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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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
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. -
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
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
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
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
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
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:
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
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
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.
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.
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
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.
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
૩
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.
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
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
૨
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.
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.
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.
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.
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.
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
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).
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
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
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.
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.
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
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
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
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.
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
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
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
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
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
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
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
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.
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
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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
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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
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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
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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
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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
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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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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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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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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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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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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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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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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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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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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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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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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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Figure 3-1: Meteorological Wind Rose Diagram for October 2016 to January 2017 on Google Earth (Primary data)
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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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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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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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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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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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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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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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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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Figure 3-7: Ground Water Prospect Map
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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)
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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