality – Physico-chemical Analysis of Ground Water

Sr.

No.

Test

Parameters IS : 10500

Sample Code

& Location Units

Project Site

(GW1)

Mota Dahisara

(GW2) Bodki (GW3) Vavaniya (GW4)

Virparda

(GW5) Desirable Permissible

1. pH - 7.9 8.4 8.1 8.00 7.80 6.5-8.5

No Relaxation

2. Temperature °C 30.2 31.4 31.5 31.6 32 -- -- 3. Color CU B.D.L(DL=5) B.D.L(DL=5) B.D.L(DL=5) B.D.L(DL=5) B.D.L(DL=5) 5 15 4. EC µS 495 650 420 2690 612 -- -- 5. TDS mg/L 348 472 336 1896 432 500 2000 6. TSS mg/L 53 83 50 97 77 -- -- 7. Chloride as Cl- mg/L 90.0 110.0 70.0 519.8 99.7 250 1000

8. Sulphate as

SO4-2

mg/L 8.0 20.0 18.6 148.3 15.0 200 400

9. Total Hardness

as CaCO3 mg/L 130 150 100 570 120

200 600 10. Ca Hardness mg/L 50 40 30 220 20 -- -- 11. Mg Hardness mg/L 80 110 70 350 100 -- --

12. Calcium as

Ca++ mg/L 20.0 16.0 12.0 88.2 8.0

75 200

13. Magnesium as

Mg++ mg/L 19.4 26.7 17.0 85.1 24.3

30 100

14. Alkalinity as

CaCO3 mg/L 40 60 30 190 50

200 600 15. Carbonate mg/L B.D.L(DL=5) 20.0 B.D.L(DL=5) B.D.L(DL=5) B.D.L(DL=5) -- --

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Sr.

No.

Test

Parameters IS : 10500

Sample Code

& Location Units

Project Site

(GW1)

Mota Dahisara

(GW2) Bodki (GW3) Vavaniya (GW4)

Virparda

(GW5) Desirable Permissible

16. Bicarbonate mg/L 40.0 60.0 30.0 190.0 50.0 -- -- 17. Boron as B mg/L B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1) 0.5 1

18. Nitrate as NO3- mg/L B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1)

45 No

Relaxation 19. Fluoride as F- mg/L 0.60 0.55 0.45 0.40 0.25 1 1.5 20. Sodium as Na+ mg/L 39.0 53.0 57.0 79.0 48.0 -- --

21. Residual

Chlorine mg/L B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1) B.D.L(DL=1)

0.2 1 22. Odour -- Unobjectionable Unobjectionable Unobjectionable Unobjectionable Unobjectionable Agreeable Agreeable

23. Nitrite mg/L 2.2 1.8 1.6 1.1 1.2 -- --

24. Total Coliform MPN /

100 ml Absent Absent Absent Absent Absent Absent Absent

25. Fecal Coliform MPN /

100 ml Absent Absent Absent Absent Absent Absent Absent

26. Chloramines mg/L 2.4 2 1.6 1.4 1.1 4 No

Relaxation

27. E.Coli MPN /

100 ml Absent Absent Absent Absent Absent Absent Absent

Note: BDL = Below Detection Limit, DL = Detection Limit

Permissible Limit is applicable in the absence of Alternate source

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B. Discussions – Ground Water

Source of water at project site is tanker water, the source of water for tanker supplier is bore

well. People are not using water of Bodki well for drinking purpose. The water of open well in

Vavniya village is used for cloth washing. At all the locations Narmada water is available for

drinking purpose except for Virparda village, in this village water from hand pump is used for

drinking as well as household purpose.

Quality of water of Vavaniya village is not meeting drinking water standards, but it can be

used for domestic purpose. The levels of TDS, chlorides, hardness, magnesium, calcium,

sodium at this location is high than other locations as it is located near small rann of Kutch.

At all other locations water can be used for drinking purpose after treatment in RO.

3.4.3 Surface Water Quality

A. Monitoring Locations and Results

Surface water locations were identified using topomap (Figure 2-2). To finalize locations

Guidelines for Water Quality Monitoring by Central Pollution Control Board, Parivesh Bhawan,

East Arjun Nagar, Delhi-32 published in December 2007 were taken in to consideration.

Samples were collected at 5 locations as mentioned in Table 3-13. Sampling locations are

shown in Figure 3-5 while analysis results are given in Table 3-14.

Table 3-13: Surface Water Monitoring Locations

Code Location Distance (km) Direction GPS Coordinates

SW1 Jhinjhoda River 4.3 SSW 22°55'2.60"N

70°33'52.30"E

SW2 Phulku River 3.1 E 22°57'22.00"N

70°36'55.00"E

SW3 Bodki Pond 3.9 SSW 22°55'15.00"N

70°33'60.00"E

SW4 Virparda Pond 8.0 ESE 22°54'39.00"N

70°39'3.00"E

SW5 Vavaniya Pond 6.5 NNE 23° 0'18.12"N

70°36'29.53"E

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Jhinjhoda River

Phulku Nadi

Photograph 3-4: Photographs of Surface Water Sampling

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Figure 3-5: Google Image Showing Surface Water Sampling Locations

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Table 3-14: Water Quality – Physico-chemical Analysis of Surface Water

Sr. No.

Test Parameters

IS : 10500

Sample Code Units Jhinjhoda

River (SW1)

Phulku River (SW2)

Desirable Permissible

1. pH - 8.1 9.0 6.5-8.5 No Relaxation

2. Temperature °C 31.2 30.2 -- --

3. Color CU B.D.L(DL=5) B.D.L(DL=5) 5 15

4. DO mg/L 8.9 5.7 -- --

5. EC µS 4221 3852 -- --

6. Turbidity NTU 13.5 5.5 1 5

7. TDS mg/L 3188 2724 500 2000

8. TSS mg/L 153 79 -- --

9. Chloride as Cl- mg/L 744.8 689.8 250 1000

10. Total Hardness

as CaCO3

mg/L 970 370 200 600

11. Ca Hardness mg/L 290 140 -- --

12. Mg Hardness mg/L 680 230 -- --

13. Calcium as

Ca++

mg/L 116.2 56.1 75 200

14. Magnesium as

Mg++

mg/L 165.2 55.9 30 100

15. Alkalinity as

CaCO3

mg/L 530 280 200 600

16. Carbonate mg/L B.D.L(DL=5) 160.0 -- --

17. Bicarbonate mg/L 530.0 280.0 -- --

18. Sulphate as

SO4-2

mg/L 241.0 51.4 200 400

19. Boron as B mg/L B.D.L(DL=1) B.D.L(DL=1) 0.5 1

20. Nitrate as NO3- mg/L 0.1 0.2 45 No Relaxation

21. Residual

Chlorine

mg/L 4 3.1 0.2 1

22. Fluoride as F- mg/L 1.50 1.10 1 1.5

23. Sodium as Na+ mg/L 93.0 63.0 -- --

24. Potassium as

K+

mg/L 28.0 11.0 -- --

25. COD mg/L 448.0 408.0 -- --

26. BOD mg/L 147.1 134.4 -- --

27. Odour -- Unobjectionable Unobjectionable Agreeable Agreeable

28. Nitrite mg/L 2.6 2.0 -- --

29. Total Coliform

MPN /

100 ml

40 35 Absent Absent

30. Fecal Coliform MPN / 100

ml

24.6 21.6 Absent Absent

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 97

Sr. No.

Test Parameters

IS : 10500

Sample Code Units Jhinjhoda

River (SW1)

Phulku River

(SW2) Desirable Permissible

31. Chloramines mg/L 1.6 0.8 4.0 No Relaxation

32. E.Coli MPN / 100

ml

12.4 10.8 Absent Absent

Note: BDL = Below Detection Limit, DL = Detection Limit, NS = Not Specified

Permissible Limit is applicable in the absence of Alternate source

B. Discussions – Surface Water

Levels of TDS, chlorides, hardness, calcium, magnesium, alkalinity, COD, BOD, coliforms are

high at both the locations hence the water can be used for domestic purpose only. The

reason behind high levels of TDS, chlorides and harness are salt pans located near the

sampling points.

3.5 Soil

3.5.1 Sampling Methodology and Analysis

Disturbed soil samples were collected from the rotary cuttings and bailers and also from split

spoon samplers. Un-disturbed tube samples were collected using thin walled tubes. Soil

samples were collected such that structure and moisture content of the soil do not get

altered. In accordance with IS: 2720, split samples were carefully extracted from the

samplers.

Meticulous was paid to collect adequate amount of composite soil samples for analysis. The

samples were packed in dependable, waterproof containers and marking specified accurately

and distinctly. All the soil samples and core boxes were carefully transported to the testing

laboratory.

All ‘Soil sampling and analysis’ will be followed and done by Indian Standard IS – 2720.

Parameters analyzed for soil samples were pH, organic matter, Electrical Conductivity,

sodium, potassium, cation exchange capacity, water holding capacity, SAR etc.

3.5.2 Sampling Locations and Results

For soil quality analysis 5 sampling sites were chosen to understand Physic-chemical and

biological status of the soil. Sites are marked in this will establish the baseline characteristics

and will facilitate identifying the contamination if any due to the proposed project. The

sampling sites are depicted in the Figure 3-6 & Table 3-15 analysis results are given in

Table 3-16.

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Table 3-15: Soil Sampling Location

Code Location Distance (km) Direction GPS Coordinates

S1 Project site - - 22°57'6.04"N

70°35'7.60"E

S2 Mota Dahisara 2.6 ENE 22°57'35.39"N

70°36'34.22"E

S3 Bodki 3.9 SSW 22°55'23.36"N

70°33'46.66"E

S4 Vavaniya 5.9 NNE 22°59'56.88"N

70°36'37.70"E

S5 Virparda 8.9 SE 22°54'25.63"N

70°39'25.87"E

Project Site

Vavaniya

Photograph 3-5: Soil Sampling Photograph

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

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Figure 3-6: Google Image Showing Soil Sampling Locations

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Table 3-16: Physicochemical Parameters of the Soil

Sr.

No.

Test

Parameters

Results

Project

Site (S1)

Mota

Dahisara

(S2)

Bodki (S3) Vavaniya

(S4)

Viraparda

(S5)

1 pH at 25 °C 7.28 7.34 7.40 7.16 7.12

2 Organic Matter

(%)

0.62 0.45 0.40 0.58 0.52

3

Total

Phosphorus

(mg/kg)

52.12 45.23 40.22 38.56 47.10

4

Electrical

Conductivity

(mS/cm)

0.420 0.380 0.360 0.348 0.365

5 Sodium

(meq/100gm)

25 20 12 18 22

6 Potassium

(meq/100gm)

52 78 48 45 40

7

Cation Exchange

Capacity

(meq/100gm)

60 110 70 80 50

8 Water Holding

Capacity (%)

30.4 44.0 34.8 40.2 38.6

9 SAR 4.60 5.72 5.10 4.92 5.40

3.5.3 Discussion-Soil Environment

The pH of the soil extract varied from 7.12 to 7.4. The EC varied from 0.348 to 0.42 mS/cm

indicating average type soils. Organic matter in soils ranged from 0.4 to 0.62 % revealing the

distribution more than sufficient. Sodium values ranged between 12 to 25 meq/100 gm. The

Phosphorus levels ranged between 38.56 to 52.12 mg/kg. Potassium varied from 40 to 78

meq/100 gm.

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ROMAN PETROCHEMICAL

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 101

3.6 Hydrology, Ground Water & Water conservation

3.6.1 Geological Features

Repaid urban, industrial and Agricultural growth and its continuous expansion around Maliya

Town, Dist. Morvi has created problems related to water supply, Sewerage/ effluent disposal

leading to ground water depletion and pollution. The present report in corporate

hydrogeology and ground water scenario based on the scientific information with special

reference to Recharge Activity around Maliya town to envisage appropriate remedial

measures keeping environmental impact of Maliya development in view.

Total number of villages 7

Total area of Taluka 770 Sq. Kms.

Saline area - 770 Sq.Kms.

Fresh water area – NIL

Hard rock area – 770 Sq.Kms

Aluminum area – 770 Sq.Kms.

Feasibility –NIL

Quality of Ground Water- Saline

Geologically the area around Mota Dahisara village of Maliya Taluka is occupied by alluvium

formation and Basalt rock formation. The thickness of alluvium in the area is about 06 to 10

mts (APS-2 Alluvium Plain Shallow). Alluvium occurring in out fall areas of Machchhu Rivers

forms a prolific aquifer where ground water occurs under phreatic to semi confined

conditions.

Alluvium underground basalt from the aquifer more suitable for Borewell. The quality of

Ground water is Brackish at all depth in the Alluvium and under line Basalt, hence further

ground water development is not suggested. In around village is Hari par, Gala, Mansar,

Ground water is Saline or Brackish

A lineament is an interesting structure in basalt rock formation for ground water movement,

stoppage and storage. Basalts are generally formed by cooling of lave flows and the rock

itself can be identified by its dark tone. During cooling of lave and formation of a rock, joints

develop. Joints have strike, dip and spacing, some joints structurally, disturbed and they

develop fractures. Such fractures and closely spaced joints has a linear extension. So they

can be seen on imagery as a line. Adyke is an intrusion in the country rock giving a distinct

linear effect on the surface they obstruct the normal ground water flow and surface water

movement. Weathered and fractures dykes are more productive as well as recharging

purpose. Fracture zones forming the course of existing drainage are more productive as well

as recharging purpose. Deccan traps basalts is exposed of upper cretaceous to lower Eocene

age

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T. R. ASSOCIATES,

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A. Land / Soil Characteristic

The soils are generally developed from Alluvium and basalt formation and are coarse in

texture with satisfactory internal drainage. The sub soil condition below the existing ground

level are almost uniform in nature. Sub soil is composed of Clay mixed with little fine grained

silty sand, moram and Kankar with low resistivity due to clay and soil moisture. The area is

covered with recent to sub recent alluvial deposits comprising of brownish clay mixed with

little fine grained sand, silty sand. The Soil below ground level consist of top silty low plastic

soil layer having no swelling nature. Blackish brown to yellowish brown clayey silt or sand silt

layer extends to the depth of 2 to 3 mts.

B. Rain fall

30 years average annual rainfall is 449 mm.

C. Climate

The climate of the area is semi arid and is characterized by a hot summers. May is the

hottest month with mean daily maximum temperature of 43.40 C. The area has semi arid

climate with drought frequency of 34%.

3.6.2 Geo-Hydrological Status

The litho logical logs of exploratory bore holes, electrical logging results by govt. agencies in

and around Maliya Taluka have been studied to understand the subsurface geology and the

aquifer system. These bore holes have penetrated the thick sequence of Jura- Cretaceous

age down to 200 + m depth.

A. Feasibility of Source at Project Area

Area around Morbi Taluka is checked on ground water prospect Map, prepared by National

Remote Sensing Agency, Dept. of SPAC, G.O.I. Hyderabad, map sheet no. 41J09 (Figure

3-7) for feasibility of source along Kaveri river course. For feasibility of source the detail is as

under:

Table 3-17: Feasibility of Ground Water

Sr. No. Component Details

1. Hydro Geomorphic units/ land form APS – 2 (more than 3 to5 m) Amygdaloidal

Basalt (Alluvium Plain Shallow)

2. Geological sequence/ Rock type Upper cretaceous to Eocene Deccan Traps

3. Depth of water table of the area 8-30 m in Dug well (32), 120-150 m in

borewell (13)

4. Recharge condition Moderate

5. Aquifer Material in Basaltic Rock L.S. Loose Sediment

FIR. Fisher Rock

W.R.- Wheather rock

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T. R. ASSOCIATES,

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Sr. No. Component Details

6. Type of Well of the area B.W. Borewell – 120-150 m depth

100-150 LPM

7. Homogeneity in the unit & success

rate of well

Moderate

8. Quality of water Potable, at places NP

9. Ground water irrigated area 4 to 6%

10. Recharge structure suitability and

priority

Not required

11. Remarks (Problems/Limitations) Shallow water is potable High concentration of

fluoride was reported storage tanks are to be

constructed and dug wells are suggested on

Tank Beds itself to tap fresh water. Thickness

of alluvial is shallow Underlying basalts forms

the aquifer.

B. Ground Water Condition

In the area under investigation, around water occurs both under phreatic and semi confined

condition in alluvium formation. The occurrence and movement of ground water is mainly

controlled by primary porosity of inter granular pore spaces. Ground water is being developed

extensively by means of combination tubewell for water supply both in domestic and

agricultural sector

C. Depth of Ground Water Table

Shallow aquifer (Phreatic) development (up to 30 m depth) in the area is limited due to rapid

urbanization inferior quality and low yields. In general the ground water occurs under water

table condition & confined condition where water level ranges from 30 to 60 m depth

depending upon the rock type. Pumping water level of the area is 70 to 80 m. tube wells and

DCB yield portable water up to 80 m. depth and Quality deteriorates with depth.

3.6.3 Drainage Pattern of the surrounding Region

The area has a drainage pattern which is of the parallel and trellis type and which is

controlled by the topography and structure and tectonics of the region. All the small streams

flow from the higher grounds and meet ultimately flow from south to north direction to south

west direction near project area. The area Drainage ultimately meet with Gulf of Kutch.

Area has diverse landscape made up of small hills, valley, drainage flow, Platue and alluvium

plain. The terrain slope is southly in the north and westernly in the south number of major

river drains the area. Due to terrain constraint it is necessary to adopt proper soil

conservation and sand water development and management practice for w/s in sustained

basis. Because of short span of monsoon season and limited storage capacity and rapid cut

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T. R. ASSOCIATES,

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flow for hard rock aquifers, that is need to provide ground water recharge facilities to

supplement its which drawl at a time of summer.

As various components of the hydrologic system-Catchment runoff , base flow and ground

water an integrated at the level of river basins, river basin should be the unit of governance

and management of water resource such a system of governance will ensure integration of

physical sustainability consideration and the social economical and environmental

consideration in water resources management planning which ultimately result in good

governance.

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HIGHWAY, TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

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Figure 3-7: Ground Water Prospect Map

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T. R. ASSOCIATES,

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3.7 Land Use

3.7.1 Introduction

The land-use & lad cover map of the 10 km radius study area from the project site has been

prepared using IRS P6 LIS III satellite image procured from NRSC (National Remote sensing

Centre), Hyderabad. Land use pattern of the study area as well as the catchment area was

carried out by standard methods of analysis of remotely sensed data and followed by ground

truth collection (Bench mark) and interpretation of satellite data. The outcome of land use

study has been presented below in subsequent table and figures. The data was processed

through ArcGIS Software tools available with ESRI Package. The Land use map of the 5 km

study area is presented in Figure 3-9.

3.7.2 Land Use & Land Cover Classification

Land Cover is the physical material at the surface of the earth (it include grass, asphalt, trees,

bare ground, water, etc.) whereas Land use is the human use of land.

Land Use involves the management and modification of natural environment or wilderness

into built environment such as fields, pastures, and settlements. It has also been defined as

"the arrangements, activities and inputs people undertake in a certain land cover type to

produce, change or maintain it".

There is no one ideal classification of land use and land cover, and it is unlikely that one could

ever be developed. There are different perspectives in the classification process, and the

process itself tends to be subjective, even when an objective numerical approach is used.

Concepts concerning land cover and land use activity are closely related and in many cases

have been used interchangeably. The purposes for which lands are being used commonly

have associated types of cover, whether they are forest, agricultural, residential, or industrial.

Remote sensing image-forming devices do not record activity directly. The remote sensor

acquires a response which is based on many characteristics of the land surface, including

natural or artificial cover. The interpreter uses color, tones, textures, shapes, size, patterns,

and site associations to derive information about land use activities from what is basically

information about land cover.

To begin with, there is considerable diversity of opinion about what constitutes land use,

although present use of land is one of the characteristics that are widely recognized as

significant for planning and management purposes.

The classification must be scientifically defensible presenting a logical progression of its

applicability over large areas, amenable for use with remote sensor data. The classification

scheme is adopted for extracting information for on most possible land use/land cover classes

in general and all the agricultural seasons in particular and hence enable to repeat the

process at regular time intervals.

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The present Land use / Land cover map for the proposed project activity is prepared by

current vintage of satellite image. This report thus will enable assessing the impact on land

use pattern in the study area due to the proposed project activity.

A. Data Used

Current vintage data of Indian Remote Sensing satellite IRS P6 LISS III digital FCC (False

Color Composite) has been used for preparation of Land use/ Land cover thematic map of

study area. Survey of India Topo sheet (Figure 2-2) as a reference map on 1:50,000 scales

have been used for preparation of base layer data like road, rail network, village and mine

site and for geo-referencing of satellite image.

B. Technical Details

Satellite Image - IRS P6 LISS III

Satellite Data Source - NRSC, Hyderabad

Software Used - Earth Resources Data Analysis System (ERDAS) Imagine 9.2 and

ArcGis10.

C. Methodology

Land use / Land cover map preparation, Base map creation; Geometric and Radiometric

correction of satellite image has been processed using ERDAS Imagine 9.2 Software.

Salient features of the adopted methodology are given below:

Acquisition of satellite data.

Preparation of base map from Survey of India Topo sheet.

Data analysis using visual interpretation techniques.

Ground truth studies or field checks.

Finalization of the map.

Digitization using heads up vectorisation method.

Area calculation for statistics generation.

D. Interpretation of Remote Sensing Data

Satellite images are composed of array of grid, each grid has a numeric value that is known

as digital number. Smallest unit of this grid is known as a pixel that captures reflectance of

ground features represented in terms of Digital number, each representing specific land

features. Using image classification technique, the satellite data is converted into thematic

information, map based on the user’s knowledge about the ground area. Hybrid technique

has been used i.e. visual interpretation and digital image processing for identification of

different land use and vegetation cover classes based on spectral signature of geographic

feature.

Spectral signature represents various land use classes. Image interpretation keys are

developed based on image characteristics like color, tone, size, shape, texture, pattern,

shadow, association etc, which enables interpretation of satellite images for ground feature.

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Training sites are then assigned based on their spectral signature and interpretation

elements. Using image classification algorithm land use map is generated.

A total of seven land use/land cover classes have been demarcated in the study area

following Level I, II and III classification Table 3-18. A thematic map suitable for 1:25,000

scale map generation incorporating these classified categories has been prepared and

considering that the area of the project is considerably small a large scale map is prepared

Figure 3-9. The area as a whole represents plain area with very gentle sloping to nearly

level area & to the north of area flowing from south to north and it is also observed that the

major stream (Phulki & Jhjhoda) are linked with these two main drainage that debouche into

the Littel Run of Kachchh.Medium level industrial zone covered for 0.72 km2, the total land

area of scrub land covered 24.86 km2 and 175.69 km2 area covered under agriculture land as

well as plantation / Transportation 0.76 km2 has developed mainly in the area adjacent to

the rivers.

The adjoining area of project site is totally agricultural land including Kharif, Rabi and

Summer crop, constitute the dominant category of land use covering as much as 175.69 km2

of the total area. Active river canal forming the perennial water body together with the

numerous open & wastelands form a major and minor land cover category. Active river and

its tributaries flowing into it cover about 7.86 km2 of the total project area. Due to large

seasonal variation in discharge of these rivers, the area coverage of this category various in

space and time. The consistently shifting nature of the (canal name) and consequent bank

migration has resulted in large uncultivated & rural settlement along the active plain area

towards the site location. The land use for settlement is mostly confined to the ‘rural and

urban settlement’ (built up-rural) 3.71 km2 and land without scrub feature 4.43 km2 of the

total area & as such there is no current fallow land because the satellite used is of March

month when most of the crop is towards senence or maturity.

Table 3-18: Land Use Land Cover- (Based on GIS Studies)

S. No. LULC Class Area (km2) Percentage

1. Mixed settlement 3.71 1.18

2. Mining / Industries 0.72 0.23

3. Transportation 0.76 0.24

4. Crop land 175.69 55.93

5. Agriculture plantation 0.02 0.01

6. Forest 7.67 2.44

7. Manfrove / Swamp Area 49.18 15.65

8. Salt affected 5.10 1.62

9. Waterlogged 3.11 0.99

10. Scrub land Dense 24.86 7.92

11. Scrub land Open 4.43 1.41

12. River / Stream / Drain 7.86 2.50

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S. No. LULC Class Area (km2) Percentage

13. Lakes / Ponds 2.03 0.65

14. Reservoir / Tanks 2.40 0.76

15. Saltpan 26.61 8.47

Total 314.15 100

E. Land-Use Based on Census Data

The land use of the study area has been studied by analysing the available secondary data

such as the District Primary Census Handbook of Rajkot for the year 2011.

For computation of the land use pattern in the study area based on the village-wise land use

data given in the census records, the geographical area of all settlements covered within the

study area, though many villages in the peripheries of the circular study area are partially

covered. Perfect delineation and quantification of land uses for the partially covered parts of

villages in the study area is not possible, hence the entire village area is considered for the

study, irrespective of its coverage within the study area circle.

The land use details from census-2011 (Village wise) are presented in Table 3-19. This

includes forests, cultivated area, cultivable waste and the area not available for cultivation.

Figure 3-8: Land use of Study Area (as per Census 2011)

Page 110: DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR...T. R. ASSOCIATES, AHMEDABAD, GUJARAT TABLE OF CONTENTS 1 DRAFT ENVIRONMENTAL IMPACT ASSESSMENT REPORT FOR Proposed Synthetic Organic

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

FOR PROPOSED RESIN PROJECT

ROMAN PETROCHEMICAL

SURVEY NO. 922/P2, VILLAGE: MOTA DAHISARA, NAVLAKHI HIGHWAY,

TALUKA: MALIYA, DISTRICT: MORBI, GUJARAT.

T. R. ASSOCIATES,

AHMEDABAD, GUJARAT CHAP-3: DESCRIPTION OF ENVIRONMENT 110

Table 3-19: Land use data within study area (As per census 2011)

Distance District Sub District Village

Land use (Area in Hectares)

Forest

Area

Area under Non-

Agricultural

Uses

Barren & Un-

cultivable

Land Area

Land Under

Miscellaneous

Tree Crops etc.

Area

Culturable

Waste Land Area

Fallows Land

other than

Current

Fallows Area

Fallows Land

Current Fallows

Area

Net Area

Sown

Total

Unirrigated

Land Area

Area

Irrigated by

Source

3-5 km

Rajkot Maliya Mota Dahisara 60.7 24.2 440.96 0 0 0 0 3109.6 3109.6 0

Rajkot Maliya Bodki 0 0 405.17 0 0 0 0 511.3 511.3 0

Rajkot Maliya Kuntasi 0 1.17 133.36 0 0 0 0 1581.05 1581.05 0

5-7 km Rajkot Maliya Vavaniya 201 0 1275.35 0 0 0 0 274.5 274.5 0

Rajkot Morvi Rajpar 20.2 14.97 321.93 0 17.09 0 0 1682.43 872.43 810

7-10 km

Rajkot Maliya Chamanpar 0 25.06 24.55 0 0 0 0 609.99 609.99 0

Rajkot Maliya Nana Bhela 0 1.57 52.96 0 0 0 0 759.56 759.56 0

Rajkot Maliya Targhari 0 3.8 92.83 0 0 0 0 1090.36 1090.36 0

Rajkot Morvi Virparda 0 7.73 66.11 0 0 0 0 1087.44 1087.44 0

Rajkot Morvi Hajnali 0 6.47 86.31 0 0 0 0 620.95 617.72 3.23

Total 281.9 84.97 2899.53 0 17.09 0 0 11327.18 10513.95 813.23


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