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Draft Environmental Impact Assessment Impact Assessment
Report
Sponge Iron, Steel Billets, MS, Power plant
Proposed Project
AtSurvey no. 394/1(P), 394/2, 395, 398, 397, 399 & 400
Vill Chh d d T l k Bh h
P j t P t
Village: Chhadawada, Taluka: Bhachau, District: Kutch (Gujarat)
Project Proponent
ASR Multimetal Private Limited
3rd Floor, K. G. Chambers,
Prepared By:
Opp. Gujarat Samachar Press, Udhna Darwaja, Ring Road,
Surat - 395 002.
NABET Certificate No. NABET/ EIA/ 1619/ RA 62 dated 25.07.2017Valid till 9.7.2019
ASR MULTIMETALS PVT LTD.
1
EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
CONTENTS
1 PROJECT SUMMARY ................................................................................... 12
2 INTRODUCTION ........................................................................................ 15
2.1 PROJECT PROPONENT ................................................................................. 15
2.2 PROJECT DETAILS ...................................................................................... 15
2.2.1 EXISTING PROJECT .................................................................................... 15
2.2.2 PROPOSED PROJECT DETAILS ..................................................................... 16
2.3 NEED OF PROJECT ..................................................................................... 17
2.4 COST OF PROJECT ..................................................................................... 17
2.5 PROJECT SITE DETAILS .............................................................................. 17
2.6 SALIENT FEATURES OF SITE ........................................................................ 21
2.7 LAND AREA BREAK UP ................................................................................ 22
2.8 LIST OF MAJOR INDUSTRIES IN THE VICINITY ............................................... 23
2.9 PURPOSE OF STUDY ................................................................................... 23
2.10 APPLICABLE LEGISLATION .......................................................................... 24
2.11 DEFINITION OF EIA .................................................................................... 24
2.11.1 METHODOLOGY ......................................................................................... 25
2.11.2 SCOPE OF STUDY ...................................................................................... 25
2.11.3 STRUCTURE OF EIA REPORT ........................................................................ 39
3 PROCESS DESCRIPTION ............................................................................ 41
3.1 PRODUCT DETAILS .................................................................................... 41
3.2 EQUIPMENT DETAILS ................................................................................. 41
3.3 RAW MATERIAL DETAILS ............................................................................ 42
3.4 PROCESS DESCRIPTION ............................................................................. 44
3.4.1 SPONGE IRON PLANT ................................................................................. 44
3.4.2 BILLETS ................................................................................................... 46
3.4.3 TMT BARS ................................................................................................. 49
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EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
3.5 MATERIAL BALANCE ................................................................................... 50
3.5.1 SPONGE IRON PLANT ................................................................................. 50
3.5.2 INDUCTION FURNACE ................................................................................. 50
3.5.3 ROLLING MILL ........................................................................................... 50
3.5.4 CAPTIVE POWER PLANT .............................................................................. 51
3.6 WATER DETAILS FOR EXISTING PLANT AND PROPOSED PROJECT ..................... 51
3.6.1 WATER SOURCE ........................................................................................ 51
3.6.2 WATER CONSUMPTION ............................................................................... 51
3.6.3 WASTE WATER GENERATION ....................................................................... 53
3.7 POWER REQUIREMENT FOR EXISTING AND PROPOSED PLANT ......................... 53
3.8 STACKS DETAILS FOR EXISTING AND PROPOSED PROJECT ............................. 54
3.9 SOLID WASTE GENERATION FOR EXISTING AND PROPOSED PROJECT .............. 54
3.10 HAZARDOUS WASTE GENERATION FOR EXISTING AND PROPOSED PROJECT ..... 55
4 BASELINE STUDY ...................................................................................... 56
4.1 METEOROLOGY STUDY ............................................................................... 56
4.2 AMBIENT AIR QUALITY ............................................................................... 58
4.2.1 STUDY PERIOD AND AREA .......................................................................... 58
4.2.2 DETAILS OF PARAMETER MONITORED AND ANALYSIS METHOD ADOPTED ......... 58
4.2.3 AMBIENT AIR QUALITY MONITORING LOCATIONS .......................................... 58
4.2.4 BASELINE DATA......................................................................................... 61
4.3 WATER ENVIRONMENT ............................................................................... 63
4.3.1 BASELINE STUDY ....................................................................................... 63
4.3.2 STUDY PERIOD AND SAMPLING FREQUENCY .................................................. 63
4.3.3 DETAILS OF PARAMETER MONITORED AND ANALYSIS METHOD ADOPTED ......... 63
4.3.4 WATER SAMPLING LOCATIONS .................................................................... 65
4.3.5 GROUND WATER QUALITY ........................................................................... 65
4.3.6 SURFACE WATER QUALITY .......................................................................... 68
ASR MULTIMETALS PVT LTD.
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EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
4.4 SOIL ENVIRONMENT .................................................................................. 69
4.4.1 SOIL QUALITY ........................................................................................... 70
4.5 NOISE ENVIRONMENT ................................................................................ 72
4.6 GEOLOGY OF STUDY AREA .......................................................................... 73
4.7 HYDRO GEO MORPHOLOGY OF THE AREA ...................................................... 75
4.8 DETAILS OF DRINAGE PATTERN ................................................................... 76
4.9 TRAFFIC STUDY ......................................................................................... 76
4.9.1 MONITORING LOCATIONS ........................................................................... 76
4.10 LAND USE STUDY ...................................................................................... 78
4.10.1 METHODOLOGY ......................................................................................... 78
4.10.2 PRIMARY DATA COLLECTION ....................................................................... 78
4.10.3 SECONDARY DATA COLLECTION .................................................................. 79
4.10.4 LAND USE/ COVER PATTERN OF STUDY AREA ................................................ 79
4.10.5 AREA STATISTICS OF LAND USE/ COVER CLASSES ......................................... 79
4.11 BIO ECOLOGY STUDY ................................................................................. 81
4.11.1 FLORAL DIVERSITY OF STUDY AREA ............................................................. 81
4.11.2 FAUNAL BIODIVERSITY OF STUDY AREA ....................................................... 83
4.12 SOCIO ECONOMIC DATA ............................................................................. 85
4.12.1 DATA FINDINGS BASED ON FGD AND VILLAGE PROFILE .................................. 86
4.12.2 DATA FINDINGS BASED ON INDIVIDUAL INTERACTION AND FGD WITH THE
COMMUNITY MEMBERS ............................................................................... 91
4.12.3 NEEDS TO BE FOCUSED FOR THE DEVELOPMENT ........................................... 91
4.12.4 DEVELOPMENT ACTIVITY PLAN .................................................................... 94
5 IMPACT IDENTIFICATION ......................................................................... 99
5.1 PROJECT ACTIVITIES CAUSE IMPACTS .......................................................... 99
5.2 POLLUTION SOURCE .................................................................................. 99
5.3 POTENTIAL IMPACT ON AIR ENVIRONMENT .................................................. 100
5.3.1 CONSTRUCTION PHASE ............................................................................. 100
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AND POWER PLANT
DETOX CORPORATION PVT. LTD.
5.3.2 OPERATION PHASE ................................................................................... 100
5.3.3 DETAILS OF AIR MODELING ....................................................................... 103
5.4 POTENTIAL IMPACT ON NOISE ENVIRONMENT .............................................. 108
5.4.1 CONSTRUCTION PHASE ............................................................................. 108
5.4.2 OPERATION PHASE ................................................................................... 108
5.4.3 NOISE QUALITY MODELING ........................................................................ 109
5.5 POTENTIAL IMPACT ON WATER ENVIRONMENT ............................................. 111
5.5.1 CONSTRUCTION PHASE ............................................................................. 111
5.5.2 OPERATION PHASE ................................................................................... 111
5.6 POTENTIAL IMPACT DUE TO SOLID WASTE GENERATION ............................... 113
5.6.1 CONSTRUCTION PHASE ............................................................................. 113
5.6.2 OPERATION PHASE ................................................................................... 113
5.7 HAZARDOUS WASTE GENERATION .............................................................. 114
5.8 ECOLOGY & FLORA- FAUNA ........................................................................ 115
5.8.1 ECOLOGICAL IMPACT ASSESSMENT ............................................................ 115
5.9 SOCIO ECONOMIC ENVIRONMENT ............................................................... 130
5.10 IMPACT MATRIX ....................................................................................... 130
6 ENVIRONMENT MANAGEMENT PLAN ....................................................... 137
6.1 ADMINISTRATIVE ASPECTS OF EMP ............................................................. 137
6.2 ENVIRONMENT MANGEMENT PLAN – CONSTRUCTION PHASE .......................... 137
6.3 ENVIRONMENT MANAGEMENT PLAN - OPERATION PHASE FOR CONTROL OF
FUGITIVE EMISSION ............................................................................................ 138
6.3.1 POINT SOURCE EMISSION ......................................................................... 139
6.3.2 FUGITIVE EMISSIONS CONTROLS ............................................................... 139
6.3.3 GREEN BELT TO MITIGATE POLLUTION ........................................................ 139
6.4 ENVIRONMENT MANAGEMENT FOR NOISE ENVIRONMENT .............................. 142
6.5 ENVIRONMENT MANAGEMENT PLAN FOR WATER ENVIRONMENT ..................... 144
6.5.1 WATER CONSERVATION ............................................................................. 144
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AND POWER PLANT
DETOX CORPORATION PVT. LTD.
6.5.2 RAIN WATER HARVESTING ......................................................................... 144
6.5.3 WASTE WATER MANAGEMENT .................................................................... 144
6.6 ENVIRONMENT MANAGEMENT PLAN - SOLID WASTE ...................................... 145
6.6.1 FLY ASH MANAGEMENT .............................................................................. 146
6.7 HAZARDOUS WASTE ................................................................................. 147
6.8 ENVIRONMENT MANAGEMENT CELL ............................................................. 147
6.8.1 BUDGETARY ALLOCATION FOR ENVIRONMENT MANAGEMENT PLAN ................. 149
7 ENVIRONMENT MONITORING PLAN ........................................................ 150
7.1 AMBIENT AIR QUALITY MONITORING ........................................................... 150
7.2 STACK MONITORING ................................................................................. 150
7.3 NOISE ENVIRONMENT ............................................................................... 150
7.4 WATER AND WASTE WATER QUALITY MONITORING ...................................... 151
7.4.1 ENVIRONMENT LABORATORY ...................................................................... 151
7.5 POST PROJECT ENVIRONMENT MONITORING BUDGETARY ALLOCATION: .......... 151
8 PROJECT BENEFITS ................................................................................. 152
8.1 EMPLOYMENT POTENTIAL ........................................................................... 153
9 DISCLOSURE OF CONSULTANT ................................................................ 154
List of Tables Table 2-1: Existing Product Profile for Rolling Mill ....................................................... 15
Table 2-2: Products considered for Existing EC ........................................................... 16
Table 2-3: Product Profile with proposed Expansion .................................................... 16
Table 2-4: Salient Features Of Site ........................................................................... 21
Table 2-5: Existing and proposed Land details with Survey Number .............................. 22
Table 2-6: Land Area Break up ................................................................................ 22
Table 2-7: ToR Compliance...................................................................................... 26
Table 2-8: Structure of EIA Report ........................................................................... 39
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EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Table 3-1: Product Details ....................................................................................... 41
Table 3-2: Equipment details ................................................................................... 42
Table 3-3: Raw material Details ............................................................................... 42
Table 3-4: Raw Material Details for power plant .......................................................... 43
Table 3-5: Coal and Coal Char analysis results ........................................................... 43
Table 3-6: Material Balance of Sponge Iron Plant ........................................................ 50
Table 3-7: Material Balance of Induction Furnace ........................................................ 50
Table 3-8: Material Balance of Rolling Mill .................................................................. 50
Table 3-9: Material Balance of Captive Power Plant ..................................................... 51
Table 3-10: Fresh Water Consumption Details ............................................................ 51
Table 3-11: Waste water Generation ......................................................................... 53
Table 3-12: Power Requirement ............................................................................... 53
Table 3-13: Stack Details & APC Measures for existing & proposed ................................ 54
Table 3-14: Solid waste generation .......................................................................... 55
Table 3-15: Hazardous Waste generation .................................................................. 55
Table 4-1: Meteorology Data ................................................................................... 56
Table 4-2: Analysis methods .................................................................................... 58
Table 4-3: Justification of monitoring locations ........................................................... 58
Table 4-4: Air Monitoring Locations .......................................................................... 60
Table 4-5: Concentration of Various Pollutants ........................................................... 61
Table 4-6: Analysis method for water parameters ....................................................... 63
Table 4-7: Water Monitoring Locations ...................................................................... 65
Table 4-8: Ground Water Quality .............................................................................. 66
Table 4-9: Surface Water Quality ............................................................................. 68
Table 4-10: Methodology of soil sample analysis ......................................................... 69
Table 4-11: Soil Quality .......................................................................................... 71
Table 4-12: Noise Quality in the study area ............................................................... 72
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AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Table 4-13: Geological Succession of the surrounding area .......................................... 74
Table 4-14: Litho log of cut cliff of Project Site ........................................................... 75
Table 4-15: Details of Traffic Monitoring Stations ........................................................ 76
Table 4-16: Details of Satellite Data ......................................................................... 78
Table 4-17: Classification Levels .............................................................................. 79
Table 4-18: Land use/cover Classes Area Statistics within 10 km Radius of Project Site.... 79
Table 4-19: Species provided Protection as per Wild Life Protection Act 1972 .................. 84
Table 4-20: List of villages cover in 10 Km Radius ...................................................... 85
Table 4-21:Availability of Health facilities .................................................................. 86
Table 4-22: Availability of Education facilities ............................................................. 87
Table 4-23: Occupation Details ................................................................................ 87
Table 4-24: Facilities available ................................................................................. 89
Table 4-25: Common facilities ................................................................................. 89
Table 4-26: Facilities of Sanitation and Drinking water ................................................ 90
Table 4-27: Availability of fuel source ........................................................................ 90
Table 4-28: Village wise requirements ....................................................................... 91
Table 4-29: Development activity with estimated allocation of funds ............................. 94
Table 4-30 : Demographic Characters ....................................................................... 96
Table 5-1: No. of dumpers/ trucks used for transportation .......................................... 101
Table 5-2: Stack Details for Existing & Proposed Plant (Input data) .............................. 102
Table 5-3: Resultant Concentration due to incremental increase Proposed ..................... 103
Table 5-5: Noise level generation from induction furnace ............................................ 108
Table 5-6: Noise level generation from Rotary Kiln ..................................................... 108
Table 5-7: Noise level generation from AFBC ............................................................ 109
Table 5-8: Solid Waste Generation .......................................................................... 113
Table 5-9: Slag analysis result ................................................................................ 113
Table 5-10: Hazardous Waste generation ................................................................. 114
ASR MULTIMETALS PVT LTD.
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EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Table 5-11: Ecological Impact assessment of Proposed expansion of M/s ASR Multimetals
Private Limited’s new integrated steel plant and power plant ....................................... 120
Table 5-12: Impact Matrix ...................................................................................... 131
Table 6-1: Recommended Plant Species for Green Belt Development ........................... 141
Table 6-2: Estimated cost of implementation of EMP .................................................. 149
Table 7-1: Monitoring schedule ............................................................................... 151
Table 8-1: Employment generation for the proposed expansion project ......................... 153
List of Figures Figure 2-1: Satellite image showing the existing project site and surrounding features ..... 18
Figure 2-2: Site map with surrounding features in 10 km radius of project site ............... 19
Figure 2-3: Photographs of proposed Projects & Surroundings ...................................... 20
Figure 2-4: Green belt photographs .......................................................................... 23
Figure 3-1: Process flow sheet of sponge iron plant ..................................................... 45
Figure 3-2: Flow Diagram of Steal based Turbo Generator Set ...................................... 46
Figure 3-3: Process flow for manufacturing MS Billets ................................................. 48
Figure 3-4: Process flow of TMT Bars ........................................................................ 49
Figure 3-5: Water balance diagram for existing and proposed project ............................ 52
Figure 4-1: Wind Rose Diagram ............................................................................... 57
Figure 4-2: Air Monitoring Locations on site map of study area ..................................... 59
Figure 4-3: Geological Map of Bhachau, Kutch ............................................................ 74
Figure 4-4: Traffic count from Bhachau to Samakhiyali ................................................ 76
Figure 4-5: Traffic count from Samakhiyali to Bhachau ................................................ 77
Figure 4-6: Land use/Land cover Map of 10 km radius ................................................. 80
Figure 5-4: Isopleths for PM (Proposed) ................................................................... 105
Figure 5-5: Isopleths for Sox (Proposed) .................................................................. 106
Figure 5-6: Isopleths for Nox (Proposed) .................................................................. 107
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EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Figure 5-7: Noise quality model for proposed project ................................................. 110
Figure 5-8: TDS Balance for proposed Project ........................................................... 112
Figure 6-1: Photographs of existing wind barriers and storage shed ............................. 138
Figure 6-2: Cross section and plan of Ash pond ......................................................... 146
Figure 6-3: Environment Management Cell ............................................................... 148
List of Annexure ANNEXURE 1: LAY OUT MAP & TOPOSHEET
ANNEXURE 2: EXISTING CC&A, NOC CERTIFICATE & EC COPY
ANNEXURE 3: IRON ORE AND COAL LINKAGE DOCUMENTS
ANNEXURE 4: MOU FOR FLY ASH
ANNEXURE 5: WATER ALLOCATION CERTIFICATE
ANNEXURE 6: HSE POLICY
ANNEXURE 7: LAND ACQUISITION DOCUMENTS
ANNEXURE 8: TRAFFIC STUDY REPORT
ANNEXURE 9: PHOTOGRAPHS OF BASELINE STUDY AND AMBIENT AIR QUALITY
MONITORING DATES
ANNEXURE 10: EC COMPLIANCE OF EXISTING UNIT AND CC&A COMPLIANCE
ANNEXURE 11: CREP GUIDELINES COMPLIANCE
ANNEXURE 12: BIO ECOLOGY REPORT
ANNEXURE 13: RISK ASSESSMENT AND DISASTER MANAGEMENT PLAN
ANNEXURE 14: LAND USE STUDY
ANNEXURE 15: SOCIO ECONOMIC STUDY
ANNEXURE 16: NABET CERTIFICATE
ANNEXURE 17: TOR COPY
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AND POWER PLANT
DETOX CORPORATION PVT. LTD.
List of Abbreviation
AAQ: Ambient Air Quality
APC: Air Pollution Control
AFBC: Atmospheric Fluidized Bed Combustion
APHA: American Public Health Association
AWWA: American Water Works Association
BOD: Biological Oxygen Demand
CPCB: Central Pollution Control Board
COD: Chemical Oxygen Demand
CETP: Common Effluent Treatment Plant
DO: Dissolved Oxygen
EIA: Environment Impact Assessment
EC: Environmental Clearance
EMP: Environment Management Plan
ESP: Electrostatic Precipitator
EMC: Environmental Management Cell
FAE: Functional Area Expert
FGD: Focus Group Discussion
GWIL: Gujarat Water Infrastructure Limited
GLC: Ground Level Concentration
HSE: Health Safety and Environment
IUCN: International Union for Conservation of Nature
ISC-ST: Industrial Source Complex – Short Term
ID fan: Induced Draft Fan
LRFs: Ladle Refining Furnace
LULC: Land Use Land Cover
MTPA: Metric Tonne per Annum
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AND POWER PLANT
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MoEF: Ministry of Environment and Forest
MoU: Memorandum of Understanding
MT: Metric Tonne
MPN: Most Probable Number
NRSA: National Remote Sensing Centre
NABET: National Accreditation Board for Education and Training
NABL: National Accreditation Board for Testing and Calibration Laboratories
OSHA: Occupational Safety and Health Administration
PEL: Permissible Exposure level
PUC: Pollution Control Certificate
RO: Regional Office
RSPM: Respirable Suspended Particulate Matter
SPCB: State Pollution Control Board
STG: Steam Turbine Generator
SPM: Suspended Particulate Matter
ToR: Terms of Reference
TPD: Ton per Day
TMT: Thermo Mechanically Treated
TDS: Total Dissolved Solids
TON: Total Organic Nitrogen
WPCF: Water Pollution Control Federation
WHRB: Waste Heat Recovery Boilers
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EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Chapter 1 Project Summary
1 PROJECT SUMMARY
ASR Multimetals Pvt. Ltd. proposes to expand existing integrated steel and power plant at
survey no. 394/2, 398, 399 & 400, 394/1(P), 395, 397 Village: Chhadawada, Taluka:
Bhachau, District: Kutch (Gujarat).
The company has 220250.5 sq m in Survey nos. 394/2, 398, 399 & 400 on which the
existing unit is operative. The company has now procured additional land of 94433 sq m
with Survey No. 394/1 (P), 395 & 397. The industrial units for proposed expansion project
will be build on the existing available land. Whereas the additional land procured will be
used for green belt development and other utilities. The total green belt area within the
plant premises will be 144753.5 sq m.
Existing unit has installed capacity of MS (2000 MT/month), Steel billets (12333 MT/month),
Sponge iron (5500 MT/month), Power plant (WHRB – 4 MW and AFBC – 4 MW).
Now the company plans for expansion with addition in production capacity of 24000
MT/month for MS Rods, Wires Flats and Re Rolled steel Product of MS, 24000 MT/month for
Steel Billets, 15000 MT/month for Sponge Iron, 17 MW for AFBC and 8 MW for WHRB. The
project fall under category A, section 3 (a) and 1 (d) i.e. Metallurgical Industries (ferrous &
non-ferrous) & Thermal Power Plants respectively of EIA notification.
The proposed project is located at distance of 3.2 km from nearest village (Samakhiali).
Project site is connected with existing NH 8A is at distance of 500 meters from the project
site. There will be increase in traffic of 120 dumpers/ day due to proposed expansion
project. The internal road is concreted with 3 lanes and is sufficient to take the additional
load.
For the expansion project, the company proposes to install Rotary kiln (2 × 250 MT),
induction furnace (2 × 30 MT), Rolling Mill (24000 MT/month), AFBC (17 MW) and WHRB (8
MW).
The raw material required for the proposed expansion of steel plant will be Iron ore pellets
(24000 MT/month), Coal (18000 MT/month), Dolomite (500 MT/month), Limestone (600
MT/month) for sponge iron, Scrap (17000 MT/month) and sponge iron/ Hot Briquetted iron
(15000 MT/month) for induction furnace and Steel Billets/ Ingots (26000 MT/month) for
Rolling Mill Products.
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For proposed power plant Imported coal (7200 MT/month) and Coal Char (5600 MT/month)
will be utilized.
The required quantity of water shall be met through Gujarat Water Infrastructure Limited
(GWIL). The total water consumption for proposed project will be 1000 KL/day and waste
water generation will be 303 KL/day. The waste water generated will be mainly from blow
down from cooling tower and boiler and DM reject. Generated waste water shall be collected
and will be reused within the plant premises after neutralization for green belt and dust
suppression. The TDS level in neutralized waste water will be below 346 mg/L which is well
below the norms for Plantation and gardening. Domestic waste water generated will be
disposed through septic tank/ soak pit. No liquid waste shall be discharge from the project.
Rain water harvesting will be implemented with provision for collection of water in rainwater
harvesting tank.
As per the present land use pattern of the study area 82.11 % of area categorized as
agricultural land. The major crop cultivated in the study area are Green gram (Vigna
radiata), castor (Ricinus Communis), cotton (Gossypium spp.), Guvar (Cyamopsis
tetragonolobus), Til (Sesamum indicum) during monsoon. Mostly in summer, castor and
fodder crop are grown and at places bajra. During winters, Jeera (Cuminum cyminum),
Fenugreek (Trigonella foenum-graecum), and Mustard (Brassica juncea) are cultivated.
Agriculture is monsoon depended.
The Air Pollution Control Measures that shall be installed are Electrostatic Precipitator (ESP)
with AFBC stack (60 m) and Rotary Kiln Stacks (45 m) and Bag Filters with Induction
Furnace stack (30 m). The incremental increase during operation Phase of plant is predicted
with for Particulate matter (1.637 µg/m3), SO2 (1.658 µg/m3) and NOx (9.707 µg/m3)
respectively at North East direction at distance of 1.118 Km for SO2, 0.7 Km for and NOx
and PM.
The resultant incremental noise concentration was enumerated using noise model (CUSTIC
3.2). The Impact of Noise generated from the proposed equipment and process will be in
the range of 0.78 km radius from the Project site. The expected level of the noise at 0.78
km is 11.06 dB. There is no residential area at this distance. Hence impact due to noise will
be negligible and localized. The receptors are mainly workers in the Project site. The impact
can be minimized by use of proper PPE Devices. Ambient noise level standards are
maintained at the plant boundary.
The solid waste expected to be generated will be Total ash (294 MT/day), Coal Char (160
MT/day) and Slag (140 MT/day). Fly ash generated will be sold to brick manufacturing unit.
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AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Fly ash will be stored in 3 fly ash silos having capacity of 50 Tonnes which will cater for
twenty four hours fly ash generation. Provision of ash pond is given to store excess of fly
ash. Coal char will be reused as raw material for AFBC Boilers and partly sold to registered
dealers. Slag generated will be sold as binding material for road construction activity. Used
Lube oil (75 MT/annum) expected to be generated. The same shall be reused within plant
premises as lubrication oil or sold to registered recycler.
A detail baseline study was conducted for the proposed project. The predominant wind
direction observed during the study period (15 March 2015 to 15 June 2015) was South
West to North East. Total eight locations were selected for baseline Ambient Air Quality
Monitoring. The minimum and maximum concentration of PM10 was observed to be 60
µg/m3 (Chadwada) and 99 µg/m3 (Project Site) respectively. The minimum and maximum
concentration of PM2.5 was observed to be 20 µg/m3 (Chadwada) and 55 µg/m3 (Project site
& Amaliyara) respectively. The minimum and maximum concentration of SO2 was observed
to be 3.73 µg/m3 (Lakhpat) and 26.14 µg/m3 (Project site & Samakhiali) respectively. The
minimum and maximum concentration of NOx was observed to be 8.31 µg/m3 (Amaliyara)
and 35.02 µg/m3 (Samakhiali) respectively.
Total eight ground water and four surface water samples were analyzed for water
environment in the study area. Soil Quality in total seven villages was monitored in the
study area. Daytime and Nightime noise levels were monitored in eight villages.
Among the enumerated flora in the study area, none of them were assigned any threat
category by RED data books of Indian plants (Nayar and Sastry 1990) and RED list of
threatened Vascular plants (IUCN - 2010, BSI - 2003). No natural forest land was observed
in the study area except few scattered scrub Forest dominated by Acacia neotica and
Prosopis julifera at Rampar Village.
A detail socio economic study with primary data collection was conducted in villages in near
vicinity. Company has allocated funds for various socio economic activities in the area. The
major activities undertaken by the company under Corporate Social Responsibility (CSR) are
building of toilet blocks, providing fodder in Village Gaushala, building of protection wall on
pond for water management etc. Total manpower required for the proposed project is 400.
The total cost of project is Rs. 250 Crores.
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AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Chapter 2 Introduction
2 INTRODUCTION
2.1 PROJECT PROPONENT
M/s. ASR Multimetals Private Limited is a state-of-the-art Manufacturing unit of high
strength deformed steel Re-bars and Structural Steel Sections. ASR is fully equipped to
ensure quality at every stage of production, so as to deliver quality product. Latest
machinery, testing and quality checks along with qualified operators make the task easy for
the company to deliver the best every time.
The Group has a very strong base in the local and international market at number of
destinations abroad including Asia, Middle East, Europe and Africa. The ASR brand is very
well accepted by Local Markets so, it will support at international level also.
In order to meet the market demands, the company now propose to install a new integrated
steel plant and power plant at Survey no. 394/2, 398, 399 & 400, 394/1(P), 395, 397
Village: Chhadawada, Taluka: Bhachau, District: Kutch (Gujarat).
2.2 PROJECT DETAILS
2.2.1 Existing Project
The plant is operative from 2005. Initially company had installed rolling mill products in
name of ASR Multimetals Private Limited located at Survey numbers: 394/2, 398, 399 &
400, Village: Chhadwada, Taluka: Bhachau, District: Kutch, Gujarat. The details of rolling
mill products for existing plant are as mentioned in Table 2-1.
Table 2-1: Existing Product Profile for Rolling Mill
PRODUCT QUANTITY REMARKS
MS Rods 5000 MT/month
EC was not applicable to these products. CCA was renewed vide order no. AWH 55787 dated 25/07/2013 and valid up to 13.05.18
MS Wires 2500 MT/month
MS Flats 2500 MT/month
Re rolled steel products of MS i.e channels, angles, bars, rounds, sections and profiles etc
2000 MT/month
Steel billets/ ingots 12,333 MT/month
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Later on Company applied for expansion with project for sponge iron, pig iron and captive
power plant. As these products were covered under EIA notification. EC was obtained for the
same vide letter no. F. No. J- 11011/ 251/2007- IA II (I) dated 31st March 2008 with
validity of five years. Copy of same is attached as Annexure 2.
The copy of existing environment clearance and consent to operate and NOC is attached
herewith as annexure 2.
Table 2-2: Products considered for Existing EC
Product Granted
capacity
Installed
capacity
Remark
Sponge iron 6000
MT/month
5500 MT/month Company has obtained consent to
operate for sponge iron plant and
captive power plant vide order no.
AWH 55787 dated 25/07/2013 and
the plant has commissioned.
Captive power plant
Coal/ lignite based CPP
WHRB
20 MW
16 MW
4 MW
8 MW
4 MW
4 MW
Pig iron 5400
MT/month
--- Pig iron plant was not installed
and accordingly Consent to
operate was not obtained.
2.2.2 Proposed Project details
Now the company proposes for expansion in their existing manufacturing capacity. The total
product profile with existing and proposed quantity is as mentioned in Table 2-3.
Table 2-3: Product Profile with proposed Expansion
Name of Products /By Products & Intermediate
Products
Existing quantity Proposed quantity
MT/month
Total quantity MT/month
MS (MILD STEEL) Rods 5000 MT/Month 24000 MT/Month
36000 MT/Month
MS (MILD STEEL) Wires 2500 MT/Month
MS (MILD STEEL) Flats 2500 MT/Month
Re-Rolled Steel Products of MS
(i.e. Channels, Angles, Bars,
Rounds, Sections & Profiles etc.)
2000 MT/Month
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Steel Billets / Ingots (Semi Finished Products)
12333 MT/Month 24000 MT/Month
(Along with Preheater & LRF)
36333 MT/Month
Sponge Iron 5500 MT/Month 15000 MT/Month 20500 MT/Month
Power from AFBC Boiler (Coal
Base)
4 MW 17 MW 21 MW
Power from WHRB (Waste Heat
Gases from Rotary Kiln)
4 MW 8 MW 12 MW
2.3 NEED OF PROJECT
In order to meet the increasing demand of steel product in domestic as well as in
international market the company proposes in further expansion for an integrated steel
plant.
Captive Power plant will be installed to cater the demand of Power Supply.
2.4 COST OF PROJECT
Total project Cost: 250 Crores.
Project will be completed within 24 months after obtaining EC. Payback period of Total
Project Cost is Six to Eight Years and it is depending upon market.
2.5 PROJECT SITE DETAILS
The proposed project site will be located within the existing industrial premises as well as
the additional land is procured. The location of project site on satellite image (Google earth)
is as shown in Figure 2-1. The surrounding features of project site in 10 km radius as
shown in Figure 2-2.
In the Existing premises additional facilities will be installed. Only foundation work of Kilns,
Furnaces etc shall be done in construction activity. The additional procured land shall be
developed for green belt and other facilities like Labour colony and Utility (Admin building,
Parking, OHC, Medical Room, washroom).
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Figure 2-1: Satellite image showing the existing project site and surrounding features
National highway: 0.5 Km
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Figure 2-2: Site map with surrounding features in 10 km radius of project site
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Figure 2-3: Photographs of proposed Projects & Surroundings
Front side of the Plant Back side of the Plant
Right side of the Plant Left side of the Plant
Surroundings of the plant site
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2.6 SALIENT FEATURES OF SITE
The salient features of site are as noted below in Table 2-4.
Table 2-4: Salient Features Of Site
Feature Description
Survey No. Existing Survey no. 394/2, 398, 399 & 400,
Additional Land procured Survey no.: 394/1(P), 395, 397
Village: Chhadawada, Taluka: Bhachau,
District: Kutch (Gujarat)
Latitude and Longitudes of the
project site
Corner Latitude Longitude
A 23°18'38.25"N 70°28'2.35"E
B 23°18'41.51"N 70°28'15.72"E
C 23°18'20.00"N 70°28'14.57"E
D 23°18'17.47"N 70°27'55.70"E
Type of Land Existing Industrial Land
Nearest Village Samkhiyali (~ 3.2 Km)
Nearest Town/City Bhachau (~ 12 Km)
Nearest railway station Samkhiyali (~ 3.67 Km)
National Highway NH 8A (~ 0.5 Km)
Nearest port Kandla (~ 40 km)
Total Land available 314683.5 sq m
Nearest Lake/ pond/ reservoir/ canal None
Source of water Gujarat Water Infrastructure Limited (GWIL)
Source of electricity Electricity requirement shall be obtained from captive
power generation.
Remaining additional power requirement shall be procured
from SEB
Any Protected areas notified under None within 10 km of project site.
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Wild Life (Protection) Act, 1972,
Notified Eco sensitive area,
Interstate boundary in 10 Km radius
Critically polluted area None within the study area.
*Arial distance from project boundary.
2.7 LAND AREA BREAK UP
The total land available is 314683.5 sq m. out of which 94433 sq m area is envisages for
proposed expansion project.
Table 2-5: Existing and proposed Land details with Survey Number
Details Existing Additional land Total
Survey No. 394/2, 398, 399 & 400 394/1(P), 395, 397 394/2, 398, 399 & 400, 394/1(P), 395, 397
Land area 220250.5 sq m 94433 sq m 314683.5 sq m
The detailed land area break up for the existing and proposed expansion project site is as
mentioned below Table 2-6. 100 % land is acquired by company and is converted into non
agricultural land. Land documents are attached as Annexure 7.
Table 2-6: Land Area Break up
Purpose Existing plant in Sq.m
Proposed expansion project in existing S. No. (sq m)
Additional S. No. – Land area (Sq m)
Total area in existing land (sq m)
Industrial area 45528 62575 --- 108103
Raw material storage
area
10144 15216 --- 25360
Product Storage Area 6581 9872 --- 16453
Fly ash storage area 4840 7260 --- 12100
Other utility 1254 ---- --- 1254
Green belt 56980.5 ---- 87773 144753.5
Labour colony --- --- 4400 4400
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Utility (admin building,
parking, OHC, Medical
room, Wash room)
--- --- 2260 2260
Total 125327.5 sq m 94923 sq m 94433 sq m 314683.5
The lay out map of the site is attached as Annexure 1.
Only foundation work for kiln, Furnaces shall be constructed for proposed Project. Rest all
utility shall be used from existing unit. Hence no major impact envisaged for Construction
Phase.
Figure 2-4: Green belt photographs
2.8 LIST OF MAJOR INDUSTRIES IN THE VICINITY
There are major two industries located in the vicinity i.e Gallantt Metal Limited and
Electrotherm India Limited. The major products of these industries are steel and power. The
industries are located at distance of 1.5 km – 2.5 km respectively.
2.9 PURPOSE OF STUDY
The project fall under category A, section 3 (a) and 1 (d) i.e. Metallurgical Industries
(ferrous & non-ferrous) & Thermal Power Plants respectively of EIA notification, September
2006 and amendment thereof vide notification no. S.O 3067 (E) dated 1st December 2009;
which requires prior Environmental Clearance before starting construction, production or
any other allied activities related to the project. For obtaining the Environmental Clearance;
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it is required to carry out the Environmental Impact Assessment (EIA) study and prepare
EIA report as per the Terms of Reference issued by MoEF.
For the preparation of EIA study report, ASR Multimetals Private Limited has retained M/s
Detox Corporation Private Limited. The status of accreditation of M/s Detox Corporation
Private Limited is attached as Annexure 16.
2.10 APPLICABLE LEGISLATION
The lists of applicable regulations for the proposed plant are as follows:
EIA Notification, 2006 and amendments thereof
The Noise (Regulation and Control) Rules, 2000
The Water (Prevention and Control of Pollution) Act, 1974.
The Water (Prevention and Control of Pollution) Cess Act, 1977.
The Water (Prevention and control of Pollution) Cess (Amendment) Act, 2003.
The Air (Prevention and Control of Pollution) Act, 1981.
The Environment (Protection) Act, 1986.
The Hazardous Wastes (Management and Handling) Rules, 1989 as amended in
2000.
The Manufacture, Storage and Import or Hazardous Chemical Rules, 1989 as
amended in 2000.
The Public Liability Insurance Act, 1991.
The National Environment Tribunal Act, 1995.
The Fly Ash Notification, 1999.
The Municipal Solid Wastes (Management and Handling) Rules, 2000.
The Batteries (Management and handling) Rules, 2001.
2.11 DEFINITION OF EIA
Environmental Impact Assessment (EIA) is a formal process used to predict how industrial
development or construction project will affect natural resources such as water, air, land,
socioeconomic and bio ecological environment.
An EIA usually involves a sequence of steps:
Screening
Scoping
Public consultation
Appraisal
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2.11.1 Methodology
Environmental Impact Assessment (EIA) studies include identification, assessment,
quantitative evaluation and prediction of probable impacts. To minimize the impact of the
project on various environmental attributes, mitigation measures are suggested for
implementation along with the project.
The methodology of this study can be schematized as detailed below:
To gather information on present environmental conditions and relevant national
environmental guidelines and EIA procedures.
Scoping
Assessment of significant impacts.
Description of residual impacts.
Description of mitigating, all significant/ residual impacts
Development of monitoring plans.
To inform all relevant and involved authorities through public hearing regarding the impact
of the project on the environment and the proposed mitigation measures.
2.11.2 Scope of Study
The report represents environmental impact assessment & management plan of the
proposed expansion project of Sponge Iron, Steel Billets/Ingots, Rolling Mill Products &
Power Plant (WHRB & AFBC) at Village: Chhadwada, Taluka: Bhachau, District: Kutch,
State: Gujarat.
As per the requirements stated in the Environmental Impact Assessment Notification 2006
and its subsequent amendments, Environmental Impact Assessment (EIA) study has been
undertaken to assess the environmental impacts of the proposed project and to develop a
site specific environmental management plan and risk mitigation measures. Subsequently,
baseline environmental studies have been conducted during the summer season (15 March
2015 to 15 June 2015) as per the standard ToR issued by MoEF.
The EIA report has been prepared as per the ToR issued by MoEF vide letter no. F. No. J -
11011/251/2007-IA-II (I) dated 7th July 2015. The extension for TOR was considered in
EAC meeting held on 8th May 2018 and the TOR validity was extended till 06.07.2019. The
copy of terms of reference is attached as Annexure 17. The detailed ToR compliances are
mentioned in Table 2-7 below.
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Table 2-7: ToR Compliance
Sr.
No.
TOR Points Compliance Status
1 Executive Summary Refer Chapter 1, Page no. 12
Separated executive summary
submitted
2 Introduction
Refer chapter 2, Section 2, Page no.
15
I Details of the EIA Consultant including NABET
accreditation
Refer Annexure 16, on Page no. A-
223.
II Information about the project proponent
Refer chapter 2, Section 2.1, Page
no. 15.
III Importance and benefits of the project Refer Chapter 2, Section 2.3, Page
no. 17 for importance of project
Refer chapter 8, Page no. 152 for
project benefits
3 Project Description
Refer chapter 2 , Section 2.2, Page
no. 15.
I Cost of project and time of completion.
Refer chapter 2, Section 2.4, Page
no. 17.
II Products with capacities for the proposed project.
Refer chapter 2, Section 2.2.2, Table
2-3, Page no. 16 for Product Profile
with proposed Expansion.
III If expansion project, details of existing products
with capacities and whether adequate land is
available for expansion, reference of earlier EC if
any.
Refer chapter 2 , Table 2-1, Page no.
15 for Existing Product Profile for
Rolling Mill.
Table 2-2, Page no. 16 for products
considered in existing EC.
Refer Chapter 2, Section 2.7, Page
no. 22 for land area consideration
IV List of raw materials required and their source
along with mode of transportation.
Refer chapter 3, Table 3-3 Page no.
42 for Raw material for steel product
Refer chapter 3, Table 3-4, Page no.
43 for raw material details of power
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plant
V Other chemicals and materials required with
quantities and storage capacities
No additional chemicals and material
required.
Refer chapter 3, Table 3-3 Page no.
42 for Raw material for steel products
Refer chapter 3, Table 3-4, Page no.
43 for raw material details of power
plant
VI Details of Emission, effluents, hazardous waste
generation and their management.
Refer Chapter 3, Table 3-13, Page
no. 54 for emission details
Refer Chapter 3, Table 3-11, Page
no. 53 for Waste water Generation.
Refer chapter 3, Table 3-14, page no.
55 for solid waste generation
Refer chapter 3, Table 3-15, Page no.
55 for hazardous waste generation.
VII Requirement of water, power, with source of
supply, status of approval, water balance
diagram, man-power requirement (regular and
contract)
Refer chapter 3, Section 3.6.2, Table
3-10, page No. 51 for water
requirement
Refer chapter 3, Section 3.7, Table
3-12, page no. 53 for Power
Requirement.
Refer Chapter 3, Section 3.6.1, Page
no. 51 for source of water
Refer chapter 3, Figure 3-5, Page no.
52 for Water Balance
Refer Chapter 8, Section 8.1, Page
no. 153 for manpower details
VIII Process description along with major equipments
and machineries, process flow sheet (quantities)
from raw material to products to be provided.
Refer chapter 3, Section 3.4, Page
no. 44 for process description
Refer chapter 3, Table 3-2, Page no.
42 for equipment details.
Refer chapter 3, Section 3.5, Page
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no. 50 for raw material to product
(material balance)
IX Hazard identification and details of proposed
safety systems.
Refer Annexure 13, Page no. A-131
for details risk assessment study
X Expansion/modernization proposals:
a Copy of all the Environmental Clearance(s)
including Amendments thereto obtained for the
project from MOEF/SEIAA shall be attached as an
Annexure. A certified copy of the latest Monitoring
Report of the Regional Office of the Ministry of
Environment and Forests as per circular dated
30th May, 2012 on the status of compliance of
conditions stipulated in all the existing
environmental clearances including Amendments
shall be provided. In addition, status of
compliance of Consent to Operate for the
ongoing. Existing operation of the project from
SPCB shall be attached with the EIA-EMP report.
EC copy is attached as Annexure 2 on
page no. A-4. EC compliance report is
regularly submitted to MoEF&CC
Bhopal every six monthly. We have
applied to MoEF&CC for certification
of EC compliance on 06.04.2018. The
copy of EC & CCA compliance report
is attached as Annexure 10 page no.
A-86.
b In case the existing project has not obtained
environmental clearance, reasons for not taking
EC under the provisions of the EIA Notification
1994 and/or EIA Notification 2006 shall be
provided.
Copies of Consent to Establish/No Objection
Certificate and Consent to Operate (in case of
units operating prior to EIA Notification 2006, CTE
and CTO of FY 2005- 2006) obtained from the
SPCB shall be submitted. Further, compliance
report to the conditions of consents from the
SPCB shall be submitted.
The existing Project already obtained
EC, CC& A & Consent to Establish/No
Objection Certificate. The copy of the
same is attached as Annexure 2 on
page no.A-4.
4 Site Details
I
Location of the project site covering village,
Taluka/Tehsil, District and State, Justification for
selecting the site, whether other sites were
Refer chapter 2, Section 2.6, Table
2-4 on Page No. 21 for location of
project with village, Taluka/ Tehsil,
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considered. District and State name
Refer Chapter 2, Figure 2-1, Page no.
18 for project site location map
The proposed project is within the
existing industrial premises. No
alternative site was considered
II A toposheet of the study area of radius of 10km
and site location on 1:50,000/1:25,000 scale on
an A3/A2 sheet. (including all eco-sensitive areas
and environmentally sensitive places)
Refer Annexure 1, Page no. A-3 for
toposheet showing the Project
Location.
III Co-ordinates (lat-long) of all four corners of the
site.
Refer chapter 2, Table 2-4 on Page
No. 21 for Co-ordinates of four
corners of the Project Site.
IV Google map-Earth downloaded of the project site.
Refer chapter 2 , Figure 2-1, on page
no. 18 for google map of project site.
V Layout maps indicating existing unit as well as
proposed unit indicating storage area, plant area,
greenbelt area, utilities etc. If located within an
Industrial area/Estate/Complex, layout of
Industrial Area indicating location of unit within
the Industrial area/Estate.
Refer Annexure 1, Page no. A-2 for
Layout map indicating existing unit as
well as proposed unit.
VI Photographs of the proposed and existing (if
applicable) plant site. If existing, show
photographs of plantation/greenbelt, in particular.
Refer chapter 2 , Figure 2-3 and
Figure 2-4, Page no. 20 & 23
respectively for Photographs of plant
along with Plantation/greenbelt.
VII Landuse break-up of total land of the project site
(identified and acquired), government/private -
agricultural, forest, wasteland, water bodies,
settlements, etc shall be included. (not required
for industrial area)
Refer chapter 2 , Section 2.7, on
Page no.22 for detailed Land area
break of the project site.
VIII A list of major industries with name and type
within study area (10 km radius) shall be
incorporated.
Land use details of the study area
Refer chapter 2 , Section 2.8, on
Page no.23 for major industries.
Refer Chapter 4, Section 4.10, Page
no. 78 for land use study
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IX Geological features and Geo-hydrological status of
the study area shall be included.
Refer Chapter 4 , Section 4.6, Page
no. 73 for Geological features and
Section 4.7 for Geo-hydrological
status of the study area on page no.
75.
X Details of Drainage of the project upto 5km radius
of study area. If the site is within 1 km radius of
any major river, peak and lean season river
discharge as well as flood occurrence frequency
based on peak rainfall data of the past 30 years.
Details of Flood Level of the project site and
maximum Flood Level of the river shall also be
provided. (Mega green field projects).
Refer Chapter 2, Figure 2-2, Page no.
19 for site map with details of
drainage. Chapter 4, Section 4.8,
Page no. 76 for drainage system
No major river in 1 Km radius of
project site.
J Status of acquisition of land. If acquisition is not
complete, stage of the acquisition process and
expected time of complete possession of the land.
100 % land is acquired. Land
acquisition document is attached as
Annexure 7, on page no. A-44.
XII R&R details in respect of land in line with state
Government policy.
Not Applicable.
5 Forest and wildlife related issues (if applicable): Not applicable
I
Permission and approval for the use of forest land
(forestry clearance), if any, and recommendations
of the State Forest Department. (If applicable).
Not Applicable.
II Landuse map based on High resolution satellite
imagery (GPS) of the proposed site delineating
the forestland (in case of projects involving forest
land more than 40 ha).
Not Applicable.
III Status of Application submitted for obtaining the
stage I forestry clearance along with latest status
shall be submitted.
Not Applicable.
IV The projects to be located within 10 km of the
National Parks, Sanctuaries, Biosphere Reserves,
Migratory Corridors of Wild Animals, the project
proponent shall submit the map duly
authenticated by Chief Wildlife Warden showing
Not Applicable.
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these features vis-à-vis the project location and
the recommendations or comments of the Chief
Wildlife Warden-thereon.
V Wildlife Conservation Plan duly authenticated by
the Chief Wildlife Warden of the State
Government for conservation of Schedule I fauna,
if any exists in the Study area.
Not Applicable.
VI Copy of application submitted for clearance under
the Wildlife (Protection) Act, 1972, to the
Standing Committee of the National Board for
Wildlife.
Not Applicable.
6 Environmental Status
I
Determination of atmospheric inversion
level at the project site and site-specific
micro-meteorological data using
temperature, relative humidity, hourly wind
speed and direction and rainfall.
Refer Chapter 5 , Section 5.3.2.2, on page
no. 102 for Determination of atmospheric
inversion level at the project site and
ground level concentration of pollutants
from the stack emissions.
Refer Chapter 4, Section 4.1, on Page no.
56 for site Specific micro-meteorological
data.
II AAQ data (except monsoon) at 8 locations
for PM10, PM2.5, SO2, NOX, CO and other
parameters relevant to the project shall be
collected.
The monitoring stations shall be based
CPCB guidelines and take into account the
pre-dominant wind direction, population
zone and sensitive receptors including
reserved forests.
Refer Chapter 4, Table 4-4 on page no. 60,
Figure 4-2, page no. 59 for location of AAQ
monitoring.
The justification of monitoring locations as
per CPCB guidelines is as given in Chapter
4, Table 4-3, page no. 58
III Raw data of all AAQ measurement for 12
weeks of all stations as per frequency given
in the NAQQM Notification of Nov. 2009
along with – min., max., average and 98%
values for each of the AAQ parameters from
data of all AAQ stations should be provided
Refer Annexure 9, on page no. A-82 for
Raw data of all AAQ measurement for 12
weeks of all stations along with monitoring
dates and photographs.
Refer Chapter 4 , Section 4.2.4, Table 4-5
on page no. 61 for min., max., average and
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as an annexure to the EIA Report.
98% values for each of the AAQ parameters
from data of all AAQ stations.
IV Surface water quality of nearby River (60m
upstream and downstream) and other
surface drains at eight locations as per
CPCB/ MoEF & CC guidelines.
Refer Chapter 4 , Section 4.3.4 on page no.
65 for surface water monitoring location.
Refer Chapter 4, Section 4.3.6, on page no.
68 for surface water quality.
V Whether the site falls near to polluted
stretch of river identified by the CPCB/
MoEF &CC.
No.
VI Ground water monitoring at minimum at 8
locations shall be included.
Refer Chapter 4, Section 4.3.4 on page no.
65 for Ground water monitoring location.
Refer Chapter 4, Table 4-8 on page no. 66
for Ground water Quality.
VII Noise levels monitoring at 8 locations within
the study area.
Refer Chapter 4, Section 4.5, Table 4-12 on
page no.72 for Noise level monitoring.
VIII Soil Characteristic as per CPCB guidelines.
Refer Chapter 4, Table 4-11 on page no.71
for Soil Quality.
IX Traffic study of the area, type of vehicles,
frequency of vehicles for transportation of
materials, additional traffic due to proposed
project, parking arrangement etc.
Refer Chapter 4, Section 4.9 on page no.
76. for Traffic study.
The detailed Traffic Study report is attached
as Annexure 8 on page no. A-67.
X Detailed description of flora and fauna
(terrestrial and aquatic) existing in the
study area shall be given with special
reference to rare, endemic and endangered
Species. If Schedule-I fauna are found
within the study area, a Wildlife
Conservation Plan shall be prepared and
furnished.
Refer Annexure 12, on Page no. A-104 for
detailed Bio ecology study.
XI Socio-economic status of the study area.
Refer Annexure 15, on page no. A-196 for
detailed Socio Economic Study.
7 Impact Assessment and Environment Management Plan
Assessment of ground level concentration of Refer Chapter 5 , Table 5-3 on page
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I pollutants from the stack emission based on site-
specific meteorological features.
In case the project is located on a hilly terrain,
the AQIP Modelling shall be done using inputs of
the specific terrain characteristics for determining
the potential impacts of the project on the AAQ.
Cumulative impact of all sources of emissions
(including transportation) on the AAQ of the area
shall be well assessed.
Details of the model used and the input data used
for modeling shall also be provided.
The air quality contours shall be plotted on a
location map showing the location of project site,
habitation nearby, sensitive receptors, if any.
no. 103 for ground level
concentration of pollutants from the
stack emissions (Proposed).
The project is not located on hilly
terrain so AQIP Modelling is not
applicable.
Refer Chapter 5, Table 5-3, Page no.
103 for cumulative impact of all
sources of emissions on AAQ. The
baseline study shows emission due to
existing stacks
Refer Chapter 5, Section 5.3.3, on
page no. 103 for details of the model
used.
Refer Chapter 5, Figure 5-1 to Figure
5-3, Page no. 105 to 107 for
modeling and air quality contours of
PM, Sox & Nox respectively for
proposed project.
II Water Quality modeling – in case, if the effluent is
proposed to be discharged in to the local drain,
then Water Quality Modeling study should be
conducted for the drain water taking into
consideration the upstream and downstream
quality of water of the drain.
Not Applicable
III Impact of the transport of the raw materials and
end products on the surrounding environment
shall be assessed and provided.
In this regard, options for transport of raw
materials and finished products and wastes (large
quantities) by rail or rail cum road transport or
conveyor-cum-rail transport shall be examined.
Refer Chapter 5, Section 5.3.2.1 (ii)
on page no.100 for impact of
transportation of raw material and
products.
Refer Chapter 3, Section 3.3, Table
3-3 on page no. 42 for mode of
transportation for raw material and
finished products.
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IV A note on treatment of wastewater from different
plant operations, extent recycled and reused for
different purposes shall be included. Complete
scheme of effluent treatment. Characteristics of
untreated and treated effluent to meet the
prescribed standards of discharge under E (P)
Rules.
The project is Zero Liquid discharge
Refer Chapter 5, Section 5.5, on page
no.111 to 113 for Treatment scheme
of effluent (waste water) generated.
V Details of stack emission and action plan for
control of emissions to meet standards.
Refer Chapter 5, Table 5-2, on page
no.102 for details of stack emission.
Refer Chapter 6, Section 6.3 on page
no.138 for action plan for control of
emissions.
VI Measures for fugitive emission control
Refer Chapter 6, Section 6.3.2 on
page no. 139 for action plan for
control of fugitive emissions.
VII Details of hazardous waste generation and their
storage, utilization and disposal.
Copies of MOU regarding utilization of solid and
hazardous waste shall also be included.
EMP shall include the concept of waste-
minimization, recycle/reuse/recover techniques,
Energy conservation, and natural resource
conservation.
Refer Chapter 3, Section 3.10, Page
55 for hazardous waste generation
and disposal plan.
Refer Annexure 4, on page no. A-31
for MoU regarding utilization of fly
ash.
Refer Chapter 6, on page no.137 for
detailed EMP.
VIII Proper utilization of fly ash shall be ensured as
per Fly Ash Notification, 2009. A detailed plan of
action shall be provided.
Refer Chapter 6, Section 6.6.1, on
page no.146 for detailed fly ash
management plan.
Refer Annexure 4, on page no. A-31
for MoU regarding utilization of fly
ash.
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IX Action plan for the green belt development plan in
33 % area i.e. land with not less than 1,500 trees
per ha. Giving details of species, width of
plantation, planning schedule etc. shall be
included. The green belt shall be around the
project boundary and a scheme for greening of
the roads used for the project shall also be
incorporated.
Refer Chapter 6, Section 6.3.3, on
page no.139 for Action plan for green
belt development plan.
X Action plan for rainwater harvesting measures at
plant site shall be submitted to harvest rainwater
from the roof tops and storm water drains to
recharge the ground water and also to use for the
various activities at the project site to conserve
fresh water and reduce the water requirement
from other sources.
Refer Chapter 6, Section 6.5.2 on
page no.144 for Action plan for
rainwater harvesting.
XI Total capital cost and recurring cost/annum for
environmental pollution control measures shall be
included.
Refer Chapter 6, Section 6.8.1 on
page no.149 for Total capital cost for
environmental pollution control
measures.
XII Action plan for post-project environmental
monitoring shall be submitted.
Refer Chapter 7 on page no.150 for
post-project environmental
monitoring.
XIII Onsite and Offsite Disaster (natural and Man-
made) Preparedness and Emergency Management
Plan including Risk Assessment and damage
control. Disaster Management plan should be
linked with District Disaster Management Plan.
Refer Annexure 13, on page no. A-
131 for detailed Risk Assessment and
Disaster Management Plan.
8 Occupational health
I Details of existing Occupational & Safety Hazards.
What are the exposure levels of above mentioned
hazards and whether they are within Permissible
Exposure level (PEL). If these are not within PEL,
what measures the company has adopted to keep
them within PEL so that health of the workers can
be preserved,
Refer Annexure 13, on page no. A-
131 for detailed Risk Assessment and
Disaster Management Plan.
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II Details of exposure specific health status
evaluation of worker. If the workers’ health is
being evaluated by pre designed format, chest x
rays, Audiometry, Spirometry, Vision testing (Far
& Near vision, colour vision and any other ocular
defect) ECG, during pre placement and periodical
examinations give the details of the same. Details
regarding last month analyzed data of
abovementioned parameters as per age, sex,
duration of exposure and department wise.
Regular Health check up of workers
in existing unit is done and records
are maintained as per Factory Act.
III Annual report of heath status of workers with
special reference to Occupational Health and
Safety.
It is been conducted as per Factory
Act.
IV Plan and fund allocation to ensure the
occupational health & safety of all contract and
casual workers.
Refer Chapter 6, Section 6.8.1 on
page no.149 for Total capital cost for
occupational health & safety.
9 Corporate Environment Policy
I Does the company have a well laid down
Environment Policy approved by its Board of
Directors? If so, it may be detailed in the EIA
report.
Refer Annexure 6, on page no. A-42
for HSE Policy.
II Does the Environment Policy prescribe for
standard operating process / procedures to bring
into focus any infringement / deviation / violation
of the environmental or forest norms / conditions?
If so, it may be detailed in the EIA.
Refer Annexure 6, on page no. A-42
for HSE Policy.
III What is the hierarchical system or Administrative
order of the company to deal with the
environmental issues and for ensuring compliance
with the environmental clearance conditions?
Details of this system may be given.
Refer Chapter 6, Section 6.8, on page
no. 147 for environment
management cell
IV Does the company have system of reporting of
non compliances / violations of environmental
norms to the Board of Directors of the company
and / or shareholders or stakeholders at large?
Refer Chapter 6, Section 6.8, on page
no. 147 for environment
management cell
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This reporting mechanism shall be detailed in the
EIA report
10 Details regarding infrastructure facilities such as
sanitation, fuel, restroom etc. to be provided to
the labour force during construction as well as to
the casual workers including truck drivers during
operation phase.
As the proposed project is in the
existing industrial premises, all these
facilities are readily available.
11 Enterprise Social Commitment (ESC)
I Adequate funds (at least 2.5 % of the project
cost) shall be earmarked towards the Enterprise
Social Commitment based on Public Hearing
issues and item-wise details along with time
bound action plan shall be included. Socio-
economic development activities need to be
elaborated upon.
Refer Chapter 8, on page no. 152 for
existing and future Socio-economic
development activities &
employment.
12 Any litigation pending against the project and/or
any direction/order passed by any Court of Law
against the project, if so, details thereof shall also
be included. Has the unit received any notice
under the Section 5 of Environment (Protection)
Act, 1986 or relevant Sections of Air and Water
Acts? If so, details thereof and compliance/ATR to
the notice(s) and present status of the case.
Not Applicable.
13 ‘A tabular chart with index for point wise
compliance of above TORs.
Refer Chapter 2, Table 2-7, on page
no.26.
14 The TORs prescribed shall be valid for a period of
three years for submission of the EIAEMP reports
along with Public Hearing Proceedings (wherever
stipulated).
Noted.
ADDITIONAL TORS FOR INTEGRATED STEEL PLANT
1 Iron ore/coal linkage documents along with the
status of environmental clearance of iron ore and
coal mines
Refer Annexure 3, on page no. A-28
for Iron ore and coal linkage
documents.
2 Quantum of production of coal and iron ore from
coal & iron ore mines and the projects they cater
Refer chapter 2, Table 3-3 Page no.
42 for mode of transportation of coal
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to. Mode of transportation to the plant and its
impact
from mines to Project site.
3 For Large ISPs, a 3-D view i.e. DEM (Digital
Elevation Model) for the area in 10 km radius
from the proposal site. MRL details of project site
and RL of nearby sources of water shall be
indicated.
Refer Annexure 14, on page no. A-
178 for detailed LU Study.
4 Recent land-use map based on satellite imagery.
High-resolution satellite image data having 1m-
5m spatial resolution like quickbird, Ikonos, IRS
P-6 pan sharpened etc. for the 10 Km radius area
from proposed site. The same shall be used for
land used/land-cover Mapping of the area.
Refer Chapter 4, figure 4.6 on Page
no.80 for 10 Km radius land use map
of proposed site.
5 PM(PM10 and PM2.5) present in the ambient air
must be analysed for source analysis – natural
dust/RSPM generated from plant operations (trace
elements) of PM10 to be carried over
Refer Chapter 4, Table 4-5 on page
no.61 for Various air pollutants
present in the ambient air.
6 All stock piles will have to be on top of a stable
liner to avoid leaching of materials to ground
water.
Not Applicable.
7 Plan for the implementation of the
recommendations made for the steel plants in the
CREP guidelines.
Refer Annexure 11, on page no. A-
100 for CREP Guideline Compliance.
8 Plan for slag utilization Refer Chapter 3, Table 3-14, Page
no. 55 for Slag generation and
disposal plan.
9 Plan for utilization of energy in off gases (coke
oven, blast furnace)
The energy will be used in WHRB
(Waste Heat Recovery Boiler)
10 System of coke quenching adopted with
justification.
Not Applicable.
11 Trace metals Mercury, arsenic and fluoride
emissions in the raw material.
Refer Chapter 3, Table 3-5 on page
no. 43 for raw material analysis
report.
12 Trace metals in waste material especially slag. Refer Chapter 5, Table 5-8, on page
no. 113 for slag analysis report.
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13 Trace metals in water There is not any trace metals
reported in water analysis.
2.11.3 Structure of EIA Report
This report is organized into nine sections:
Table 2-8: Structure of EIA Report
Sr. no. EIA structure Content
1 Project Summary Brief summary of project report
2 Introduction Purpose of the report
Identification of project & project proponent
Brief description of nature, size, location of the project and
its importance to the country, region
Scope of the study – details of regulatory scoping carried
out (As per Terms of Reference)
3 Project Description Depicts the details of the proposed project, auxiliary and
supporting facilities. It includes technology and process
description
4 Description of
Environment
Baseline environmental conditions in the vicinity of the
project site and within 10 Km radius of the project. Data
pertaining to the ambient air quality, surface and ground
water quality, soil quality, land-use pattern, flora – fauna
study and socioeconomic environment has been presented
5 Anticipated
environmental impacts
and mitigation measures
Predicted environmental impacts due to construction and
operational phases of the proposed sponge iron, steel
billets & power plant. Air quality modeling results and
minimum required stack heights, water requirement -
wastewater generation and solid and hazardous waste
handling requirements have been discussed. In addition to
this the likely residual impacts on the ecological and
biological environment and socioeconomic aspects have
been analyzed
6 Environment
Management Plan
Various environmental management plans. Various
resources conservation and recycling opportunities has
been discussed
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Sr. no. EIA structure Content
7 Environment Monitoring
Program
Technical aspects of monitoring the effectiveness of
mitigation measures (incl. frequency, location, data
analysis, reporting schedules, detailed budget)
8 Project Benefits Improvements in the physical infrastructure
Improvements in the social infrastructure
Employment potential – skilled; semi-skilled and unskilled
Other tangible benefits
9 Disclosure of Consultant The details of the Consultants engaged.
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Chapter 3 Process Description
3 PROCESS DESCRIPTION
3.1 PRODUCT DETAILS
ASR Multimetals Pvt Ltd. had set up an integrated steel plant at Village: Chhadawada,
Taluka: Bhachau, District: Kutch, Gujarat for manufacture of Sponge iron, Re-Rolled Steel
Products of MS, Steel billets, M.S Bars, Miss Rolled Bars and captive power plant. Depending
on the demand supply gap there was a need of additional quantity of these products. The
Company has hence applied for expansion for following products as mentioned in Table 3-1.
Table 3-1: Product Details
Name of Products /By
Products & Intermediate
Products
Existing
quantity
Proposed
quantity
MT/month
Total quantity
MT/month
MS (MILD STEEL) Rods 5000 MT/Month 24000 MT/Month
36000 MT/Month
MS (MILD STEEL) Wires 2500 MT/Month
MS (MILD STEEL) Flats 2500 MT/Month
Re-Rolled Steel Products of
MS (i.e. Channels, Angles
Bars, Rounds, Sections &
Profiles etc.)
2000 MT/Month
Steel Billets / Ingots (Semi
Finished Products)
12333
MT/Month
24000 MT/Month
(Along with Pre
heater & LRF)
36333 MT/Month
Sponge Iron 5500 MT/Month 15000 MT/Month 20500 MT/Month
Power from AFBC Boiler
(Coal Base)
4 MW 17 MW 21 MW
Power from WHRB (Waste
Heat Gases from Rotary Kiln)
4 MW 8 MW 12 MW
3.2 EQUIPMENT DETAILS
The list of equipment to be installed as a part of expansion project with the existing list is as
mentioned in Table 3-2.
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Table 3-2: Equipment details
Product Equipment Existing equipment Proposed equipment Total
Sponge Iron Rotary kiln 2x100 MT 2x250MT 20500 MT/ Month
Steel Billets Induction furnace 3 Nos. 2x 30MT 36333 MT/ Month
Rolling Mill
Products
Rolling Mill 12000 MT/Month 24000 MT/Month 36000 MT/ Month
Power Plant AFBC Boiler 4 MW 17 MW 21 MW
Power plant WHRB 4 MW 8 MW 12 MW
3.3 RAW MATERIAL DETAILS
Raw Material for the proposed expansion project & existing project is as mentioned in Table
3-3.
Table 3-3: Raw material Details
Name of raw
material
Existing
quantity
MT/month
Proposed
Quantity,
MT/month
Total
Quantity,
MT/month
Source Mode of
transport
(road, rail,
sea)
Sponge Iron/
Hot Briquetted
iron (HBI)
7500
MT/Month
15000
MT/Month
22500
MT/Month
Local/Imported Road / Sea
Scrap 8500
MT/Month
17000
MT/Month
25500
MT/Month
Indonesia & South
Africa (Imported)
Road / Sea
Steel Billets /
Ingots
13000
MT/Month
26000
MT/Month
39000
MT/Month
Local/Imported Road
Iron Ore/
pellets
8800
MT/Month
24000
MT/Month
32800
MT/Month
Jindal Saw Limited
imported/domestic
Road / Sea
Coal for
Sponge
6600
MT/Month
18000
MT/Month
24600
MT/Month
Indonesia & South
Africa (Imported)
Road / Sea
Lime Stone for
Sponge
220
MT/Month
600 MT/Month 820
MT/Month
Domestic /local Road / Sea
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Dolomite for
Sponge
200
MT/Month
500 MT/Month 700
MT/Month
Domestic /local Road / Sea
HSD 30 Litre/day 200 Litre/day 230
Litre/day
Local Market Road / Sea
FO 1000
Litre/day
2000 Litre/day 3000
Litre/day
Local Market Road / Sea
Raw material consumption for power plant due to proposed amendment is as mentioned in
Table 3-4.
Table 3-4: Raw Material Details for power plant
Name of raw
material
Existing Quantity
MT/month
Proposed Quantity,
MT/month
Total Quantity,
MT/month
Source Mode of transport
(road, rail, sea etc)
Coal for CPP 1700 MT/Month 7200 MT/ Month
8900 MT/Month
Indonesia & South Africa (Imported)
Road / Sea
Char Coal for CPP
1300MT/Month 5600 MT/ Month
6900 MT/Month
In House Production
Conveyor / Truck
Coal used will have gross calorific value ranging from 5500 Kcal/ kg whereas that of coal
char shall be around 2500 Kcal/kg. The Coal allocation detail is attached as Annexure 3.
The detail analysis report of imported coal and coal char is given in Table 3-5.
Table 3-5: Coal and Coal Char analysis results
Sr.
No.
Constituent Imported Coal
for Sponge
Iron
Imported Coal
for Captive
Power Plant
Coal Char to be
used in CPP
1 Carbon (%) 50 % Min 50 % Min 28 – 30 %
2 Sulphur (%)(0.55) 0.1 % max 0.1 % max 0.55 % max
3 Moisture Content (%) 7.3 % max 7.3 % max -
4 Ash (%) 20.0 % max 20.0 % max 35 - 45.0 % max
5 Gross Calorific Value :
Kcal/kg (ADV )
5500 Kcal/kg 5500 Kcal/kg 2500 Kcal/kg
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3.4 PROCESS DESCRIPTION
3.4.1 Sponge iron plant
The production process of sponge iron using S/L process involves four steps namely;
I. Raw material preparation plant: The raw material preparation plant consists of
crushers and screens through which the seized material required for process is
prepared. Normally, jaw crushers are used for iron ore crushing and roll or impact
crushers for coal. The feeding for the crushers are done through the conveyors and
vibrating feeders.
II. Stock house: The stock house consists of the raw material storage bins; which store
material up to 24 hours plant requirement. There are four bins one each for iron ore,
feed coal, limestone and injection coal. The raw materials are fed into a rotary kiln
through the volumetric/weigh feeders at a predetermined rate.
III. Reduction kiln: The processing of the materials consists mainly of kiln and cooler
system. The iron ore is pre-heated and reduced in a rotary kiln and passes to the
rotary cooler; where it gets cooled. The cooled material is then passes to the belt
conveyor; where the cooler discharge is fed to the product house conveyor. The
material is then led to the product separation circuit. An intermediate bin is provided
to take care of any eventualities occurring due to breakdown of the product
separation circuit.
IV. Product separation plant: in the product separation section, the sponge iron and the
coal-char (un-burnt coal) are separated. The cooler discharge material is screened to
different sizes, and fed into magnetic separator. The sponge iron is magnetic and
hence, it gets attracted to the magnet present in the magnetic separator and is
discharged to separate bins the dust in hot gases settles and gets cleaned.
Operation of Rotary Kiln and Cooler:
Rotary Kiln: Rotary kiln is 4.2 m in diameter and 70 m long; and it is positioned inclined at
an angle of 1.432o approximately. It is rotated by AC variable speed motor at a stem less
variable speed ranging from 0.2 to 1.0 RPM. Due to the inclination and the rotary motion in
kiln; the material moves from the feed end of the kiln to the discharge end in approximately
4.5 hours. The fine coal is blown from the discharge end to maintain the required
temperature profile. The material and the hot gases move in the counter current direction.
As a result, the iron ore gets preheated and gradually reduces by the time it reaches
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discharge end. The reduced material is then transferred to the rotary cooler via transfer
chute.
Rotary Cooler: The rotary cooler is 3.0 m in diameter and 42 m in length. It is also inclined
at 1.432o approximately. It rotates at 1.2 RPM. It is driven by AC motor. The water is
sprayed on top of shell; which cools the material inside the cooler indirectly. The material
reaches 80 oC temperatures approximately; and discharged by the double pendulum valve
to the conveyor. The double pendulum valve actually acts as a seal for prevention of
atmospheric air entering the rotary cooler. The material discharged on conveyor is then sent
for product separation system. Here, the material is segregated in different sizes and also
magnetic sponge iron is separated from non-magnetic char.
Figure 3-1: Process flow sheet of sponge iron plant
AFBC Power Plant
Steam Turbine Generator (STG) is the main assembly in the Power Plant. Coal char and
imported coal shall be used as main fuel in the STG. The steam generator shall be
Atmospheric Fluidized Bed Combustion (AFBC) type.
The boiler shall receive the water from specialized Water Treatment System; which shall
convert raw water to De-mineralized water suitable for the boiler application. The steam
generated at Boiler will be passed through the Turbine attached to it. In turbine Generator,
the steam will be used to rotate the blades of the turbine which in turn rotates the coupled
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generator shaft wounded with coil to magnetic field to produce electricity. The simplified
process flow diagram of the proposed power plant is attached herewith as Figure 3-2.
Figure 3-2: Flow Diagram of Steal based Turbo Generator Set
Part of the steam shall be used to regenerate the feed water temperature and thereby
improve the thermodynamic cycle efficiency. The steam after doing work in STG shall pass
through an Air Cooled condenser. This condensate so formed shall be pumped back via
vacuum pumps to the deaerator to remove the residual oxygen and then pumped to the
boiler using Boiler Feed Pump.
The coal/coal-char combustion will emit exhaust gases, which shall be passed through an
Electrostatic Precipitator, which will reduce the emission levels before passing out through
the chimney. The ash generated from the boiler shall be collected at Ash silo using dense
phase pneumatic ash handling system.
There will be other auxiliary systems which shall be used to like Compressed air system, air-
conditioning system, etc; detailed description of the same is given in subsequent sections.
3.4.2 Billets
The Induction Furnace will be installed for the production of Billets. The major raw material
will be scrap and sponge iron.
Induction arc Furnace
The induction arc furnace is the principle furnace type for the production of the Alloy Steels.
The primary application of the furnace is for the remelting of the steel scrap or sponge iron.
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Furnace Operations:
The induction arc furnace operates as a batch melting process producing batches of molten
steel known “heats”. The furnace operating cycle is called the tap-to-tap cycle and is made
up of the following operations:
Furnace charging
Melting
Refining
De-slagging
Tapping
Furnace turn-around
Refining in Ladle Refining Furnace.
Charging:
The charging material consisting of steel scrap & additives is loaded into the furnace in such
a way that large and high melting pieces stand parallel close to crucible while low melting
Components in the middle of the crucible.
Melting:
At the beginning of melting the furnace works for 5 to 10 minutes on low power until the
surge of current fed from the generator disappear. The furnace power is then brought up to
a maximum. The charge melts with the crucible held closed. When the charge approaches
the fluid stages than the solid pieces are pressed back with a crow bar. The furnace is then
loaded to its capacity by adding small size of scrap as soon as the charge melted. The slag
is formed to protect the metal from oxidation and to avoid reduce the melting loss. Excess
slag is skimmed off periodically. At the last, Ferro Manganese, Silicon Manganese & Ferro
Silicon is added to deoxidize the metal.
Ladle Refining Furnace:
Ladle refining furnace (LRFs) are used to desulfurize steels, remove other impurities and
hold the molten steel for casting operations. Without LRFs, higher tap temperatures are
normally required from steel making furnaces due to heat losses during refining during
conventional ladles. Costs of extended furnace time, refractory wear and power or fuel
consumption can all be reduced using LRFs to perform holding and refining. The ladle
refining furnace also acts as a buffer between the steel making furnace and continuous
caster, reducing casting costs and allowing greater flexibility in steel making operations.
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Ladle Refining Process:
Large ladles are used in most metal melting operations to transfer molten metal from
melting furnaces to refining or pouring stations. Ladle refining furnaces are basically ladles
with a heating source and lid. LRFs are used to reheat or maintain steel tapped from a steel
making furnace to a precise temperature and or refine it to exact chemical specifications.
Refining is performed by adding chemicals to remove impurities, adding ingredients which
enhance strength, and homogenizing the molten steel to achieve uniform characteristics.
LRFs provide an ideal reining station with precise temperature control, stirring action for
homogeneity, and ports for alloy addition and slag removal. Reheating steel in a ladle
refining furnace is typically accomplished by electric arc heating.
Figure 3-3: Process flow for manufacturing MS Billets
Raw material preparation Sponge Iron + Scraps (SIZING
& Processing)
Blending in Predetermined Ratio
Tapping of Molten Metal to Ladle
Transfer of molten metal in to LR Furnace
Refining Process in LRF
Melting in Induction furnace
Tapping of molten metal to Tundish
Casting in CONCAST machine
MS Billets
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3.4.3 TMT Bars
Hot Billet received from Steel Melt Shop are inspected and cut to length as per the size of
TMT to be rolled. These hot billets are directly sent to rolling mill via hot charging conveyor
and also provision for Pre-Heating the Billet is provided as optional.
The hot Billets are first passed through roughing mill and then go to Intermediate mill and
finally passed through Continuous Stands of finishing mill. These stands are with A.C. motor
for Variable speeds.
After several passes through the mills, the final rolled product passed through TMT Box
where it goes under Thermo Mechanical Treatment to improve upon Corrosion Resistance
and Mechanical properties like Yield Stress, Elongation, Bending, Tensile strength, etc.
After passing through TMT box, the bar is cut into lengths to accommodate on cooling bed.
After the bar is cooled it is cut into fix lengths as per requirement of market through
Shearing Machine.
At an interval of 1 hour a sample is drawn for checking weight per meter and mechanical
properties.
Figure 3-4: Process flow of TMT Bars
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3.5 MATERIAL BALANCE
The material balance for different products is mentioned in the Table 3-6, Table 3-7, Table
3-8 and Table 3-9.
3.5.1 Sponge Iron Plant
Table 3-6: Material Balance of Sponge Iron Plant
Input Output ITEM QUANTITY
(TPA) ITEM QUANTITY (TPA)
Iron Ore 288000 Sponge Iron 180000 Coal 216000 Dolochar 58400 Dolomite 6000 Ash/dust 74202
Limestone 7200 Wet Scrapper Sludge 9720 Accretion Slag 5139
Gases 464724 Gases 654463 Total 981924 Total 981924
3.5.2 Induction Furnace
Table 3-7: Material Balance of Induction Furnace
Input Output ITEM QUANTITY
(TPA) ITEM QUANTITY (TPA)
Sponge Iron 180000 Billet 288000 Scrap 204000 Slag 51100 Pig Iron + Ferro Alloys 26400 Gas Including dust 71300 Total 410400 Total 410400
3.5.3 Rolling Mill
Table 3-8: Material Balance of Rolling Mill
Input Output ITEM QUANTITY
(TPA) ITEM QUANTITY (TPA)
Billet 312000 TMT Bars 288000 Cut Scrap 20880 Mill Scale 3120
Total 312000 Total 312000
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3.5.4 Captive Power Plant
Table 3-9: Material Balance of Captive Power Plant
Input Output ITEM QUANTITY
(TPA) ITEM QUANTITY (TPA)
Coal 122616 Bed Ash 61309 Fly Ash & Dust 49046
Gases 1556000 Gases 1568260 Total 1678616 Total 1678616
3.6 WATER DETAILS FOR EXISTING PLANT AND PROPOSED PROJECT
3.6.1 Water Source
Required water for domestic and industrial purposes shall be obtained from the Gujarat
Water Infrastructure Limited (GWIL). Ground water or any other surface water will not be
utilized for any construction or industrial purposes. Water will be mainly used for cooling
purpose in steel & power plant.
The water allocation certificate for the project from GWIL is attached as annexure 5.
3.6.2 Water Consumption
Proposed water requirement is 1000 KLD. The water consumption for the project activities is
as mentioned in Table 3-10.
Table 3-10: Fresh Water Consumption Details
Purpose Quantity (KLD) Existing Proposed Total
Cooling 58 90 148
DM Water 124 300 424
Drinking 50 50 100
Process 240 400 640
Gardening and dust suppression (fresh water)
68 160 228
TOTAL 540 1000 1540
The water balance diagram for existing and proposed unit is as mentioned in Figure 3-5.
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Figure 3-5: Water balance diagram for existing and proposed project
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3.6.3 Waste water generation
After Expansion the expected waste water generation is 303 KLD. The details of waste water
generation from the project activities as mentioned in Table 3-11.
Table 3-11: Waste water Generation
Purpose Quantity (KLD) Disposal Plan
Existing Proposed Total
Cooling blow down (Sponge, Induction & Power Plant)
15 25 40 After neutralization will
be used for dust
suppression and green
belt development
Boiler blow down 69.44 168 237.44
D M Rejects 37.20 90 127.20
Domestic 20 20 40 Will be sent to septic
tank/ soak pit
TOTAL 141.64 303 444.64
404.64 KL/day of recycle water and 228 KL/day of fresh water will be used for green belt
development in area of 1,44,753 sq m.
The wastewater generated from domestic activity shall be treated through soak pit/septic
tank arrangement.
No wastewater generation from manufacturing process or any auxiliaries of the sponge iron
plant. Wastewater generated in form of boiler and cooling tower blow down from the power
plant shall be sent to neutralization Pit; from where the water shall be completely reused for
green belt development and dust suppression activities after neutralization. The project is
zero discharge plant.
3.7 POWER REQUIREMENT FOR EXISTING AND PROPOSED PLANT
Major part of Electricity requirement shall be sourced from captive power generation.
Remaining additional power requirement shall be met through from SEB. The total power
requirement for proposed project is as given in Table 3-12.
Table 3-12: Power Requirement
Source of Power Existing Power requirement
Proposed Power requirement
Total Power requirement
SEB /Grid 7.5 MW 6.0 MW 13.5 MW Captive Power Plant 8 MW 25 MW 33 MW DG Sets (Stand by) 500 KVA (1 no.) 1250 KVA (3 nos.) 4250 KVA
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3.8 STACKS DETAILS FOR EXISTING AND PROPOSED PROJECT
For abatement of air pollution, Air pollution control equipment has been installed at point
source in the existing plant. Now the company proposes for the expansion in existing
production capacity. The list of existing and proposed stack at the project site is as
mentioned in Table 3-13.
Table 3-13: Stack Details & APC Measures for existing & proposed
Existing project Proposed Expansion project
Stack
attached to
Stack
Height from
GL, meters
APC Stack attached
to
Stack Height
from GL,
meters
APC
AFBC Boiler 50 Meter Electro Static
Precipitator
AFBC Boiler 60.00 ESP
Rotary Kiln – I
& II 42.5 Meter
Electro Static
Precipitator
(Each)
Rotary Kiln-III &
IV
45.00 ESP
Induction
Furnace I to III 30 Meter
Multicyclone &
Ventury
Scrubber
Induction Furnace
I & II
30.00 Bag
filter
D.G. Set (Stand
By)
Cap. : 500 KVA
18 Meter
N/A
DG Set (3*1250
KVA)
(Standby)
17 m NA
3.9 SOLID WASTE GENERATION FOR EXISTING AND PROPOSED PROJECT
Solid waste generated as per environment clearance includes ash, char and slag. The solid
waste generation from the existing and proposed project activities is as mentioned in Table
3-14.
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Table 3-14: Solid waste generation
Type of Waste
Existing solid waste generation
Proposed expansion Solid waste generation
Total Solid waste generation
Management plan
Total Fly Ash
147 MT/Day 294 MT/Day 441 MT/Day
Will be sold to brick manufacturing unit or used as binding material for land filling
Coal Char 60 MT / Day 160 MT/Day 220 MT/Day
Will be reused as raw material within the plant for power generation through AFBC boiler / sold to registered dealers
Slag 70 MT/ Day 140 MT/Day 210 MT/Day Will be sold for road construction activity or used as binding material for land filling
MoU for Flyash reuse is attached as Annexure 4.
3.10 HAZARDOUS WASTE GENERATION FOR EXISTING AND PROPOSED PROJECT
Hazardous waste generated from the proposed unit is as mentioned in Table 3-15.
Table 3-15: Hazardous Waste generation
Waste
Generated
Existing
Quantity
Proposed
Expansion
Quantity
Total Hazardous
Waste generation
Quantity
Disposal Plan
Used Lube oil 36.365
MT/annum
75
MT/annum
111.365
MT/annum
Will be reused within plant
premises as lubrication oil/
sent to registered recycler.
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Chapter 4 Baseline Environment
4 BASELINE STUDY
This chapter comprises of the present environment scenario with respect to ambient air,
water, soil, noise, socio economic data, flora- fauna and land use/ land cover of the project
site and the surrounding villages/ area in 10 Km radius.
The parameters corresponding to air, water, soil and noise, land use and bio ecology are
individually discussed in the upcoming sections. The photographs of baseline monitoring are
attached as Annexure 9.
4.1 METEOROLOGY STUDY
Online meteorology station was set at the project site and accordingly wind rose was
prepared to determine the predominant wind direction.
The meteorology parameters studied at the project site are as below Table 4-1.
Table 4-1: Meteorology Data
Parameters Min-Max observed
Wind speed 0 m/s – 13 m/s
Predominant Wind direction South West to North East
Temperature 18 °C – 44 °C
Relative humidity 7 % – 93 %
The Average Long term rainfall for the period (1963-2002) is 364.30 mm and Average Short
term rainfall for the period (1998-2002) is 314.40 in mm.
Wind rose for the study area was prepared for study period of summer season (15 March
2015- 15 June 2015) and predominant wind direction observed was South West to North
East as shown in Figure 4-1.
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Figure 4-1: Wind Rose Diagram
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4.2 AMBIENT AIR QUALITY
4.2.1 Study period and area
The ambient air quality monitoring was carried out in 10 Km radius from the project site
during summer season for three months (15 March 2015 to 15 June 2015) as per the TOR
issued by MoEF.
4.2.2 Details of Parameter monitored and analysis method adopted
The parameters were selected based on the TOR issued by MoEF. The list of parameters
monitored with the analysis method is as mentioned in Table 4-2.
Table 4-2: Analysis methods
Parameter Frequency of monitoring
Analysis method Detection limit
Instrument Details
PM10 Twice in week for 24 hours
IS 5182 (Pt 23) 2.0 g/m3
Respirable Dust Sampler / Weigh Balance
PM2.5 Twice in week for 24 hours
--- 8.0 g/m3 Fine Particulate sampler/ Weigh Balance
SOx Twice in week for 24 hours
IS-5182(part 2):2001
EPA modified West and Gaeke method
1.6 g/m3 Respirable Dust Sampler / Spectrophotometer
NOx Twice in week for 24 hours
IS-5182(part 6):2006
Jacobs – Hochheiser method – First revision
5.5 g/m3 Respirable Dust Sampler / Spectrophotometer
CO Twice in week for 24 hours
GC Method
1000 g/m3 Gas Chromatography
4.2.3 Ambient Air quality Monitoring Locations
Total 8 monitoring locations were selected for the study of ambient air quality in the study
area. The locations were selected based on the TOR issued by MoEF and CPCB guidelines for
Ambient Air Quality Monitoring.
Table 4-3: Justification of monitoring locations
Description During study period
Predominant wind direction SW to NE Downwind locations Gharana & Lakhpat Upwind locations Chhadwada
Two downwind and one upwind direction were selected for air quality monitoring.
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Figure 4-2: Air Monitoring Locations on site map of study area
N
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The details of monitoring locations are as mentioned in the Table 4-4.
Table 4-4: Air Monitoring Locations
Sampling
Station
Code Distance w.
r. t centre of
project site
(km)
Direction
w. r. t
project
site
Justification
as per wind
regime
Latitude
Longitude
Project site (NE
Corner)
AQ1 0 NE Downwind 23°18'37.89"N 70°28'14.20"E
Lakhpat AQ2 5.8 N Crosswind 23°21'43.97"N 70°28'16.22"E
Vijpasar AQ3 5.3 NW Cross wind 23°20'28.29"N 70°25'50.79"E
Amaliyara AQ4 7.17 SE Cross wind 23°14'49.45"N 70°29'26.86"E
Chhadwada AQ5 3.5 SW Upwind 23°16'45.29"N 70°27'30.23"E
Vondh AQ6 7.20 W Cross wind 23°18'0.80"N 70°23'59.90"E
Gharana AQ7 6.75 NE Downwind 23°20'16.42"N 70°31'42.90"E
Samakhiyali AQ8 3.88 E Cross wind 23°18'14.11"N 70°30'27.90"E
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4.2.4 Baseline Data
The observed 24-hour Minimum, Maximum and average concentrations of PM10, PM2.5 SO2 & NOx have been presented in Table
4-5 below. The monitoring dates for three months at sampling locations are attached as annexure 9.
Table 4-5: Concentration of Various Pollutants
Parameters Observed
values,
µg/m3
SAMPLING LOCATIONS CPCB Standards
24 hourly,
µg/m3
AQ 1 AQ 2 AQ 3 AQ 4 AQ 5 AQ 6 AQ7 AQ8
PM10
Minimum 75 70 65 65 60 70 68 60 100
Maximum 99 94 94 98 90 93 94 93
Average 85 82 82 86 72 81 81 80
98 Percentile 98.50 93 94 97.5 89.5 92.5 94 93
PM2.5 Minimum 27 31 25 30 20 30 28 25 60
Maximum 55 50 52 55 46 52 48 48
Average 41 40 38 42 33 42 39 37
98 Percentile 55 50 51.52 55 46 52 47.54 48
SOx Minimum 11.2 3.37 7.47 3.73 7.47 3.73 7.47 11.2 80
Maximum 26.14 18.67 22.40 14.93 22.40 18.67 22.40 26.14
Average 19.24 11.19 14.62 9.56 15.38 11.35 14.31 18.67
98 Percentile 26.14 18.67 22.40 14.93 22.40 18.67 22.40 26.14
NOx Minimum 15.43 9.50 11.87 8.31 11.28 11.87 13.65 14.84 80
Maximum 29.68 22.56 27.31 20.18 30.87 24.34 31.46 35.02
Average 23.56 16.84 20.06 14.08 22.52 17.90 23.37 26.56
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98 Percentile 29.39 22.56 26.74 20.18 30.30 24.34 31.19 34.75
CO Minimum 869.64 892.52 903.96 938.29 892.52 869.64 869.64 846.75 ---
Maximum 1407.44 1533.31 1418.88 1304.45 1453.21 1464.65 1247.24 1304.45
Average 1129.72 1139.68 1113.59 1093.91 1179.04 1123.20 1071.31 1081.32
98 Percentile 1396.00 1445.00 1374.94 1282.48 1392.79 1398.74 1241.98 1293.93
PM10
Average Concentration of PM10 was found below the limits prescribed by CPCB, ranging between 72 μg/m3 to 86 μg/m3.
PM2.5
Average Concentration of PM2.5 was found below the limits prescribed by CPCB ranging between 33 μg/m3 to 42 μg/m3.
SOx
Average Concentration ranged between 9.56 μg/m3 to 19.24 μg/m3 & is below the CPCB limits.
NOx
Average Concentration ranged between 14.08 μg/m3 to 26.56 μg/m3 and is below the CPCB limits.
CO
Average Concentration ranged between 1071.31 μg/m3 to 1179.04 μg/m3.
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4.3 WATER ENVIRONMENT
4.3.1 Baseline study
For Assessment of Water quality 8 ground water sample Locations and 4 surface water
sample Locations were selected to evaluate the water quality around 10 Km radius from the
project site.
4.3.2 Study period and sampling frequency
The water samples were collected once in the study period during summer season as per
the TOR issued by MoEF.
4.3.3 Details of Parameter monitored and analysis method adopted
The analysis method followed for measuring different parameters to evaluate water quality
is given in the Table 4-6.
Table 4-6: Analysis method for water parameters
Sr No. Parameter Units Applicable standard method of analysis Detection
limit
1. Electrical conductivity Umho/c
m
IS – 3025 (Part –14) -1984
(1st Revision) (Reaffirmed - 1996)
1
2. pH -- Standard Methods – APHA 22nd Ed. 4500
pH. 4-91. IS – 3025 (Part –11) -1983
(First Revision) (Reaffirmed -2002)
1
3. Nitrite (NO2) mg/l IS- 3025 ( Part – 34 – 4 ) 0.1
4. Nitrate (NO3) mg/l IS – 3025( Part – 34) 1988
Chromo tropic Acid method
0.1
5. Phosphorus as
phosphate
mg/l Standard Methods – APHA 22nd Ed. 4500 P
.D.4- 154.
0.02
6. Potassium mg/l Standard Methods – APHA 22ND ED 3500 –
K 21st Ed B. 3 -87.
2
7. Calcium (Ca) mg/l Standard Methods – APHA 22nd Ed 3500
Ca – B. 3 – 67.
2.0
8. Magnesium (Mg) mg/l Standard Methods – APHA 22nd Ed 3500 –
Mg - B. 3 – 84 Calculation Method
2.0
9. Carbonate (CO3) mg/l IS – 3025 (Part –51) -2001- Calculation 5
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Sr No. Parameter Units Applicable standard method of analysis Detection
Method
10. Bicarbonates (HCO3) mg/l IS – 3025 (Part –51) -2001- Calculation
Method
5
11. Hardness as Ca CO3 mg/l Standard Methods – APHA 22nd Ed. 2340
C. 2- 44
2
12. Alkalinity mg/l IS – 3025 (Part –23) -1986
(1st Revision) (Reaffirmed - 1998)
5
13. Chlorides (Cl) mg/l Standard Methods – APHA 22nd Ed. 4500 Cl.
B. 4 –72. IS – 3025 (Part –32) -1988
(Reaffirmed - 1999)
1
14. Sulphate (SO4) mg/l Standard Methods – APHA 22nd Ed 4500 E.
4- 190
2
15. COD mg/l Standard Methods – APHA 22nd Ed. 5220. B.
5- 19. Open Reflux Method
2
16. Fluoride mg/l APHA 22ND ED, 4500-F-, D, 4-87 SPADNS
Method.
0.05
17. Boron mg/l Standard Method: APHA 22ND ED
4500 B., Pg no: 4-25.
0.01
18. TDS mg/l Standard Methods – APHA 22nd Ed. 2540 C.
2- 65. IS – 3025 (Part – 16) -1984 (1st
Revision) (Reaffirmed -1996)
4
19. BOD (3 days) mg/l IS – 3025 (Part –44) -1993
(1st Revision)(Reaffirmed -1999)
BOD 3- days at 27 C.
4.0
20. Sodium mg/l Standard Methods – APHA 22nd ED 3500
- Na. B. 3 -97.
2.0
21. TON mg/l Standard Methods – APHA 22nd Ed. 4500
– NH3 B & C. 4 – 131.
--
22. Sodium absorption
ration
mg/l Calculative Method -
23. Total coliforms, MPN/10
0 ml
APHA & AWWA 21st edition -
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4.3.4 Water Sampling Locations
Water sampling locations for ground and surface water samples are as mentioned in Table
4-7.
Table 4-7: Water Monitoring Locations
Monitoring
Location
Station
code
Source of
water
Distance from
site (km)
GROUND WATER
Project Site GW 1 Drinking water 0
Amaliyara GW 2 Bore well 7.23
Chhadwada GW 3 Bore well 4.12
Lakhpat GW 4 Bore well 5.70
Samakhiyali GW 5 Bore well 4.03
Gharana GW 6 Bore well 6.46
Vijpasar GW 7 Bore well 5.47
Vondh GW 8 Bore well 7.48
SURFACE WATER
Amaliyara SW 1 Village Pond 7.17
Chhadwada SW 2 Village Pond 3.55
Samakhiyali SW 3 Village Pond 3.61
Vondh SW 4 Village Pond 7.08
4.3.5 Ground Water Quality
The baseline ground water quality observed during the study period at the above locations
is as mentioned in Table 4-8.
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Table 4-8: Ground Water Quality
Sr
No.
Parameter Units GW 1 GW 2 GW 3 GW 4 GW 5 GW 6 GW 7 GW 8 Limit as per
IS:10500:2012 for
drinking water
Desirabl
e limit
Permissi
ble limit
1 Electrical conductivity µs/cm 260 250 260 350 250 270 290 3010 NS NS
2 pH Ph unit 7.50 7.77 7.88 7.77 7.93 7.89 7.60 7.22 6.5-8.5 No relax
3 Nitrite (NO2) mg/l ND ND ND ND ND ND ND ND NS NS
4 Nitrate (NO3) mg/l ND ND ND ND ND ND ND 31.0 45 No relax
5 Phosphorus as
phosphate
mg/l ND ND ND ND ND ND ND ND NS NS
6 Potassium mg/l ND ND ND ND ND ND ND 11.0 NS NS
7 Calcium (Ca) mg/l 36.07 28.06 36.07 36.07 34.47 36.07 39.28 184.37 75 200
8 Magnesium (Mg) mg/l 13.12 17.98 16.52 17.01 17.50 19.44 15.07 62.69 30 100
9 Carbonate (CO3) mg/l 24 40 40 40 60 40 20 ND NS NS
10 Bicarbonates (HCO3) mg/l 194 116 112 100 104 110 134 350 NS NS
11 Hardness mg/l 144 144 158 160 158 170 160 718 300 600
12 Alkalinity mg/l 170 156 152 140 164 150 154 350 200 600
13 Chlorides (Cl) mg/l 10.79 10.79 7.85 14.71 7.36 8.83 13.24 785 250 1000
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Sr
No.
Parameter Units GW 1 GW 2 GW 3 GW 4 GW 5 GW 6 GW 7 GW 8 Limit as per
IS:10500:2012 for
drinking water
Desirabl
e limit
Permissi
ble limit
14 Sulphate (SO4) mg/l 4.15 4.00 3.55 10.67 3.55 ND 5.33 62.22 200 400
15 COD mg/l ND ND ND ND ND ND ND ND NS NS
16 Fluoride mg/l 0.84 1.42 0.39 1.65 0.97 1.30 1.52 ND 1 1.5
17 Boron mg/l ND ND ND ND ND ND ND 0.11 0.5 1.0
18 TDS mg/l 150 150 160 270 160 170 174 1800 500 2000
NS: Not specified
Conclusion:
To evaluate the ground water quality in the study area seven bore wells were selected from nearby villages of the project site.
From the analytical result depicted in the Table 4-8, It is evident that, The Electrical conductivity varies from 250 µs/cm-3010
µs/cm, The chloride level varies from 7.36 mg/l -785 mg/l and the TDS Level varies from 150 mg/l -1800 mg/l.
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4.3.6 Surface Water Quality
The baseline surface water quality in the study area is as mentioned in Table 4-9.
Table 4-9: Surface Water Quality
Sr.
No
Parameter Units SW 1 SW 2 SW 3 SW 4
1 Electrical conductivity µs/cm 650 10,000 3650 1850
2 pH Ph unit 7.43 6.70 7.43 6.98
3 Nitrite (NO2) mg/l ND ND 1.76 0.13
4 Nitrate (NO3) mg/l 2.04 ND ND ND
5 Phosphorus as phosphate mg/l 1.39 2.31 1.28 0.95
6 Potassium mg/l 9.1 61.8 49.4 13.2
7 Calcium (Ca) mg/l 34.47 641.3 76.15 13.2
8 Magnesium (Mg) mg/l 17.50 252.7 80.19 17.01
9 Carbonate (CO3) mg/l ND ND ND ND
10 Bicarbonates (HCO3) mg/l 80 86 360 100
11 Hardness as CaCO3 mg/l 158 2640 520 160
12 Alkalinity mg/l 80 86 360 100
13 Chlorides (Cl) mg/l 132 3171 1005 589
14 Sulphate (SO4) mg/l 16.30 104 107 50.37
15 COD mg/l 20 160 100 40
16 Fluoride mg/l 0.21 ND 0.079 0.19
17 Boron mg/l 0.17 0.87 0.56 0.31
18 TDS mg/l 390 6000 2010 1060
19 BOD (3 days) mg/l ND 16 15 06
20 Sodium (Na+) mg/l 71.9 579 376 275
21 TON mg/l 0.8 0.82 0.75 0.6
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Sr.
No
Parameter Units SW 1 SW 2 SW 3 SW 4
22 Sodium absorption ration
- 2.48 4.90 7.14 9.52
23 Total coliforms, MPN/100 ml MPN/100 ml <2 4 4 <2
ND: Not Detected
Conclusion
To evaluate the Surface water quality in the study area four village ponds were selected
from nearby villages of the project site. From the analytical result depicted in the Table 4-9,
It is evident that, The Electrical conductivity varies from 650 µs/cm-10000 µs/cm, TDS
Level varies from 390 mg/l -6000 mg/l. Fluoride level Not Detected at village Chhadwada.
4.4 SOIL ENVIRONMENT
Soil samples were taken from the location within 10 Km radius of project site during
summer season as per the TOR issued by MoEF. Frequency of monitoring for soil was once
during the study period. The details of methodology used for soil sampling and analysis are
as given in Table 4-10.
Table 4-10: Methodology of soil sample analysis
Physical and
Chemical
Parameters
UNIT Details of
instrument used
for analysis
Applicable standard method for sample
analysis
Bulk Density gm/cm3 Weigh Balance DCPL/SO/ bulk Density/ 005 ( 15-01-2013)
Water Holding Capacity
% - Hand book of Methods in Environmental Studies
(Vol: 2- Air, Noise , Soil & overburden Analysis)
Porosity %
Grain Size distribution
Gravel % Sieve Shaker &
weigh Balance
Hand book of Methods in Environmental Studies(Vol: 2- Air, Noise , Soil & overburden Analysis)
Silt %
Sand %
Clay %
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Physical and
Chemical
Parameters
UNIT Details of
instrument used
for analysis
Applicable standard method for sample
analysis
Soil texture - - Hand book of Methods in Environmental Studies (Vol: 2- Air, Noise , Soil & overburden Analysis)
Soil Colour --- - -
pH --- pH Meter IS – 2720 ( Part – 26) – 1987 ( RA – 2011)
Conductivity µS/cm Conductivity Meter IS 14767 : 2000 (Reaff.2010)
Nitrogen as N % Distillation
Assembly IS 14684 : 1989 (Reaff.2000)
Phosphorus mg/kg UV-VIS
Spectrophotometer IS 10158 : 1982 (Reaff.2009)
Potassium as K mg/kg Flame phototmeter DCPL/SO/Na&K/016 ( 15 -01-2013)
Sodium as Na mg/kg Flame phototmeter DCPL/SO/Na&K/016 ( 15 -01-2013)
SAR - - Calculation Method
Calcium as Ca mg/kg - DCPL/SO/ Ca & Mg/ 017 ( 15-01-2013)
Nitrate as NO3-N
mg/kg UV-VIS Spectrophotometer
IS 14684 : 1989 (Reaff.2000)
Sulphate as SO4 mg/kg UV-VIS
Spectrophotometer IS – 2720 ( Part – XXVII) – 1977 ( RA – 2010)
Organic matter % - IS – 2720 (Part – 22) – 1972(RA -2010)
4.4.1 Soil Quality
The baseline Soil quality in the study area is as mentioned in Table 3-11.
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Table 4-11: Soil Quality
Physical and
Chemical Parameters
UNIT Sampling Station Code SQ 1
Ambaliyara SQ 2
Chadvada SQ 3
Lakpat SQ 4
Samkhayali SQ 5
Gharana SQ 6
Vijpasar SQ7
Vondh
Bulk Density gm/cm3 0.65 0.67 0.79 0.4 0.83 0.78 0.76
Water Holding Capacity
% 33.8 32 30 54 40 40 32
Porosity % 75 75 70 83 69 71 72 Grain Size distribution Granular % 05 03 06 04 04 07 06 Coarse % 17 20 19 18 21 29 28 Fine % 48 44 46 48 42 33 38 Medium % 22 26 24 22 26 22 21 Silt & Clay % 07 06 05 08 07 09 07 Soil texture ---
Sandy Loam Sandy Loam
Sandy Loam
Sandy Loam Sandy Loam
Sandy Loam
Sandy Loam
Soil Color --- Brown Brown yellow Black Brown Brown yellow pH Ph unit 7.53 7.35 7.90 7.98 7.72 7.57 7.81 Conductivity Umho/cm 10950 155 100 45600 273 168 127 Nitrogen as N
% 5.95 0.012 0.032 6.3 0.026 0.024 0.022
Phosphorus mg/kg 7.625 1.83 1.525 21.35 2.593 3.965 4.27 Potassium as K
mg/kg 94.5 50.25 30 572 52.5 37.5 22.5
Sodium as Na
mg/kg 3360.0 87 22.5 18300 37.5 45 22.5
SAR - 3.39 0.08 0.19 8.99 0.07 0.04 0.02 Calcium as Ca
mg/kg 400.8 200.4 200.4 1202.4 120.24 200.4 200.4
Nitrate as NO3-N
mg/kg 238 20.36 7.38 224 13.58 53.47 40.59
Sulphate as SO4
mg/kg 910 104.0 168 2041.0 228 335 293
Organic matter
% 1.2 0.46 1.2 8.7 0.51 0.46 0.46
Conclusion
The objectives of soil testing in the study area was, to estimate the available nutrient
status, reaction (acidic/alkaline) of a soil and to evaluate the fertility status of soils. For
evaluating soil quality of the study area, soil was collected from seven villages in the study
area with the help of auger/ spade. The composite soil samples were prepared at each
location.
Soil of the study area collected from the agriculture fields of all village were analyzed for the
17 critical parameters to evaluate the suitability of these soil with respect to its agriculture
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potential. Soil of this region is Sandy loam texture. Water holding capacity of this soil was
found to be 30-54%.
From the soil analysis it is evident that, the soil in the study area in most of the sampling
locations is in slightly alkaline pH (7.35-7.98). The Conductivity varies from 100 mho/cm–
45600 mho/cm.
Organic matter content in the soil lesser than 0.75% is considered as low, medium level of
organic matter in soil is between 0.75 -1% and above 1% is considered as high. In the
seven sampling locations selected, organic matter content were with lower organic matter
content found at Village Chadvada, gharana, vijpasar and Vondh.The higher organic matter
content was found at Village Ambaliyara,Lakhpat and Samakhiyali Village. The SAR ratio
varies from 0.02 – 8.99.
The nutrient availability of the soil is quite high in this region, which may be due to the
excessive fertilizer use, The available nitrogen content in the soil varies from 0.012 -6.3%.
Phosphorus content in the soil varies from 1.525 mg/kg -21.35 mg/kg .Potassium varies
from 1.525 mg/kg – 21.35 mg/kg.
4.5 NOISE ENVIRONMENT
The ambient noise environment consists of the total noise generated in the area at various
distance around the sampling locations. The noise level varies depending on the type of
activities carried out in the surrounding area. The baseline noise environment was studied
at the project site as well as the surrounding villages. The locations considered for the noise
monitoring are tabulated below along with the CPCB limits. The base line level of noise is as
given in the Table 4-12.
Table 4-12: Noise Quality in the study area
Area
code
Sampling
Station
Type of area Equivalent Noise Level
L(eq) in dB(A)
CPCB Limits
Day Times Night
Time
Day
time
Night
time
NQ 1 Project Site Industrial 70.9 57.5 75 70
NQ 2 Lakhpat Residential 57.5 37.2 55 45
NQ 3 Vijpasar Residential 60.9 46.0 55 45
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NQ 4 Amaliyara Residential 52.1 36.7 55 45
NQ 5 Chhadwada Residential 56.0 38.1 55 45
NQ 6 Vondh Residential 54.7 41.8 55 45
NQ 7 Gharana Residential 54.9 36.2 55 45
NQ 8 Samakhiyali Residential 62.7 51.0 55 45
Conclusion
Daytime time and Night time noise levels were observed was exceeding the limit in Lakhpat,
Vijpasar & samakhiyali due to Transportation activity of nearby Highway at the time of
Monitoring.
4.6 GEOLOGY OF STUDY AREA
Geologically the Bhachau taluka of Kachchh district shows rock formation ranging from
Jhurio formation of Mesozoic to Alluviums of Recent Quaternary age.
The Mesozoic rocks in Kachchh constitute one of the best developed and complete
successions in the world, and have preserved in them a valuable invertebrate faunal
assemblage.
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Figure 4-3: Geological Map of Bhachau, Kutch
The Tertiary formations fringe the entire southern rockiest strip of the mainland Kutch and
from a width of 10 to 20 Km. these also border Jurassic in Patcham, Khadir and Bela, and
Cretaceous and Jurassic in Wagad highland. These Tertiary formations (together with the
old Mesozoic) have been involved folding movements, which began in Miocene time and
continued interminably right up to the Pleistocene and even to Recent times. Rocks
belonging to quaternary age are represented by coarse sandy limestone identical to the
Miliolite of Saurashtra.
Table 4-13: Geological Succession of the surrounding area
Quaternary
Alluvium, Rann, blown sand tidal flats etc. Recent and
Sub recent
Porbandar Series
(15-20m)
Calcareous and Oolitic
Limestone with Miliolites.
Pleistocene
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Tertiary
Kankavati Series(370m)
Pink Grit with fossil wood.
Gray Sandstone and
clays.
Pliocene
(Equivalent to
Manchar).
Khari Series (350m)
Khari-Stage (340m) Shales and Siltstones Miocene
Waior Stage (10m) Creamy Marls and Oolites
Lakhpat Series (10-12m) Marls and Lime stones Oligocene
Berwali Series(130m) Eocene
Babia stage (85m)
Lime stones & Ochreous
and greenich clays.
Kirthar
Kakdi stage (45 m) Lime stones and shales Laki
Madh series
(30-40m)
Laterites, clays,
Sandstones
Paleocene
Dominant rocks occurring in the case study area on surface is alluvium of recent age. Well
inventory and cliff observation shows the thickness of alluvium ranges from 0.5 Mts. to 6
Mts. followed by patches of Laterite and Kankavati sandstone at some places.
The patchy sub surface occurrence of sandstone and Laterite have been observed even
within a distance of less than one km between vertically cut cliff of project site within
project area and litho log of an open well located north of the project site.
Table 4-14: Litho log of cut cliff of Project Site
Thickness (M)
Rock
0 – 1.2 Soil
1.2-12.30 Sandstone 4.7 HYDRO GEO MORPHOLOGY OF THE AREA
Area is composed of thin layer of alluvium underlain by sandstone of Wagad series. Patches
of laterite are also seen. Area is moderately elevated, gently dipping in southern direction,
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comparatively steep in other directions and devoid of any major drainage. The groundwater
flow is in all the directions. The sandstone is underlain by thick layer of compact sticky clay.
As per surface geological observations and composition of various strata clearly shows the
surface soil layer that constitutes of admixtures of clay, gravels and loosely alluvial strata
and has very low permeability. The underlying compact sticky clay layer has even no
permeability in comparison to alluvial admixtures at surface and at shallow depth.
4.8 DETAILS OF DRINAGE PATTERN
There is no major river passing through 1 Km radius. Kutch region has very less rainfall and
we have proposed to install rain conservation scheme within the plant premises.
4.9 TRAFFIC STUDY
4.9.1 Monitoring Locations
The survey work was carried out on 10-11 May.
As the project is industrial units and the impact of vehicular traffic is not frequently involved
in traffic pattern only 24 hour traffic survey is carried out at the below mentioned two
locations.
Table 4-15: Details of Traffic Monitoring Stations
Sr. No
Traffic particulars Survey station
1 National highway 8A/41 Bhachau to Samakhiyali Samakhiyali to Bhachau
Figure 4-4: Traffic count from Bhachau to Samakhiyali
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Conclusion (Traffic from Bhachau to Samakhiyali)
The total one way traffic is 13985 during 24 hours. The peak traffic of one way is 1567
vehicle between the 19:00 to 20:00.
The column chart shows different types of vehicles passing from Bhachau to Samakhiyali
during every hour of day.
Type of
vehicles
No. of Vehicle passing from survey
point from Bhachau to Samakhiyali
bicycle : 13
2 Wheeler : 1187
Auto : 491
Car : 3922
Truck/Bus : 4860
LCV : 3499
Other vehicles : 13
Figure 4-5: Traffic count from Samakhiyali to Bhachau
Conclusion (Traffic from Samakhiyali to Bhachau)
The total one way traffic is 15236 vehicles in 24 hour. The peak traffic of one way is 1511
vehicle between the 11:00 to 12:00.
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The column chart shows different types of vehicles passing from Samakhyali to Bhachau
every hour of day.
Type of vehicles
No. of Vehicle passing from survey
point from Samakhyali to Bhachau
bicycle : 4
2 Wheeler : 1640
Auto : 1136
Car : 4385
Truck/Bus : 4434
LCV : 3642
Other vehicles : 31
Existing road is sufficient to cater the additional load. Detail Traffic Survey report attached
as Annexure 8.
4.10 LAND USE STUDY A detailed Land use study was carried out within 10 km radius from center point of
expansion project of ASR Multimetals Pvt. Ltd. located at Chhadavada village of Bhachau
taluka of Kachchh district. Area covers total around 21 villages of Bhachau taluka with
habitation. Detailed Report for same is attached as Annexure 14.
4.10.1 Methodology
Study and collection of relevant documents and maps
Interpretation of satellite data
Field Survey / Ground Truthing
Generation of final land use and land cover map
Impact assessment and mitigation measure suggestions
4.10.2 Primary Data Collection
The land use/land cover mapping was carried out using digital satellite imagery procured
from NRSA, Hyderabad. Details of the satellite data are as given in below table
Table 4-16: Details of Satellite Data
Satellite Sensor Bands Year
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Resourcesat 2 (91-56 A) LISS IV 2,3,4 25th November, 2013
4.10.3 Secondary Data Collection
The ancillary data collected for the study were District planning series maps and Census
maps as base information for interpretation.
4.10.4 Land Use/ Cover Pattern of Study Area
The land use and land cover in the region comprises of five first level classes and Nine
second level classes as given in below Table 4-17.
Table 4-17: Classification Levels
S. No. First Level Classification Second Level Classification 1 Built-up Land or Habitation Residential / Commercial
Industrial 2 Agricultural Land Crop Land / Fallow land Plantation 3 Wastelands Barren land 4 Water Bodies Water body (Reservoir / Lakes /
Ponds / Tanks)
River bed 5 Vegetation Cover Scrub
Open vegetation
4.10.5 Area Statistics of Land Use/ Cover Classes
The area statistics of these classes are presented in Table 4-18. The major portion of the
study region is covered by agriculture, scrub and open vegetation respectively in descending
order of the area covered.
Table 4-18: Land use/cover Classes Area Statistics within 10 km Radius of Project
Site
Sr. No. Class Area (Ha.) Area (sq. km.) Area (%) 1. Habitation 473.01 4.73 1.51 2. Industrial Area 230.56 2.31 0.73 3. Agriculture Land 25783.74 257.84 82.11 4. Plantation 23.20 0.23 0.07 5. Barren Land 21.40 0.21 0.07 6. Water Body 272.63 2.73 0.87 7. River bed 180.73 1.81 0.58 8. Scrub 2237.54 22.38 7.13 9. Open Vegetation 2177.19 21.77 6.93
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Figure 4-6: Land use/Land cover Map of 10 km radius
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4.11 BIO ECOLOGY STUDY
The baseline study for the evaluation of the floral and faunal biodiversity of the terrestrial
environment of the study area was done within 10 km radius of proposed expansion project
of M/s ASR Multimetals Pvt. Ltd. near Chhadavada Village, Taluka Bhachau, and District
Kachchh.
4.11.1 Floral Diversity of Study Area
The objective of this floral inventory of the study area is to provide necessary information
on floristic structure in the study area for formulating effective management and
conservation measures. The climatic, edaphic and biotic variations with their complex
interrelationship and composition of species, which are adapted to these variations, have
resulted in different vegetation cover, characteristic of each region. The following account of
floral inventory has been, based on the field survey conducted for a short duration in the
December, 2015, is not very comprehensive data and is aimed only to give a general
pattern of vegetation of this region during the study period as a baseline data in absence of
available secondary data. Listing of the endangered, threatened and endemic species of
flora in a locality and drawing the attention to the occurrence of such species, would aid in
creating awareness amongst the local people as a whole to protect such species from
extinction, and to take necessary measures for their conservation. These type of floristic
study is an inventory for such purpose and hence a necessity. List of Floral diversity in the
study area is discussed in Annexure 12.
The tree species, herbs, shrubs, climbers and major crops, were documented during this
base line study.
Trees
The dominant trees in the study area were generally planted either as farmland plantation
or Homestead plantation or as road side plantation. Otherwise natural tree cover is very less
in this part of Kachchh District. Dominant tree species in the farmland was dominated
Prosopis cineraria (Khyigdo), Salvadora oleoides (Piludi), Salvadora persica ( Piludi) Acacia
nilotica (Bhaval), Azadirachta indica (Limbado) and Ailanthus excelsa (Aurdso), Homestead
plantation was dominated by, Azadirachta indica (Limbado), Mangifera indica (Keri),
Moringa oleifera (Sargavo ), and Salvadora oleoides (Piludi). Road side Plantations were
dominated by Peltophorum pterocarpum (Sonmukhi), Delonix regia (Gaulmor), Casuarina
equisetifolia (Sharu), Azadirachta indica (Limbado), Acacia nilotica (Baval), Prosopis
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cineraria (Khyigdo), Ficus benghalensis (Piplo), Pongamia pinnata (Karanj), Salvadora
oleoides (Piludi), and Ailanthus excelsa (Aurdso).
Detail list of trees in study area is given in bioecology report attached as Annexure 12.
Shrubs
Shrubs observed during the present survey are given in the Table-2 of the detailed
bioecology report attached as annexure 12. 26 shrub species belong to 17 families are
enumerated from the study area. The dominant shrub community in this area was
represented by, Prosopis juliflora (Gando baval), Calotropis procera, C. gigantea (Akado),
Leptadenia pyrotechnica(Khip/Ranser), Balanites aegyptiaca (Ingorio) Ipomoea fistulosa
(Nasarmo), and Lawsonia inermis (Mendhi)
Detail list of Shrubs in study area is given in bioecology report attached as Annexure 12.
Herbs
The herbs observed in the sampling plots, during the survey period, 38 species of herbs
belongs to 17 families were documented from the sampling plots laid in different habitats
within the study area.
Detail list of Herbs in study area is given in bioecology report attached as Annexure 12.
Climbers & Twiners
14 species of climbers/ twiners belongs to 6 families are recorded from the area
Detail list of Climbers & Twiners in study area is given in bioecology report attached as
Annexure 12.
Cultivated Plants in the study area
During the period of survey in December 2015, very cultivation was practiced in this region
with Ricinus communis L. (Castor), and and Gossypium herbaceum L. (Cotton). The other
remarkable observation in this area was that, the villagers started growing Cassia italica,
locally known as “Mindhi vavdi or Mindhi aval,or Pat Mindhi vaval” as an alternative crop
in agriculture fields of many part of the study area , especially at Rampar village, Lakhpat
village, Vijpasar village.
Detail list of cultivated plants in study area is given in bioecology report attached as
Annexure 12.
Major Crops: The major agricultural crops, practiced in this area during the monsoon
season are Mug (Viginia angularis (Willd), Jowar (Sorghum bicolor (L.). during winter
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season Ricinus communis L. (Castor), practiced while, Bajra (Pennisetum typhoides ) mainly
cultivated as fodder and The other minor crops practiced at isolated pockets are Makai (Zea
mays L) and Gossypium herbaceum L. (Cotton)
During summer few farmers are cultivating Bajra (Unadadnu Bajri) and Rajko as fodder
substitute.
Horticulture Practices and fruit grown
Plantation of Phoenix dactylifera (Khajur or Dates) were observed a few localities mainly at
Lakhpat village and Rampar village. Mango trees were seen in adjacent to the residential
area of almost all villages.
Rare and Endangered flora in the study area
Among the enumerated flora in the study area, none of them were assigned any threat
category, by RED data book of Indian Plants. (Nayar and Sastry, 1990) and Red list of
threatened Vascular plants (IUCN,2010, BSI, 2003)
Status of Forest and their category in the study area
No natural forest land was observed in the study area except few scattered scrub Forest
dominated by Acacia nelotica and Prosopis juliflora Rampar village
4.11.2 Faunal Biodiversity of Study Area
For the documentation of the faunal biodiversity of the study area with respect to birds,
reptiles, amphibians, and butterfly species, a baseline survey had been conducted in
December, 2015.
The most commonly spotted bird species of this area were; Cattle Egret, Pond Heron, Black
Ibis, Blue Rock Pigeon, Ring Dove etc. Few migrant species are spotted in the study area
are Demoiselle Crane and Ruff.
Rare and Endangered Fauna in Study Area
Among the sighted fauna no species are categorized in any threatened category of IUCN.
(2014).
Some of the sighted fauna were given protection by the Indian Wild Life (Protection) Act,
1972 by including them in different schedules. Among the birds in the study area, Pea fowl
(Pavo cristatus) is included in schedule I .of Wild life protection Act (1972), while many
other are included in schedule IV.
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Among the reptiles, Indian Mud or Flap shell Turtle (Lissemys punctate (Lacepede) is a
schedule -I reptile, while Indian Cobra (Naja naja), is provided protection as per Schedule-
II of Wild life protection act, (1972).
Among mammals; Common Mongoose (Herpestes edwardsi), is a schedule –II mammals.
Nilgai (Boselaphus tragocamelus) and Wild Boars (Sus scrofa Linnaeus) are provided
protection by incorporating them in schedule–III, Hares and five stripped squirrels are
included in schedule IV of Wild Life Protection act 1972.
Table 4-19: Species provided Protection as per Wild Life Protection Act 1972
Group Species Nearest village
Coordinates Number Schedule Wild Life
Protection act 1972.
Birds
Pea fowl (Pavo cristatus),
Rampar village pond premises
230 22’ 15.5” 700 26’ 26.7.”
7 females 10 males
Schedule I
Most of other birds Throughout the area
Schedule-IV
Reptiles
Indian Mud or Flap shell Turtle
(Lissemys punctate ( Lacepede)
In a village pond of
Vondhada Village
230 20’ 44.8” 700 25’ 55.6.”
4
Schedule I
Indian Cobra (Naja naja),
Secondary Schedule-II
Mammals
Common Mongoose (Herpestes edwardsi),
Lakhpat village
230 21’ 49.9” 700 28’ 12.3.”
1adult Schedule-II
Five striped Palm squirrel
(Funambulus pennanii
(Wroughton)
Many places
--
>10
Schedule-IV
Nilgai (Boselaphus tragocamelus)
Lakhpat
230 24’ 04.3” 700 28’ 10.5.”
1male 3 females
Schedule-III
Wild Boars (Sus scrofa Linnaeus
Secondary Schedule-III
Hare (Lepus sp.) Rampar 230 21’ 29.9”
700 25’ 33.4.”
1 Schedule-IV
= Not sighted but included as per the information provided by villagers, during the interaction with
them with pictorial presentation.
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4.12 SOCIO ECONOMIC DATA
Socio economic data are drawn from the primary sources like census and district statistical
hand book etc. We defined the frame work of socio economic environment in terms of the
following components:
1. Demographic characteristics which defines the human development level of the
village community
2. Economic characteristics which provides indicator of the economic development level
3. Social data matrix which provide the social composition of the community which
would reflect the socio cultural dimensions
The detailed Socio Economic Environment Study Report is attached as Annexure 15.
A detailed analysis will not only highlight the relevant issues but also would provide guiding
path of the development of the project area villages. The villages considered in the study
area are as mentioned in Table 4-20.
Table 4-20: List of villages cover in 10 Km Radius
Sr. no. Village name Sr. no. Village name
1 Chhadavada 12 Amaliyara
2 Jangi 13 Gharana
3 Laliana 14 Rajansar
4 Katariya Nava 15 Katariya Juna
5 Lakadiya 16 Shivlakha
6 Pasa 17 Vondhada
7 Rampar 18 Halra
8 Vijpasar 19 Vondh
9 Karmariya 20 Lakhpat
10 Samakhiyari 21 Adhoi
(Pasakayara) 11 Piprapati
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4.12.1 Data Findings based on FGD and Village Profile
In this part of the report all the findings have been elaborated in detail, and the data area
gathered from the community at grass root level in major three villages of Study area based
on their proximity to Project Site.
4.12.1.1 Health
Health is a state of complete physical, mental and social well being, and not merely the
absence of disease or infirmity. During the discussion on this topic community shared many
things related to health, looking to these 3 villages they are not in interior part of the rural
area so generally people are aware about the health care.
Table 4-21:Availability of Health facilities
Name of the Villages
Health Centers
PHC Sub
Centre Private Clinics
Govt. Hospital
RMP Doctors
Traditional Healers
Home Remedies
Samakhiyali YES YES YES NA NA NA NA Chhadawada NA NA YES NA NA NA NA Vijpasr NA NA Yes NA NA NA NA Source: Data based on data collection (NA-Not Available)
During the field visit we came to know that out of 3 villages, only 1 village having Public
Health center, rest of the villages do not have this facility. From all this villages, community
is going to Samakhiyali for the treatment. Some of the special information mentioned
below:
In some of the villages like Chhadavada and Vijpasar of Bhachau taluka do not have
any PHC or sub center in the village, so they are going to nearby village or taluka
level for the health treatment. Needs to provide them some basic health facility on
monthly or weekly basis.
Mainly in all the villages they are facing problem at the time of delivery, but 108
helping a lot.
4.12.1.2 Education
Education means to discover new things which we don't know about and increase our
knowledge. An educated person can contribute to the society. From the interaction with the
community we came to know that education level in the village is comparatively good,
means more than 75% people are literate. There are some education facilities which are
listed in Table 4-22.
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Table 4-22: Availability of Education facilities
No Name of
the Villages
Education Facilities Anganv
adi Primary
Upper Primary
High School
Intermediary College
1 Samakhiyali YES YES YES NA NA NA 2 Chhadawada YES YES NA NA NA NA 4 Vijpasr YES YES YES NA NA NA
Source: Secondary Data, data collection (NA-Not Available)
Aganwadi is basic amenities at village level, as per the Govt. rule almost each and every
village having Aganwadi, in this all three village having aganwadi which needs some
beautification and up gradation for better services.
Government is doing many efforts to promote primary education. In the village people
mindset have been changed compare to past, parents are taking interest in their children
education. Table 4-22 shows available education facilities in the village.
All three villages having primary school
Two villages Samkhyali and Vijpasar having upper primary school.
Students are going to Bhachau or Adipur for the higher studies.
Limited teachers are the basic problem in all the schools
Quality of infrastructure is also one of the weak point
School Management Committee should be strengthen.
4.12.1.3 Livelihood
A “livelihood” is defined as one’s “means of support or subsistence” or the activities that
economically support a person and his/her family. We are focused on providing
opportunities for the working poor (in various occupations) to increase their income-
generating capacity. In all the villages community is associated with various occupations,
the details mentioned in Table 4-23.
Table 4-23: Occupation Details
No Name of the Villages Agriculture Agriculture
Labor
Working as wage labor
in other sectors
Private Job
1 Samakhiyali 60% 20% 15% 5% 2 Chhadawada 50% 20% 20% 10% 3 Vijpasar 70% 20% 5% 5% Source: secondary data, data collection
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Data shows that majority of the population are associated with agriculture related activities.
Out of 12 months people are getting work more than 4 months in the agriculture.
The most important and good thing is there is no wage discrimination between male and
female.
Rs. 150-200/day they are getting from the agriculture work, while in private sector they are
getting Rs. 250-300/day based on the skill of the worker.
Only one village is name of the lakhpat having good irrigation facility because of that people
are associated with the agriculture for the entire year.
Majority of the farmers (90%) are small farmers, rest of the big farmers having more than 5
acre land.
4.12.1.4 Animal Husbandry
A large number of farmers in India depend on animal husbandry for their livelihood. In
addition to supplying milk, meat, eggs, wool and hides, animals, mainly bullocks, are the
major source of power for both farmers and dryers.
Almost 50% to 60% villagers are selling milk at the dairy in the village. All three village
having facility of pvt. Dairy, only vijpasar don’t have any dairy.
4.12.1.5 Women Empowerment
Only Samakhiyali village having Self Help Groups and women are doing saving activities in
the groups but not associated with any type of income generation work.
Skill development, absence of advanced knowledge and information are the basic problems
for the women empowerment.
4.12.1.6 Benefits of the government schemes
Government Schemes plays important roles in development of society. During interaction
with community and PRI members we came to know that, in most of the villages’ people
received benefits of Indira Awas, Sardar Awas, Chiranjivi Yojna. While there is very less
awareness about sanitation in all the villages, approx only 5 to 15% villagers having
sanitation facility at their home.
4.12.1.7 Infrastructure facilities
Infrastructure is the most important contributors to the economy of the State.
Infrastructure is the subset of the infrastructure sector and plays a significant role in
generating revenue for the economy. During the study we have received information about
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facilities available in the villages, which are listed Table 4-24.
Table 4-24: Facilities available
No Name of
the Villages
Facilities
Road (Nos) Internal road
Electricity
in HHs
Public Transportation in a day (Nos)
Pucca Katcha Mud Bus Share Auto
Other
1 Samakhiyali 52 3 NA 100% 100 250 NA 2 Chhadawada 6 2 2 95% NA 20 NA 3 Vijpasar 1 2 3 90% 1 2 NA
Source: Secondary data, data collection (NA-Not Available) Road facilities are most important in any village. While we talking about our study area,
from the table we can see that road facility is moderate in Samakhiyali. In other 2 village
(Chhadawada, Vijpasar) it is very poor.
While we talking about electricity, it is the basic facility of any households. In our study
area, we can see good scenario in all the villages. Frequency of the public transport is also
good in all the study villages except Chhadavada and Vijpasar.
Table 4-25: Common facilities
No Name of
the Villages
Facilities
PDS Panchayat/Sarpanch
Office Community
Hall SHG
Building TV
Room 1 Samakhiyali Available Available Available NA Available
2 Chhadavada Available Available NA NA NA
3 vijpasar Available Available NA NA NA
Source: Secondary data, data collection, (NA-Not Available) While we talking about common facilities in the villages, it is quite moderate in all the
villages except Samakhiyali. Panchayat CEO is one of the good concept, under CSR activity
it should be covered so village community will able to get hand holding support for
administration work.
4.12.1.8 Sanitation and Drinking water facilities
Sanitation generally refers to the provision of facilities and services for the safe disposal of
human urine and feces. Inadequate sanitation is a major cause of disease world-wide and
improving sanitation is known to have a significant beneficial impact on health both in
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households and across communities. The word 'sanitation' also refers to the maintenance of
hygienic conditions, through services such as garbage collection and wastewater disposal.
During the study we have received some information about availability of Sanitation and
Drinking water facilities which are listed Table 4-26.
Table 4-26: Facilities of Sanitation and Drinking water
No
Name of the
Villages
Facilities Sanitation Drinking Water
Individual HHs (%)
Common
Toilets
School Toilets
Market
Place
Overhead tanks
Hand Pump
Street/Pub
lic taps
Individual Connectio
ns
Underground tanks
Ponds
1 Samakhiyali
80% YES YES NA YES NA YES YES YES YES
2 Chhadawada
15% NA YES NA YES NA YES YES YES YES
3 Vijpasr 20% NA YES NA NA NA NA YES YES NA Source: Secondary data, data collection (NA-Not Available)
From the above mentioned data we can say that result about sanitation is very poor except
Samakhiyali village.
Government has launched the scheme for sanitation and gives subsidy for toilet
construction.
4.12.1.9 Source of fuel
During the visit we came to know that level of fuel source is very low in the study villages.
Very few HHs has LPG connection in every village. They are still using wood for cooking.
Table 4-27: Availability of fuel source
No
Name of the
Villages
Sources Sources Fuel Wood
LPG (%)
Bio-gas
Kerosene
Solar energy
Natural Forest
Mangrove Forest
1 Samakhiyali YES NA YES NA YES NA 2 Chhadawada YES
2% NA YES NA YES NA
4 Vijpasr YES 3%
NA YES NA YES NA
Source: Secondary data, data collection (NA-Not Available)
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4.12.2 Data Findings based on individual interaction and FGD with the community
members
4.12.2.1 CSR Activities
Company has done CSR activities in VONDH village, in this village they have provided basic
sanitation facilities to the community during FGD and individual interaction we found that
Vondh is not developed village only one aganwadi, one primary school and limited
infrastructure, literacy rates also not match with avg, country rate. Youth needs more
guidance on future development
Under CSR company has provided 12 individual, earlier they were facing many
problems, in winter or in rainy season it was difficult to go out for sanitation in open
area.
Under CSR activities Company is giving facility to provide fodder into Gaushala.
In Chadawada, company has built up protection wall on pond in 2015 which helps for
water management and also adding some infrastructure value.
4.12.3 Needs to be focused for the development
During the interaction with respondents research team has collected information about the bottlenecks of the development and major issue which are impede into development of the village.
Village specific needs are mentioned in Table 4-28.
Table 4-28: Village wise requirements
Values (%) Respondents Detail Samakhiyali Chhadavada
Vondh Vijpasr
Road 35.7 81.8 69.2 30.8 Drainage 14.3 18.2 30.8 30.8 Transportation 21.4 36.4 0 0 Loan 14.3 0 15.4 7.7 Government Help 14.3 0 23.1 0 Toilets 14.3 45.5 30.8 30.8 Housing 7.1 9.1 23.1 38.5 Street Light 7.1 36.4 23.7 7.7 Employment 14.3 27.3 7.7 0 Source: Secondary data, data collection
To know about the impact of the CSR activities and to know about community need FGD
were planned in all the villages. In this part of the report details have been mentioned.
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Village: Chhadavada
Health
In this village health facility is not good, people are going to Bhachau for the
treatment which is 14 Kms far from the village because of the health seeking
beahivour is very low in the community.
Education
Only Primary school available in this village. 75% people are literate, female literacy
level is comparatively low in the community (30-40%).
Girls are not allowed for higher education, parents are not allow their girls to go
outside of the village, also they are having mentality that why should we invest
money for girl education?
Livelihood
In the village majority of the population are associated with agriculture and animal
husbandry. 20%people are going to saltpan; people do not have any skill to do other
work. theyhave not received much benefit from the company for the livelihood, only
two people are getting job in the company.
Agriculture
People are taking two corps in a year; main crops are Guvar, Bajara and castor. Main
market is Bhacahu. Land is very dry in the village which is the major problem.
Animal Husbandry
People are not happy with current dairy structure, they are not getting good price of
the milk.
CSR activities
ET and Essar Company have provided some funds for the fodder of the Animals.
Village: Vondh
This is common for Scio ecomomic and impact of CSR activities. As per the study will cover
all the topics. In the cash of CSR impact theme wise before and after condition will be
asked.
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Health:
In the village Sub center is not available and PHC is far away 8 km in bhachau. ANM
is coming near samakhyali village so people are going to nearby village or taluka
(Bhachau) level for the health Treatment. Delivery time women are going to Bhachau
Private Hospitals.
Education
2 Primary schools available in this village. One is girl’s school (1 to 8 std.) and other
Boys School (1 to 8 std) and one high school available in this village.
Students are going to Samakhiyali or bhachau for the higher studies. Paretns are not
sending their girls for higher education because of transportation and also worried
for their safety.
Livelihood
Only agriculture and animal husbandry are the major options in the village.
The most important and good things is there is no wage discrimination between male
and female.
Rs 200- 250/day they are getting from the agriculture work. While in private sector
they are getting Rs 250 – 300/day based on the skill of the worker.
1 people are working with ASR Multimetals Limited for driving work
Animal Husbandry
Two Private dairies are available in this village. No any Government dairy available in
this village. vondh village members are not happy with private dairy structure, They
are not getting satisfactory price.
Women empowerment
This village doesn’t have any Self Help Groups.
CSR Activity
ASR Company has approved 2.5 lakhs for the construction of toilet for fodder of the
individual, from which they have credited 2.5 lakhs in the year of 2015.
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Village: Vijpasar
Health
Any one heth survic are not available in this village but only ANM is vailabel for
health services, basic treatment is providing to women and children. Male members
are going to samakhyali or Bhachau.
Education
Only Primary school available in this village. 80% people are literate. 20% people are
illiterate. Girds education for higher study and for high school is one of the sensitive
issue in the village, parents are not allow their girls to go out of the village for the
education, safety and financial conditions are major problems behind that.
Livelihood:
Mainly community is associated with agriculture work, 60% of the members having
their own land and others are doing agriculture labour in the village. Because of good
irrigation in the village people are taking three crops in the year.
4.12.4 Development activity plan
We proposed the appropriate development action plan to the welfare of the villages
community of project area villages i.e. Samakhiyali, Chhadawada & Vijpasar
During the field study, our research team had done interaction with respondent to identify
the development needs & the priorities to the villages.
Expected allocation of budget has also made clear in the prefeasibility report. Thus 2.5 crore
are available over a period of next five years to meet the priority needs of villages
communities, we may list out the following development activity with estimated allocation of
funds. The estimated allocation is Rs. 50 lacs/year.
Table 4-29: Development activity with estimated allocation of funds
Sr No.
Development Activities Maximum Allocation (Rs. Lakh)
Minimum Allocation (Rs. Lakh)
1 Employment & Income
generation through self help
groups
25 15
2 “Shauchalaya” construction 25 15
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3 Roads Maintenance & approach
Roads
10 05
4 Education Assistance to School 15 05
5 Health Awareness & Preventive
Action Support
15 05
6 Drainage Support Fund 10 05
Total Expected allocation 100.00 50.00
Implementation mechanism & the development activities could be suggested as follow,
i. Company will appoint responsible person with authority to co-ordinate the development activities.
ii. A small village community Representation committee may be formulated for effective participation of community & monitoring of works.
iii. An appropriate work plan is designed instead of casual demand driven activities.
iv. Regular quarterly meeting will be organized to monitor the works.
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Table 4-30 : Demographic Characters
Name of Villages No_HH TOT_P TOT_M TOT_F P_06 P_SC P_ST P_LIT M_LIT F_LIT P_ILL M_ILL F_ILL
Vondhada 203 913 29631 456 135 137 0 482 292 190 431 165 266
Rampar 158 668 350 318 102 62 0 344 230 114 324 120 204
Adhoi (Pasakayara) 2401 10794 5453 5341 1794 2230 182 5506 3356 2150 5288 2097 3191
Gharana 705 3469 1757 1712 596 208 5 1616 998 618 1853 759 1094
Lakhpat 216 807 371 436 81 71 0 413 232 181 394 139 255
Vijpasar 475 2417 1236 1181 382 292 0 1150 728 422 1267 508 759
Vondh 1877 6972 3462 3510 1126 521 18 3394 2013 1381 3578 1449 2129
Chhadavada 410 1953 999 954 280 149 82 821 546 275 1132 453 679
Samakhiari 2482 10402 5748 4654 1577 856 92 6463 4133 2330 3939 1615 2324
Laliana 525 2488 1300 1188 368 354 0 1267 783 484 1221 517 704
Amaliyara 482 2262 1138 1124 389 198 3 923 561 362 1339 577 762
Piprapati 46 262 148 114 55 0 0 119 76 43 143 72 71
Jangi 913 4713 2383 2330 780 809 0 2043 1311 732 2670 1072 1598
Rajansar 122 680 340 340 177 0 0 277 178 99 403 162 241
Katariya Nava 90 543 293 250 84 0 0 305 197 108 238 96 142 Katariya Juna 558 2619 1283 1336 346 384 0 1366 799 567 1253 484 769 Lakadiya 1915 8651 4427 4224 1656 959 93 4367 2647 1720 4284 1780 2504
Shivlakha 502 2200 1130 1070 393 203 1 1152 645 507 1048 485 563
Karmariya 198 880 449 431 161 81 0 395 253 142 485 196 289
Halra 94 554 279 275 107 23 7 235 150 85 319 129 190
Continue Table 4-30
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NAME TOT_W
ORK_P
MAIN
WORK
_P
MAIN_
CL_P
MAIN_
AL_P
MAIN_
HH_P
MAIN_
OT_P
MARG
WORK_
P
MARG
_CL_P
MARG_
AL_P
MARG
_HH_P
MARG_
OT_P
NONWO
RK_P
Vondhada 286 284 92 126 0 66 2 0 2 0 0 627
Rampar 312 172 32 106 0 34 140 1 137 0 2 356
Adhoi (Pasakayara)
3387 2839 593 344 119 1783 548 21 130 6 391 7407
Gharana 1123 1024 360 240 2 422 99 5 51 0 43 2346
Lakhpat 264 262 165 79 0 18 2 0 1 0 1 543
Vijpasar 822 609 284 266 3 56 213 4 190 0 19 1595
Vondh 2840 2784 806 525 5 1448 56 16 26 0 14 4132
Chhadavada 666 643 152 264 6 221 23 2 10 0 11 1287
Samakhiari 3617 3511 289 474 32 2716 106 3 32 7 64 6785
Laliana 798 752 353 260 0 139 46 2 30 1 13 1690
Amaliyara 720 474 176 98 2 198 246 15 118 1 112 1542
Piprapati 90 90 1 85 0 4 0 0 0 0 0 172
Jangi 1575 1451 335 554 10 552 124 7 68 11 38 3138
Rajansar 190 163 90 63 0 10 27 0 20 0 7 490
Katariya Nava 195 195 137 43 0 15 0 0 0 0 0 348
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Katariya Juna 701 697 174 231 3 289 4 1 3 0 0 1918
Lakadiya 2616 2201 326 851 22 1002 415 11 262 1 141 6035
Shivlakha 931 675 435 122 1 117 256 0 233 1 22 1269
Karmariya 356 312 72 94 17 129 44 4 22 3 15 524
Halra 175 171 109 28 0 34 4 0 4 0 0 379
No_HH: Number of house hold
TOT_P: Total Population
TOT_M: Total Male
TOT_F: Total Female
P_06: 0-6 year population
P_SC: SC population
P_ST: ST population
M_LIT: Male literates
F_LIT: Female literates
M_ILL: Male illiterates
F_ILL: Female illiterates
TOT_WORK_P: Total working population
Total CL: Total (Main + Marginal) cultivators
Total AL: Total (Main + Marginal) agriculture
Total HH: Total (Main + Marginal) household
Total OT: Total (Main + Marginal) other workers
NON_WORK_P: Non working population
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Chapter 5 Impact Identification & Mitigation Measures
5 IMPACT IDENTIFICATION
This section discusses the impacts of the project activities on the environmental receptors
that stand to get affected by the project. It discusses probable impacts during various
phases of the project lifecycle to the environmental receptors.
Many scientific techniques and methodologies are available to predict impacts on physico-
ecological and socio-economic environment. Such predictions are superimposed over the
baseline (pre-project) status of environmental quality to derive the ultimate (post-project)
scenario of environmental conditions. The prediction of impacts helps to identify and
implement environmental management plan during and after the execution of the
developmental activity to minimize the deterioration of environmental quality.
5.1 PROJECT ACTIVITIES CAUSE IMPACTS
The project activities which can cause impact to surrounding environment receptors are
listed below:
Manufacturing & Operation activities of various plants i.e Steel plant, Rolling mill,
Power Plant
Storage and handling of raw material and products
Transportation of raw materials, products and personnel.
Water supply, storage and treatment
Solid Wastes Generation.
Hazardous Waste Generation.
Waste Water Generation
Gaseous Emission
5.2 POLLUTION SOURCE
The source of pollutants in the environment will be mainly in form of:
Cooling water blow down, Boiler blow down.
Flue gases from furnaces, boiler.
Fugitive emission .from process, movement of vehicles and handling of raw material
Noise from turbine, D.G. set, fans, and vehicular movement.
Storage and handling of solid wastes.
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5.3 POTENTIAL IMPACT ON AIR ENVIRONMENT
5.3.1 Construction Phase
Construction activities will be included to any construction laying of foundations for Kiln,
Furnace etc. Negligible Impact of fugitive emission envisaged due to same.
5.3.2 Operation Phase
The source of emission will be mainly in form of point source and fugitive emission.
5.3.2.1 Fugitive emission
The major sources of fugitive emissions are as detailed below
i) Loading/ unloading of Raw material at project site.
ii) Transportation of coal from port to plant
iii) Stacking of Coal in Coal storage area.
iv) Transfer of coal from storage yard to screening, crusher house and coal storage bin.
v) Fugitive emission from fly ash storage area.
i. Coal Loading/ Unloading:
Fugitive emission may occur due to the loading and unloading of coal at the port and
the project site. The same shall be prevented by reducing the dropping height and
regular water sprinkling.
ii. Transportation System
Vehicular emissions will principally arise out of emissions from the exhausts of vehicles
used for the transport of Raw materials, fly ash and the transport of the workers. All
vehicles shall have Pollution Control Certificate (PUC) with regular maintenance check.
However, their effects are highly localized. In the dry season, there will also be some
air pollution caused by re-entrainment dust caused by operation of vehicles on dry
roads and it’s proposed to control the same by sprinkling water on regular interval.
Either covered dumpers or trucks covered through tarpaulin shall e used to prevent
fugitive emissions due to on road Transportation.
Due to the proposed expansion project there would be increase in vehicular movement.
National highway 8A/41 with the major district road will be used for the transportation
purpose. The detail bifurcation with respect to the numbers of truck is as mentioned in
Table 5-1.
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Table 5-1: No. of dumpers/ trucks used for transportation
Material
transported
Vehicle used Existing
No. Of Vehicles
per day
Proposed
No. of vehicles
per day
Total
No. of vehicles
per day
Raw material Dumpers/
trucks
Iron Ore: 9
Coal sponge: 9
Coal CPP: 6
Iron Ore: 25
Coal sponge: 24
Coal CPP: 25
Iron Ore: 34
Coal sponge:33
Coal CPP: 31
Fly ash Dumper/ trucks Approx 5 Approx 10 Approx 15
Finished Product Dumper/trucks Approx 18 Approx 36 Approx 54
Total dumpers/trucks Approx 47 Approx 120 Approx 167
On an average movement of 167 trucks/ dumpers (approx) will be expected to the existing
traffic. Due to the increase in vehicular traffic there would be increase in the fugitive
emissions level. Also minor increase would be observed in the noise level. But the major
movement is restricted to highways and other major road as Project is located close to the
Highway 8A/41.
The site is connected to major district road and highways.
The detail management plan for prevention of fugitive emission due to transportation is
mentioned in chapter 6, section 6.3.
Coal Storage Area
Fugitive emission shall arise due to windblown dust from the coal storage area. The detail
management plan for prevention of fugitive emission due to Coal Storage is mentioned in
chapter, section 6.3.
iii. Coal Transfer
Coal shall be transferred from coal storage yard to the intermediate bin, rotary kiln and
boilers through closed conveyor belt. There shall be increase in the fugitive emissions during
the coal transfer within the plant premises. The same can be decreased by usage of closed
conveyor belt.
iv. Fly Ash Handling
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Increase in the fugitive emission shall occur due to the fly ash handling at the project site. The detail management plan of same
is discussed in chapter 6, Section 6.6.1.
5.3.2.2 Point source emission/ Air modeling for proposed expansion project
Point source emission will be mainly due to stacks installed & to be installed as expansion. The details of proposed stack for
expansion project as well as existing project considered for air modeling is as given in Table 5-2.
Table 5-2: Stack Details for Existing & Proposed Plant (Input data)
Stack
attached to
Particulars
Induction furnace I to III stack AFBC boiler stack Rotary kiln - III & IV DG Set stack
(Standby)
Proposed Proposed Proposed Proposed
No. of stacks 1 1 1 3
Stack height 30 m 60 m 45 m 17 m
Stack Diameter 0.8 1.2 1.8 0.35
Exit Gas Velocity 15 15 17 15
Exit Gas temperature 150 °C 150°C 180 °C 100°C
Emission in g/s
PM
Sox
NOx
1.069
--
8.022
1.203
8.709
18.051
3.286
8.68
49.295
0.180
0.041
1.354
Air Pollution Control
Measures
Bag Filter(each) Electro Static
Precipitator
Electro Static
Precipitator(each)
N/A
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5.3.3 Details of Air Modeling
The stack details as mentioned in Table 5-2 were used as input data for prediction of impact
due to proposed point source emission in the area.
The incremental increase in the concentration of pollutants, after the installation of the
proposed stacks was predicted using mathematical model.
Industrial Source Complex – Short Term 3 (ISC-ST 3) model by Lakes and Environment was
used for the prediction of incremental increase.
The ISCST-3 (Industrial Source Complex – Short term 3) from Lakes and Environment is
based on Gaussian Plume Model. For the present study, this model is used for the prediction
of maximum ground level concentration (GLC). ISCST3 model is executed using stability
classes developed by Pasquill and Gifford.
The inputs data given to the model includes data relating to emissions (stack details as
mentioned in Table 5-2) with effective stack height, hourly meteorology details like ambient
temperature, wind speed, wind direction, relative humidity, pressure, cloud cover etc for
summer season.
After giving the input data to the model, the incremental concentration of the pollutant due
to the point sources from the proposed activities was calculated. The maximum incremental
concentration due to emission from point sources was recorded at the respective location
with its distance and direction from the proposed project site.
The maximum incremental ground level concentration was superimposed on the maximum
average baseline concentration in the respective location at the recorded distance and
direction by the model.
The maximum predicted 24 hr average concentration of pollutants is given in Table 5-3.
Table 5-3: Resultant Concentration due to incremental increase Proposed
Pollutant Incremental
Concentration
g/m3
Baseline Concentration, g/m3 *
Resultant
Concentration g/m3
Direction wrt stack location
Distance wrt stack location, km
NAAQS as per LULC(Industrial + rural)
PM 1.637 85 86.637 North East
0.7 100
SO2 1.658 19.24 20.898 North East
1.118 80
NOx 9.707 23.56 33.267 North East
0.7 80
* Baseline average concentration of location in North East direction from the project site was considered (i.e AQ 1)
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Conclusion
The above scenario was for the Proposed project. PM emission were considered for induction
furnace stack. No Sox and NOx emission is envisaged from the induction furnace hence the
same is not considered for air modeling.
As tabulated in Table 5-3, the maximum incremental concentration for Particulate matter,
Sulphur dioxide and nitrogen oxide for proposed project is found to be 1.637 g/m3, 1.658
g/m3, 9.707 g/m3 respectively. The incremental increase was observed in North East
direction at distance of 1.118 Km for SO2, PM and NOx from the stack location.
The incremental increase calculated by the air modelling software was super impose on the
average concentration observed at monitoring location (AQ1 Project site) which was located
in down wind direction of the stack location.
It is observed from Table 5-3, that the resultant concentration for PM, SO2 and NOx are
observed to be below the National Ambient Air Quality Standards published by CPCB during
the study period.
The maximum incremental concentration is observed at the distance of 0.7 & 1.118 km.
As per the land use study conducted, the area where maximum ground level concentration
was observed has Agricultural land use.
The major agricultural crops found in the area are Castor and Cotton & during winter Makai
and Bajra mainly cultivated for fodder. During monsoon mainly Mug and Jowar cultivated.
These crops will be mainly impacted due to the proposed project.
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Figure 5-1: Isopleths for PM (Proposed)
N
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Figure 5-2: Isopleths for Sox (Proposed)
N
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Figure 5-3: Isopleths for Nox (Proposed)
N
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5.4 POTENTIAL IMPACT ON NOISE ENVIRONMENT
5.4.1 Construction Phase
No major Construction activity envisaged as this expansion project on additional area hence
noise generation due to Construction activity will be minimum and restricted to project site
itself.
5.4.2 Operation Phase
The major noise generating from various sources from the Project activity are as mentioned
in Table 5-4, Table 5-5 and Table 5-6 with the expected level of noise from each equipment
at 1 m distance from source.
Table 5-4: Noise level generation from induction furnace
Noise generating sources Noise level at 1 m from source
Induction furnace 88 dB(A)
Outside induction furnace concrete room 84 dB(A)
ID fan 85 dB(A)
Cooling tower 80 dB(A)
Bag Filters 82 dB(A)
Knock out machine/ grinding area 82 dB(A)
D G set 80 dB (A)
Table 5-5: Noise level generation from Rotary Kiln
Noise generating sources Noise level at 1 m from source
In front of Rotary Kiln & Cooler
Near Crusher & Screen
Near Bag Filter
Near Main Gate
82 dB(A)
78 dB(A)
80 dB(A)
68 dB(A)
Billet casting Machine Section 80 dB(A)
Rolling Mill Section 85 dB(A)
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Material Handling 75 dB(A)
Material Charging & Conveying 78 dB(A)
Compressors 80 dB(A)
Pumps 80 dB(A)
ID Fans 85 dB(A)
Table 5-6: Noise level generation from AFBC
Noise generating sources Noise level at 1 m from source
Boiler room 90 dB(A)
Turbine 92 dB(A)
Compressors 80 dB(A)
Pumps 80 dB(A)
ID Fans 85 dB(A)
From the expected Noise level from the various source of Project activity, it can be
concluding that the noise at Project site is varies from 75-92 dB (A). The details
management plan is discussed in Chapter 6, Section 6.4, Page no 142. The maximum
exposure receptors are workers in the Project Site. This impact can be minimized by use of
proper PPE Devices.
5.4.3 Noise Quality Modeling
Noise Quality modeling for the proposed project is run by CUSTIC Software. The Noise data
used for modeling study is as per the Table 5-4, Table 5-5 and Table 5-6.
The Noise quality model for proposed project is shown in Figure 5-4.
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Figure 5-4: Noise quality model for proposed project
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Conclusion
Based on the Noise Quality modeling, the Impact of Noise generated from the proposed
equipment and process will be in the range of 0.78 km radius from the Project site.
The expected level of the noise at 0.78 km is 11.06 dB. There is no residential area at this
distance. Hence impact due to noise will be negligible and localized. The receptors are
mainly workers in the Project site. The impact can be minimized by use of proper PPE
Devices. The ambient noise level at plant gate will be within CPCB standards.
5.5 POTENTIAL IMPACT ON WATER ENVIRONMENT
The detail water consumption pattern and waste water generation details is as discussed in
Chapter 3, Section 3.6, Page no. 51.
5.5.1 Construction Phase
No major Construction activity envisaged. Waste water generation due to Construction
activity is negligible.
5.5.2 Operation Phase
The major waste water generation during operation phase will be from cooling tower blow
down, boiler blow down and domestic wastewater from activity. The waste water generated
will be with high TDS level. The same shall be neutralized in the collection pit and reused
within the plant premises for green belt development and water sprinkling for dust
separation.
The TDS balance diagram for the Waste water envisaged from different sources from the
proposed project is given in Figure 5-5.
443 m3 of waste water expected from Project activity. After proper treatment of
Neutralization. The TDS level of the expected combined waste water stream will be 346.5
ppm. This water can be used for gardening in addition to Dust suppression.
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Figure 5-5: TDS Balance for proposed Project
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The project is zero discharge plant. No waste water generated will be disposed off outside
the company premises.
Domestic waste water will be treated in the existing septic tank and soak pit arrangement.
5.6 POTENTIAL IMPACT DUE TO SOLID WASTE GENERATION
5.6.1 Construction Phase
No major Construction activity envisaged for this Expansion Project hence Solid waste
generation due to Construction activity will be minimum. Whatever solid waste generated,
can be used at site for leveling.
5.6.2 Operation Phase
Solid waste generation is mainly in the form of slag, coal char and ash. The quantum of
solid waste generated is as discussed in Chapter 3, Section 3.9, Page no.54.
Table 5-7: Solid Waste Generation
Sr. No.
Type of waste Proposed Solid waste generation
Disposal Method
1 Total Ash 294 MT/Day
Will be sold to brick manufacturing unit or used
as binding material for land filling
2
Coal Char 160 MT/Day
Will be reused as raw material within the plant
for power generation through AFBC boiler or
sold to registered dealers
3 Slag 140 MT/Day
Will be sold for road construction activity or
used as binding material for land filling
The analysis result of slag is as given in Table 5-8.
Table 5-8: Slag analysis result
Parameters Unit Leachate Quality Result
pH (10% soln. in Dist. Water) pH unit 7.0
Total Phenols mg/l ND
Arsenic mg/l ND
Lead (Pb) mg/l 0.02
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Parameters Unit Leachate Quality Result
Cadmium (Cd) mg/l ND
Chromium - VI (Cr) mg/l ND
Copper (Cu) mg/l ND
Nickel (Ni) mg/l 0.02
Mercury (Hg) mg/l ND
Zinc (Zn) mg/l ND
Fluoride mg/l ND
Ammonia mg/l ND
Cyanide mg/l ND
Nitrate mg/l ND
Adsorbable Organic Bound Chlorine mg/l -
Water Soluble Compounds except
Salts
% -
Oil & Grease % ND
5.7 HAZARDOUS WASTE GENERATION
The hazardous waste expected to be generate is Used oil which shall be reused for
lubrication purpose in the Project site itself.
Table 5-9: Hazardous Waste generation
Sr. No. Waste Generated
Proposed
Quantity Disposal Plan
1
Used Lube oil 75 MT/annum
Will be reused within plant
premises as lubrication oil/
sent to TSDF site.
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5.8 ECOLOGY & FLORA- FAUNA
5.8.1 ECOLOGICAL IMPACT ASSESSMENT
Ecological Impact Assessment (EcIA) is the process of identifying, and evaluating the
identified potential impacts of defined actions on ecosystems or their components. If
properly implemented, it provides a scientifically defensible approach to ecosystem
management (Treweek, 1999).
EcIA studies are often based on a so called “ecological risk assessment” approach. The
objective of this approach is to systematically identify and evaluate the relationships
between stressors as caused by anthropogenic activity (exposure analysis), and subsequent
impacts on receptors (effects analysis).
In the context of this report ‘ecological resources’ relate to sites, habitats, features,
assemblages, species or individuals that occur in the vicinity of a project and upon which
impacts are possible. The term ‘ecological receptors’ is used when impacts upon them
(‘ecological resources’) are likely.
Stressors can be all single characteristics of a project or activity that lead to an ecological
effect. Stressors can be of chemical, physical, or biological nature, such as for example the
release of a chemical, the mechanical impact from construction, or the introduction of an
alien species.
The purpose of EcIA is to provide decision-makers with clear and concise information about
the likely, significant ecological effects associated with a project. This EcIA generally relies
on ecologist’s using their professional judgement. Judgements were made on the basis of an
objective assessment of the best information available at the time of survey.
5.8.1.1 Potential impacts on the environment
Having identified the project activities likely to give rise to significant impacts as per the
data provided, it is then necessary to describe the resultant biophysical changes and to
characterize the impacts on the ‘key ecological receptors’The objective of the exposure
analysis is to describe the exposure of receptors in terms of intensity, space, and time. To
this end, exposure pathways are established, including the stressor source, the spatial and
temporal distribution of stressors in the environment, and the extent and pattern of contact
or co�occurrence with receptors.
The ecological effects analysis then investigates the relationship between stressor levels and
resulting responses. In essence, the ecological risk assessment approach is based on an
analysis of how exposure to stressors is likely to occur and on an analysis of the significance
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of the associated impacts. The result is a list of stressor�response relationships, often also
termed cause�effect relationships.
As ecosystems are diverse and complex systems, these relationships are often interrelated
and have a netlike rather than a linear structure, as one stressor may lead to multiple
exposures and may also cause secondary (indirect) effects.
The level of detail and accuracy of the cause effect relationships depends on how well
information on stressor sources, exposure opportunities, characteristics of the ecosystem at
risk and ecological effects is available.
Risk assessments are typically conducted at a time when not all necessary information is
available about the project. Risk characterization is to be distinguished from risk
management and decision making, which involves the selection of a course of action in
response to the identified risks and other factors.
The stressors and receptors provide the system boundaries for EIA studies. Stressors are
usually classified according to life cycle stage and project components. In the following
section, stressors, relevant to a proposed expansion of M/s ASR Multimetals Private
Limited’snew integrated steel plant and power plant are listed as provided by the
consultant.
Proposed expansion project will be set up within the existing premises of the project
site of a steel plant, the total land available with the proponent is 314683.5sq m.
near Chhadawada village , in out of which 94,433 sq m area is envisages for
proposed expansion project.
The Expansion project involves Sponge Iron Plant, Rotary Kiln, Rotary Cooler,
Atmospheric Fluidized Bed Combustion (AFBC) type power plant and the induction
arc furnace.
Coal char and imported coal shall be used as main fuel in the STG.
Stressors
Stressor sources of The Expansion project which involves Sponge Iron Plant, Rotary Kiln,
Rotary Cooler,Atmospheric Fluidized Bed Combustion (AFBC) type power plant andthe
induction arc furnace, can be subdivided into the following life cycle stages and key
elements:
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Construction
o No additional land requirement as the proposed expansion project will be set up
within the existing premises of the steel plant.
o No new road connectivity required
o Construction activities will be slightly increased the concentration of particulate
matter (PM) in ambient air.
Operation
o Major Pollutants expected are Particulatematters ,SO2, NOx, and various vapours
from the flue gas stacks attached to induction furnace, AFBC stack, Rotary Klin
stack, and D.G set Stack.
o No wastewater generation from manufacturing process or any auxiliaries of the
sponge iron plant. Wastewater generated in form of boiler and cooling tower blow
down from the power plant shall be sent to neutralization Pit; from where the water
shall be completely reused for green belt development and dust suppression
activities. The project is zero discharge plant.
o All the equipment in the existing unit have been designed and operated to have the
noise level not exceeding 75-80 dB (A) at a distance of 1.5 m. from the equipment.
o After expansion About 74 number trucks trips for transportation of Raw materials 36
trucks trips per day for product transport and 10 truck trip per day for
transportation for fly ash are envisaged
Receptors
An environmental assessment should address the effects of a project on fauna, flora, water,
air, climate and landscape, including all direct and indirect effects and the interactions
between single factors. Based on this definition the following categories will used for
describing the potential impacts, of t he expansion project which involves Sponge Iron
Plant, Rotary Kiln, Rotary Cooler,Atmospheric Fluidized Bed Combustion (AFBC) type power
plant and the induction arc furnace on the environment:
o Landscape, nearby agriculture area
o Terrestrial flora and fauna, which can be further subdivided into different functional
and taxonomic groups, i.e. plant communities and habitat types or animal taxonomic
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groups such as invertebrates, mammals, amphibians, reptiles, and birds including
migratory and roosting birds.
o Certain threatened fauna observed in the study area during baseline survey
5.8.1.2 Impact Identification and Prediction
Based on the project details provide by the client /consultant and ecological baseline
information gathered by AEC, the ecological assessment was carried out to identify and
predict potential ecological impacts caused by the proposed development.
All potential impacts, including direct, indirect, on-site, off-site, primary, secondary,
induced, additional, synergistic, cumulative impacts, etc. has been considered. Predictions
were made with sound scientific basis.When describing changes/activities and impacts on
ecosystem structure and function, reference have been made to the following parameters,
o Magnitude of Impact;
o Extent;
o Duration
o Reversibility; and
o Timing and frequency.
o Consequence and Significance
Magnitude:
Magnitude refers to the 'size' or ‘amount’ of an impact, determined on a quantitative basis if
possible.
Extent:
The extent of an impact is the area over which the impact occurs. When the receptor being
considered is the habitat itself, magnitude and extent may be synonymous.
Duration:
The time for which the impact is expected to last prior to recovery or replacement of the
resource or feature. This should be defined in relation to ecological characteristics (for
example species lifecycles) rather than human timeframes.
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Reversibility
An irreversible (permanent) impact is one from which recovery is not possible within a
reasonable timescale or for which there is no reasonable chance of action being taken to
reverse it. A reversible (temporary) impact is one from which spontaneous recovery is
possible or for which effective mitigation is possible.
Timing and frequency
Some changes may only cause an impact if they happen to coincide with critical life-stages
or seasons (for example, the bird nesting season). This may be avoided by careful
scheduling of the relevant activities, e.g. by the implementation of an EAP that specifies
important constraints in relation to the timing of works.
Integration of impact characteristics
An informed integration, for each potentially significant impact, of each of these impact
characteristics is necessary in order to underpin the determination of impact significance set
out below.
The following scale should be applied (adapted from IEEM 2006):
Near-certain: >95% chance of occurring as predicted
Probable: 50-95% chance of occurring as predicted
Unlikely: 5-50% chance of occurring as predicted
Extremely unlikely: <5% chance of occurring as predicted
Consequence and Significance:
The significance of an impact is defined as a combination of the consequence of the
impact occurring and in what probability that the impact will occur.
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Table 5-10: Ecological Impact assessment of Proposed expansion of M/s ASR Multimetals Private Limited’s new
integrated steel plant and power plant
Ecological
Criteria
Identified
Impacts
Ecological
significance of
Impact
Spatial
Extend
Magnitude
/
intensity
Duration
/Timing/
Frequency
Reversibility
Consequence/
significance
without EMP
Mitigation
measures
Significance
after
proposed
EMP
Measures
Construction Phase
Zone of
Influence
in
Project
site
Project
site
habitat
Due to
Site
clearance
The proposed
project of M/s
ASR Multimetals
Private Limited’s
is for increasing
the existing
capacities.
Expansion
project involves
Sponge Iron
Plant, Rotary
Kiln, Rotary
Cooler,
Atmospheric
Fluidized Bed
Localized
Negligible
Within the
area
procured
for
industrial
developmen
t
Long time
Permanent
low
Any work
involving
disturbance
to soil or
excavation
of soil
should be
carried out
only with
the
following
stipulations
the top soil
to a depth
of 30 cm
Very Low
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Combustion
(AFBC) type
power plant and
the induction arc
furnace
No additional
land
requirement,
expansion is
restricted to
already allocated
area.
No additional
road construction
required
should be
first
gathered,
piled aside
and
covered
with a
tarpaulin or
suitable
other
material.
The topsoil
should be
re-spread
as early as
possible.
Zone of
Influence
of
Emission
Ecological
Impact
Surroundi
ng
habitat
due to
Not much impact
on the
surrounding
habitat is
envisaged due to
the construction
activity except
some fugitive
Localized
Notable
Only during
the
construction
activity
Reversible
low/ very low
As given in
EMP
chapter
Very low
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fugitive
emission
emission
High levels of
Suspended
Particulate
Matter (SPM)
which may be
noted due to
various
construction
activities &
handling and
storage of
construction
materials and
movement of
vehicles.
However,
continuous water
sprinkling will be
done to prevent
the said
problem.
Zone of
Influence
Ecological
Impact
During
Construction
Only during
the
Reversible
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of Noise
Surroundi
ng
habitat
due to
Noise
level
phase;
construction
equipment
including dozer,
scrapers,
concrete mixers,
generators,
vibrators and
power tools and
vehicles will be
the major noise
source.
Localized
Notable
construction
activity
Noise level
will be within
safe exposure
limit and is
expected to
be of short
duration And
is
Reversible
Low/ very low As given in
EMP
chapter
Very low
Operation phase
Zone of
Influence
Due to
Project
emission
Ecologic
al
Impact
on
Surroun
ding Eco
sensitive
habitat
due to
emission
from
The health
effects caused by
air pollution are
realized through
a lengthy chain
that includes
physical,
chemical,
behavioural and
physiological
processes. The
Mid-
During
operation
Medium impact
on agriculture
EMP
measures
to reduce
emission of
gaseous
pollutants
and vapor
from
stacks
Low
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Process
and
utility
emission
Major
sources
of air
pollutant
s of the
propose
d unit
will be
process
gas
stacks
and flue
gas
emission
s
Mainly
from
stacks
attached
chain starts with
emissions into
the atmosphere,
where the
pollutants are
dispersed and
diluted, forming
a variable spatial
and temporal
distribution of
concentrations.
The project site
is located in an
area with many
other industrial
establishments
,surrounded by
agriculture fields
The nearest
habitation are in
Samakhiyari
village and
Chhadavada
village located
range
Notable phase
reversible crops
Green belt
developme
nt in the
premises
considering
the
predomina
nt wind
direction
will further
reduce the
impact
emission
with
respect to
the
magnitude
and
distance
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to
inductio
n
furnace,
AFBC
stack,
Rotary
Klin
stack,
and D.G
set
Stack.
Major
Pollutant
s
expected
are
Particula
te
matters
,SO2,
NOx, and
various
vapours
from the
3.2 km, 3.8 and
respectively
away from the
project site. As
per model
prediction
resultant
Concentration
due to
incremental
increases
expected at only
1.118 km and
0.7 form the
project site, at
North East
Direction
Hence no
impact in these
village premises
is anticipated
during the
operation phase.
Only few
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flue gas
stacks
attached
to coal
fired
Boiler
agriculture land
located at this
distance may be
affected.
Agriculture
activity in this
locality of
Kachchh district
is monsoon
dependent.
Zone of
Influence
of waste
water
discaherg
e
Ecologic
al
Impact
on
Surroun
ding Eco
sensitive
habitat
due to
waste
water
generate
d from
The assessment
shall cover all
Effluent/sewage
collection,
treatment and
disposal facilities
affected by the
project. The
actual extent will
depend on the
quality and
quantity of
wastewater
discharged the
capacity of the
Localized
No
discharg
e
Negligible
During
operation
phase
Continuous
Long term
No discharge
Low
The project
is zero
discharge
plant.
A given in
the EMP
chapter
Very low
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the
project
activity
sewerage
systems, and the
assimilative
capacity and
water quality
objectives of the
receiving water
bodies.
About 303 KLD
wastewater is
expected to be
generated during
operation phase
.Wastewater
generated in
form of boiler
and cooling
tower blow down
from the power
plant shall be
sent to
neutralization
Pit; from where
the water shall
be completely
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reused for green
belt development
and dust
suppression
activities. The
project is zero
discharge plant.
Zone of
Influence
of Noise
generation
Ecologic
al
Impact
on
Surroun
ding Eco
sensitive
habitat
due to
Noise
generate
d from
the
project
activity
The main
sources
The impact on
ambient noise
level will be
restricted only
on the factory
premises and
may not have
any significance
increase in the
surroundings
due to the
project activity
The major
source of noise
during operation
phase will be
operation of,
Localized
notable
During
operation
phase
Continuous
Long term
irreversible
medium
As given in
EMP
low
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of noise
pollution
during
operatio
n phase
would be
boiler,
D.G. set,
blowers,
pumps
and
motors,
etc.
pumps,
compressors and
cooling tower
etc. All the
equipment in
Unit has to
designed and
operate to have
the noise level
not exceeding
75-85 dB (A) at
a distance of 1.5
m from the
equipment.
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5.9 SOCIO ECONOMIC ENVIRONMENT
A positive impact on the socio economic environment of the area is expected due to
increase in direct/ indirect job opportunity.
5.10 IMPACT MATRIX
Environmental impacts could be positive or negative, direct or indirect, local or regional and
also reversible or irreversible. The primary function of an environment impact assessment
study is to predict and quantify the magnitude of these impacts, evaluate and assess the
importance of the identified changes, present information and monitor actual changes. The
activities of the proposed project are studied. The impacts of various activities of the
proposed project are identified and presented as matrix Further the characteristics of these
impacts have been evaluated and they are presented as matrix.
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Table 5-11: Impact Matrix
List of activities Type of Impact Quantification of impact EMP Suggested/
Mitigation measures
CONSTRUCTION PHASE
Only foundation work for kiln, Furnaces etc shall be constructed for proposed Project. Rest all utility shall be used from existing
unit. Hence no major impact envisaged for Construction Phase
OPERATION PHASE
Transportation of Raw Materials,
Products and personnel
Fugitive emissions
Noise level rise due to
vehicles
Increase in Traffic
Road Infrastructure
Spillage leading to soil
contamination
Fugitive emission is
mainly due to activities
listed in Chapter 5,
section 5.3.2.1. on page
no.100
Noise level rise due to
proposed project is
quantified in Chapter 5,
Section 5.4.3 on page
no. 109
Increase in Traffic due to
proposed project is
quantified in Chapter 4,
section 4.9 on page no.
76
Vehicles with PUC
certificate shall be
allowed
Maintenance check for
vehicles shall be
registered
Covered conveyor belt
will be installed for
transportation of raw
material within the
premise to control
fugitive emission
Frequency of sprinkling
may be increased to
keep dust emissions
under control
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Good Housekeeping is
maintained at the facility
to minimize
spillage/contamination.
Concrete Roads available
till site
Manufacturing & operation activities –
Steel Plant, Rolling Mill & Power Plant
Noise
Spillage
Heat stress
Dust/Fugitive emission
Noise level rise due to
proposed project is
quantified in Chapter 5,
Section 5.4.3 on page
no. 109
Fugitive emission is
mainly due to activities
listed in Chapter 5,
section 5.3.2.1. on page
no.100
Enclose the process
buildings and / or
insulate them to reduce
Noise
Regular maintenance
and repair of lifting,
electrical, and transport
equipment should be
conducted
Proper ventilation and
air draft available at all
site of the plant
Storage and manual handling of raw
material and products
Spillage/Soil
Contamination
Dusting during raw
material handling
Closed Storage
Barricaded wall with
good height
Good Housekeeping is
maintained at the
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Health impact to workers facility.
Use appropriate PPE
(e.g. insulated gloves
and shoes, goggles to
protect against
radiation, and clothing
to protect against heat
radiation, dusting and
liquid metal splashes)
Install cooling
ventilation to control
extreme temperatures
Truck goes for unloading (Internal
transportation)
Fugitive emission Fugitive emission is
mainly due to activities
listed in Chapter 5,
section 5.3.2.1. on page
no.100
Sprinkling of water over
raw materials & roads
Unloading Spillage
Fugitive emission
Ground water and soil
contamination
Fugitive emission is
mainly due to activities
listed in Chapter 5,
section 5.3.2.1. on page
no.100
Concrete area
Working/operation of Rotary kiln, Ash generation Quantity of ash Fly Ash will be sold to
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power plant & induction furnace Flue gas emission
Electrical Hazard
generation is mentioned
in Chapter 3, section 3.9
on page no. 54
Quantification of Flue
gas emission due to
proposed project is
mentioned in Chapter 5,
Section 5.3.2.2, Table
5-2 on page no. 102.
brick manufacturing unit
or used as binding
material for land filling
Waste water generation Land Environment
Flora & Fauna
Socio Economic aspect
The area where
maximum ground level
concentration was
observed has
Agricultural land use.
Zero Liquid Discharge
Plant. The waste water
generated will be treated
and reuse in gardening
and plantation within plant
premises.
Solid waste generation
Ash
Coal char
slag
Fugitive Emission
Solid waste
quantification is as per
Chapter 5, Table 5-7,
Page no. 113
Fly Ash will be sold to
brick manufacturing unit
or used as binding
material for land filling
Coal char will be reused
as raw material within
the plant for power
generation through AFBC
boiler / sold to
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registered dealers
Slag will be sold for
road construction
activity or used as
binding material for land
filling
Hazardous waste generation
Used oil
The spillage of oil on land
will lead to contamination
of soil and in later stages
will contaminate the
ground water in the area
Quantification of quantity
of used oil is discussed in
section 3.10, Table 3-15
on page no.55.
Used oil will be used for
lubrication; in case it
needs to be stored it
shall be stored in
designated isolated HW
Storage Area.
Separate storage area
shall be constructed with
concrete base
The waste should be
stored in separate
containers
The area shall be isolated
and covered in order to
prevent the infiltration of
rainy water
Cleaning of Accretion Material Fugitive Emission Fugitive emission is Safety wears.
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Possibility of fire due to
combustion
Health Hazard
mainly due to activities
listed in Chapter 5,
section 5.3.2.1. on page
no.100
Planned shutdown for
clean up
Regular medical checkup
of worker as per Factory
Act.
Socio economic status
Positive impact Employment generation
due to proposed project
is mentioned in Chapter
8, Section 8.1, Table 8-1
on page no.153.
Change in personal
income resulting from
new employment of
workers, purchase of
services from local area
vendors, lease, and
production payments
Induced economic
activity from local
purchases of land,
equipments, supplies and
services
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Chapter 6 Environment Management Plan
6 ENVIRONMENT MANAGEMENT PLAN
From construction and operation activities of the process, environmental impact has been
identified, predicated and evaluated to mitigate the standards specified by the statutory
authority and minimize the impact on eco system. Environmental Management Plan
provides control measures of potential environmental impacts. Environmental Management
System for different environmental attributes is discussed in subsequent topics.
6.1 ADMINISTRATIVE ASPECTS OF EMP
The basis of the operational philosophy of ASR Multimetals Pvt. Ltd. is that the activities
proposed in production of Steel and power plant shall be operated in complete compliance
with all applicable Laws, Regulations, Standards and Permits, procedures, specifications,
rules, standards and guidelines.
Existing project of ASR Multimetals Pvt. Ltd. has been operative under compliance to
environmental conditions stipulated in the Environment Clearance & Consent to Operate.
Compliance of existing plant with respect to conditions mentioned in Consent to Operate &
EC is enclosed as Annexure 10.
In order to achieve this, ASR Multimetals Pvt. Ltd. has established a resource base for the
management of health, safety, environmental and social issues during construction and
operation of Plant.
The HSE Management System Process which has been developed for use as part of the
implementation of the operations philosophy will be followed, together with the
commitments contained within the ASR Multimetals corporate Health, Safety and
Environment (HSE) Policy. The System also contains adequate security measures that are
designed to protect people and property.
6.2 ENVIRONMENT MANGEMENT PLAN – CONSTRUCTION PHASE
Only foundation work of kilns, furnaces etc shall be done in construction activity. All the
other utilities of existing units shall be used.
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6.3 ENVIRONMENT MANAGEMENT PLAN - OPERATION PHASE FOR CONTROL OF
FUGITIVE EMISSION
In order to meet the standards as prescribed in NAAQS, the following management plan was
implemented.
Regular & periodic sprinkling of water on all exposed surfaces to suppress emission of
dust. Frequency of sprinkling may be increased to keep dust emissions under control.
Erecting the walls high to act as wind shield during storage of raw materials. The same
which had been implemented for the existing project which is depicted in the
photographs below:
Figure 6-1: Photographs of existing wind barriers and storage shed
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Enclose conveyer transfer points with dust-controls;
Cleaning the return belts in the conveyor belt systems to remove loose dust;
Vehicles shall be given speed limit of 10 km/hr within the premise.
Implementation of correct loading and unloading practices.
Materials shall be transported in securely covered trucks to reduce dust emission.
The workers should be given dust masks to avoid inhalation of dust & fugitive
emissions.
6.3.1 Point source emission
Stack height shall be based as per the statutory requirement of CPCB. The stack height for
DG sets are based on the below
H = h + 0.2 √KVA
Where H = height of stack; h = height of building/ Base of installation
Stack height for kiln, boilers shall be as per the standard equation
H = 14 Q0.3
Where H = height of stack; Q is the pollutant load in kg/hour
Installation of proper stack height will lead to proper dispersion of pollutants
6.3.2 Fugitive Emissions Controls
Transportation will also lead to fugitive emission. Connecting roads from site to main roads
should be concreted to minimize increase in particulate matter due to transportation of final
product. Vehicular emission will lead to increase in SO2 and NOx in the area. The vehicles
used for transportation should have valid PUC certificate and a check of same shall be done
at the entry gate of site. Covered conveyor belt will be installed for transportation of raw
materials within the premises.
Workers are provided with Respiratory Protectors in order to reduce the effect of fugitive
emissions.
6.3.3 Green belt to mitigate pollution
Greenbelts are an effective mode of control of air pollution, where green plants form a
surface capable of absorbing air pollutants and forming a sink of pollutants. Leaves with
their vast area in a tree crown, sorbs pollutants on their surface, thus effectively reduce
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pollutant concentration in the ambient air. Often the adsorbed pollutants are incorporated in
the metabolic pathway and the air is purified. Plants grown to function as pollution sink are
collectively referred as greenbelts.
An important aspect of a greenbelt is that the plants are living organism with their varied
tolerance limit towards the air pollutants. A green belt is effective as a pollutant sink only
within the tolerance limit of constituent plants. Planting few, known pollutant sensitive
species along with the tolerant species within a green belt however, do carry out an
important function of indicator species
Apart from function as pollution sink, greenbelt would provide other benefit like aesthetic
improvement of the area and providing suitable habitats for birds and animals.
6.3.3.1 Selection of plants for Greenbelts:
The main limitation for plants to function as scavenger of pollutants are, plant’s interaction
to air pollutants, sensitivity to pollutants, climatic conditions and soil characteristics. While
making choice of plants species for cultivation in green belts, due consideration has to be
given to the natural factor of bio- climate. Xerophytes plants are not necessarily good for
greenbelts; they with their sunken stomata can withstand pollution by avoidance but are
poor absorber of pollutants.
Character of plants mainly considered for affecting absorption of pollutant gases and
removal of dust particle are as follows.
For absorption of Gases:
Tolerance towards pollutants in question, at concentration, that are not too
high to be instantaneously lethal
Longer duration of foliage
Freely exposed foliage
Adequate height of crown
Openness of foliage in canopy
Big leaves( long and broad laminar surface)
Large number of stomatal apertures
For Removal of Suspended Particular matter
Height and spread of crown.
Leaves supported on firm petiole
Abundance of surface on bark and foliage
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Roughness of bark
Abundance of axillary hairs
Hairs or scales on laminar surface
Protected Stomata
The following trees and shrubs are suggested for green belt development within the plant
premises. The highlighted species are more suitable for plantation in the semi -arid region
of Kachchh district as well as considering the prevailing dust emission.
Table 6-1: Recommended Plant Species for Green Belt Development
PLANT SPECIES
LOCAL NAME HABIT TOLERANCE LIMIT
STOMATAL INDEX
MODE OF
REGENERATION
Acacia auriculiformis
Austrialanbaval Tree Tolerant 10.9 Seeds
Acacia leucophloea
Hermobhaval Shrub T 12.01 Seeds
Ailanthus excelsa
Moto Aurdso Tree T 13.01 Seeds, shoot, root cuttings
Alstona scholaris
Saptaparni Tree T 15.23 seeds
Azadirachta indica
Limbado Tree T 29.2 Seeds
Bauninia recemosa
Kanchner Tree T 25.68 Seeds
Bougainvillea spectabilis
Bougainvel Shrub T 32.53 Cutting
Cassia javanica L. var. indochinensis
Pink Cassia Tree T seeds
Cassia siamea Tree T 21.2 Seeds
Kegelia Africana Tabudiyo Small tree
T 12.90 Seeds
Lowsonia intermis
menthi Shrub T 17.0 Seeds/cuttings
Mangifera indica Ambo Tree S 30.77 Seeds/ budding/grafting
Melia azadirachta
Bakan limdo Tree T - Seeds /stem cutting
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Nerium indicum
Lalkaren Shrub T 15.7 Cutting
Peltophorum pterocarpum
Sonmukhi Tree T 16.78 Seeds
Polyathia longifolia
Asopalav Tree Sensitive 22.27 sedds
Prosopis cineraria
Khyigdo Tree T 18.1 Seeds/root suckers
Salvadora oleoides Decne
Piludi Tree - Seeds/ cuttings
Salvadora persica L.
Piludi Tree T - seeds
Terminalia catapppa
Desi Badam Tree T 20.9 seeds
Thespesia populnea L.
Paras pipalo Tree T 29.81 Seeds/ cuttings
Thevetia peruviana
Pili karan Shrub T 27.8 Seeds
T: Tolerant S- sensitive, (--) =Not available Sources: CPCB (March, 2000) Guidelines for developing
green belts PROBES/75/1999-2000
6.4 ENVIRONMENT MANAGEMENT FOR NOISE ENVIRONMENT
Operation Phase
The major noise generation during operation phase will be from the equipments listed in
Chapter 5, Section 5.4.2, Table 5-4 to Table 5-6 on page no.108.
The mitigation measures to be adopted while working close to the noise generating
equipments are as follows:
Noise producing equipment shall be placed at distance from each other to reduce the
cumulative noise level.
Rotation of workers shall be done based on their exposure to noise level during the
working hours as per the Factory Act, 1948 and amendments thereof.
Working hours as per the Factory Act, 1948 and amendments thereof.
Total time of exposure (continuous or a number of short-term exposures) per day in hours.
Sound pressure level in dBA
8 90 6 92 4 95
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3 97 2 100
11/2 102 1 105
3/4 107 1/2 110 1/4 115
Notes
No exposure in excess of 115 dBA is to be permitted.
For any period of exposure falling in between any figure and the next higher or lower figure as indicated in column
1, the permissible sound pressure level is to be determined by extrapolation on a proportionate basis.
Entry to the working area wherein the noise generating sources are located should
be permitted with PPE’s like ear muff, ear plugs
Workers in grinding area should be equipped with gloves.
Regular audiometric test of workers should be done and the medical reports of same
should be maintained.
Display should be made clearly indicating noise prone area along with dB level
All the vibrating parts will be checked periodically and serviced to reduce the noise
generation. The equipment, which is prone to generate excessive noise, will be
provided with enclosures etc.
To reduce the Noise generation during the transportation activities; the vehicle shall
be kept periodically serviced and maintained as per the requirement of latest trend in
Automobile industry. Only those Vehicles with PUCs and spark arresters shall be
allowed for the transportation.
The industry has proposed to develop green belt around the periphery of the plant.
This will help in reducing the adverse effect of pollution in general.
All equipment in the plant would be designed/operated to have a total noise level not
exceeding 85 to 90 dB (A) as per the requirement of OSHA (Occupational Safety and
Health Administration) standard and the Environment (Protection) Rules
Develop proper awareness among workers by regular training session
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6.5 ENVIRONMENT MANAGEMENT PLAN FOR WATER ENVIRONMENT
6.5.1 Water Conservation
The first step towards the management of water environment would be conservation of the
water. Proper step shall be taken to conserve the water, apart from the reuse and recycle of
the wastewater generated.
Faucets uses are of low water consumption type.
W.C, Flush and Urinal Flush valve shall be of low water consumption type
Treated Industrial waste water will be reused within the plant premises for green belt
development and dust suppression
Rain water harvesting scheme shall be implemented. The expected ground water
recharge proposed is an average of 371 KLD in rainy season.
We were also accumulated rain water every year in our storage tank having Capacity
800000 liter, such as 400000 liters in previous year and used in our Plantation and
Sprinkling System.
Primary Treatment Plant to recycle water for gardening and plantation purpose.
6.5.2 Rain water Harvesting
Long term rainfall data is used for its analysis, probability of rainfall occurrence, rainfall
intensity, analysis of daily rainfall, average evaporation.
The actual plan for Rain water Harvesting is extremely based on available average rain fall
322 mm in last year.
Rain water harvesting is deliberate attempt for collecting /concentrating, storing and
distributing rain water. The method is site specific and need based.
Catchments includes Roof top, Compounds and pavements, land surface or hill slope,
pits, check dams, Impervious / semi pervious surface (tanks) etc.
The storm water is collected in rain water harvesting pond. The same water is used in
process.
6.5.3 Waste water Management
The wastewater generated shall be neutralized & used for dust suppression & green belt
development. Zero liquid Discharge Plant.
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6.6 ENVIRONMENT MANAGEMENT PLAN - SOLID WASTE
Environment Management plan to be implemented for solid waste generation will include
the following points:
Recyclable material to be separated at source, & shall be sold to contractors for
recycling.
No waste will be dumped at any location outside site boundary.
Fly Ash generate shall be sold as raw material to approved site holders. MoU of the
same is enclosed herewith as Annexure 4.
Slag will be utilized for construction of road where as coal char will be used as raw
material in AFBC boiler
Waste will be stored in covered area to prevent fugitive emission.
The analysis report of slag is mentioned in Chapter 5, Table 5-8 , Page no. 113. The cross
section of ash pond and its plan is as shown in Figure 6-2. Ash pond with 15 days storage
capacity will be constructed at site.
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Figure 6-2: Cross section and plan of Ash pond
6.6.1 Fly Ash management
The fly ash generated will be collected and stored in fly ash silos.
Regular water sprinkling shall be done in the fly ash storage area.
The fly ash generated shall be transported in dumpers from generation point to the
final disposal point
The fly ash generated will be sold to brick/cement manufacturers. MoU for the same
is enclosed herewith as Annexure 4.
Ash will be partly sold to landfilling site wherein it will be used as binding material for
solidification and stabilization.
Ash handling system
The ash handling system envisages wet extraction and disposal of bottom ash & dry
extraction for fly ash. The fly ash will be extracted in dry form from the electrostatic
precipitator hoppers, economizer & air heater hoppers and stack hopper and transported to
storage silo as a measure for promoting ash utilization.
Disposal of Fly Ash from Silo
Dry fly ash from the air pre-heater, stack hopper, Eco hoppers and ESP hoppers will be
collected in the fly ash storage silo. The storage silos three nos will be designed to have a
storage capacity of 50 tonnes each which caters for twenty four hours of fly ash generation.
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The dry fly ash collected in the storage silo will be normally disposed in the dry conditioned
form. The fly ash will be unloaded in dry form through rotary feeder and double shaft paddle
type dust conditioners to open trucks for utilization of fly ash. The fly ash conveying air will
be vented to the atmosphere through vent bag filter to mitigate the environmental
pollution. Fly ash silos will be provided with three (3) outlets - one for disposal of ash in
conditioned form into open trucks through ash conditioner and other for disposal of fly ash
in dry form to closed container trucks.
Disposal of Bottom ash
The bottom ash will be disposed in ash pond. Bottom ash collected in silo will be transported
through trucks to the ash dyke. Provisions in the silo will be as that of fly ash silo. Efforts
will be made to dispose the ash to landfill use etc.
Ash Disposal Area
An ash dyke will be installed mainly to dispose off bottom ash incase the off take by other
agencies is delayed due to unforeseen reasons. The ash pond dyke will be of maximum 15
m height. Suitable impervious lining for the ash pond will be provided to prevent leaching of
ash from the pond. Water Sprinklers will be provided to contain fugitive dust emission.
Efforts will be made to grow plantation over the dyke.
6.7 HAZARDOUS WASTE
Operation phase
Hazardous waste will be separated from other waste & stored in designated areas with
restricted access & proper marking; this shall be disposed of through approved
manager/contractor. In the proposed expansion project only used oil will be generated and
the same shall be reused within the plant premises for lubrication purpose.
6.8 ENVIRONMENT MANAGEMENT CELL
A separate Environment Management Cell will be earmarked for monitoring of pollutants
and development of greenbelt as per Environmental Management Plan. Environmental
Management Cell (EMC) will meet at least once a month to assess the progress and analyze
the data collected for the month. Any deviation/variation noticed shall be immediately taken
into consideration for improvement of the same. Yearly action plan of EMP will be updated
with respect to results achieved and proposed activities for next year.
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Figure 6-3: Environment Management Cell
The major duties and responsibilities of Environmental Management Cell shall be as given
below:
To implement the environmental management plan
To assure regulatory compliance with all relevant rules and regulations
To ensure regular operation and maintenance of pollution control devices.
To minimize environmental impacts of operations as by strict adherence to the EMP
To initiate the environmental monitoring as per approved schedule
Review and interpretation of monitoring as per approved schedule and corrective
measures in case monitoring results are above the specified limits
Maintain documents of good environmental practices and applicable environmental
laws as ready reference
We shall develop the Environment Cell, by appointment of Environment Engineer,
Safety Officer and all monitoring will be done by government approved third Party
including audits.
Maintain environmental related records
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Coordination with regulatory agencies, external consultants, monitoring laboratories
Maintain of log of public complaints and the action taken
Allocation of Resources, Responsibility and Authority will result in successful implementation
of EMP during construction and operational phase.
6.8.1 BUDGETARY ALLOCATION FOR ENVIRONMENT MANAGEMENT PLAN
Table 6-2 depicts the resources required during construction and operation stages and the
estimated budget against each resource for environment management.
Table 6-2: Estimated cost of implementation of EMP
Activities Existing + Proposed unit
Water and Waste water management 50 Lacs
Air pollution control Equipments 250 Lacs
Fire fighting system 30 Lacs
Construction of septic tank/ soak pit 3 Lacs
Environmental Monitoring And Management 7 Lacs per year
Occupational Health & Safety 5 Lacs per year
Green Belt 12 Lacs per year
TOTAL 357 Lacs
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Chapter 7 Environment Monitoring Plan
7 ENVIRONMENT MONITORING PLAN
Based on the baseline conditions of the area and the environment management plan, a
detailed monitoring program for the construction and operation phase is designed.
Environment monitoring will serve as an indicator for any deterioration in environment
conditions due to operation of the project. Regular monitoring of environment parameters
will serve as a measure to check the efficiency of Pollution control measures implemented.
Company shall appoint MoEF - NABL approved laboratory for the sampling and analysis of
environment parameters.
The main attributes for which monitoring shall be carried out are:
Ambient air Quality
Stack Emission
Wastewater Quality
Drinking water Quality
Noise Level
7.1 AMBIENT AIR QUALITY MONITORING
The ambient air quality with respect to NOx, SO2, PM10 and PM2.5 shall be monitored at
project location.
The selected monitoring stations shall be monitored for a period of 24 hours quarterly. The
log book shall be maintained at environmental cell for evaluation of impact and to decide
required mitigatory measures
7.2 STACK MONITORING
The stacks in the proposed project shall be monitored on monthly basis, with respect to
temperature, oxides of nitrogen (NOx), Suspended Particulate Matter (SPM), Sulphur dioxide
(SOx), HC, CO. It is also recommended the relevant parameter will be monitored by external
agency approved by MoEF - NABL.
7.3 NOISE ENVIRONMENT
Monitoring of the noise levels is essential to assess the effectiveness of Environmental
Management Plan implemented to reduce noise levels. A good quality sound level meter and
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noise exposure meter may be procured for the same. Audiometric tests shall be conducted
periodically for the employees working close to the high noise sources. The noise levels due
to machines/equipments should be monitored regularly.
7.4 WATER AND WASTE WATER QUALITY MONITORING
Drinking water shall be analyzed to check the drinking water standards as prescribed in IS
10500:2012.
7.4.1 Environment laboratory
Methods prescribed in "Standard Methods for Examination of Water and Wastewater"
prepared and published jointly by American Public Health Association (APHA), American
Water Works Association (AWWA) and Water Pollution Control Federation (WPCF), Book on
Water and Wastewater Analysis published by NEERI, Nagpur are recommended for
collection and analysis of water and wastewater samples.
Table 7-1: Monitoring schedule
Area of monitoring Frequency of
Sampling
Parameters to be analyzed
Ambient air Quality Quarterly PM10 and PM2.5 NOx, SO2
Stack Monitoring for major
stacks (rotary kiln, AFBC,
induction f/c, reheating f/c)
Monthly Temperature, NOX, SO2, SPM
Stack Monitoring for all
stacks
Monthly Temperature, NOX, SO2, SPM
Noise Quarterly (day time
and night time)
Sound pressure level (Leq)
Waste Water from collection
pit
Daily pH, Conductivity, TDS, TSS,
BOD, COD, Oil and grease
Environmental management cell shall be created and qualified persons would be in charge
of monitoring the parameters by using suitable instruments. The detail of same is discussed
in chapter 5.
7.5 POST PROJECT ENVIRONMENT MONITORING BUDGETARY ALLOCATION:
The total cost allocated for post project monitoring is given in chapter 6, Section 6.8.1,Table
6-2, on page no.149.
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Chapter 8 Project Benefits
8 PROJECT BENEFITS
The Proposed Expansion is within the existing Premises. There is an existing Road
Connectivity to the NH 8A/41.
During the Construction and Operational Phase, thee will b a opportunity for the
employment. The required Man power shall be employed from the nearby Villages based on
their qualification. This will be result in a Positive impact on the Employment Opportunity.
More over the Steel Products from this plant will be supplied to many countries to full fill the
requirement for Steel.
Recommendation for Socio economic activities
Based on the various studies conducted during the baseline survey the following points
related to social environment have been highlighted in the study area
Workers from nearby villages shall be given priority for employment as per their
skills.
Company’s current socio-economic activities
In Chadawada village, company has built up protection wall on pond in 2015 which
helps for water management and also adding some infrastructure value.
Under CSR activities Company is giving facility to provide fodder into Sadavada
village Gaushala.
Under CSR company has provided 12 individual toilet blocks in Vondh village, earlier
they were facing many problems, in winter or in rainy season it was difficult to go
out for sanitation in open area.
Further Plan on Socioeconomic Activities
The company is committed for contribution of funds and provides the services for the
upliftment of local community in the nearby villages. The different activities which shall be
considered by the company, under the directives of Govt. of Gujarat are mentioned in this
chapter
Plantation on Road side.
Contribution in construction of toilet block for 100 poor family under
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“Pradhanmantri’s Swacchata Abhiyaan”
Contribution in towards health awareness Programmes.
Contribution in providing better medical infrastructure in nearby area of kutch
district.
Development of school at nearby Villages.
Scholarships to bright students.
Programs for environmental education and public participation shall be developed
with the help of audio visual aids to create awareness about the activities.
Proper awareness campaign shall be organized by the project proponent for water
conservation.
In order to increase the aesthetic environment, road side plantation program shall be
carried out in the nearby villages.
Group Insurance to all employees over and above the Employees State Insurance
Scheme
Annual get-together and rewards for workers’ kids who have shown brilliance in
education, sports, cultural activities
Fire & Safety Training will be imparted to employees.
Fire fighting and Safety Week will be organize and quiz and essay competitions will
be organized to develop awareness in employees on the subject.
Celebration of World Environment Day every year on 5th June will be marked by
plantation of number of trees by employees in order to develop awareness in them
about protecting environment from pollution and to save earth.
Community Awareness programmed like Aids awareness, Polio camps, Eye camps
and blood donation camps will be organized in the company and in its vicinity from
time to time for the benefit of employees and their families and people living in the
surrounding area.
8.1 EMPLOYMENT POTENTIAL
There will be increase in the employment facilities due to the proposed expansion project.
The total no. of worker to be employed for the proposed project is as given in Table 8-1.
Table 8-1: Employment generation for the proposed expansion project
Manpower Skilled Unskilled Total
250 150 400
ASR MULTIMETALS PVT LTD.
154
EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
Chapter 9 Disclosure of Consultant
9 DISCLOSURE OF CONSULTANT
The preparation of EIA was done by M/s Detox Corporation Pvt. Ltd. having NABET
accreditation for conducting EIA studies for project activities listed under Metallurgical
industry . The baseline study for the project was conducted by in-house laboratory of M/s
Detox Corporation Pvt. Ltd. having NABL certification. The EIA Team engaged in the
preparation of EIA report consist of professionals with multidisciplinary skill and relevant
experience required for undertaking this project.
KEY FACTS
Established in the year – 1995
Our Growth through years -
1995: Laid Foundation Stone of Detox Corporation Pvt Ltd. Firm Activities covered
fabrication & equipment supply
1997: Diversified into Turnkey Project Execution & Developed Core Competency for
Environmental Audit Reports
1998: Developed a Full Fledged State of Art Laboratory
1998: Construction of ETP’s & STP’s
2000: Developed core competence for preparation of EIA Study Reports
2002: Expansion and Modernization of Lab & Office.
2004: Certified for ISO 9001: 2000 (QMS)
2004: Established First Branch Office at Gandhidham, Kutch
2005: Tie up with Ozmotech, Australia for Converting Waste Plastic to Diesel
2006: Foundation laid for setting up a Total Hazardous Waste Management site at Kutch,
Gujarat
2008: Started Development of Integrated Common Hazardous waste management facility
in Kutch region in name of SEPPL
2009: Accreditated with NABET for EIA Study Reports NABL for State of Art Laboratory.
2013: Started Development of Integrated Common Hazardous waste incineration facility in
Dahej region in name of SEPPL
2014: Laid Foundation Stone of ACPTCL, CETP (Zero Liquid Discharge)
2016: Foundation laid for India’s largest TSDF in Central Gujarat.
ASR MULTIMETALS PVT LTD.
155
EIA, EMP, RA/DMP FOR STEEL
AND POWER PLANT
DETOX CORPORATION PVT. LTD.
ACCREDITATIONS
ISO 9001-2008 certification
NABL (National Accreditation Board for Testing & Calibration Laboratories)
NABET (National Accreditation Board for Education & Training) registration from
Quality Council of India as EIA Consultant
REGISTRATIONS
Class AA Contractor registration from Surat Municipal Corporation (SMC)
Recognized Environmental Auditors from GPCB
MoEF Registration for recognized Environmental Lab.
LIST OF EC & FAE INVOLVED IN REPORT PREPARATION
The list of experts involved in report preparation with authorization for MD of organization is
attached as second page of report.