Welcome to Environment - FINAL EIA AND EMP...
Transcript of Welcome to Environment - FINAL EIA AND EMP...
FINAL EIA AND EMP REPORTOf
Capacity Enhancement of Steel Manufacturing Unit
by
Replacing Existing Induction Furnaces and
Enhance production capacity from 45,000 MTPA to
1, 40,000 MTPA
By
M/s Vardhman Ispat Udyog
Located at
Village Bathri, Dist. Una, State-Himachal Pradesh
ToR Letter No: - F.No. . J-11011/187/2019-IA.II (I) dated 17th September, 2019
Monitoring Done by SHIVALIK SOLID WASTE MANAGEMENT LTD. (NABL
CertificateNo. NABET/EIA/1922/RA 0128 valid until 16.02.22 and MoEF & CC
Recognized)
PREPARED BY
SHIVALIK SOLID WASTE MANAGEMENT LIMITED
QCI/NABET EIA CONSULTANT ORGANIZATIONS
Registered Office:
Village Majra, Post Office Dabhota, Tehsil Nalagarh
Distt. Solan, Himachal Pradesh - 174101
Corporate Office:
SCO 20-21, 1st Floor, Near Hotel Dolphin, Baltana,
Zirakpur Punjab- 140 604
Phone/Telefax: 01762 – 509496
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 1
Table of Contents
CHAPTER-1: INTRODUCTION...................................................................................................... 46
1.1 INTRODUCTION ....................................................................................................................... 46
1.1.1 PURPOSE OF THE REPORT ................................................................................... 47
1.2 IDENTIFICATION OF THE PROJECT AND PROJECT PROPONENT ......... 48
1.3 BRIEF DESCRIPTION OF THE PROJECT AND ITS IMPORTANCE ............ 49
1.3.1 NATURE OF THE PROJECT ..................................................................................... 49
1.3.2 SIZE OF THE PROJECT .............................................................................................. 49
1.3.3 LOCATION OF THE PROJECT ................................................................................ 51
1.3.4 IMPORTANCE TO THE COUNTRY & REGION ............................................... 52
1.4 SCOPE OF THE STUDY – DETAILS OF REGULATORY SCOPING
CARRIED OUT (AS PER TERMS OF REFERENCE) ......................................................... 54
1.5 STRUCTURE OF THE EIA REPORT ............................................................................. 54
1.7 LAWS APPLICABLE TO THIS PROJECT .................................................................... 56
CHAPTER-2: PROJECT DESCRIPTION .................................................................................. 62
2.1 TYPE OF PROJECT ................................................................................................................ 62
2.2 NEED FOR THE PROJECT ................................................................................................ 62
2.3 LOCATION OF PROJECT (MAPS SHOWING GENERAL LOCATION,
SPECIFIC LOCATIONS, PROJECT BOUNDARY AND PROJECT SITE LAYOUT)
63
2.3.1 PROJECT SITE BREAK-UP ....................................................................................... 69
2.4 SIZE OR MAGNITUDE OF OPERATION ..................................................................... 69
2.5 SCHEDULE FOR APPROVAL AND IMPLEMENTATION .................................... 70
2.6 TECHNOLOGY AND PROCESS DESCRIPTION .................................................... 71
2.6.1 PROCESS DESCRIPTION .......................................................................................... 72
2.6.2 FACILITIES PROPOSED UNDER THE EXPANSION ................................... 76
2.7 WATER, MAN-POWER REQUIREMENT, POWER REQUIREMENTS AND
OTHER SITE SERVICES ................................................................................................................... 80
2.7.1 WATER SOURCE AND UTILIZATION .................................................................. 80
2.7.2 MAN-POWER REQUIREMENT ................................................................................ 82
2.7.3 POWER REQUIREMENT ............................................................................................ 82
2.8 COST OF THE PROJECT .................................................................................................... 83
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 2
2.9 DESCRIPTION OF MITIGATION MEASURES INCORPORATED INTO THE
PROJECT TO MEET ENVIRONMENTAL STANDARD, ENVIRONMENTAL
OPERATING CONDITIONS OR OTHER EIA REQUIREMENTS- ................................. 83
2.9.1 AIR POLLUTION & ITS MITIGATION MEASURES ........................................ 83
2.9.2 INDUSTRIAL WASTE WATER .................................................................................. 85
2.9.3 DOMESTIC WASTE WATER ..................................................................................... 85
2.10 List of industries ..................................................................................................................... 86
List of some major industries of district Una, are given below: ........................................ 86
2.11 SUMMARY ............................................................................................................................... 86
CHAPTER-3: DESCRIPTION OF THE ENVIRONMENT .................................................. 88
3.1 INTRODUCTION ....................................................................................................................... 88
3.2 SITE DESCRIPTION AND ITS ENVIRONMENT ...................................................... 88
3.3 METEOROLOGY ...................................................................................................................... 91
3.3.1 CLIMATE, TEMPERATURE AND RAINFALL .................................................... 91
3.3.2 METEOROLOGICAL SCENARIO OF THE STUDY AREA ......................... 92
3.3.3 WIND ROSE ....................................................................................................................... 92
3.3.4 ATMOSPHERIC INVERSION LEVEL/MIXING HEIGHT ............................... 93
3.4 LAND ENVIRONMENT .......................................................................................................... 94
3.4.1 LAND USE ........................................................................................................................... 94
3.4.2 LAND USE LAND COVER CLASSIFICATION USING REMOTE
SENSING DATA ................................................................................................................................. 95
3.4.3 GEOLOGY ........................................................................................................................... 99
3.4.4 TOPOGRAPHY ................................................................................................................. 99
3.4.5 SEISMIC CONSIDERATIONS ................................................................................ 100
3.4.6 SOIL CHARACTERISTICS ....................................................................................... 100
3.4.7 SAMPLING PROCESS & ANALYSIS ................................................................. 101
3.4.8 INTERPRETATION ...................................................................................................... 106
3.5 WATER ENVIRONMENT ................................................................................................... 107
3.5.1 HYDROGEOLOGY ....................................................................................................... 110
3.5.2 DRAINAGE PATTERN OF THE AREA .............................................................. 111
3.5.3 WATER QUALITY ASSESSMENT ....................................................................... 115
3.5.4 CONCLUSIONS:............................................................................................................ 123
3.6 AIR ENVIRONMENT ............................................................................................................ 123
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 3
3.6.1 AMBIENT AIR QUALITY MONITORING ........................................................... 123
3.6.2 PARAMETERS CONSIDERED FOR AIR QUALITY ASSESSMENT .. 123
3.6.3 AMBIENT AIR QUALITY MONITORING STATIONS .................................. 124
3.6.4 ANALYTICAL METHODS FOLLOWED FOR AMBIENT AIR QUALITY
MONITORING: ................................................................................................................................. 124
3.6.5 RESULTS AND CONCLUSIONS .......................................................................... 129
3.7 NOISE ENVIRONMENT ..................................................................................................... 131
3.7.1 AMBIENT NOISE MONITORING .......................................................................... 131
Table 3-13: Location of Noise Quality Monitoring Stations ......................................... 132
3.7.2 AMBIENT NOISE STANDARD ............................................................................... 134
3.7.3 ANALYSIS OF THE DATA ........................................................................................ 135
3.8 BIOLOGICAL ENVIRONMENT ....................................................................................... 135
3.8.1 INTRODUCTION ........................................................................................................... 135
3.8.2 OBJECTIVES OF ECOLOGICAL STUDIES .................................................... 135
3.8.3 METHODOLOGY ADOPTED FOR THE SURVEY ....................................... 136
3.8.4 FOREST COVER .......................................................................................................... 136
3.8.5 GENERAL VEGETATION STUDY OF THE AREA: ..................................... 137
3.8.6 STUDY PERIOD AND METHODOLOGY .......................................................... 138
3.8.7 METHODOLOGY .......................................................................................................... 138
3.8.8 TYPES OF FORESTS IN UNA DISTRICT: ...................................................... 139
3.8.9 FLORA OF THE STUDY AREA: ............................................................................ 140
3.8.10 FAUNA OF THE STUDY AREA ......................................................................... 142
3.8.11 WASTE LAND: ........................................................................................................... 144
3.8.12 CONCLUSION: .......................................................................................................... 144
3.9 SOCIO ECONOMIC STUDY ............................................................................................ 145
3.9.1 STUDY AREA ................................................................................................................. 146
3.9.2 METHODOLOGY .......................................................................................................... 146
3.9.3 BASELINE DATA .......................................................................................................... 147
3.9.4 DEMOGRAPHIC DETAILS OF THE STUDY AREA IN HIMACHAL
REGION .............................................................................................................................................. 151
3.9.5 OCCUPATIONAL PATTERNS OF THE STUDY AREA IN HIMACHAL
REGION .............................................................................................................................................. 151
3.9.6 DEMOGRAPHIC DETAILS OF THE STUDY AREA IN PUNJAB
REGION .............................................................................................................................................. 155
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 4
3.9.7 OCCUPATIONAL PATTERNS OF THE STUDY AREA IN PUNJAB
REGION .............................................................................................................................................. 155
3.9.8 BASIC AMENITIES ...................................................................................................... 159
3.9.9 SOCIAL IMPACT ASSESSMENT & CONCLUSION: .................................. 161
3.10 REHABILITATION &RESETTLEMENT (R&R) ACTION PLAN ................... 161
CHAPTER-4: ANTICIPATED ENVIRONMENTAL IMPACTS & MITIGATION
MEASURES 162
4.1 INTRODUCTION .................................................................................................................... 162
4.2 IMPACTS ON LAND ENVIRONMENT ........................................................................ 162
4.2.1 IMPACTS DURING CONSTRUCTION PHASE ............................................. 163
4.2.2 IMPACTS DURING OPERATIONAL PHASE .................................................. 163
4.2.3 MITIGATION MEASURES ........................................................................................ 163
4.3 IMPACTS ON AIR ENVIRONMENT ............................................................................. 163
4.3.1 IMPACTS DURING CONSTRUCTION PHASE ............................................. 163
4.3.2 IMPACTS DURING OPERATION PHASE ........................................................ 164
4.3.3 MITIGATION MEASURES ........................................................................................ 164
4.4 PROCESS AND FUGITIVE EMISSION AND CONTROL MEASURES ...... 169
4.4.1 IMPACT OF THE TRANSPORTATION AND MITIGATION MEASURES
171
4.4.2 TRAFFIC ANALYSIS ................................................................................................... 171
4.4.3 AIR QUALITY MODELING ....................................................................................... 173
4.5 IMPACTS OF NOISE AND VIBRATION DURING CONSTRUCTION PHASE
180
4.5.1 NOISE EXPECTED DURING OPERATION PHASE ..................................... 180
4.5.2 NOISE IMPACT ASSESSMENT AND MITIGATION MEASURE .......... 181
4.5.3 OTHER MEASURES ................................................................................................... 182
4.6 IMPACTS ON WATER ENVIRONMENT .................................................................... 182
4.6.1 IMPACTS DURING CONSTRUCTION PHASE ............................................. 182
4.6.2 IMPACTS DURING OPERATION PHASE ........................................................ 183
4.6.3 MITIGATION MEASURES ........................................................................................ 183
4.7 SOLID WASTE GENERATION AND ITS IMPACT ................................................ 183
4.8 IMPACT ON SOCIO-ECONOMIC ENVIRONMENT ............................................. 184
4.8.1 POSITIVE IMPACTS ................................................................................................... 184
4.8.2 ADVERSE IMPACTS: ................................................................................................. 185
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 5
4.8.3 MITIGATION MEASURES OF SOCIO ECONOMIC ENVIRONMENT 185
4.9 IMPACTS ON BIOLOGICAL ENVIRONMENT ........................................................ 186
4.10 RECOMMENDED PLANTS FOR GREEN BELT DEVELOPMENT .......... 187
4.11 RAIN WATER HARVESTING ...................................................................................... 189
4.11.1 RAIN WATER HARVESTING POTENTIAL OF THE AREA ................ 189
CHAPTER-5: ANALYSIS OF ALTERNATIVE TECHNOLOGY AND SITE ............ 192
5.1 ALTERNATE TECHNOLOGY .......................................................................................... 192
5.2 TECHNOLOGY ....................................................................................................................... 192
5.3 SITE ALTERNATIVES ......................................................................................................... 192
CHAPTER-6: ENVIRONMENT MONITORING PLAN ...................................................... 193
6.1 INTRODUCTION .................................................................................................................... 193
6.2 ENVIRONMENTAL MONITORING ............................................................................... 193
6.2.1 SOIL QUALITY MONITORING ............................................................................... 194
6.2.2 AIR QUALITY MONITORING .................................................................................. 194
6.2.2.1 STACK EMISSIONS ........................................................................................... 195
6.2.3 NOISE QUALITY MONITORING ........................................................................... 195
6.2.4 WATER QUALITY MONITORING ......................................................................... 195
6.2.4.1 GROUND WATER QUALITY MONITORING ......................................... 195
6.2.4.2 EFFLUENT QUALITY ......................................................................................... 196
6.2.5 GREENBELT DEVELOPMENT .............................................................................. 196
6.2.6 OCCUPATIONAL HEALTH ...................................................................................... 196
6.2.7 REPORTING SCHEDULE ........................................................................................ 196
6.2.8 MONITORING OF POLLUTION CONTROL EQUIPMENT ...................... 196
6.3 ENVIRONMENTAL MANAGEMENT ............................................................................ 197
6.3.1 OPERATION AND MAINTENANCE OF POLLUTION CONTROL
SYSTEM .............................................................................................................................................. 198
6.3.2 BUDGET FOR ENVIRONMENTAL MONITORING PROGRAM ............ 199
CHAPTER-7: ADDITIONAL STUDIES .................................................................................... 200
7.1 INTRODUCTION .................................................................................................................... 200
7.2 PUBLIC CONSULTATION ................................................................................................. 200
7.2.1 Advertisement OF Public Hearing ......................................................................... 201
7.3 ENVIRONMENTAL RISK ASSESSMENT ................................................................. 208
7.4 IDENTIFICATION OF HAZARDS ................................................................................... 209
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 6
7.5 ENVIRONMENTAL RISK EVALUATION.................................................................... 211
7.6 RISK MANAGEMENT MEASURES .............................................................................. 213
7.6.1 ON-SITE EMERGENCY PLAN ............................................................................... 213
7.6.2 OFF-SITE EMERGENCY PLANNING ................................................................ 214
7.7 OCCUPATIONAL AND SAFETY HAZARDS AND PREVENTIVE
MEASURES ........................................................................................................................................... 214
7.7.1 FIRST AID MEASURES ............................................................................................. 214
7.8 EXPOSURE CONTROLS AND PERSONAL PROTECTION ........................... 215
7.8.1 EXPOSURE CONTROLS.......................................................................................... 215
7.8.2 PERSONAL PROTECTIVE EQUIPMENT (PPE) .......................................... 215
7.8.3 FIRE FIGHTING FACILITIES .................................................................................. 217
7.9 OCCUPATIONAL HEALTH& SAFETY ........................................................................ 217
7.9.1 MAJOR HAZARDS ....................................................................................................... 218
7.10 DISASTER MANAGEMENT PLAN (DMP) ............................................................ 219
7.10.1 OBJECTIVES .............................................................................................................. 220
7.10.2 LEVEL OF ACCIDENTS ........................................................................................ 221
7.11 RESETTLEMENT & REHABILITATION (R&R)................................................... 222
CHAPTER-8: PROJECT BENEFITS ........................................................................................ 223
8.1 PHYSICAL INFRASTRUCTURE .................................................................................... 223
8.2 EMPLOYMENT OPPORTUNITIES ............................................................................... 223
8.2.1 INDIRECT EMPLOYMENT ....................................................................................... 223
8.2.2 INDUSTRIES ................................................................................................................... 223
8.3 SOCIAL INFRASTRUCTURE .......................................................................................... 224
8.4 CORPORATE ENVIRONMENT RESPONSIBILITY (CER) ............................... 224
8.5 CONCLUSION ......................................................................................................................... 225
CHAPTER-9: ENVIRONMENTAL COST BENEFIT ANALYSIS ................................. 226
9.1 ENVIRONMENTAL COST BENEFIT ANALYSIS ................................................... 226
CHAPTER-10: ENVIRONMENTAL MANAGEMENT PLAN ............................................ 227
10.1 INTRODUCTION ................................................................................................................ 227
10.2 PROPOSED ENVIRONMENTAL MITIGATION MEASURES ...................... 227
10.3 DETAILS OF MANAGEMENT PLAN ....................................................................... 231
10.3.1 AIR ENVIRONMENT ............................................................................................... 231
10.3.2 AIR POLLUTION CONTROL EQUIPMENTS .............................................. 233
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 7
10.3.3 NOISE ENVIRONMENT ........................................................................................ 233
10.3.4 WATER ENVIRONMENT ...................................................................................... 234
10.3.5 GREEN BELT DEVELOPMENT ........................................................................ 234
10.4 HEALTH AND SAFETY .................................................................................................. 236
10.5 IMPLEMENTATION OF EMP AND MONITORING ........................................... 238
10.6 ENVIRONMENT MANAGEMENT CELL ................................................................ 238
10.6.1 MONITORING & RESPONSIBILITY ............................................................... 240
10.7 BUDGETARY PROVISION FOR EMP IMPLEMENTATION ........................ 241
CHAPTER-11: SUMMARY AND CONCLUSIONS ............................................................... 242
11.1 SUMMARY ............................................................................................................................ 242
11.2 CONCLUSIONS ................................................................................................................. 243
CHAPTER-12: DISCLOSURE OF CONSULTANTS ........................................................... 244
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 8
List of Tables
Table 1-1: Salient Feature of the Project .................................................................................... 49
Table 1-2: Laws Applicable To the Project ................................................................................. 57
Table 2-2: Project Site Break-Up.................................................................................................... 69
Table 2-3: Project Details ................................................................................................................ 70
Table 2-4: Project Implementation Schedule ......................................................................... 71
Table 2-5: Proposed Machinery ..................................................................................................... 71
Table 2-6: Proposed Melting & Casting Section ........................................................................ 77
Table 2-7: Rolling Mill Section ........................................................................................................ 77
Table 2-8: Annual Raw Material Requirement At 100% Capacity ..................................... 78
Table 2-9: Project Cost Break-Up .................................................................................................. 83
Table 2-10: Induction Furnace of Capacity ................................................................................ 84
Table 2-11: Fugitive Emission Sources & Mitigation Measures .......................................... 84
Table 3-1: Observed Meteorological Data .................................................................................. 91
Table 3-2: 10 km Radius Buffer Land Use/ Land Cover Classification ............................. 98
Table 3-3: Soil Quality Data Locations ...................................................................................... 101
Table 3-4: Standard Soil Classification ...................................................................................... 102
Table 3-5: Soil Quality Data (March, 2019-May, 2019) ....................................................... 104
Table 3-6: Location of Ground Water Monitoring Stations ............................................... 115
Table 3-7: Groundwater Monitoring Results ......................................................................... 117
Table 3-8: Surface Water Locations ........................................................................................... 120
Table 3-9: Surface Water Quality Monitoring Results ........................................................ 122
Table 3-10: Ambient Air Quality Monitoring Locations ..................................................... 124
Table 3-11: Methods Adopted For Ambient Air Parameters ............................................ 126
Table 3-12: Ambient Air Quality Data ....................................................................................... 128
Table 3-13: Location of Noise Quality Monitoring Stations .......................................... 132
Table 3-14: Permissible ambient noise standards in dB (A) ............................................ 134
Table 3-15: Noise Quality Data .................................................................................................... 134
Table 3-16: Mode of Data Collection & Parameters Considered During the Survey 138
Table 3-17: Flora of the Core Zone ............................................................................................. 140
Table 3-18: Flora of the Buffer Zone .......................................................................................... 140
Table 3-19: Fauna of the Core Zone ....................................................................................... 142
Table 3-20: Fauna of the Buffer Zone ........................................................................................ 142
Table 3-21: Demographic Profile of the Study Area within the Boundary of Two
Tehsils in Two Districts and States ............................................................................................ 148
Table 3-22: Demographic Profile of the Study Area within 10 Km Radius from the
Project Site (Himachal Region) ................................................................................................... 149
Table 3-23: Demographic Profile of the Study Area within 10 Km Radius from the
Project Site (Punjab Region) ........................................................................................................ 152
Table 3-24: Demographic Profile of the Study Area (10km) In Tehsil & District
Una Himachal Pradesh ................................................................................................................... 155
Table 4-1: Solid and Hazardous Wastes Management Plan .............................................. 183
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 9
Table 4-2: Recommended Plant Species for Green Belt Development .......................... 188
Table 6-1: Ambient Air Quality Frequency and Parameters ............................................. 194
Table 6-2: Stacks to Be Monitored After the Implementation of the Expansion Plan195
Table 6-3: Monitoring of Effluent Quality.................................................................................. 196
Table 6-5: Environmental Monitoring (Operation Phase) ................................................ 197
TABLE 6-6: Cost Of Environmental Monitoring Program .................................................. 199
Table 10-3: Environment Management Cell ........................................................................... 238
Table 10-4: EMP Budget ................................................................................................................. 241
List of Figures
Figure 1-1: Location Map .................................................................................................................. 52
Figure 2-1: Pillar Co-Ordinate Map of Project Site .................................................................. 65
Figure 2-2 : Topographical Map of the Project Site ................................................................. 66
Figure 2-3: Plant Layout .................................................................................................................... 67
Figure 2-4: Site Photographs ........................................................................................................... 68
Figure 2-5: Existing Manufacturing Process Flow Diagram ................................................. 72
Figure 2-6: Material Balance Diagram ......................................................................................... 79
Figure 2-7: Water Balance Chart .................................................................................................... 81
Figure 3-1: Location Map ................................................................................................................ 90
Figure 3-2: Wind Rose Diagram ..................................................................................................... 93
Figure 3-3: Mixing Height for the Study Area Are Given Below For the Pre-
Monsoon Season .................................................................................................................................. 94
Figure 3-4: Land use Map ................................................................................................................. 97
Figure 3-5: Graphical Presentation of Land Use/ Land Cover Classification ................. 99
Figure 3-6: Soil Monitoring Location ......................................................................................... 103
Figure 3-7: Digital Elevation Model ........................................................................................... 109
Figure 3-8: Drainage Map of the Area ....................................................................................... 112
Figure 3-9: Contour Map ................................................................................................................ 114
Figure 3-10: Groundwater Monitoring Location ................................................................... 116
Figure 3-11: Surface Water Monitoring Locations ............................................................... 121
Figure 3-12: Air Quality Monitoring Locations ...................................................................... 127
Figure 3-13: Noise Monitoring Locations ................................................................................ 133
Figure 3-14: Showing Location of Villages’within10 Km Radius of Boundary ........... 147
Figure 4-1: Induction Furnace And Its Air Pollution Control Device ........................ 166
Figure 4-2Spatial distribution of predicted GLCs of PM10 ................................................ 176
Figure 4-3Spatial distribution of predicted GLCs of PM2.5 ............................................... 177
Figure 4-4Spatial distribution of predicted GLCs of SO2 .................................................... 178
Figure 4-5 Spatial distribution of predicted GLCs of NO2 .................................................. 179
Figure 4-6 Rain Water Harvesting Pit Design ........................................................................ 191
Figure 6-1: Organization Structure of Environmental Management ............................. 198
Figure 7-1 : Environmental Risk Qualitative Analysis Flow Sheet .................................. 212
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 10
Figure 10-1 Proposed Environmental Mitigation Measures ............................................. 227
Figure 10-2 List of plant species for green belt development .......................................... 235
LIST OF ANNEXURES
Annexure 1: Executive Summary
Annexure 2: NABET Certificate
Annexure 3: Land Documents
Annexure 4: Permission of water
Annexure 5: Permission of Power
Annexure 6: CTO
Annexure 7: Drainage Map
Annexure 8: Undertaking for producer gas
Annexure 9: Baseline Test Reports
Annexure 10: Panchayat letter for Green Belt Area
Annexure 11: APCD test report
Annexure 12: Ash test report
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 11
ToR Letter
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 12
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 13
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 14
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 15
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 16
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 17
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 18
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 19
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 20
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 21
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 22
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 23
Compliance of ToR
The compliance of Terms of Reference (TOR) for “Capacity Enhancement of Steel
Manufacturing Unit by Replacing Existing Induction Furnaces and Enhance
production capacity from 45,000 MTPA to 1,40,000 MTPA by M/s Vardhman Ispat
Udyog Located at Village Bathri, Dist. Una, State-Himachal Pradesh”. The
compliance of Terms of References is given in Table below-
S. No.
TOR Points Compliance Reference
1 Executive Summary Executive Summary attached as Annexure 1 with EIA Report
Annexure 1
2 Introduction
i. Details of EIA Consultant including NABET accreditation.
Shivalik Solid Waste Management Limited is an NABET accredited consultant for the project.
Certificate No. NABET/EIA/1922/RA0128and valid up to 16thFeb, 2022and NABET Certificate is attached as Annexure 2.
Annexure 2
ii. Information about the project proponent
Shri. Pradeep Garg & Shri. Subodh Singlais Board of Directors of the company.
M/s Vardhman Ispat Udyog Limited is a Limited company in the business of production of MS Billets and Rolled products. The company has been promoted by a Group of experience businessmen who are presently engaged in manufacturing and trading of various products.
Chapter 1, Item No. 1.2
iii. Importance and Benefits of the Project
Importance of Project:
In India, a major part of steel is consumed in engineering applications, followed by automobiles and construction. As the growth of steel, as is well known, is dependent upon the growth of economy, industrial production and infrastructure sectors, demand of steel is day by day increasing. India has been a net importer of steel but in recent
Chapter 1, Item No.1.3.4
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 24
years, we might become a net exporter. Therefore, production of steel at the regional level will be highly beneficial & help in reduction of imports.
Benefits of Projects:
This project will benefit the local people by way of direct & indirect employment which would improve the living conditions of the people and infrastructure development through socioeconomic measures taken up by proponent.
Chapter 8
3 Project Description
i. Cost of Project and time of completion
Cost of the project is Rs. 3038.00Lacs. Chapter2, Item No. 2.8
Completion schedule of the project is 24 months. “Zero date” for a project is reckoned as the date on which the all statutory clearance to start the project are received.
Chapter 2, Item No. 2.5.1
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 25
ii.
Products with capacities for the proposed project.
S. No.
Details Existing After Expansion
1. Induction Furnace
IFs of 4 TPH and 6 TPH & Rolling Mill
2 IFs of 10 TPH each +
Rolling Mill
2. Production Capacity
18,000 MT/Annum through IFs and CCM
27,000 MT/annum through Reheating Furnaces.Total 45000MTPA
1,40,000 MT/annum
3. Raw materials
47,250 MT/annum
1,47,000 MT/annum
4. Products
TMT Bars TMT Bars
Chapter 2, Item No.-2.4
iii. If expansion Project, details of existing products with capacities and whether adequate land is available for expansion, reference of earlier EC if any.
The proponent plans to replace existing induction furnace capacity of 4 T & 6 T to new furnaces of 2x10 T each based on the latest technology. The new furnace is power efficient leading to saving of 50 units of electricity (Reduction from 600 units to 550 units). Total Plot Area – 2.708Ha.
Land documents are attached as Annexure 3.
The office Memorandum issued by Ministry of Environment and Forests,
Chapter 2, Item No.-2.4,
Land documents as Annexure 3
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 26
Government of India dated 24th December 2013, states that the nontoxic secondary metallurgical processing industries involving operation of furnaces, such as induction and electric arc furnaces, submerged arc furnaces and cupola with capacity <30,000 MTPA doesn’t come under the purview of EIA. Hence EC was not required for the existing production capacity
iv. List of raw materials required and their source along with mode of transportation
MS Scrap and Ferro alloys and other additives will be used as raw material. Raw materials will be transported to site through trucks.
Chapter No. 2, Item No. 2.6.2
v. Other chemicals and materials required with quantities and storage capacities.
Not applicable as there are no chemicals used in process. Only Lab chemical used for laboratory testing.
---
vi. Details of Emission, effluents, hazardous waste generation and their management.
The main source of emissions will be from Induction Furnace and that will be controlled by the Air Pollution Control System like, Pulse Jet Bag filter, I.D. Fan.
Closed circuit cooling system will be adopted in SMS (Steel Melting Shop) & rolling mill. Hence, there will not be any wastewater generation from process and cooling. The only wastewater generated from domestic use. Domestic waste water which will be treated in STP and treated water will be used for plantation purpose
The APCD dust from Bag filters as well as used oil is the hazardous waste generated from the project which are stored and transported to TSDF.
Chapter No. 2, Item No. 2.9
vii. Requirement of water, power, with source of supply, status of approval, water balance diagram, manpower requirement (regular and contract)
Approximately 31KLD water will be used out which 21KLD is used for operation purpose and 10KLD is used for domestic purpose.
Chapter No. 2, Item No. 2.7.1
Source of water: Bore well
Permission has been applied to Irrigation and Public Health Department, Himachal Pradesh.
Chapter No. 2, Item No. 2.7.1
Annexure 4
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 27
Application has been attached as Annexure 4.
Power load of 9,925 KW (Existing 6398 KW & additional 3527 KW) will be available to run the plant & machinery during Construction and Operation Phase.
Source: Himachal Pradesh State Electricity Board. Permission from HPSEB vide letter no.8055-62 dated 16.11.2018 has been attached Annexure 5.
Chapter No. 2, Item No. 2.7.3
Annexure 5
In case of power failure, existing DG set of 125 KVA is there & after expansion, DG sets of 125 & 250 KVA will be provided.
After expansion, total 184 workers will be there, out of which, 14 will be residing within the project premises.
Chapter No. 2, Item No. 2.7.2
Detailed given in Chapter 2.
viii.
The project proponent shall furnish the requisite documents from the competent authority in support of drawl of ground water and surface water and supply of electricity.
NOCApplication of Water and HPSEB permission has been attached as Annexure 4 & 5
Annexure 4 & 5
ix. Process description along with major equipment’s and machineries, process flow sheet (quantitative) from raw material to products to be provided
Process description of Induction furnace, Continuous Casting Machine given with schematic process flow diagram in chapter 2.
Chapter No. 2, Item No. 2.6
x. Hazard identification and details of proposed safety systems.
Details of Hazard identification with the process, Risk Analysis and Mitigation measures are incorporated in the EIA report.
Chapter 7, Item No. 7.4
xi. Expansion/Modernization proposals
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 28
a. Copy of all the environmental clearance(s) including amendments thereto obtain for the project from MOEF/SEIAA shall be attached as annexure. A certified copy of the latest monitoring report of the Regional Office of the Ministry of Environment and Forests as per circular dated 30thMay, 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 on-going/existing operation of the project from SPCB shall be attached with the EIA-EMP report.
As per the Ministry of Environment & Forests, New Delhi notification, dated 14th September, 2006, All the Induction Furnace and Rolling Mill plants were listed at S.N. 5(k) 3(a) under Secondary Metallurgy Industry under Category ‘B’ in EIA Notification, 2006. The proposal shall be appraised at the Central level from the MoEF&CC as the location of project is within 10 Kms. radius of Inter State boundary and applicability of General Condition for Induction Furnaces as per amendment issued on 1st December, 2009 and office memorandum 24th December 2013.
Proposed addition of two Induction Furnaces of 2x10 MT Each for making additional capacity of 95,000MT/annum with total capacity (existing & proposed) 1,40,000 MT/Annum.
Hence, the project has freshly applied for Environmental Clearance. The existing project was accorded Consent to Operate by Himachal Pradesh State Pollution Control Board vides letter. No. HPSPCB /PCB-ID10611 (H N Steel) & HPSPCB /PCB-ID10264 (S R Steel) validity of CTO is up to 31.03.2019 and 31.03.2023(Attached as Annexure 6) respectively.
Annexure 6
b. In case the existing project has not obtained environmental clearance reasons for not taking EC under the provisions of the 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,
The office Memorandum issued by Ministry of Environment and Forests, Government of India dated 24th December 2013, states that the nontoxic secondary metallurgical processing industries involving operation of furnaces only, such as induction and electric arc furnaces, submerged arc furnaces and cupola with capacity <30,000 MTPA doesn’t come under the purview of EIA. Hence, EC was not required earlier for the production of 95 MTPA (28800 MT/year) CTE application for expansion.
Compliance to CTO is being done
…...
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 29
compliance report to the conditions of consents from the SPCB shall be submitted.
continuously by project proponent.
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 considered.
M/s Vardhman Ispat Udyog Limited is located at Village Bathri, Tehsil Haroli & Dist. Una, Himachal Pradesh
Location of the project site covering and justification for selecting the site mentioned in report.
Details are given in chapter 2.
Chapter 2, Item No. 2.3
ii. A toposheet of the study area of radius of 10 km 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).
A toposheet of the study area of radius of 10 km and site location incorporated in the report. There is no eco-sensitive area located within 10 km study area of the project site.
Chapter 2 as Figure 2-2
iii. Co-ordinates (lat-long) of all four corners of the site.
Map showing co-ordinates (latitude-longitude) of all corners of the site is given in EIA Report.
Detailed in chapter 2.
Chapter 2 as Figure 2-1,
iv. Google map-Earth downloaded of the project site.
The project site is surrounded by various steel & pharmaceutical industries site and is surrounded by MDR41 (at a distance of approx. 2 km). Google map-Earth downloaded for the project attached in a report. There are no eco sensitive areas located within 10 km study area of the project. River Swan lies in the east of the project side (At a distance of approx. 2 km).
Chapter 2 ,as Figure 2-2
v. Layout maps indicating existing units as well as proposed unit indicating storage area, plant area, greenbelt area, utilities etc. If located within an industrial area/ Estate/
Plant is located on the private land owned by M/s. Vardhman Ispat Udyog. Layout maps of the proposed unit indicating storage area, plant area, greenbelt area, utilities etc. given in chapter 2.
Chapter 2; Figure 2-3
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 30
Complex, layout of the industrial Area indicating location of unit within the industrial area Estate.
vi. Photographs of the proposed and existing (if applicable) plant site. If existing, show photographs of plantation greenbelt, in particular.
Photographs of the proposed and existing plant site attached in report and as per CPCB Guidelines, green belt will be developed. i.e. 33percent of the total area (0.80 hectare).
Chapter 2; Figure 2-4
vii. Land use break-up of total land of the project (identified and acquired), government/ private – agricultural, forest, wasteland, water bodies, settlements etc. Shall be included (not required for industrial area)
As plant site is already established and the proposed project will be carried out in the existing premises. It is private land.
Land use breakup of project site given in chapter 2 of EIA Report.
Chapter 2; Item No. 2.3.1
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.
A list of major industries with name and type of the district is incorporated in the report.
Chapter 2,Item No.2.10
ix. Geological features and Geo-hydrological status of the study area shall be included.
Geo-Hydrological status of the area incorporated in chapter 3 in the EIA Report.
Chapter 3 Item No. 3.4.2
x. Details of drainage of the project up to 5 km 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
There are two streams located within 10 km east of the project site flowing from north to south.
Swan river and Sutlej river are the perennial rivers is located within 10 km. in the east of the project site and flows from north to south. There is no flood history in the last 30 years.
Drainage Map of the Study area as attached as Annexure 7 in EIA Report.
Chapter 3 Item No. 3.5.2
Annexure 7
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 31
and maximum flood level of the river shall be provided. (mega green field projects)
xi. Status of acquisition of land. If acquisition is not complete, stage of the acquisition process and expected time of complete possession of the land.
M/s Vardhman Ispat Udyog has acquired M/s H.N Steel Casting Pvt. Ltd, M/s S.R Steels along with the land of Mr. Rakesh Kumar in village Bathri, Distt. Una for manufacturing of TMT Bars. Land documents are attached as Annexure3.
Annexure 3
xii. R & R details in respect of land in line with state Government policy.
There is no displacement of any person due to the project and hence the R&R Plan is not required.
Chapter 7, Item No. 7.11
5 Forests and wildlife related issues (if applicable)
i Permission and approval for the use of forest land (forestry clearance), if any, and recommendations of the State Forest Department (if applicable).
Such permission is not required as the project does not involve any forest land.
---
ii. Land use map based on High resolution satellite imagery (GPS) of the proposed site delineating the forestland (in case of projects involving forestland more than 40 ha)
Land use map based on High resolution satellite imagery (GPS) of the proposed site incorporated in the report.
Chapter No. 3, Item 3.4.2&Figure 3-4
iii. Status of Application submitted for obtaining the stage I forestry clearance along with latest status shall be submitted.
No such clearance is required.
iv. The projects to be located within 10 km of the National Parks, Sanctuaries, Biosphere Reserves, Migratory
There are no National Parks, Sanctuaries, Biosphere Reserves, and Migratory Corridors of wild animals within 10 km radius of the study area.
Chapter 2, Figure 2-2
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 32
Corridors of wild animals, and the project proponent shall submit the map duly authenticated by chief wildlife warden showing these features vis-à-vis the project location and the recommendations or comments of the chief wildlife warden-thereon.
10 km buffer map attached in EIA report
v. Wildlife Conservation Plan duly authenticated by chief wildlife warden of the state government for conservation of schedule I fauna, if any exists in the study area.
There is no Scheduled I fauna within 10 km radius of the project.
List of flora and fauna is incorporated in chapter 3 in the EIA Report.
Chapter 3, Item No. 3.8.9
vi. Copy of application submitted for clearance under wildlife (Protection) Act, 1972 to the standing committee of the National Board Wildlife.
Not Applicable as there is no wildlife/national park within 10 km radius of the project site.
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.
Atmospheric Inversion Level/Mixing Height
Atmospheric inversion, a reversal of the normal behavior of temperature in the troposphere (the region of the atmosphere nearest the Earth's surface), in which a layer of cool air at the surface is overlain by a layer of warmer air. Inversions are a result of the vertical temperature profile of air.
Chapter 3, ItemNo.3.3.4
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,
Based on CPCB guidelines, monitoring of Air Quality for the study area of the project has been done in 9 locations and incorporated in the report.
Air Quality Baseline data incorporated in the Chapter 3 and reports are attached as Annexure 9.
Chapter 3,
Air testing locations are given in table 3-10and test results are given in table 3-12
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 33
population zone and sensitive receptors including reserve forests.
Annexure 9
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 as an annexure to the EIA report.
As per NAQQM Notification of Nov, 2009 the AAQ measurement for 12 weeks of all the stations are attached.
Min., max., average and 98 percentile values for each of the AAQ parameters from data of all AAQ stations are also given.
Baseline Monitoring reports attached as Annexure 9
Chapter 3; Table 3-12
Annexure 9
iv. Surface water quality of nearby River (60m upstream and downstream) and other surface drains at 8 locations as per CPCB/MoEF& CC guidelines.
The surface water quality of 3 locations from the nearby river & other surface drains has been made as per the guidelines issued by CPCB/MoEF& CC guidelines.
Details in chapter 3 and baseline Monitoring reports attached as Annexure 9.
Chapter 3;Table 3-5
Annexure 9
v. Whether the site falls near to polluted stretch of river identified by the CPCB/MoEF& CC guidelines.
No, the site is not falling near polluted stretch of the river, but Swan River is approx. 2.0 km away from the project site.
5 km drainage map attached as Annexure 8.
Annexure 8
vi. Ground water monitoring at minimum at 8 locations shall be included.
Ground water monitoring of 9 locations has been done and their analysis results incorporated in EIA Report.
Detailed in Chapter 3; and also attached
Chapter 3; Ground water sample location given in Table 3-6and results given in Table 3-7
Annexure
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 34
as Annexure9 9
vii. Noise levels monitoring at 8 locations within the study area.
Noise levels monitoring has been done and incorporated in EIA report.
Detailed in Chapter 3 and Lab report attached as Annexure9
Chapter 3; Item No. 3.7.1
Lab report attached as Annexure 9
viii.
Soil characteristic as per CPCB guidelines
Characteristics of Soil has been done and incorporated in the report.
Detailed in Chapter 3 and Lab reports are attached as Annexure 9
Chapter 3; Item No. 3.4.7
Annexure 9
ix. Traffic study of the area, type of vehicles, frequency of vehicles for transportation of materials, additional traffic due to proposed project, parking arrangements etc.
Trucks will be used for the transportation purpose while movements covered trucks with tarpaulin will be preferred, proper tuning of vehicles will be maintained while exiting or entering of trucks in the site premises. Proper parking area for vehicles already exists within the site premises.
Traffic study for the project has been done and given in chapter 4 in the EIA Report.
Chapter 4,
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.
Ecology & Biodiversity study for 10 km radius of the project site has been done & incorporated in chapter 3 in the EIA Report.
Chapter 3, Item No.3.8
xi. Socio-economic status of the study area.
Project is positively upgrading the socio-economic status while providing employment.
Socio-economic study for 10 km radius
Chapter No. 3; Item No. 3.9
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 35
study area has been done and incorporated in EIA Report. Detailed in chapter 3.
7 Impact Assessment and environment Management Plan
i Assessment of ground level concentration of pollutants from the stack emission based on site-specific meteorological features. In case the project is located on a hilly terrain the AQIP modeling shall be done using inputs 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.
The project is not located on a hilly terrain.
Air Quality Modeling for the cumulative emission estimation from the stack and transportation is given in chapter 4.
Chapter 4, Item No.4.4.2
ii. Water quality modeling- in case, if the effluent is proposed to be discharged into 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.
Recycling of water will be done, and surplus recycled water will be used for the plantation purpose. No effluent will be discharged out from the premises.
Hence such modeling is not applicable.
---
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 36
iii. Impacts of the transport of the raw materials and end products on the surrounding environment shall be assessed and provided. In the 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.
Transportation of raw materials will be done through trucks from nearby markets.
During transportation covered trucks will be used from the nearby associated industries for the raw material.
Regular water sprinkling will be done during transportation to suppress the dust emission as this is one of the major impacts during transportation.
It is also certified that only Pollution certified vehicles will only use for the same purpose.
Chapter 4, Item no. 4.4.1
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.
Complete water balance for the proposed project incorporated in the report. This project is based on “Zero Liquid Effluent Discharge” Concept as complete recycling of water will be done and treated water from soak pit will be used for plantation purpose. Domestic wastewater which will be treated in STP and treated water will be used for plantation purpose.
Detailed in Chapter 2.
Chapter 2, Item No. 2.7.1
v. Details of stack emission and action plan for control of emissions to meet standards.
Emissions from all the stacks shall be monitored once in a quarter using the manually operated stacks emissions monitoring equipment.
Chapter; Item No. 6.2.2.1
vi. Measures for fugitive emission control
Main source of Fugitive emission is from the induction furnace and pulse jet controller will be used as air pollution control device.
Chapter 4, Item No. 4.3.3
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
APCD dust and used oil are generated hazardous waste.
APCD dust sent to TSDF site for disposal. Used oil will sent to authorized recyclers.
Chapter 4, Item No. 4.6.3
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 37
concept of waste-minimization, recycle/recover techniques, energy conservation and natural resource conservation.
Detailed in chapter 4.
viii.
Proper utilization of fly ash shall be ensured as per Fly Ash Notification, 2009. A detailed plan of action shall be provided.
Fly ash will not be generated during processing.
---
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.
As per CPCB Guidelines 33% of the total land (i.e.0.8 hectare) will be used for Green Belt Development. Layout Plan showing proposed green belt area has been incorporated in the EIA report.
Detailed in Chapter 2.
Panchayat Letter for Green/belt is attached as annexure 10.
Chapter 10, Item No.10.4
Greenbelt layout given in Chapter 2, Figure 2-3
Annexure 10.
x. Action plan for rainwater harvesting measures at plant site shall be submitted to harvest rainwater from the roof tops and storm water drain and also to use for the various activities at the project site to conserve fresh water and reduce the water requirement from other sources.
Approx.12849 m3 of run-off rainwater will be harvested every year.
Detailed Rainwater Harvesting has been incorporated in the EIA Report
Chapter 4, Item No. 4.10
xi. Total capital cost and recurring cost/annum for environmental pollution control measures shall be included.
Total capital cost and recurring cost/annum for environmental pollution control measures have been incorporated in the report.
Chapter 10, Item No. 10.8
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 38
xii. Action plan for post-project environmental monitoring shall be submitted.
Action plan for post-project environmental monitoring has been incorporated in the report and details are given in chapter 6.
Chapter 6; Item No. 6.2
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.
Onsite and Offsite Disaster (natural and Man-made) preparedness and emergency management plan including Risk Assessment and damage control incorporated in the report which is linked with District Disaster Management Plan. Details in Chapter 7.
Chapter 7, Item No. 7.6
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 so that health of the workers can be preserved.
Proper Occupational & Safety Hazards measures are incorporated in the report.
Periodical health check-up of workers will also be carried out.
Details in Chapter 7.
Chapter 7, Item No. 7.9
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, color vision and any other ocular defect) ECG during pre-placement and periodical examinations give the details of the same. Details regarding
As this is existing unit, therefore proper health checkup of the workers has been carried out and recorded.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 39
last month analyzed data of above mentioned parameters as per age, sex, duration of exposure and department wise.
iii. Annual report of health status of workers with special reference to Occupational Health and Safety.
Occupational Health and Safety measures detailed in the chapter 7 of the EIA report.
Annual checkup of employees is done.
Chapter 7, Item No. 7.9
iv. Plan and fund allocation to ensure the occupational health & safety of all contract and casual workers.
Protective equipment’s will be provided to the workers to ensure the occupation health & safety.
A budget of Rs.2.0 Lakhs has been kept for occupational health & safety.
Chapter 7, Item No. 7.9
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.
Environmental Policy for the company has been incorporated in the report.
Chapter 10, ItemNo.6.2.2.1
ii. Does the environment Policy prescribe for standard operating process procedures to bring into focus any infringement/deviation/violation of the environmental clearance conditions? Details of this system may be given.
Environment Policy will be committed to comply with the legal and other requirements.
Company will have the system of reporting of Non-conformances/violation of any Environmental Law/Policy to their Board of Directors as per their management system.
Chapter 10, Item No. 10.7
iii. What is the hierarchical system or administrative order of the company to deal with the environmental issues and for ensuring compliance with the
A well-defined Environment Monitoring Cell will be constituted to deal with the environmental issues and for ensuring compliance with the environmental clearance conditions.
Chapter 10, Item No. 10.7
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 40
environmental clearance conditions? Details of this system may be given.
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? This reporting mechanism shall be detailed in the EIA report.
Yes the company has well laid down system of reporting of non-compliances/violations of environmental norms to the Board of Directors of the company and/or shareholders.
Chapter 10, Item No. 10.7
10 Details regarding infrastructure facilities such as sanitation, fuel, restroom etc. to be provided to the labour force during constructions as well as to the casual workers including truck drivers during operation phase.
As this is operational plant, these facilities exist. No additional facilities will be required.
---
11 Corporate Environment Responsibility (CER)
i. To address the Public Hearing issues, an amount as specified under Ministry’s Office Memorandum vide F. No. 22-65/2017-IA.III dated 1st May 2018 amounting to Rs….crores, shall be earmarked by the project proponent, towards Corporate Environment Responsibility (CER). Distinct CER projects shall be carved out
Corporate Environment Responsibility (CER) Budget towards capital expenditure in accordance to the MoEF&CC’s Office Memorandum F.No. 22-65/2017-IA.III dated 01.05.2018 for Social Welfare. 1.0% of project cost i.e 25 lakhs will be earmarked for the corporate environment Responsibility (CER).
Chapter 8; Item No. 8.4
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 41
based on the local public hearing issues. Project estimate shall be prepared based on PWD schedule of rates for each distinct Item and schedule for time bound action plan shall be prepared. These CER projects as indicated by the project proponent shall be implemented along with the main project. Implementation of such program shall be ensured by constituting a Committee comprising of the project proponent, representatives of village Panchayat & District Administration. Action taken report in this regard shall be submitted to the Ministry’s Regional Office. No free distribution/donations and or free camps shall be included in the above CER budget
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
No litigation is pending against the project.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 42
status of the case.
13 A tabular chart with index for point wise compliance of above TORs.
Complied
14 The TOR prescribed shall be valid for a period of three years for submission of EIA-EMP reports along with Public Hearing Proceedings (wherever stipulated)
Complied
Additional TORs for Induction/arc furnace/cupola furnaces 5 TPH or more
1. Complete process flow diagram describing each unit, its processes and operations, along with material and energy inputs & outputs (material and energy balance).
Complete process flow diagram describing each unit, its processes and operations, along with material and energy balance diagrams are given in Chapter-2 of EIA Report.
Chapter 2; Item No.2.6.1 and Figure 2-6
2. Emission from sulphuric acid plant and sulphur muck management.
Not Applicable -
3. Details on installation of Continuous Emission Monitoring System with recording with proper calibration system
Post commissioning monitoring and submission of half yearly report on compliance to the Regional office of MoEF&CC in Dehradun, Uttrakhand.
Budgetary provision for online continuous emission monitoring system is given in EMP.
Chapter 4 Item No.4.3.3
4. Details on toxic metals including fluoride emissions
NA -
5. Details on stack height.
Stack height will be 30m and sampling point and sampling platform will be provided with ladder and guard.
Chapter 4; Item No. 4.3.3
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 43
6. Details on ash disposal and management
APCD dust is toxic waste material generated due to manufacturing process and APCD dust will sent to TSDF for proper disposal. APCD dust and ash test report has been incorporated as Annexure 11&12
Chapter2, Item No. 2.6.2 Annexure 11&12
7. Complete process flow diagram describing process of lead/zinc/copper/ aluminium, etc.
NA
8. Details on smelting, thermal refilling, melting, slag fuming, and Waelz kiln operation
Not Applicable -
9. Details on Holding and de-gassing of molten metal from primary and secondary aluminium, materials pre-treatment, and from melting and smelting of secondary aluminium
Not Applicable ---
10. Details on toxic metal content in the waste material and its composition and end use (particularly of slag).
APCD dust is toxic waste material generated due to manufacturing process and APCD dust will sent to TSDF for proper disposal. There is no toxic metal content in the Slag. APCD dust and slag(ash) test report has been incorporated as Annexure 11 &12
Chapter2, Item No. 2.6.2 Annexure 11&12
11. Trace metals in waste material especially slag.
There is no toxic metal content in the Slag. Slag(Ash) testing reports have been attached as Annexure 12
Annexure 13
12. Plan for trace metal recovery
The slag obtained is given to recyclers for recovery of valuable metal and rest will be sent to TSDF Site for disposal from where it will be sold to Paver Industry for Interlock block making and brick making
Chapter 2, Item no. 2.10
13. Trace metals in water Trace metal in the water are present in less
than permissible limits. Test reports for the Chapter 3, Item No.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 44
ground water and surface water are incorporated in the EIA report.
3.5.2
Specific ToR’s
1 PP shall undertake rainwater harvesting and recharge, and the quantum of water so channelized shall be more than the water consumption in the project area.
Approx.12849 m3 of run-off rainwater will be harvested every year.
Detailed Rainwater Harvesting has been incorporated in the EIA Report
Chapter 4, Item No. 4.10.1
2 Stack emissions shall be attained below 30mg/Nm3
The stack emission details and details of Air pollution Controlling Device incorporated in Chapter 6.
Chapter 4; Item No. 4.3.3
3 PP shall develop green belt in an additional area of 1 hectare by planting local broadleaved tree species outside the project site within the study area
As per CPCB Guidelines 33% of the total land (i.e.0.8 hectare) will be used for Development. Layout Plan showing proposed green belt area has been incorporated in the EIA report.
Detailed in Chapter 2.
Addition area of 1 hectare
Chapter 10, Item No.10.4
Greenbelt layout given in Chapter 2, Figure 2-3.
4 PP shall prepare detailed engineering drawing showing shop wise details of facilities installed and to be installed, expansion of storage yard for raw materials and products, and for creation of green belt shall be furnished.
Plant layout showing the green belt area, shop wise details various facilities,storage yard for raw materials and products is incorporated in the report.
Detailed in chapter 2.
Chapter 2, Figure 2-3
5 PP shall not use producer gas for reheating
100% hot charging and no use of producer gas for reheating will be done during the operation. Undertaking will be attached as annexure 8
Annexure 8
6 PP shall ensure 100% utilization of waste
The main source of emissions will be from Induction Furnace and from the work zone and that will be control by the Air Pollution
Chapter No. 2, Item
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 45
generated in the plant Control System like Pulse Jet Bag filter, I.D. Fan.
Closed circuit cooling system will be adopted in SMS (Steel Melting Shop) & rolling mill. Hence, there will not be any waste water generation from process and cooling. The only waste water generated from domestic use which will be treated in STP.
Undertaking has been attached as annexure 8.
No. 2.10
Annexure 8
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 46
CHAPTER-1: INTRODUCTION
1.1 INTRODUCTION
M/s Vardhman Ispat Udyog (VIU), established in 2005 is a Partnership firm promoted
by Mr. Pradeep Garg and Mr. Subodh Kumar. VIU is an authorized distributor of
Kamdhenu Ispat Limited’s (KIL) steel product in Punjab. It also supplies the products
in Himachal Pradesh. The firm has a dealer network of 400 dealers through which
the distribution is done. As per the arrangement between VIU & Kamdhenu, any sale
of Kamdhenu TMT (retail or institutional) is being routed through VIU only in Punjab.
M/s Vardhman Ispat Udyog acquired M/s H.N Steel Castings & M/s S.R. Steel along
with Rakesh Kumar’s land (10199 sq.m) in the village Bathri and formed a new unit
in the name of M/s Vardhman Ispat Udyog. M/s. H. N. steel had two induction
furnaces of capacity of 4T & 6T respectively and M/s. SR Steel had its rolling mill.
Both these units were located adjacent to each other at Village Bathri district Una
Himachal Pradesh.
M/s Vardhman Ispat Udyog now proposes to increase the production capacity of the
plant by replacing the induction furnaces by bigger capacity IFs and augmenting
other units at Village Bathri, Distt. Una (HP).
The existing project was accorded Consent to Operate by Himachal Pradesh
State Pollution Control Board vides letter. No. HPSPCB /PCB-ID10611 (H N
Steel) & HPSPCB /PCB-ID10264 (SR Steel), validity of CTO is up to 31.03.2019
and 31.03.2023(Attached as Annexure 6) respectively.
The existingunits are in running condition. The TMT bar being manufactured by the
firm is of the grades: Fe 415, Fe 500 and Fe 550; Fe415D, Fe 520D, Fe 550D and of
sizes ranging from 8 mm to 32 mm. The installed capacity of the purchased plants is
45,000 MTPA which would be enhanced to 1,40,000 MTPA post Capacity
enhancement.
This secondary metallurgical processing industry is listed as Item 3(a) of the
schedule and needs Environmental Clearance from the MoEF&CC as per the
EIA Notification, 2006 as the project is classified under Category A therein due
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 47
to “General Conditions” (Interstate Boundary between Himachal Pradesh and
Punjab, 1.0 km from project site).
This Environmental Impact Assessment has, therefore, been prepared to assess the
likely impact of the proposed capacity enhancement on various factors, which may
be affected, with the implementation of the programme and to suggest remedial /
precautionary and mitigation measures, if any.
The project proponent, submitted an application in the prescribed format along with
Form-1, PFR and other reports to the Ministry online on 7th May 2019 vide Online
Application No. IA/HP/IND/104614/2019 and ToRhas been granted vide letter no.
F.No.IA-J-11011/187/2019-IA.II (I) dated 17.09.2019.
1.1.1 PURPOSE OF THE REPORT
The purpose of EIA study report is to take stock of the prevailing quality of
environment, to assess the impacts of proposed industrial activity on environment
and to plan appropriate environmental control measures to minimize adverse
impacts and to maximize beneficial impacts. The following major objectives have
been considered:
• Assess the existing status of environment
• Assess the impacts due to the modification-cum-expansion of project
• Suggest pollution control and ameliorative measures
• Prepare an action plan for implementation of suggested ameliorative measures.
• Suggest a monitoring program to assess the efficacy of the various adopted
environmental control measures.
• Assess financial considerations for environmental control plans.
• Develop Environment Management Cell within the project/plant to see that the
provisions of the EC are implemented.
• Comply with post commissioning requirements of reporting to regional office.
• Take measures to judiciously decide spending of CER amount allocated yearly.
In pursuance of Government of India Policy, under ‘The Environment Protection Act
1986” and Himachal Pradesh State Pollution Control Board (HPSPCB), the proposed
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 48
project will require clearance from environmental angle. The present EIA/EMP report
is prepared based on monitored data for one season covering three months (March -
May 2019).
The present report is prepared in accordance with the guidelines issued by
MoEF&CC as per the standard Terms of Reference issued by Ministry of
Environment, Forest and Climate Change vides Memo No. F.No.IA-J-
11011/187/2019-IA.II (I) dated 17.09.2019. It also takes into account and complies
with the additional TOR points issued by the MoEF&CC.
For carrying out the Environmental Impact Assessment (EIA) study, the area falling
within 10 km radius of project site has been considered for generation of base line
data with respect to present air quality, water quality, noise level, soil quality,
ecology, socio-economic and meteorology etc.
An in-depth analysis of the baseline environmental data generated by actual field
monitoring and collected from various secondary sources has been carried out for
identifying and predicting the probable environmental impacts due to the expansion
of project. Based on the findings a suitable environmental management plan has
been suggested.
1.2 IDENTIFICATION OF THE PROJECT AND PROJECT PROPONENT
M/s Vardhman Ispat Udyog acquired M/s H.N Steel Castings & M/s S.R. Steel along
with Rakesh Kumar’s land (10199Sq.m) in the village Bathrimanufacturing of TMT
bars.
The proponent plans to replace existing induction furnace capacity of 4 T &6 T to
new furnaces of 2x10 T each based on the latest technology. The new furnace is
power efficient leading to saving of 50 units of electricity (Reduction from 600 units to
550 units). There is no national park, wildlife sanctuary and other sensitive areas
within 10 km of the project. The process adopted is eco-friendly.
THE BOARD OF DIRECTORS OF THE COMPANY
1. Shri. Pradeep Garg
2. Shri. Subodh Singla
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 49
The company aims for efficient management of the unit, which will require judicious
work force planning, selection of qualified and experienced personnel and
appropriate organizational structure, clearly defining the functions and
responsibilities of the managerial and supervising staffs for ensuring, maintaining
and compliance of committed environmental guidelines on obtaining environment
clearance.
1.3 BRIEF DESCRIPTION OF THE PROJECT AND ITS IMPORTANCE
1.3.1 NATURE OF THE PROJECT
As per EIA Notifications 14thSeptember 2006 and its subsequent amendments, M/s
Vardhman Ispat Udyog, falls under activity 3(a) as a Secondary Metallurgical
Industry Project and due to the presence of interstate boundary within 1 km from the
project site, the project is Category “A”, needing Environmental Clearance from the
Government of India.
1.3.2 SIZE OF THE PROJECT
Table 1-1: Salient Feature of the Project
S.
No. Parameters Description
1 Identification of
project
Project falls under Metallurgical Industries (secondary
metallurgical processing) Item 3(a) of the schedule of
EIA notification of Sept 14, 2006 issued by MOEF &
CC.
2 Project Proponent M/s Vardhman Ispat Udyog
3 Brief description of
nature of the project
The proposed project is for the capacity enhancement
of manufacturing unit by replacing existing induction
furnace (4 T & 6 T to 2x10 T each), Rolling Mill and
thereby enhance production capacity 45,000 MTPA to
1,40,000 MTPA.
4 Salient Features of the Project
4.1 Proposed plant
capacity
45,000 MTPA to 1,40,000 MTPA
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 50
S.
No. Parameters Description
4.2 Total Plot Area 27078.0 Sq.m.
4.3 Location Village- Bathri, Distt. Una, State-Himachal Pradesh
4.4 Water requirement Water for construction and domestic purpose will be
drawn from Bore well. Approximately, 31KLD (21
Industrial + 10 Domestic) water will be required after
capacity enhancement.
4.5 Source of water Bore well
4.6 Wastewater At present, 3.2 KLD of wastewater is being generated
from the project which is being treated in existing STP
plant. Water is being used for cooling purpose and
same is being reused within the plant premises after
neutralization and addition of makeup water.
After expansion, 8 KLD of wastewater will be
generated which will be treated in proposed STP of
10 KLD capacity.
4.7 Man Power After expansion, total 184 workers will be there, out of
which, 14 will be residing within the project premises.
4.8 Electricity/Power
requirement
At present, 6,398 KW of power load is available. After
expansion, electrical power requirements will be
9,925 KW.
Source: Himachal Pradesh State Electricity Board.
(HPSEB).
In case of power failure, an existing DG set of 125
KVA is there & after expansion, DG sets of 125 & 250
KVA will be provided.
4.9 Alternative Site The proposed addition will be established in the
existing plant premises only.
4.10 Land form, Land use
and land ownership
Private land, owned by M/s. Vardhman Ispat Udyog.
5 Nearest Highway The project site is adjacent to MDR-41.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 51
S.
No. Parameters Description
6 Nearest River Swan River (approx. 2 km in East direction)
7 Nearest Railway
Station
Nangal Railway Station 9 Km in North East direction.
8 Nearest Airport The Nearest Airport is Ludhiana Airport about 61 km
away from project site.
9 Nearest National
park/Wildlife
sanctuaries/Biosphere
reserves
No National Park, Wild life sanctuaries and Bio-
sphere reserve exists within 10 km of the study area.
10 Nearest Protected
Forest
No protected forest. However, area is predominantly
occupied by forests.
11 Working Days 350
12 Nearest Town/ city Santokhgarh located about 5 km from project site.
13 Seismic zone Zone – IV [as per IS 1893 (Part-I): 2002]
14 Project cost After expansion, total estimated Project cost will be
approximately Rs. 3038.66 Lakhs.
1.3.3 LOCATION OF THE PROJECT
The project is located at Village Bathri, Dist. Una, and State-Himachal Pradesh. The
coordinates are given in Table below-
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 52
Figure 1-1: Location Map
1.3.4 IMPORTANCE TO THE COUNTRY & REGION
Steel is extensively used due to its good strength, formability, weldability, easy
availability and has no substitute product. The country’s living standard has now
become proportionate with the steel demand. Therefore, to meet this steel demand
the renowned as well as the small private industries have put extra effort to increase
the quality of these products to international standards.
Steel demand at present day scenario is bound to grow with the boom in
construction, housing and infrastructural projects. With our Govt. policy to give more
stress to the infrastructural development of the country, the construction has reached
its boom. Moreover, the housing sector is growing very fast. Considering the rate of
increase of demand, it is expected that M.S. Rolled products manufacturing unit will
perform well and will have no difficulty to market its products.
• The Indian steel industry has entered a new development stage from 2007-08,
riding high on the resurgent economy and rising demand for steel.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 53
• Rapid rise in production has resulted in India becoming the 4th largest producer
of crude steel and the largest producer of sponge iron or DRI in the world.
• As per the report of the Working Group on Steel for the 12th Plan, there exist
many factors which carry the potential of raising the per capita steel
consumption in the country, currently estimated at 55 kg (provisional).
These include among others, an estimated infrastructure investment of nearly a
trillion dollars, a projected growth of manufacturing from current 8% to 11-12%,
increase in urban population to 600 million by 2030 from the current level of 400
million, emergence of the rural market for steel currently consuming around 10 kg
per annum buoyed by projects like Bharat Nirman, Pradhan Mantri Gram
SadakYojana, Prime MinisterAwaasYojana among others.
At the time of its release, the National Steel Policy 2005 India had envisaged steel
production to reach 110 million tonnes by 2019-20. However, based on the
assessment of the current ongoing projects, both in Greenfield and Brownfield, the
Working Group on Steel for the 12th Plan has projected that the crude steel capacity
in the county is likely to be 140MT by 2016-17 and has the potential to reach 149 MT
if all requirements are adequately met. It is noteworthy that India’s steel production in
2018 has been at 106.5 MT up by 4.9% from101.5MT in 2017 replacing Japan as
the world’s second largest steel producing country which produced 104.3 MT in 2018
MT “World Steel” has said’. The growth in the India’s steel sector has been driven by
domestic availability of raw materials such as iron ore and cost-effective labor.
Consequently, steel sector has been a major contributor to India’s manufacturing
output.
The Indian steel industry is very modern with state of the art steel mills. It has always
strived for continuous modernization and up-gradation of older plants and higher
energy efficiency levels. While plant closures are rare in India, the private sector is
the engine of growth in the steel industry and technological changes and
modernization are taking place in the both the public and private sector integrated
steel plants in India.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 54
1.4 SCOPE OF THE STUDY – DETAILS OF REGULATORY SCOPING
CARRIED OUT (AS PER TERMS OF REFERENCE)
Expert Appraisal committee (Industry) considered the case during its 7th meeting on
29th to 31th May, 2019 for prescribing TORs for undertaking detailed EIA/EMP and
Standard ToR Letter for the above mentioned project was granted by MoEF&CC
vide its File No.F.No.IA-J-11011/187/2019-IA.II (I) dated 17.09.2019.
The scope of the EIA study includes detailed characterization of the existing status of
the land, water, air and biological environment within the 10 km study area around
the project site, identification of the potential environmental impacts of the project,
and formulation of an effective Environmental Management Plan (EMP) to prevent,
control & mitigate any adverse environmental impacts, and ensuring the
environmental compliance. The scope of the EIA in brief includes:
• Establishment of baseline environmental status/condition of the environment in
the study area of 10 km radius around the project site.
• Collection and review of available secondary literature/data/information.
• Field study, survey and monitoring in the study area for primary data collection.
• Study of the project activities in terms of construction and operation to identify
the potential sources/causes of impacts.
• Identification and assessment of potential impacts on the environment during
construction and operation phase of the project.
• Recommendation of preventive, control and mitigation measures to
eliminate/minimize the adverse impacts.
• Formulation of an effective Environmental Management Plan (EMP) to ensure
the implementation of mitigation measures for environmental sustainability.
• Utilization of CER funds judiciously through a properly constituted committee
• Commitment to regularly report to Regional office of MoEF&CC of post
construction compliance of EC.
1.5 STRUCTURE OF THE EIA REPORT
The purpose of this report is to carry out Environment Impact Assessment study for
capacity Enhancement of Steel Manufacturing Unit by Replacing Existing Induction
Furnace and Enhance production capacity 45,000 MTPA to 1,40,000 MTPA by M/s
Vardhman Ispat Udyogand to prepare Environment Management Plan. The report
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 55
is divided into twelvechapters including this chapter, the details of which are
summarized below:
Chapter 1: Introduction - The present chapter gives brief outline of the project and
its proponent, brief description of the nature, size, and location of the project and
its importance, and extent of the EIA study, including the scope of the study.
Chapter 2: Project Description - This chapter deals with the details of the project
and various parameters like mineral requirements, existing production, proposed
production, site location details etc. and also the facilities to monitor and treat the
pollutants. The various features of the proposed project are described in this
chapter.
Chapter 3: Description of Environment - This chapter presents the baseline data of
existing situation of air, water, noise, soil, flora and fauna and socio-economic
environment. Various sections of the chapter discuss the site profile, landform and
existing land use and drainage pattern, climate and meteorological parameters.
Both primary and secondary data collected for the study are depicted in this
chapter.
Chapter 4: Impact Assessment & Mitigation Measures - This chapter describes the
anticipated impact on the environment and mitigation measures. The method of
assessment of impact including studies carried out and modeling techniques
adopted to assess the impact where pertinent have been elaborated in this
chapter. The details of the impact on the baseline parameters, both during the
construction and operational phases and the mitigation measures to be
implemented by the proponent have been suggested.
Chapter 5: Analysis of Alternatives (Technology & Site) - This chapter gives details
of various alternatives both in respect of location of site and technologies to be
deployed. Alternatives have been compared in terms of their potential
environmental impacts, suitability under local conditions, and institutional training
and monitoring requirements.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 56
Chapter 6: Environment Monitoring Plan - This chapter covers the planned
Environmental Monitoring Program. It also includes the technical aspects of
monitoring the effectiveness of mitigation measures.
Chapter 7: Additional Studies - This chapter covers the details of the additional
studies required in addition to those specified in the ToR and which are necessary
to cater to more specific issues applicable to the project.
Chapter 8: Project Benefits - This chapter highlights the benefits accruing to the
locality, neighborhood, region and nation as a whole. It brings out details of
benefits by way of improvements in the physical infrastructure, social infrastructure,
employment potential and other tangible benefits.
Chapter 9: Environmental Cost Benefit Analysis - This chapter includes Project
Cost, cost of pollution control facilities and project implementation schedule.
Chapter 10: Environment Management Plan - This chapter comprehensively
presents the Environmental Management Plan (EMP), which includes the
administrative and technical setup, summary matrix of EMP, the cost involved to
implement the EMP, both during the construction and operational phase and
provisions made towards the same in the cost estimates of project construction
and operation.
Chapter 11: Summary & Conclusions – This chapter deals with the overall
summary of the project giving details of project i.e. salient features, baseline
monitoring of various attributes of environment their mitigation measures, project
benefits etc. which have discussed in the above chapters
Chapter 12: Disclosure of the Consultant - This chapter presents in brief about the
consultant engaged along with the key experts as per QCI/ NABET accreditation
scheme.
1.7 LAWS APPLICABLE TO THIS PROJECT
The Acts, Notifications, Rules and Amendments applicable for setting up a new
industry or its expansion of an existing plant and for operation of a plant include the
following:
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 57
Table 1-2: Laws Applicable Tothe Project
Legal Channel Responsible Ministries/Bodies
Objective of Legislation
Action Plan
The Water (Prevention & Control of Pollution) Acts1974/ Rules1975
CPCB, SPCB The prevention and control of water pollution and maintaining or restoring the wholesomeness of water
• Not to discharge any effluent, not confirming to standards, prescribed by HPSPCB into any stream, well, sewers or land
• Not to discharge air pollutant(s) in excess of standards, prescribed by the State PCB/ CPCB
• Obtain ‘Consent to Establish’ prior to establish any production unit, process operation or treatment system
• Obtain ‘Consent to Operate’ prior to operation of system which is likely to discharge effluent
• Apply for renewal of the ‘Consent to Operate’ well before its expiry
• Comply with conditions as prescribed under consents
The Air (Prevention & Control of Pollution) Acts1981/ Rules1982
CPCB, SPCB The prevention, control and abatement of air pollution
The Environment (Protection) Acts1986/Rules 1986
MoEF&CC, CPCB, SPCB
Protection and Improvement of the Environment
• Prevent discharge or emission of environment pollutants in excess of the prescribed standards
• Submit ‘Environmental Statement’ every year
The Environmental Impact Assessment (EIA) Notification, 2006
MoEF&CC, CPCB, SPCB,SEIAA
Mechanism to have control for betterment of all aspects of environment at all stages of project implementation, operation and
• Project Proponent must Obtain prior “Environmental Clearance’ from MoEF&CC in case of new project or for Modernisation / Expansion
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 58
after commissioning
• Complying with the judicious spending of CER funds for socio-economic causes developed during socio-economic survey/study and during public hearing commitments or/and decided in the process of obtaining EC.
• Comply with the EMP provisions at every stage of plant operation.
Hazardous and Other Wastes (Management and Transboundary Movement) Rules, 2016
MoEF&CC, CPCB, SPCB
Management & Handling of hazardous wastes in line with the Basel convention
• It is the responsibility of the occupier to identify the hazardous wastes in their units and ensure proper handling and disposal
• M/s Vardhman Ispat Udyog to take all steps to contain contamination, prevent accident and limit consequences on human being and environment
• Obtain authorization from SPCB and comply with the conditions.
• Maintain records of Hazardous Waste generated in Form-3 and submit yearly return for generation, treatment, recycling, disposal etc., to SPCB in Form-4
• Used Oil to be sent / sold
• to the registered recycler, re-processor, registered authorized facility
• Shall be transported in accordance with the rule.
• Site storage is allowed for 90 days only.
MoEF notification S0 804 (E) dated
MoEF&CC, SPCB Damage Assessment, Remediation plan
• Preparation of EIA/EMP report along with the Bank Guarantee equal to
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 59
14/03/2018 and its subsequent amendments
and Natural & Community Augmentation plan due to Violation of EIA notification 2006.
the damage assessed due to violation and implementation of Natural & Community Augmentation Plan in process of EC.
Factories Act, 1948 (as amended till 1987)
Ministry of Labor, DGFASLI and Directorate of Industrial Safety and Health/Factories Inspectorate
Control of workplace environment, and providing for good health and safety of workers
• Obtain and renew factory license and obtain permission for the site from State Government or the Chief Inspector of Factories in case of new or extension of any Factory.
• Ensure health, safety and welfare of all workers while they are at work in the Factory as far as reasonably practicable.
• Ensure effective and adequate ventilation of work place and adequate measures to be taken to protect workers particularly in the processes involving excessive temperature.
• Ensure effective and adequate ventilation of work place and adequate measures to be taken to protect workers particularly in the processes involving excessive temperature
The Central Motor Vehicle Rules, 1989
Ministry of Shipping, Road Transport and Highways
To consolidate and amend the law relating to motor vehicles including to regulate the transportation of dangerous goods with a view to prevent loss of life or damage to the environment
• Ensure compliance to safety provisions in the transport vehicle carrying dangerous and hazardous substances inside works
• Display of emergency information panels at front, back and both side of vehicle
• Every transporter to ensure safe
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 60
transportation of dangerous/ hazardous goods.
• Earthing chain for grounding, any prevalent static charge.
• All motor vehicle entering the works shall have properly maintained brakes, lights, signal system for brakes, blinkers and registration number displayed, and valid Pollution under Control Certificate.
The Solid Waste Management Rules, 2016
CPCB, SPCB To manage/ utilize the generated solid waste without damaging the environment and surroundings
• Segregate waste in to three streams, Wet (Biodegradable), Dry (Plastic, Paper, metal, wood, etc.) and domestic hazardous wastes (diapers, napkins, empty containers of cleaning agents, mosquito repellents, etc.) and handover segregated wastes to authorized rag-pickers or waste collectors or local bodies.
Batteries (Management and Handling) Rules, 2001.
SPCB, CPCB and MoEF&CC
To control the hazardous waste generation (lead waste) from used lead acid batteries
• It is the responsibility of the generator to ensure, used batteries are not disposed of in any manner other than depositing with dealer, manufacturer, importer, re-conditioner registered recycler or at designated collection centre
• Submit half yearly return for disposal of used batteries to State PCB by 30th June & 31st December, every year
• In case of auction, ensure batteries are auctioned to the registered recycler only
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 61
• File half yearly return for the auction
• Maintain record for such auction
Noise Pollution (Regulation and Control) Rules, 2000 and its amendments
CPCB, SPCB, MoEF&CC
To maintain the noise levels with respect to the place/equipment/ industry
• Noise Quality Monitoring & submission of reports on weekly/monthly basis.
• Providing Ear plugs and Muffs to the workers working in noise prone areas.
• Dampening the source noise level or making the noise characteristics less annoying by providing suitable enclosures and barriers
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 62
CHAPTER-2: PROJECT DESCRIPTION
2.1 TYPE OF PROJECT
M/s Vardhman Ispat Udyog has acquiredtwo running plants M/s H.N Steel Casting
Pvt. Ltd, and M/s S.R Steels along with the land of Mr. Rakesh Kumar in village
Bathri, Distt. Una for the production of TMT Bars, The proponent plans to replace
existing induction furnaces capacity of 4T &6T to new furnaces of 2x10 T each
based on the latest technology. The new induction furnace is power efficient leading
to saving of 50 units of electricity (Reduction from 600 units to 550 units). Installed
Capacity of Purchased plant is 45,000 MTPA which would be enhanced to 1,40,000
TPA. The existing setup included two induction furnaces having capacity of 4T & 6 T
which would be replaced by two new furnaces of 10 T each based on latest
technology at Village, Bathri, Distt. Una, (HP).
The TMT bars being manufactured by the firm are of the grades: Fe 415, Fe 500 and
Fe 550; Fe415D, Fe 520D, Fe 550D and of sizes ranging from 8 mm to 32 mm. The
installed capacity of the purchased plants is 45,000 MTPA which would be enhanced
to 1,40,000 MTPA post Capacity enhancement.
The existing plants were accorded Consent to Operate by Himachal Pradesh State
Pollution Control Board vides letter. No. HPSPCB /PCB-ID10611 (H N Steel) &
HPSPCB /PCB-ID10264 (S R Steel) validity of CTO is up to 31.03.2019 and
31.03.2023(Attached as Annexure 6) respectively. Theproposed expansion will be
done in the existing plant premises only.
This secondary metallurgical processing industry is listed as Item 3(a) of the
schedule and needs Environmental Clearance from the MoEF&CC as per the EIA
Notification, 2006 as the project is classified under “Category A” therein due to
“General Conditions” (Interstate Boundary between Himachal Pradesh and Punjab,
1.0 km from project site).
2.2 NEED FOR THE PROJECT
Steel production of India accounted for 14.33 million tons in 1990-91, which
gradually increased to 36.12 million tons in 2003-04. Rapid rise in production has
resulted in India becoming the third largest producer of crude steel in 2015 and the
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 63
country continues to be the largest producer of sponge iron or DRI in the world. As
per the report of the Working Group on Steel for the 12th Five Year Plan, there exist
many factors which carry the potential of raising the per capita steel consumption in
the country. These include among others, an estimated infrastructure investment of
nearly a trillion dollars, a projected growth of manufacturing from current 8% to 11-
12%, increase in urban population to 600 million by 2030 from the current level of
400 million, emergence of the rural market for steel currently consuming around 10
kg per annum. At the time of its release, the National Steel Policy 2005 had
envisaged steel production to reach 110 million tons (MT) by 2019-20. However,
based on the assessment of the current ongoing projects, both in Greenfield and
Brownfield, the Working Group on Steel for the 12th Five Year Plan has projected
that domestic crude steel capacity in the county is likely to be 140 MT by 2016-17
and has the potential to reach 149 MT if all requirements are adequately met. The
National Steel Policy 2005 is currently being reviewed keeping in mind the rapid
developments in the domestic steel industry (both on the supply and demand sides)
as well as the stable growth of the Indian economy since the release of the Policy in
2005.
India has become the world's second largest producer of crude steel in the year
2018 and is projected to increase its steel production capacity to about 300 MT by
2025. Huge scope for growth is offered by India’s comparatively low per capita steel
consumption and the expected rise in consumption due to increased infrastructure
construction, housing and the thriving automobile and railways sectors.
2.3 LOCATION OF PROJECT (MAPS SHOWING GENERAL LOCATION, SPECIFIC LOCATIONS, PROJECT BOUNDARY AND PROJECT SITE LAYOUT)
The project is located at Village Bathri, Dist. Una, and State-Himachal Pradesh. The
coordinates are given below
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 64
The general location of the proposed project site is shown in Figure 2-1.
Topographical map showing project location and features within 10 km of study area
is attached as Figure 2-2. The project site layout plan is given in Figure 2-3 and the
site photographs are given in Figure 2-4.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 65
Figure 2-1: Pillar Co-Ordinate Map of Project Site
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 66
Figure 2-2 : Topographical Map of the Project Site
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 67
Figure 2-3: Plant Layout
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 68
Figure 2-4: Site Photographs
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 69
2.3.1 PROJECT SITE BREAK-UP
The total project site area is 27,078 Sq. M. The Land use breakup of project site is
as follows:
Table 2-1: Project Site Break-Up
S. No. Particulars Area (in Sq.m.)
1. Cooling Bed area 721.65
2. Rolling mill area 1744.71
3. Finished goods area 3839.58
4. Workshop area 519.10
5. Reheating Furnace & Ingot Yard Area 915.19
6. Caster & Workshop Area 1668.70
7. Raw Material store area 1158.01
8. Slag shed area 25.80
9. Proposed Extended rolling mill area 873.04
10. DC Panel Room area 137.28
11. Office Block area 356.88
12. Labors Accommodation & Mess Hall Area 85.49
13. Staff accommodation & mess hall area 109.45
14. Electrical Room Area/APCD 55.0
15. Peer Dargaah& Shed area 105.47
16. Store Area 226.21
17. Toilet Block Area 23.83
18. Security room area 49.98
19. Cooling Tower Area 55.53
20. Cooling Water Area 96.52
21. Water Tank Area 35.03
22. Generator Shed Area 28.12
23. Green Area 8947.77
24. Road area 1797.24
25. Parking Area 1215.47
26. Open Area 2286.95
Total 27070.08
2.4 SIZE OR MAGNITUDE OF OPERATION
M/s Vardhman Ispat Udyog, village Bathri, Distt. Una (HP) will produce TMT bars
being of the grades: Fe 415, Fe 500 and Fe 550; Fe415D, Fe 520D, Fe 550D and of
sizes ranging from 8 mm to 32 mm. The installed capacity of the purchased plants is
45,000 MTPA which would be enhanced to 1, 40,000 MTPA.
The existing setup included an induction furnace 4T & 6 T which would be replaced
by two new furnaces of 10 T each based on latest technology. The details of the
project is given below-
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 70
Table 2-2: Project Details
S. No. Details Existing After Expansion
1. Induction Furnace IFs of 4 TPH and 6 TPH &Rolling Mill
2 IFs of 10 TPH each + Rolling Mill
2. Production Capacity
18,000 MT/Annum through IFs and CCM 27,000 MT/annum through Reheating Furnaces. Total 45000MTPA
1,40,000 MT/annum through IFs and CCM
3. Raw materials 47,250 MT/annum 1,47,000 MT/annum
4. Products
TMT Bars TMT Bars
5. Manpower
84 workers Total 184 workers
6. Total Water Demand
10 KLD 31 KLD
7. Cooling Water Demand
6 KLD 21 KLD
8. Domestic water Demand
4 KLD 10 KLD
9. Wastewater generated
3.2 KLD (Treated in Septic tank)
8 KLD (It will be treated in proposed STP of 10 KLD capacity)
10. Power Load 6,398 KW
9,925 KW
11. DG sets
1 DG set of capacity 125 KVA
2 DG sets of capacity 125 & 250 KVA each
12. Domestic Solid Waste
17 kg/day 40 kg/day
13. Slag 1,890 MT/annum 5,880 MT/annum
2.5 SCHEDULE FR APPROVAL AND IMPLEMENTATION
11.09.2018 Submission of Form-1/PFR
11.12.2019 Public Hearing
Implementation schedule of the project is 24 months. “Zero date” for a project is
generally reckoned as the date on which the date on which Consent to Establish of
expansion of the project is received. For implementation of the project “SPLIT
PACKAGE BASIS” mode of procurement for project execution is proposed. The
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 71
proposed solution shall help in optimizing project investment and minimizing
entrepreneur risk due to unknown circumstances.
Table 2-3: Project Implementation Schedule
S. No. Activity Schedule in Months
1. Consent to Establish Zero date
2. Placement of Order 1 months
3. Civil & Structural work 5 months
4. Procurement, Installation & Commissioning 18 months
Total 24 months
2.6 TECHNOLOGY AND PROCESS DESCRIPTION
TMT bars are being manufactured in-house using scrap in the induction furnaces
continuous steel casting route and manufactured from Ingots/billets. These billets
/ingots are reheated before they are manually fed to the rolling mill for conversion
into TMT Rebars.
In the proposed manufacturing process, hot charging lines (continuous casting) will
be installed wherein billets are directly transferred to rolling mill for conversion into
TMT Rebars. Such process is expected to result in substantial cost savings (~INR
2000/Tonnes) as the billet is not required to be reheated.
CAPACITY ENHANCEMENT OF EXISTING UNIT
Two new furnaces of 10 tons each based on latest technology would be replacing
the old furnaces of 4T & 6 T. The new furnace would be power efficient leading to
saving of 50 units of electricity (reduction from 600 units to 550 units) for every tons
of TMT manufactured. The new furnaces would also reduce the processing time for
manufacturing of billets by half an hour (from 2 hours to 1.5 hours).
Table 2-4: Proposed Machinery
Sr. No Machinery Quantity
1. Steel Frame induction furnace of 3500 KW/10 T 1
2. Furnace Transformer 1
3. ETMC 1x with secondary Automation 1
4. PDLM of 10 MT 1
5. Steel frame induction furnace of 3500 kw/10T 1
6. Furnace Transformer 1
7. EOT Crane 35/15 MT 2
8. EOT Crane 25/10 MT 1
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 72
Figure 2-5: Existing Manufacturing Process Flow Diagram
2.6.1 PROCESS DESCRIPTION
INDUCTION FURNACE
A coreless induction furnace operates on a similar principle to a transformer, i.e., the
induction coil acts as primary coil, having many turns, and the charge acts as a
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 73
secondary coil, with only as single turn. When an alternating current is applied to the
induction (primary) coil of a furnace, a significantly larger current is induced in the
metallic charge materials. The resistance to the passage of induced current within
the furnace charge causes the charge to heat up until it eventually melts. Once the
metal is molten, the magnetic field generated creates a stirring action in the bath,
producing both homogenization of the chemical composition and assimilation of any
bath additions. Electrical energy at 11 kV (3-phase) is converted to 1250 V, through
a transformer. It is further subjected to a 3-phase rectifier and inverter system which
converts the power to single phase, high voltage-high frequency. The frequency
converter amplifies the frequency from 50 Hz to 500 Hz. This power is applied to
furnace coil to generate heat.
The greatest advantage of the induction furnace is its low capital cost compared with
other types of meeting units.
Its installation is relatively easier and its operation is simpler. Among other
advantages, there is very little heat loss due to rotation from the furnace as the bath
is constantly covered and there is practically no noise attending its operation. The
molten metal in an induction furnace is circulated automatically by electro-magnetic
action so that when alloy additions are made, a homogeneous product is ensured in
minimum time. While making mild or carbon steel in an induction furnace, the
primary consideration is the optimum utilization of the furnace as well as elimination
of delays.
THE CHARGE
Scrap constitutes the major raw material for steelmaking in the induction furnace.
The charge should be compact and should consist of a number of small pieces of
steel, selected steel scrap mixed with clean turnings, borings, and a moderate
amount of heavy melting of commercial grade. This is to provide the initial conditions
of a high flux path through the charge for facilitation generation of heat and
commencement of melting. As soon as the furnace is charged, the switches
admitting current to the induction coil are closed.
MELTING THE CHARGE
The furnace is turned on, current starts flowing at a high rate producing an induced
magnetic field inside the central space of the coils where the crucible is located. The
induced magnetic flux thus generated cuts through the highly resistive path of the
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 74
scrap mix, generates tremendous amount of heat and melting of scrap starts. The
magnetic flux can be controlled by varying input of power to the furnace.Soon a pool
of molten metal is formed in the bottom, causing the charge to sink. Any remaining
charges are added at this point gradually.
The scrap charged into the furnace gets heated and melted at a temperature of
about 1200°C to 1670°C. As soon as the charge has melted clearly, any
objectionable slag is skimmed off, and the necessary alloying elements are added.
When these additives also melt, temperature is increased by increasing the power
input to bring it up to the point most desirable for pouring. The current is then turned
off and molten material is poured, the furnace crucible is tilted by means of hydraulic
system and the molten material is poured into ironmoulds. This gets cooled to form
the finished product – M.S. ingots.The molded material is rolled with roller machine
thereafter.
CONTINUOUS CASTING
Continuous casting machine for a particular level of output depends primarily on the
number of heats cast per day. The actual casting time will depend on heat size, size
of billets to be cast, steel grade, casting speed and no. of strands used.
The main operations involved in the whole process of turning out billets/blooms are:
1. Checking the individual major components of the casting machine and their
synchronized operation.
2. Insertion of a dummy bar to close the bottom end of the mould.
3. Accurate centering of the tundish over the mould.
4. Transferring the ladle to the casting aisle and placing it on the ladle stand of the
casting machine.
5. Pouring of liquid steel from the ladle through a slide gate mechanism into the
lined tundish.
6. Pouring of liquid steel into the water cooled mould through tundish.
7. Passage of liquid steel through water cooled mould tubes initiated by
withdrawing dummy bar.
8. Oscillation of the mould.
9. Maintaining a constant level of liquid steel in the mould.
10. Introducing lubricants into the mould throughout the casting process.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 75
11. Controlling the intensity of cooling of the emerging billets in the primary &
secondary cooling areas.
12. Straightening & cutting of billets.
The most important component of the casting machine is the bottomless water
cooled copper mould. The internal shape & size of the mould tube is the same as
that of the cross section of the billet to be cast. To initiate casting, a dummy bar is
inserted to the bottom end of each mould, while the other end of the dummy bar is
held by withdrawal/straightening rolls.
Molten steel at the correct temperature is poured into the mould& when it reaches
the stipulated level, the withdrawal rolls, mould reciprocation unit are operated;
cooling water circulation through the mould& in the secondary circuit is started few
minutes earlier than the actual casting operation is started.
BILLET CUTTING
The automatic gas cutting torches are provided for cutting billets to a desired length.
The equipment comprises of a water cooled structure for trolley support. The trolley
moves on the rail above the hot strand into the direction of discharge. During cutting,
torch swings like pendulum across the hot strand at a pre-determined cutting speed.
In the forward direction trolley moves at casting speed swing to the clamping of the
hot strand whereas retracting the trolley to the home position is carried out by
motorized drive. It includes:
1. Positioning of the torch at the edge of the billet.
2. Clamping of hot strands by the clamps through pneumatic cylinder,
3. Ignition of the torch by releasing oxygen & acetylene gas.
4. Torch drive starts thereby swinging the ignited torch across the hot strand and
thereby cutting it.
The following functions soon take place:
1. Ignition of the torch will be put off.
2. After that movement of the torch by the drive will be stopped and the torch
retracts back to the home position.
3. First group of discharge roller table will be made on thereby separating the cut
billet from the hot strand.
4. Clamps holding the hot strand will be released.
5. Trolley will retract to the home position.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 76
This complete one full cycle of cutting a billet, complete operation is automatic,
however can also be carried out by means of push buttons located on the control
desk.
ROLLING MILL
The billets produced in CCM will be fed directly to Rolling Mill of the steel plant.
There will be one Hi speed rolling mill for of capacity 1x20 TPH for production of
TMT bars varying from 12mm to 25mm in size.
APCD DUST
The client intends to install an Air Pollution control Device to minimize and control
the emission of air polluting contents generated in the furnace. There will be two
induction furnaces of capacity 10 ton and 2 crucibles each. For this, bag house filters
has been proposed to be equipped after the furnaces to separate the particulate
matter from the flue gas coming out of the induction furnace. There has been
proposed the containment of emissions from one furnace of capacity 10 ton in phase
1 through rotary type side suction hood &for second furnace of capacity 10 ton in
phase 2.
❖ Inlet Concentration of PM 5000 mg/Nm3
❖ Outlet Concentration of PM <50 mg/Nm3
❖ Removal of PM efficiency > 98%
❖ Air/cloth Ratio 1.4.
The air pollution control equipment ordered is one of the most efficient dust
collectors in existence. The system uses controlled blasts of compressed air to run
the bag cleaning and dust dislodging equipment.
2.6.2 FACILITIES PROPOSED UNDER THE EXPANSION
(a) INDUCTION FURNACE
The proponent plans to replace existing induction furnace capacity of 4 T &6 T to
new furnace of 2x10 T each based on the latest technology. However, existing rolling
mill will also exist after expansion. The new furnace is power efficient leading to
saving of 50 units of electricity (Reduction from 600 units to 550 units).The raw
materials will be transported through tarpaulin covered trucks only.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 77
Table 2-5: Proposed Melting & Casting Section
Number of Furnace Two Furnaces
Capacity of Each Furnace Existing: 2 IFs of 4 TPH & 6 TPH capacity each.
After Expansion: Replacement of existing IFs i.e. 2 IFs of 10 TPH capacity each.
Number of heats per day 20 Heats per day
Number of working hours 24 hrs
Number of working days 350 days
Capacity of Billet Production
Existing Raw material 20,000 MT/annum
Existing Capacity 18,000 MT/Annum
Proposed Raw Material 1,54,000 MT/annum
Total Proposed Annual Capacity 1,40,000 MT/annum
Required Iron Scrap 1,54,000 MT/annum
Add 10% Wastage 14,000 MT/annum
Total Scrap Required 1,54,000 MT/annum
Table 2-6: Rolling Mill Section
ROLLING MILL SECTION EXISTING TONS/DAY
EXISTING TOTAL TONS/ANNUM
Required Rolling Material 94 MT/day 28,080 MT/annum
Less : Wastage@ 4% 4 MT/day 1,080 MT/annum
Hot Rolled Strips/ Bars 90 MT/day 27,000 MT/annum
Billets / Ingots Required 94 MT/day 28,080 MT/annum
Less : Billets / Ingots In House - -
Balance Purchases From Open Market
94 MT/day 28,080 MT/annum
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 78
Table 2-7: Annual Raw Material Requirement At 100% Capacity
ROLLING MILL SECTION AFTER EXPANSION TONS/DAY
AFTER EXPANSION TOTAL TONS/ANNUM
Required Rolling Material 416 MT/day 1,45,600 MT/annum
Less : Wastage@ 4% 16 MT/day 5,600 MT/annum
Hot Rolled Strips/ Bars 400 MT/day 1,40,000 MT/annum
Billets / Ingots Required 416 MT/day 1,45,600 MT/annum
Less : Billets / Ingots In House 400 MT/day 1,40,000 MT/annum
Balance Purchases From Open Market
16 MT/day 5,600 MT/annum
Total raw material required will be purchased from local market.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 79
Figure 2-6: Material Balance Diagram
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 80
2.7 WATER, MAN-POWER REQUIREMENT, POWER REQUIREMENTS AND
OTHER SITE SERVICES
2.7.1 WATER SOURCE AND UTILIZATION
The water requirement in the plant is mainly for the following purposes:
• Industrial Purposes: Coil and panel cooling of induction furnace, CCM mould
cooling, CCM spray and open machinery cooling etc.
• Domestic Purposes: Drinking and sanitation, spraying and cleaning etc.
Water consumption for the unit will be as small as the requirement for the cooling
system where water will be re-circulated in the closed circuit. About 31 KL will be
required on daily basis out of which 21 KL is required for compensating the
evaporation losses. In addition, to this about 10 KLD of water will be needed for 184
workers.8 KLD of water from the domestic sewerage system will be recoverable for
green belt development.
Expected source of water:Water for construction and domestic purpose will be
drawn from bore well. Application for Permission has beensubmitted to Irrigation and
Public Health Department, Himachal Pradesh.Certificate has been attached as
Annexure 4.Water Balance for the project has been shown in Figure 2-7.
Water supply facilities include supply of industrial water, soft water, drinking water
and fire-fighting water to various proposed units of the plant. The concept of
extensive recycling of water has been adopted in the design of plant water systems.
Blow down from plant water recirculation will be considered for cascaded reuse in
the plant water system as far as practicable and maintain minimum plant effluent
discharge. There are no trace metals like Mercury and Arsenic in water.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 81
Figure 2-7: Water Balance Chart
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 82
2.7.2 MAN-POWER REQUIREMENT
Existing Man power: 84 workers
After Expansion: 184 workers; out of which, 14 persons will be residing.
The distribution of the manpower has been given below:
Administrative Staff No. of Persons
Existing
No. of Persons
After Expansion
General Manager 1 1
Finance Manager 1 1
Accountants 4 8
Purchase Manager 1 1
Marketing Executives 2 3
Peon cum Watchman 2 2
Security Guards 6 8
Total 17 24
Factory Staff and Labour No. of Persons Existing
No. of Persons After Expansion
Production Manager 1 1
Metallurgist 4 7
Chemist/Technician 4 5
Laboratory Assistant 4 6
Electrician 8 10
Skilled Workers 26 81
Unskilled Workers 20 50
Total 67 160
*Source: Project Report
2.7.3 POWER REQUIREMENT
The electric power supply & distribution for a steel plant with auxiliaries, illumination
system for in-plant and outdoor area including, internal road lighting is all included in
power distribution.
Himachal Pradesh State Electricity Board will supply power. Existing Power load of
6,398 KW & additional 3,527 KW will be used to run plant & machinery during
construction and operational phase. The total power required for running the plant &
machinery during operational phase will be 9,925 KW.
In case of power failure, existing DG set of 125 KVA is there & after expansion, DG
sets of 125 & 250 KVA will be provided.Permission from Himachal Pradesh State
Electricity Board vide letter no.8055-62 dated 16.11.2018 has been attached
annexure 5.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 83
2.8 COST OF THE PROJECT
Estimated cost of the proposed project for Installation of the additional 2 nos. of
InductionFurnace of 10Ton shall be Rs. 30.38 Cr.
Table 2-8: Project Cost Break-Up
S. No. Particulars Cost (Rs. In Crores)
Existing
1. Existing Project Cost 3.61
Proposed
2. Civil & Structural Cost 12.82
3. Plant & Machinery 2.50
4. Electrical installation
5. Contingencies 5.00
6. Margin Money for Working Capital 1.21
7. Interest during Construction 5.24
8. Misc.
Total Rs. 30.38 Cr
2.9 DESCRIPTION OF MITIGATION MEASURES INCORPORATED INTO THE PROJECT TO MEET ENVIRONMENTAL STANDARD, ENVIRONMENTAL OPERATING CONDITIONS OR OTHER EIA REQUIREMENTS-
2.9.1 AIR POLLUTION & ITS MITIGATION MEASURES
Air in and over the plant area and beyond its boundaries gets polluted with gases,
fumes and dust particles emanating from the stacks, transfer points of conveying and
handling equipment. The air pollutants in the plant may be classified broadly into
particulate matter like dust, fumes etc. and gases like Sulphur dioxide, carbon
monoxide, nitrogen oxide etc. The flue gases are generated during melting of scrap.
Quantity and quality of flue gases mainly depends upon type of scrap used in the
furnace, i.e. with the degree of contamination of scrap. These flue gases need
proper treatment for removal of dust particles before being discharged into the
atmosphere.
The Pulse Jet type Dust collector is continuous automatic suction or pressure type of
dust collector capable of filtering dust laden air through a felted filter media.The dirty
or contaminated gas enters the dust collector through the module inlet. A baffle plate
distributes the air uniformly throughout the housing and drops out the heavy particles
into the hopper. The dust laden air then passes through a number of filter tubes
which retain the dust particles on the exterior surface while allowing the clean gas to
pass through to the module outlet.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 84
As the Pulse Jet type Bag Filter operates, the collected dust begins to form a dust
cake which eventually diminishes the porosity of the filter tubes. This reduction in
porosity is measured by a U tube manometer. As the pressure drop increases the
ventilation volume of the collector decreases.
To maintain a moderate pressure drop, the cleaning cycle is employed to provide
continuous cleaning of the filter bags. The cleaning system consists of a solid state
program timer which actuates electric solenoids governing the air valves. These air
valves deliver a momentary burst or pulse of high compressed air through the
manifold pipe into the filter tube. The pulse of air creates a reverse air flow which
expands the filter tube to remove the dust collected on the outside.
The cleaning procedure happens on a row by row basis, therefore only a fraction of
the total filter air is interrupted for cleaning allowing continuous cleaning of dust
laden air. The dust cake when pulsed from the filter bags falls directly into the
hopper from where it is removed by the dust conveying system.
Emission Characteristics:
Table 2-9: Induction Furnace of Capacity
S. No. Particulars & Unit Existing
1 No. of Furnace 2
2 Capacity 20 MT
3 Power Requirements (Proposed) 9,925 kW
4 Heat Time 90 minutes each
5 Volume of Flue gases 50,000 m3/hr.
6 Temperature of Gases at Suction Hood 80o C – 100o C
Table 2-10: Fugitive Emission Sources & Mitigation Measures
S.NO. FUGITIVE EMISSION SOURCE
MITIGATION MEASURES
1 From Induction Furnace Gaseous discharge will be passed through APCDSystem, Pulse Jet Bag filter, I.D.Fan and the Stack.
2 From Work Zone Area The help of APCD System will mitigate fugitive emissions.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 85
2.9.2 INDUSTRIAL WASTE WATER
The concept of extensive recycling of water has been adopted in the design of plant
water systems. Quality of circulating water will be maintained through dosing of
conditioning chemical. Blow down from plant water recirculation will be considered
for cascaded reuse in the plant water system as far as practicable and maintain
minimum plant effluent discharge. Through cascaded re-use of blow-down, the water
scheme ensures practically zero liquid discharge from the industrial water circuit.
Water mainly required will be taken from bore well. No wastewater will be generated
from the plant; only domestic wastewater is generated, which again will be reused for
green belt development.
2.9.3 DOMESTIC WASTE WATER
Fecal sewage from toilets and other service units would be collected through a
sewer network, treated and disposed of through STP. Closed circuit cooling system
will be adopted in SMS (Steel Melting Shop) & rolling mill. Hence, there will not be
any wastewater generation from process and cooling. The only wastewater
generated from domestic use. Domestic wastewater, which will be treated in STP
and treated water will be used for plantation purpose.
At present, 3.2 KLD of wastewater is being generated from the project which is being
managed in existing septic tank. Water is being used for cooling purpose and same
is being reused within the plant premises after neutralization and addition of makeup
water. After expansion, 8 KLD of wastewater will be generated which will be treated
in proposed STP of 10 KLD capacity.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 86
2.10 List of industries
List of some major industries of district Una, are given below:
2.11 SUMMARY
Impact on the environment due to transportation of raw material and finished product
to and from transport route, where traffic density is moderate. Ambient Air Monitoring
station shall be selected on the transport route and as per wind-rose pattern.
Impact on air pollution due to operation of additional facilities after expansion of
plant. This shall be predicted and mitigation measures shall be provided to keep the
impact on the environment low. This shall be designed considering the other
Industrial units within the vicinity of the plant.
Closed circuit cooling system will be adopted in SMS (Steel Melting Shop) & rolling
mill. The APCD dust from Bag filters as well as used oil is the hazardous waste
generated from the project which are stored and transported to TSDF.
Blow down from plant water recirculation will be considered for cascaded reuse in
the plant water system as far as practicable and maintain minimum plant effluent
discharge. Through cascaded re-use of blow-down, the water scheme ensures
practically zero discharge from the industrial water circuit. The only waste
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 87
watergenerated from domestic use, which again will be reused for green belt
development.
Plant area is surrounded by many Industries and Agricultural fields. Impact on the
soil due to the existing plant operation and proposed project shall be assessed and
proper management plan shall be suggested.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 88
CHAPTER-3: DESCRIPTION OF THE ENVIRONMENT
3.1 INTRODUCTION
To assess environmental impacts from a project at a specific location, it is essential
to establish baseline status and monitor the environmental quality prevailing in the
surrounding area prior to expansion of the project. The environmental status within
the impact zone could be used for identification of significant environmental issues
to be addressed in the impact assessment study. The chapter contains information
on existing environmental scenario for the following parameters.
❖ Meteorology
❖ Land Environment
❖ Water Environment
❖ Air Environment
❖ Noise Environment
❖ Traffic pattern and density
❖ Biological Environment
❖ Socio-economic Environment
This chapter illustrates the description of the existing environmental status of the
study area with reference to the major environmental attributes. The existing
environmental setting is considered to establish the baseline conditions that are
described with respect to physical environment, air environment, water environment,
noise environment, traffic pattern and density, land environment, biological
environment and socio-economic environment.
The monitoring of environmental parameters has been conducted within the core
zone and buffer zone (10 km radial distance offsetting plant boundary) from project
site at Bathri Distt Una, HP.
3.2 SITE DESCRIPTION AND ITS ENVIRONMENT
The project site is located at village Bathri, Dist. Una (HP). The study area map for
developing the baseline environment extends for a radius of 10 km from the
proposed project site. The location map showing the project site is given in Figure
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 89
3.1.The baseline information was gathered from both primary and secondary
sources; field surveys were conducted for one season from Marchto May, 2019.
The nearest railway station is Nangal Railway station, which is 9 km from the project
site, while the nearest airport is Ludhiana Airport at 61 Km. The site is approachable
by metallic roads from National MDR 41, adjacent to project site.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 90
Figure 3-1: Location Map
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 91
3.3 METEOROLOGY
3.3.1 CLIMATE, TEMPERATURE AND RAINFALL
Climate of the district is tropical to sub-temperate in nature, as the terrain varies from
plains to high hills. Temperature varies from minimum of 4 oC in winter to maximum
of 46 oC in summer. The area receives rainfall during monsoon period, extending
from June to September and non-monsoon period (winter). The annual average
rainfall in the area is about 1040mm, with about 55 average rainy days. The winter
season starts from November and continues till Februaryand summer season starts
from March and continues till the last week of June followed by the monsoon period
extending from July to September end.
Table 3-1: Observed Meteorological Data
0
10
20
30
40
50
60
MARCH APRIL MAY
RAINFALL(mm)
RAINFALL(mm)
0
5
10
15
20
25
30
35
40
45
MARCH APRIL MAY
TEMPERATURE MIN
TEMPERATURE MAX
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 92
MONTH TEMPERATURE(OC) RAINFALL(mm)
MINIMUM MAXIMUM
MARCH,2019 13.8 27.5 49
APRIL,2019 18.8 34 14
MAY,2019 23.7 38.8 14
3.3.2 METEOROLOGICAL SCENARIO OF THE STUDY AREA
Regional meteorological scenario helps to understand the trends of the climatic
factors. It also helps in determining the sampling stations in predicting the post
project environmental scenario. Meteorological Scenario exerts a critical influence on
Air Quality as the pollution arises from the interaction of atmospheric contaminants
with adverse meteorological conditions such as temperature inversions, atmospheric
stability and topographical features like hills, canyons and valleys.
The critical weather elements that influence air pollution are wind speed, wind
direction, temperature which together determines atmosphere stability. Hence, it is
an indispensable part of any air pollution studies and requires interpretation of base
line information.
Wind speed and direction data recorded during the study period is useful in
identifying the influence of meteorology on the air quality of the area. The
meteorological data recorded at the site for the study period is used for preparation
of Wind rose on sixteen - sector. The maximum and minimum temperatures
observed are given in Table 3-1.
3.3.3 WIND ROSE
The wind rose diagram is prepared based on the available IMD data. Wind rose
diagram is given below.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 93
Figure 3-2: Wind Rose Diagram
3.3.4 ATMOSPHERIC INVERSION LEVEL/MIXING HEIGHT
Atmospheric inversion, a reversal of the normal behaviour of temperature in the
troposphere (the region of the atmosphere nearest the Earth's surface), in which a
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 94
layer of cool air at the surface is overlain by a layer of warmer air. Inversions are a
result of the vertical temperature profile of air.
Figure 3-3:Mixing Height for the Study Area Are Given Below For the Pre-
Monsoon Season
*Source:https://www.envitrans.com/mixing-height-data-
india.php?state=HIMACHAL%20PRADESH&season=WINTER#tips
3.4 LAND ENVIRONMENT
3.4.1 LAND USE
Land use/Land cover map of study area for the project is prepared by digitizing SOI
toposheet, which has helped in the study of land use pattern of the study area. Site
visit was conducted to study area for collection of real time data. Information from
ground truthing & SOI toposheet was clubbed for preparation of land use land cover
map.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 95
As per 2011 Census records, land use pattern in different villages falling within 10
km radial from the project site has been classified under the following categories:
• Forest Area
• Area under Non-Agricultural Uses
• Barren & Un-cultivable Land Area
• Permanent Pastures and Other Grazing Land Area
• Land under Miscellaneous Tree Crops etc. Area
• Cultural Waste Land Area
• Fallows Land other than Current Fallows
• Current Fallows Area
• Total Un-Irrigated Land Area
• Area Irrigated by Source
Land for the project belongs to Vardhman Ispat Udyog in village Bathri, Distt. Una
(HP). The land is alluvial flat plain, utilized for the cultivation, forest and industrial
purposes.
Major part of the study area is dominated by Forest area followed by Agricultural
land, built up area and Water bodies. The percentage distribution of land under
different categories is depicted in Table 3-2.
3.4.2 LAND USE LAND COVER CLASSIFICATION USING REMOTE SENSING
DATA
Remote sensing technology has emerged as a powerful tool in providing reliable
information on various natural resources at different levels of details in a spatial
format. It has played an important role in effective mapping and periodic monitoring
of natural resources including environment. In order to strengthen the baseline
information on existing land use pattern the following data are used.
The steps involved in procurement and analysis of remote sensing data are:
• Acquisition of Satellite data
• Data loading
• Data processing
• Geo-referencing image
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 96
• Rectification
• Supervised Classification of Land use / Land cover
• Ground Truth / field checks using Global Positioning System
• Masking
For mapping different agro-climatic zones, the land use/ land cover classification
system has been standardized by Department of Space. Land use/Land cover
distribution in the study area has been estimated using the above classification
system and digital analysis techniques.
Figure 3-4 and 3-5 represents the Land Use / Land Cover of the study area, which
has been assigned 5 major classes, which is identified by different colors as given in
the legend.
The land use/land cover classification is given along with description of category as
per NRSA guidelines given in Table 3-2. The land-use/ land-cover classification of
the 10 km radius study area reveals that as much as 52.44% area is occupied by
Agricultural Land, Scrub Land 32.87 %, and river land 2.37%, Build up land 12.05%
and water bodies 0.26%.
Land is already available with M/s Vardhman Ispat Udyog Limited at Village Bathri,
Tehsil Haroli and Dist. Una, Himachal Pradesh.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 97
Figure 3-4: Land use Map
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 98
Table 3-2: 10km Radius Buffer Land Use/ Land Cover Classification
S.no Class
Description (As per the National land use and land cover mapping guidelines by National Remote Sensing Agency 2004-05)
Area in (Ha) Percentage
1 Buildup Area It is an area of human
habitation developed due to
non-agricultural use and that
has a cover of buildings,
transport and communication,
utilities in association with
water, vegetation and vacant
lands. 3786 12.05
2 Agricultural Land These are areas synonymous
with cropping season
extending between
November/December-
February/March. It is
associated with areas under
assured irrigation irrespective
of the source of irrigation 16475 52.44
3 River -- 745 2.37
4 Water Bodies This comprises areas with
surface water, either
impounded in the form of
lakes and reservoirs or
flowing as streams, rivers,
canals etc. 83 0.26
5 Scrub Land -- 10326 32.87
Total 31415 100
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 99
Figure 3-5: Graphical Presentation of Land Use/ Land Cover Classification
3.4.3 GEOLOGY
The unconsolidated valley fill or alluvial formations, occurring in the valley area and
semi-consolidated sediments belonging to Siwalik Group form aquifer system in the
district. Porous alluvial formation forms the most prolific aquifer system in the valley
area, whereas the sedimentary semi-consolidated formation forms aquifer of low
yield prospect.
In Una valley area, the ground water occurs in porous unconsolidated / alluvial
formation (valley fills) comprising sand, silt, gravel, cobbles / pebbles etc., and forms
prolific aquifer. Ground water occurs both under phreatic and confined/artesian
conditions. Free flowing wells are also observed in the lower part of Swan river.
3.4.4 TOPOGRAPHY
Una district came into existence on 1st September 1972 and is situated in the
southwestern part of the State of Himachal Pradesh. The district, with its
headquarter at Una town, has a geographical area of 1540 Sq. km and covers 2.8 %
area of the State. It lies between North latitude 31°18’00” & 31°55’00” and East
longitude 75°55’00” & 76°28’00” and is covered by Survey of India degree sheet
12.05%
52.44%2.37%
0.26%
32.87%
Land use/ Land Cover Classification
Buildup Area
Agricultural Land
River
Water Bodies
Scrub Land
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 100
No.53A & 44M. Towards the north, it is bounded by Kangra district, towards north
and east by Hamirpur and Bilaspur districts respectively and towards south-west by
the State of Punjab.
Administratively, the district has been divided into two sub-divisions (Una &Amb) and
comprises of 4 tehsils [Una, Amb, Bangana,andHaroli] and 1 sub-tehsil (Bharwain).
Further, there are 5 CD blocks [Una, Amb, Gagret, Dhundla (Bangana) &Haroli].
There are 5 towns (Una, MehtpurBadshera, Gagret, Santhokhgarh and Daulatpur),
758 inhabited villages, 56 uninhabited and 235 Gram Panchayats in the district. Una
district is well developed in the industrial sector due to proximity to Punjab state with
Mehatpur, Gagret, Tahliwal&Amb as main industrial centers.
3.4.5 SEISMIC CONSIDERATIONS
The entire district of Una falls under Seismic Zone IV as per the Seismic Zoning
Map of India (IS Code: 1893:2002 ) which makes it likely to be affected by
earthquake shaking of up to intensity VIII. The Main Boundary Thrust (MBT) fault
passes across the district and this is the continuation of the same fault which
caused the 1905 Kangra earthquake. There are other several smaller faults that can
also generate earthquakes of high intensities within Una district. This zone is called
the High Damage Risk Zone and covers areas liable to MSK VIII. The IS code
assigns zone factor of 0.24 for Zone V.
3.4.6 SOIL CHARACTERISTICS
Soil quality is the capacity of a specific kind of soil to function, within natural or
managed ecosystem boundaries, to sustain plant and animal productivity, maintain
or enhance water and air quality and support human health and habitation. Soil
quality reflects how well a soil performs the functions of maintaining biodiversity and
productivity, partitioning water and solute flow, filtering and buffering, nutrient cycling
and providing support for plants and other structures. Thus, soil quality plays vital
role in any particular geographical phenomenon of ecology as well as physico-
chemical environment. Soil quality can indicate the current as well as future issues
related with the water, ecology and life in the particular region. Thus, it is clearly
visible that soil contamination may result in eventuality in form of contamination of
water, ecological destruction, and loss of productivity, food crisis and so threat to life.
The major source of contamination is wastes from industries as well as overuse of
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 101
fertilizers & pesticide. Thus, to determine the exact impacts of any proposed project,
it is very essential to determine the existing status of soil quality and existing stress
through a study of soil quality assessment. Considering this, surface soil samples
were collected from six locations of study area shown on map in Figure 3-6 and
Table 3-3,with names of villages, distance and direction once in study period (10 km
buffer from the periphery of plant.) Outcome of soil quality studies is given in Table
3-3.
Table 3-3: Soil Quality Data Locations
Locations
Code
Locations Distance(km) Direction Type of Land
SQ1 Project Site Buildup Area
SQ2 Kokowal 3.53 SW Agricultural Land
SQ3 Daghour 3.60 SE Near Water body
(Agricultural Land)
SQ4 SingaurfSukalan 1.68 SW Agricultural Land
SQ5 Jhungian 4.89 SW Agricultural Land
SQ6 Tahliwal 3.91 NW Buildup Area
The six collected soil samples were analyzed by laboratory. The analysis was done
for physical properties, chemical and physico-chemical characters. The evaluation of
initial soil quality based on the above characters is done and presented as below.
3.4.7 SAMPLING PROCESS & ANALYSIS
The soil samples were collected once during the study period from each location.
The sampling was done using Augur Sampler and samples were filled in polythene
bags, labeled in the field with number and site name and sent to laboratory for
analysis. Sampling & Analysis of soil was done as per ISO/ IS: 2720/ Soil Chemical
Analysis by M.L. Jackson.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 102
Table 3-4: Standard Soil Classification
S. No. Parameters Classification 1.
pH <4.5 extremely acidic 4.51 – 5.0 very strong acidic
5.01 – 5.5 strongly acidic 5.51-6.0 moderately acidic
6.1 – 6.5 slightly acidic 6.51-7.3 neutral 7.31-7.8 slightly alkaline 7.81-8.5 moderately alkaline 8.51 – 9.0 strongly alkaline >9.0 very strongly alkaline
2. Salinity Electrical Conductivity (millimho/cm) 1 mho/cm = 640 ppm
Up to 1.0 average 1-2 harmful to germination 2-3 harmful to crops
3. Nitrogen (kg/ha) Up to 50 very less 51-100 less 110-150 good 151-300 better >300 sufficient
4. Phosphorus (Kg/ha)
Up to 15 very less 15 – 30 less 31-50 medium 51-65 on average sufficient 66-80 sufficient >80 more than sufficient
5. Potassium (Kg/Ha)
0-120 very less 120-180 less 180-240 medium 241-300 average 301-360 better >360 more than sufficient
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 103
Figure 3-6: Soil Monitoring Location
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 104
Table 3-5: Soil Quality Data (March, 2019-May, 2019)
Test Parameters Units Project Site (Near Main Gate)
Shiv Mandir (Kokowal)
Daghour (Agricultural Land
Jhungian Near Cement store
Tahliwal (Satsang Bhawan)
SingaurfSukalan
pH - 8.13 8.25 7.31 8.18 7.2 7.81
Electrical Conductivity
mmhos/cm 0.203 0.503 0.264 0.147 0.109 0.25
Soil Moisture Content
% w/w 1.96 6.08 0.54 1.76 4.64 3
Organic Matter gm/cc 0.38 0.98 0.37 0.75 0.88 0.67
Soil Texture - Loamy Sand Sandy Loam Sandy Clay Loam Loam Loam Sandy Loam
Bulk Density % 1.52 1.54 1.54 1.64 1.59 1.57
Potassium Kg/Ha 181 208 167 238 172 194
Sodium Absorption Ratio
mEq/kg 0.16 0.18 0.18 0.17 0.18 0.17
Water Holding Capacity
% 25.1 25.4 20.18 28.7 29.8 25.8
Porosity % 38 45 39 40.1 39.2 40.3
Sand % 79.8 78.9 47.6 47.9 45.3 59.9
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 105
Sodium mg/kg 32 39 41 38 40.5 38.1
Permeability cm/hr 0.792 1.62 1.692 1.368 1.368 1.37
Cation Exchange Capacity
mEq/100gm 1.37 2 2.3 2.05 1.87 1.92
Silt % 12.2 11.87 20 32.1 35.1 22.3
Phosphorus as P Kg/Ha 5.94 6.02 8.66 5.69 6.61 6.83
Nitrogen % 0.37 0.32 0.35 0.42 0.31 0.45
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 106
3.4.8 INTERPRETATION
From the interpretation of field data, physical and chemical data it can be concluded
that:
❖ Physical characters: The physical characters include Bulk density, grain size
distribution (textural analysis).
❖ Grain size distribution: Texture indicates relative proportion of various sizes of
primary soil particles such as sand, silt and clay present in the soil. Based on
their quantities present in the soil sample and using the textural classification
diagram. The textural classes of six soil samples are sandy loam.
❖ Chemical Characters: The parameters considered for chemical analysis are:
Soil reaction (pH), Electrical conductivity (EC), Cations, like Calcium and
Magnesium, Macro nutrients like Available Nitrogen, Available phosphorus and
available potassium.
❖ Soil reaction (pH): The nutritional importance of pH is illustrated, thus
hydrogen ion concentration has influence not only on, solubility of nutrients, but
also upon facility with which these nutrients are absorbed by plants, even
already in soil solution for e.g. Fe,Mn and Zn become less available as pH rises
from 4.5 to 7 to 8. At pH 6.5 to7.0 utilization of nitrate and ammonia nitrogen
becomes more available. In case of phosphorus it becomes less available to
plant as pH increases above 8.5, due to its fixation in exchange complex of soil.
For the six-soil sample under consideration the pH ranges between 7.2 to 8.25
indicating soils are neutral to slightly to moderately alkaline, and for balanced
plant nutrient management, application of organic matter like compost and
composted manure to lower the pH of soils to 6.5 to 7.0 is recommended.
❖ Electrical conductivity (EC): The salt content of the soils is estimated by EC
measurements, and is useful to designate soils as normal or sodic (saline).
Electrical conductivity is expressed as µmhos/cm at 250C, µsmhos/cm or
mhos/cm or Sm/cm. The EC of six soil samples is between 0.109 to 0.503
mmhos/cm and are below the limits to be called as saline and hence the soils
are normal for crop growth.
❖ Total Kjeldahl Nitrogen (TKN) Nitrogen is a part of all living cells and is a
necessary part of all proteins, enzymes and metabolic processes involved in the
synthesis and transfer of energy. Nitrogen is a part of chlorophyll, the green
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 107
pigment of the plant that is responsible for photosynthesis. Helps plants with
rapid growth, increasing seed and fruit production and improving the quality of
leaf and forage crops. The available nitrogen in the six samples in question, as
per analysis ranges between 0.32 to 0.45 % showing sufficient nitrogen content
for crop growth.
❖ Available Phosphorus (P): Like nitrogen, phosphorus (P) is an essential part
of the process of photosynthesis involved in the formation of all oils, sugars,
starches, etc. helps with the transformation of solar energy into chemical
energy; proper plant maturation; withstanding stress, effects rapid growth,
encourages blooming and root growth. The phosphorus content of soil of six
samples ranges between 5.69 to 8.66 Kg/hector.
❖ Available Potassium (K): Potassium is absorbed by plants in larger amounts
than any other mineral element except nitrogen and in some cases calcium,
helps in the building of protein, photosynthesis, fruit quality and reduction of
diseases. The Potassium content of six soil samples ranges between 167 to
238 kg/Ha.
❖ As observed during field visit of 10 km buffer area from boundary. The soils are
brown, alluvial and grey brown podzolic, and they occur as a catenary’s
association in undulating and rolling terrains, which differ in depth, texture, color
and cropping pattern.
❖ The soils of low lying areas, especially of bottom land (narrow valley) situation
are formed on alluvial deposits. The soil has low water holding capacity due to
more space and prone to excessive soil erosion particularly during rainy
season. In addition to this, the soils of Alfisols order are also found in rainfed
and irrigated plain valley tract.
❖ The soils of this tract are comparatively fertile as compare to rainfed hilly tract. It
is most suitable for the cultivation of field crops, cash crops like vegetables and
horticulture plants etc.
3.5 WATER ENVIRONMENT
The water resources, both surface and groundwater plays an important role in the
development of an area. Likewise, the water resources of the area have been
studied to establish the status of water quality in the area.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 108
Central Ground Water Board (CGWB) has carried out hydro-geological studies and
ground water exploration in the district. Further, CGWB under its national network
maintains 10 stations for ground water regime monitoring where water level and
ground water quality is monitored on regular basis.CGWB has drilled/constructed 56
exploratory wells in the district, in the depth range of 51.00 to 220.00 mbgl. Static
water level of the tube wells ranges from 1.45 m agl to 43.20 m bgl and discharge
ranges from 553 to 3500 lpm with the drawdown less than 8-10 m free flowing bore
wells are observed along the terrace deposits on the both banks of Swan
River.Digital Elevation Model is given below:
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 109
Figure 3-7: Digital Elevation Model
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 110
3.5.1 HYDROGEOLOGY
The rock formations occupying the district range in age from pre-Cambrian to
Quaternary period. The generalized geological succession in the district is given
below:
ERA PERIOD FORMATION DESCRIPTION
Quaternary Recent to sub-Recent
Alluvium; fluvial, terrace, piedmont sand, silt, clay, gravel, pebble and cobble
etc.
Sand, silt, clay, gravel, pebble and
cobble etc.
Undifferentiated Sand, clay, gravel, pebble, cobble and
boulders
Tertiary Pliocene to Mid. Miocene
Upper Siwalik
Soft sandstone, brownish clay, shale, poorly sorted, crudely bedded conglomerate
& boulder beds.
Middle Siwalik
Gray sandstone, and brownish clay/shale
Lower Siwalik Red and purple sandstone and shale
Hydro-geologically, the unconsolidated valley fill or alluvial formations, occurring in
the valley area and semi-consolidated sediments belonging to Siwalik Group form
aquifer system in the district. Porous alluvial formation forms the most prolific aquifer
system in the valley area, where as the sedimentary semi-consolidated formation
form aquifer of low yield prospect.
In Una valley area, the ground water occurs in porous unconsolidated / alluvial
formation (valley fills) comprising sand, silt, gravel, cobbles / pebbles etc., and forms
prolific aquifer. Ground water occurs both under phreatic and confined/artesian
conditions. Free flowing wells are also observed in the lower part of Swan river.
Ground water is being extensively developed in the area by medium to deep tube
wells, dug wells, dug cum bore wells and also by hand pumps.
Depth of dug wells and dug cum bored wells in area, ranges from 4.00 to 70.00 m
bgl, whereas depth to water level ranges from near surface to 26.46 m bgl in pre
monsoon. Yield of shallow aquifer is moderate with well discharges up to 10 lps.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 111
In Una valley depth to water level shows wide variation. During pre-monsoon period
(May 2012) it ranged from less than 2 to 45 m bgl. Deeper water levels are confined
mainly in south west (Beet area) and localized patches in north eastern and central
part of Una valley. In major parts of Una valley, depth to water level ranged between
2.00 to 10.00 m bgl. Some areas in discharge zone along the river Swan, show
water logging conditions, where water level is less than 1.5 m bgl. Seasonal
fluctuation (rise) up to 3.56 m was observed between pre and post monsoon (2012)
period. Long term water level fluctuation was analyzed for the period of May 2012,
with respect to decadal average of 2002 - 2011. In general, fall in water level up to 2
m is observed in most part of the valley. However, in isolated pockets in north
western and south eastern part of Una valley rise of water level up to 4 m is also
observed.
3.5.2 DRAINAGE PATTERN OF THE AREA
The entire area is near the Shivalik foothills and has good slope from Northeast to
South-West. The area is well drained and is frequented with seasonal shower,
which take the entire rainwater flows to river Swan.Drainage Map and Contour Map
of the study area are given below:
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 112
Figure 3-8: Drainage Map of the Area
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 113
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 114
Figure 3-9: Contour Map
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 115
3.5.3 WATER QUALITY ASSESSMENT
Water samples were collected from ground and surface waters within the study
area. A total of twelve samples were taken from different locations including surface
and ground water bodies. The samples were analyzed for physicochemical
parameters. The ground water and surface water sampling locations are shown in
Table 3-6& 3-8 and in Figure 3-10 & 3-11 respectively. The sampling and analysis of
water were carried out as per standard methods of water and waste water analysis
(APHA). The results of water analysis have been compared with IS: 10500-2012
drinking water standard to assess their suitability for drinking purpose. The
analytical results of the ground and surface water samples are shown in, Table3-7&
Table3-9respectively.
Table 3-6: Location of Ground Water Monitoring Stations
Locations Code Locations Distance Direction
GW 1 Project Site - -
GW2 Bhangal 2.06 SE
GW3 Sapalwan 7.09 SE
GW4 Nangal Khurad 6.05 NW
GW5 Bhawanipur 6.29 SW
GW6 Santokhgarh 4.92 NE
GW7 Kokowal 3.53 SW
GW8 Bitan 5.0 NW
GW9 Suksal 4.28 E
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 116
Figure 3-10: Groundwater Monitoring Location
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 117
Table 3-7: Groundwater Monitoring Results
Test Parameter
Units Requirement (Acceptable
Limit)
Permissible Limit in
absence of Alternate Source
Project Site
Bhangal Sapalwan Nangal Khurd
Gurudwara Bhawanipur
Santokhgarh (peer)
Shiv Mandir
(Kokowal)
samadhi WaliKutiya(Bitan)
Sarkari School (Sukal)
Total Alkalinity as CaCO3
mg/l 200 600 246 346 356 298 355 345 255 365 298
Colour Colour Units
5 15 <5 <5 <5 <5 <5 <5 <5 <5 <5
Total Hardness as CaCO3
mg/l 200 600 242 355 410 272 250 300 282 350 440
Odour -- Agreeable Agreeable Agreeable Agreeable Agreeable Agreeable Agreeable Agreeable Agreeable Agreeable Agreeable
Total Dissolved Solids
mg/l 500 2000 297 391 450 338 372 419 364 383 486
Conductivity µS/cm Not Mentioned 429 610 679 503 513 666 512 619 689
Turbidity NTU 1 5 <0.1 <0.1 <0.1 <0.1 0.2 0.1 <0.1 <0.1 <0.1
Cyanide as CN
mg/l 0.05 No
Relaxation <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01
Chloride as Cl
mg/l 250 1000 9 13 16 10 8 24 11 12 33
Fluoride as F
mg/l 1 1.5 0.91 0.8 0.71 0.65 0.72 0.69 0.79 0.53 0.86
Nitrate as mg/l 45
No 10.3 20.2 22.9 12 1.2 21 9 12 23
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 118
NO3 Relaxation
pH -- 6.5- 8.5 No
Relaxation 7.08 7.66 6.96 7.25 7.42 7.05 7.49 7.31 7.24
Sulphate as SO4
mg/l 200 400 2.4 7.1 11.4 5.1 1.9 32 5.3 6.7 30
Calcium as Ca
mg/l 75 200 70 77 110 73 56 107 77 90 104
Boron as B mg/l 0.5 1 0.14 0.18 0.21 0.16 0.17 0.2 0.17 0.19 0.23
Copper as Cu
mg/l 0.05 1.5 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02
Total Chromium as Cr
mg/l 0.05 No
relaxation <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05
Cadmium as Cd
mg/l 0.003 No
relaxation <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001
Iron as Fe mg/l 0.3 No
Relaxation 0.15 0.22 0.14 0.19 0.18 0.21 0.23 0.26 0.16
Lead as Pb mg/l 0.01 No
relaxation <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01
Magnesium as Mg
mg/l 30 100 17 40 33 22 27 8 22 31 44
Manganese as Mn
mg/l 0.1 0.3 0.090 0.154 0.098 0.088 0.126 0.147 0.161 0.182 0.112
Phenolic Compounds as C6H5OH
mg/l 0.001 0.002 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 119
Total Arsenic as As
mg/l 0.01 0.05 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01
Mercury as As Hg
mg/l 0.001 No
relaxation <0.0005 <0.0006 <0.0007 <0.0008 <0.0009 <0.0010 <0.0011 <0.0012 <0.0013
Nickel as Ni mg/l 0.02 No
relaxation <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02
Zinc as Zn mg/l 5 15 <0.05 <0.05 <0.05 0.05 <0.05 <0.05 <0.05 <0.05 <0.05
Total Coliforms
MPN/100ml Absent - <2 <2 <2 <2 <2 <2 <2 <2 <2
E.Coli MPN/100ml Absent - <2 <2 <2 <2 <2 <2 <2 <2 <2
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 120
RESULTS AND CONCLUSIONS:
The pH of all the samples lies within the desirable limit and ranges between6.96-
7.66. Hardness of the samples is found in the range of 242-440mg/L. Total Dissolved
Solids in the samples vary from 297 - 486mg/L, which is under the desirable limit.
Chloride content of the samples range from 8 – 33mg/L, which are under the
desirable limit. Calcium and magnesium content of the water samples varied in the
range of 56-110mg/L and 8-44mg/L respectively. Fluoride content of all samples is in
the desirable limit and lies in the range of 0.53 – 0.91 mg/L. Nitrate content of all
samples varied in the range of 9-23mg/L. Sulphate in the water samples lies within
the desirable limit and ranges between 2.4-32mg/L.
Phenolic compounds such as C6H5OH are within the desired permissible limits.
Copper(Cu),Cadmium(Cd),chromium(Cr),zinc (Zn),nickel (Ni),arsenic(As), mercury
(Hg)and lead(Pb) all are under the permissible limits as desired. Total coliforms and
Coil are absent in the samples.
Table 3-8: Surface Water Locations
Location Code
Surface Water Sample Location
Distance from project Site(km)
Direction from project Site
SW-01 Upstream(Swan River) 1.90 NE
SW-02 Downstream(Swan River) 1.90 SE
SW-03 Sutlej River 9.53 NE
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 121
Figure 3-11: Surface Water Monitoring Locations
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 122
Table 3-9: Surface Water Quality Monitoring Results
Test Parameter Units Swan River (Upstream)
Swan River (Downstream)
Sutlej River
Total Alkalinity as CaCO3
mg/l 182 185 180
Total Suspended Solids
mg/l 582 622 519
Total Hardness as CaCO3
mg/l 158 162 162
Turbidity NTU 4.8 15 2
Conductivity µS/cm 441 460 430
Temperature °C 26.6 26.4 25.8
Chloride as Cl mg/l 18 18 19
Fluoride as F mg/l 0.88 0.92 0.79
Nitrate as NO3 mg/l 2 1.6 1.8
pH ---- 8.2 8.1 8.18
Sulphate as SO4 mg/l 33 28.5 28
Dissolved Oxygen (DO)
mg/l 5.2 3.8 4.4
BOD mg/l 3.2 5.7 4.8
COD mg/l 12 20 16
Total Chromium as Cr
mg/l <0.05 <0.05 <0.05
Arsenic as As mg/l <0.01 <0.01 <0.01
Iron as Fe mg/l 0.19 0.28 0.23
Calcium as Ca mg/l 36 38 42
Magnesium as Mg
mg/l 16 16 14
Sodium mg/l 40.6 51 39.5
Potassium mg/l 5.3 9.4 6.2
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 123
Zinc as Zn mg/l 0.07 0.064 <0.05
Total Coliforms MPN/100ml 39 140 170
F.Coli MPN/100ml 20 39 48
3.5.4 CONCLUSIONS:
During March, 2019 to May, 2019
❖ pH of all the three samples is alkaline and range between 8.10 to 8.20, The
pH of the samples lies within the desirable limit.
❖ Dissolved oxygen is between 3.8-5.2mg/l.
❖ Chemical Oxygen Demand of the samples varies from 12mg/L to 20mg/L;
BOD ranges between 3.8 mg/L to 5.7 mg/L.
❖ TSS in the water samples ranges from 519 to 622 mg/L.
❖ Total hardness results shows values from 158 to 162 mg/L.
3.6 AIR ENVIRONMENT
3.6.1 AMBIENT AIR QUALITY MONITORING
The main sources of air pollution in the study area are vehicular emission,
emissions from surrounding industrial units, fugitive emissions from DG Sets, fuel
burning for domestic requirements and windblown dust from the open land.
3.6.2 PARAMETERS CONSIDERED FOR AIR QUALITY ASSESSMENT
The following parameters were taken into consideration for assessing the air
quality
❖ Particulate Matter (PM10)
❖ Particulate Matter (PM2.5)
❖ Sulphur Dioxide (SO2)
❖ Nitrogen dioxide (NO2)
❖ Carbon Monoxide (CO)
❖ Ammonia(NH3)
❖ Ozone(O3)
❖ Lead(Pb)
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 124
3.6.3 AMBIENT AIR QUALITY MONITORING STATIONS
Nine numbers of sampling locations were selected to monitor the ambient air
quality. The monitoring was carried out fromMarch, 2019 to May, 2019. The
locations of the Ambient Air Quality Monitoring Stations in the study area are
given in Table 3-10 below. Figure 3-12 shows the ambient air quality monitoring
locations.
Table 3-10: Ambient Air Quality Monitoring Locations
3.6.4 ANALYTICAL METHODS FOLLOWED FOR AMBIENT AIR QUALITY
MONITORING:
The brief methodology of the parameter analyzed is as follows:
I. Particulate Matter (PM2.5): (CPCB Method) Particulate Matter (PM2.5) was
analyzed by Fine particulate sampler Envirotech Model APM 550. PM2.5 was
collected on 47mm diameter filter paper. The mass concentration of (PM2.5) fine
particles in ambient air was calculated as the total mass of collected particles
divided by the volume of air sampled.
Location
Code Sample Location Distance (km) Direction
AQ1 Project Site - -
AQ2 Bhangal 2.06 SE
AQ3 Sapalwan 7.09 SE
AQ4 Nangal Khurad 6.05 NW
AQ5 Bhawanpur 6.29 SW
AQ6 Santokhgarh 4.92 NE
AQ7 Kokowal 3.53 SW
AQ8 Beetan 5.0 NW
AQ9 Suskal 4.28 E
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 125
II. Particulate Matter (PM10): Particulate Matter (PM10) was carried out by
Respirable Dust Sampler Envirotech Model APM 460 BL. The cyclone of this
instrument is used for fractionating the dust into two fractions. PM10 dust is
accumulated on the filter paper (8ʺ ×10ʺ size) while coarse dust is collected
in a cup placed under the cyclone.PM 10 was calculated as per IS: 5182
(Part 23):2006. The mass of these particles was determined by the difference in
filter weight prior to and after sampling. The concentration of PM10 in the
designated size range was calculated by dividing the weight gain of the filter by
the volume of air sampled.
III. Sulphur Dioxide (SO2): SO2was monitored with the help of APM 411
assembly attached with APM 460 BL using the impringer. It was absorbed by
aspirating a measured air sample through a solution of Potassium
tetrachloromercurate (TCM). This procedure resulted in the formation of a dichloro
sulphite mercurate complex. The complex was made to react with para
rosaniline and methyl sulphonic acid. The absorbance of the solution was
measured by means of spectrophotometer.
IV. Nitrogen Dioxides: NO2 was monitored with the help of APM 411 assembly
attached with APM 460 BL using the impringer. It was collected by bubbling air
through a solution of sodium hydroxide and sodium arsenite. The
concentration of nitrite ion produced during sampling was determined
calorimetrically by reacting the nitrite ion with phosphoric acid, sulphanilamide
and NEDA and absorbance of highly colored azo-dye was measured at
540nm.
V. Carbon Monoxide: It is measured using CO analyzer. This analyzer issued to
measure CO in ambient air, in the range of 0-200 ppm (220 mg/m3) to a sensitivity
of 0.05 ppm (55µg/m3). The serinus 30 combines the benefits of microprocessor
control with Non Dispersive Infrared Spectrophotometry technology. CO
concentration is automatically corrected for gas temperature and pressure
changes.CO was monitored on hourly basis whereas other parameters were
monitored on 24 hourly bases.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 126
Table 3-11: Methods Adopted For Ambient Air Parameters
Parameters Technique Technical Protocol
P.M 2.5 Gravimetric method CPCB Guidelines
PM 10 Gravimetric method IS 5182 (Part-23)
Sulphur Dioxide (SO2) Improved West and Geake method IS-5182 (Part-2)
Nitrogen Dioxides (NO2)
Modified Jacob &Hochheiser method
IS-5182 (Part-6)
Carbon Monoxide (CO)
CO Analyzer(NDIR technology) CPCB Guidelines
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 127
Figure 3-12: Air Quality Monitoring Locations
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 128
Table 3-12: Ambient Air Quality Data
S. No.
Pollutant Location Code
Location Minimum (µg/m3)
Maximum (µg/m3)
Average (µg/m3)
98th Percentile (µg/m3)
1.
SO2 (µg/m3)
AQ1 Project Site 8.2 10.9 9.2 11.6
AQ2 Bhangal 7.9 10.6 8.9 10.3
AQ3 Sapalwan 8.5 11.4 9.6 11.1
AQ4 Nangal Khurad
8.3 11.1 9.4 10.3
AQ5 Bhawanpur 8.9 11.9 10.1 10.6
AQ6 Santokhgarh 10.1 13.5 11.4 13.2
AQ7 Kokowal 7.4 9.9 8.4 9.7
AQ8 Beetan 7.7 10.2 8.6 10
AQ9 Suskal 7.9 10.6 8.9 10.9
2.
NO2
(µg/m3)
AQ1 Project Site 16.1 24.2 20.1 26
AQ2 Bhangal 15.6 23.5 19.5 23
AQ3 Sapalwan 16.8 25.3 20.9 24.7
AQ4 Nangal Khurad
16.5 24.8 20.5 23
AQ5 Bhawanpur 17.7 26.5 22.0 23.7
AQ6 Santokhgarh 20.0 30.1 24.9 29.5
AQ7 Kokowal 14.7 22.0 18.3 21.6
AQ8 Beetan 15.1 22.7 18.8 22.3
AQ9 Suskal 15.6 23.5 19.4 24.3
3.
PM10 (µg/m3)
AQ1 Project Site 69.6 99 82.4 96
AQ2 Bhangal 63.8 92 75.8 89.8
AQ3 Sapalwan 66.0 95 78.2 92.5
AQ4 Nangal Khurad
64.4 98.9 77.4 98.2
AQ5 Bhawanpur 65.3 94.5 79.6 92
AQ6 Santokhgarh 67.5 91 81.9 90.5
AQ7 Kokowal 63.3 86 74.9 88.6
AQ8 Beetan 61.4 88 72.7 86
AQ9 Suskal 67.3 94 79.7 91.6
4.
PM2.5 (µg/m3)
AQ1 Project Site 37.7 62.3 45.3 55
AQ2 Bhangal 34.7 57.4 41.7 50.3
AQ3 Sapalwan 35.8 59.1 43.0 51.8
AQ4 Nangal Khurad
35.5 58.6 42.6 54.7
AQ5 Bhawanpur 37.1 62.8 44.8 51.6
AQ6 Santokhgarh 38.9 62.0 46.7 52
AQ7 Kokowal 34.3 56.7 41.2 49.7
AQ8 Beetan 33.3 55.0 40.0 48.2
AQ9 Suskal 36.5 60.3 43.8 51.3
5
AQ1 Project Site 14.9 21.4 18.1 23
AQ2 Bhangal 14.4 20.7 17.5 20.4
AQ3 Sapalwan 15.5 22.3 18.8 21.9
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 129
Ammonia(NH3)
AQ4 Nangal Khurad
15.2 21.9 18.5 20.3
AQ5 Bhawanpur 16.3 23.4 19.8 21
AQ6 Santokhgarh 18.5 26.6 22.4 26
AQ7 Kokowal 13.5 19.5 16.4 19.1
AQ8 Beetan 14.0 20.1 17.0 19.7
AQ9 Suskal 14.4 20.7 17.5 21.4
6
Ozone (O3)
AQ1 Project Site 17.6 29.7 22.8 32.6
AQ2 Bhangal 11.7 29.0 22.6 28.9
AQ3 Sapalwan 12.6 31.2 24.3 31.1
AQ4 Nangal Khurad
12.4 44.5 24.1 39.8
AQ5 Bhawanpur 14.4 32.6 25.3 29.4
AQ6 Santokhgarh 16.3 36.9 28.7 37
AQ7 Kokowal 11.9 27.1 21.0 27.1
AQ8 Beetan 12.3 27.9 21.7 27.9
AQ9 Suskal 17.1 43.6 28.8 41.4
7.
Carbon Monoxide (CO)
AQ1 Project Site 0.44 0.74 0.57 0.8
AQ2 Bhangal 0.29 0.73 0.57 0.7
AQ3 Sapalwan 0.32 0.78 0.61 0.8
AQ4 Nangal Khurad
0.31 1.11 0.60 1
AQ5 Bhawanpur 0.36 0.81 0.63 0.7
AQ6 Santokhgarh 0.41 0.92 0.72 0.9
AQ7 Kokowal 0.30 0.68 0.53 0.7
AQ8 Beetan 0.31 0.70 0.54 0.7
AQ9 Suskal 0.43 1.09 0.72 1
8.
Lead (Pb)
AQ1 Project Site 0.048 0.089 0.069 0.1
AQ2 Bhangal 0.047 0.086 0.067 0.1
AQ3 Sapalwan 0.049 0.089 0.069 0.1
AQ4 Nangal Khurad
0.051 0.094 0.073 0.1
AQ5 Bhawanpur 0.050 0.091 0.071 0.1
AQ6 Santokhgarh 0.056 0.103 0.080 0.1
AQ7 Kokowal 0.044 0.081 0.063 0.1
AQ8 Beetan 0.046 0.083 0.065 0.1
AQ9 Suskal 0.047 0.086 0.067 0.1
3.6.5 RESULTS AND CONCLUSIONS
❖ Minimum and Maximum concentrations for PM10 for all locations were
found to be in range of 63.3 to 99 μg/m3 for the study period from March,
2019 to May, 2019 which is well within the limiting values in all stations. The
average concentrations and 98 percentile for the same was between 72.7-
82.4 μg/m3 and 86-98.2 μg/m3 respectively.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 130
❖ Minimum and Maximum concentrations for PM2.5 for all locations were
found to be in range of 33.3 to 62.8 μg/m3 for the study period from March,
2019 to May, 2019. The average and 98 percentile for the same in various
locations were in the range of 40.0-46.7 μg/m3 and 48.2-55 μg/m3
respectively.
❖ NO2 concentrations for all locations were found to be in range of 14.7 to
30.1μg/m3 for the study period from March, 2019 to May, 2019. The
average and 98 percentile for the same in various locations was in the range
of 18.3-24.9 μg/m3 and 21.6-29.5 μg/m3 respectively.
❖ Minimum and Maximum concentrations for SO2 for all locations were found
to be in range of 7.4 to 13.5 μg/m3 for the study period from March, 2019 to
May, 2019. The average and 98 percentile for the same in various locations
was in the range of 8.4-11.4 μg/m3 and 9.7-13.2μg/m3 respectively.
❖ Minimum and Maximum concentrations for ammonia (NH3) for all locations
were found to be in range of 14.0 to 26.6 μg/m3 for the study period from
March, 2019 to May, 2019. The average and 98 percentile for the same in
various locations was in the range of 16.4 to 22.4 μg/m3 and 19.1 to 26
μg/m3 respectively.
❖ Minimum and Maximum concentrations for ozone (O3) for all locations were
found to be in range of 11.7 to 44.5 μg/m3 for the study period from March,
2019 to May, 2019. The average and 98 percentile for the same in various
locations was in the range of 21.0 to 28.8 μg/m3 and 27.1 to 41.4 μg/m3
respectively.
❖ Minimum and Maximum concentrations for carbon monoxide (CO) for all
locations were found to be in range of 0.29 to 1.11 μg/m3 for the study
period from March, 2019 to May, 2019. The average and 98 percentile for
the same in various locations were in the range of 0.53 to 0.72 μg/m3 and
0.7 to 1.0 μg/m3 respectively.
❖ Lead (Pb) concentrations for all locations were found to be in range of 0.044
to 0.103μg/m3 for the study period from March, 2019 to May, 2019. The
average for the same in various locations was in the range of 0.063 to
0.080μg/m3 and 98 percentile is 0.1 μg/m3 respectively.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 131
The proposed project will increase the air pollution levels of the nearby areas. Impact
on air environment is predicted and its subsequent mitigation measures are
discussed in Chapter-4.
The detailed environmental monitoring report containing analysis results of soil,
water, air and noise is enclosed as Annexure- 9.
3.7 NOISE ENVIRONMENT
Major sources of noise in the study area:
❖ Noise made by normal human activities,
❖ Noise made by vehicles, etc.,
❖ Noise made by movement of machineries, operation of pumps, etc., and
❖ Natural noise, consisting of sounds made by birds, animals etc.
The purpose of noise monitoring at different locations is to obtain baseline noise
levels for future reference.
3.7.1 AMBIENT NOISE MONITORING
Ambient noise monitoring was conducted to assess the background noise levels in
the study area. A total of seven locations within the study area were selected for
the measurement of ambient noise levels. Noise monitoring was carried out on a
24-hour basis to assess the baseline noise-levels and to evaluate the impact, if
any. The study area for noise monitoring and the locations selected for noise
analysis has been shown in Figure 3-13 and stated under Table 3-13 and the
monitoring results are given in Table 3-14.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 132
Table 3-13: Location of Noise Quality Monitoring Stations
Locations Code
Locations Distance(km) Direction
NQ1 Project Boundary-I - -
NQ2 Project Boundary-II - -
NQ3 Near village Bathri (MDR-41) 2.89 SE
NQ4 Nangal Kalan 1.12 NW
NQ5 SingaurfSurkalan 1.68 SW
NQ6 Bat Kalan 1.23 NE
NQ7 Mehindpur 1.51 SE
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 133
Figure 3-13: Noise Monitoring Locations
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 134
3.7.2 AMBIENT NOISE STANDARD
Ministry of Environment, Forest & Climate Change (MoEF& CC) has notified the
noise standards vide. Gazette notification dated February 14, 2000 for different
zones under the Environment Protection Act (1986).
Area category: I-Industrial, C-Commercial, R-Residential, S-Silence zone
Day time: 6.00 a.m. to 10.00 p.m.
Night time: 10.00 p.m. to 6.00 a.m.
Table 3-14: Permissible ambient noise standards in dB (A)
Area category Day time Night time
Industrial Area Day Time 75 dB (A) Night Time 70dB (A)
Commercial Area Day Time 65 dB (A) Night Time 55 dB (A)
Residential Area Day Time 55 dB (A) Night Time 45 dB (A)
Silence Zone Day Time 50 dB (A) Night 40 dB (A)
Table 3-15: Noise Quality Data
Ambient Noise Levels
Location Date Day Night
Project Boundary –I 28/05/2019 63 58
Project Boundary –II 28/05/2019 60 55
Near village Bathri(MDR-41) 28/05/2019 57 49
Nangal Kalan 28/05/2019 54 44
SingaurfSurfkalan 28/05/2019 53 43
Bat Kalan 28/05/2019 52 41
Mehindpur 28/05/2019 50 40
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 135
3.7.3 ANALYSIS OF THE DATA
Assessment of noise level was carried out at various locations to evaluate the
ambient noise level in the residential area as well as possible impact due to project
activities. The values of noise level during March, 2019 to May, 2019 which are
recorded lies between 50-63 dB at day time and 40-58 dB at night time. This may be
attributed to the presence of machineries and vehicular movement nearby the project
site.
3.8 BIOLOGICAL ENVIRONMENT
3.8.1 INTRODUCTION
Ecology is the scientific study of the relations that living organisms have with respect
to each other and their natural environment. Producers, consumers and
decomposers govern whole cycle of ecology. Plants and animals both are
interdependent. Producers are necessary for every consumer. Plant plays their role
in ecology as producer. Plant, animals and microorganism together with the
environment in which they live make an independent unit called the Ecosystem.
Mainly two types of vegetation cover are on the earth surface. One is self-growing
and another is cultivated. Plants are renewable resource and useful to living
organism in many ways. It is, therefore, the role of man in manipulating and
changing vegetation population. Due to lack of awareness, deforestation is
occurring, which, in turn, is responsible for the lack of equilibrium.
The main objective of an ecological survey is to find out the baseline status of flora
and fauna of the study region. An ecological survey of the study area was conducted
particularly with reference to listing of species and assessment of the existing
baseline ecological conditions in the study area.
3.8.2 OBJECTIVES OF ECOLOGICAL STUDIES
The objective of the present study was undertaken with a view to understand the
present ecosystem on the following lines:
• To assess the distribution of vegetation in and around the proposed project;
• To assess the fauna in the proposed project and 10 km surrounding areas;
• To assess the biodiversity and to understand the resource potential; and
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 136
• To understand the nature of pollution and the impact of pollution on the
ecosystem.
3.8.3 METHODOLOGY ADOPTED FOR THE SURVEY
To achieve above objectives a detailed study of the area was undertaken in 10-km
radius area with the proposed project site as its center. The different methods
adopted were as follows:
• Generation of first-hand data by undertaking site visits systematic ecological
studies in the area.
• Compilation of secondary data with respect to the study area from published
literatures and Government agencies;
• Interviews with local people so as to elicit information for local plants, animals
and their uses.
3.8.4 FOREST COVER
Based on the interpretation of IRS Resourcesat-2 LISS III satellite data of the period
Oct to Dec 2017, theForest Cover in the State is 15,433.52 sq km which is 27.72% of
the State's geographical area. In terms offorest canopy density classes, the State
has 3,112.71 sq km under Very Dense Forest(VDF), 7,125.93 sqkmunder
Moderately Dense Forest (MDF) and 5,194.88 sq km under Open Forest (OF).
Forest Cover in theState has increased by 333.52 sq km as compared to the
previous assessment reported inISFR 2017
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 137
Source: FSI-2019
District-wise Forest cover in Himachal Pradesh
3.8.5 GENERAL VEGETATION STUDY OF THE AREA:
The study area comprises of Sub-Tropical Dry Deciduous Vegetation. Several
tropical elements can be seen scattered in the area. Species of Saccharum,
Calotropis, Vitex, Zizyphus, etc. are of common occurrence. Tree species viz. Acacia
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 138
catechu, Albizzia lebbeck, Dalbergia sissoo, Morusalba, etc. are found planted along
the boundary of the agricultural lands and along the road sides.
Ground vegetation mainly consists of grasses and small shrubs. Among the grasses,
Vetiveriazizanioides, Cenchrusciliaris are very common in the area. Useful fodder
grasses, Cynodondactylon, Eleusineindica, Trifoliumalexandrinum, etc. are present
in the proposed project area.
The large weeds which infest uncultivated tracts are aak (Calotropis procera), Arind
(Ricinus communis), dhatura (Datura metel) and thor (Opuntia stricta). Other noxious
weeds and those which appear in crops are pohlior thistle (Carthamusoxyacantha),
shialkanta (Argemone mexicana), kandyari (Solanum virginianum) and bhang
(Cannabis sativa).
3.8.6 STUDY PERIOD AND METHODOLOGY
Detailed survey was conducted to evaluate floral and faunal composition of the study
area.
Primary data on floral and faunal composition was recorded during site visit and
secondary data was collected from the Forest department and published relevant
literature. Inventory of flora and fauna has been prepared on the basis of collected
data.
3.8.7 METHODOLOGY
The table gives the methodology for studying the parameters and data collection
during the survey.
Table 3-16: Mode of Data Collection & Parameters Considered During the
Survey
Aspect Data Mode of data collection Parameters monitored
Terrestrial Ecology
Primary data collection
By conducting field survey Floral and Faunal diversity
Secondary data collection
From authentic sources like Forests department of Una and available published literatures
Floral and Faunal diversity and study of vegetation, forest type, importance etc.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 139
Aquatic Ecology
Primary data collection
By conducting field survey Floral and Faunal diversity
Secondary data collection
From authentic sources like Forests department of Una and available published literatures
Floral and Faunal diversity and study of vegetation, forest type, importance etc.
3.8.8 TYPES OF FORESTS IN UNA DISTRICT:
1. Northern Dry Mixed Deciduous Forest (5B/C2): This type is characterized
by the presence of Anogeissuslatifolia, Acacia catechu. The upper canopy is
light but fairly even and continuous in the climax form. The later condition is
however, rarely encountered and irregular, often broken canopy is met with.
This forest type is found in Bilaspur, Chamba, Hamirpur, Kangra, Kullu, Mandi,
Shimla, Sirmaur, Solan and Una districts.
2. Dry Deciduous Scrub (5/DS1): A low broken soil cover of shrubby growth, 3
to 6m high including some tree species reduced to similar conditions, usually
many stemmed from the base is the common vegetation of this type. The main
tree species are Acacia catechu, Butea monosperma,
Lanneacoromandelicaetc, and the bushes include Nyctanthesarbortristis,
Dodonaeaviscosa, Woodfordiafruticosa etc. This forest type is found in
Bilaspur, Chamba, Hamirpur, Kangra, Kullu, Mandi, Shimla, Sirmaur, Solan&
Una districts.
3. Dry Bamboo Brake (5/E9): Only one species, Dendrocalamusstrictus occurs
and forms relatively low but often dense brakes. This forest type is found in
Bilaspur, Hamirpur, Kangra, Solan and Una districts.
4. Lower or Siwalik Chir Pine Forest (9/C1a): The Pinus roxburghii stands
singly or in groups with a scattered lower deciduous tree storey. These forests
occur at the elevation of 800 to 1700m. At lower elevations it confines itself
more to the cooler northern and shelter aspects while on higher elevations it
occurs all over, preferring ridges. This type occurs mainly on Shiwalik
conglomerates and sandstones. This forest type is found in Bilaspur, Chamba,
Hamirpur, Kangra, Kullu, Mandi, Shimla, Sirmaur, Solan& Una districts.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 140
Source: “ATLAS FOREST TYPES OF INDIA” by FSI-MoEF, GoI as per Champion
and Seth (1968)
There are no Reserve & Protected forests (PF’s), wildlife sanctuary has been
observed covering under the buffer zone of 10km study area.
3.8.9 FLORA OF THE STUDY AREA:
A detailed biological study of the study area i.e. 10 km radius of the proposed project
has been carried out to identify the composition of flora and fauna. A study was
carried out for assessment of vegetation for density, diversity, frequency and relative
abundance. For fauna, random sites were selected for faunal identification. For both
the parameters, data from district forest department was obtained. The plantation in
the study area mostly consists of some ornamental species and avenue and fruit
trees. The important species of plants found in the area, are given below.
Table 3-17: Flora of the Core Zone
S.No. Botanical Name Family Habit
1. Dodonaeaviscosa Sapindaceae Shrub
2. Ipomeaaquatica Convolvulaceae Shrub
3. Saccharum munja Poaceae Grass
4. Cenchrusciliaris Poaceae Grass
5. Chrysopogonzizanioides Poaceae Grass
6. Vetiver zizanioides Poaceae Grass
7. Vitex negundo Lamiaceae Shrub
8. Zizyphusmauritiana Rhamnaceae Shrub
Table 3-18: Flora of the Buffer Zone
S.No Botanical Name Family Habit
1. Abutilon indicum Malvaceae Herb
2. Acacia catechu Fabaceae Tree
3. Acacia nilotica Fabaceae Tree
4. Achyranthes aspera Amaranthaceae Herb
5. Adhatodavasica Acanthaceae Shrub
6. Ageratum conyzoides Asteraceae Herb
7. Albiziaprocera Mimosaceae Tree
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 141
8. Barleriacristata Acanthaceae Herb
9. Bauhinia variegata Fabaceae Tree
10. Boerhaviadiffusa Nyctaginaceae Herb
11. Bombax ceiba Bombacaceae Tree
12. Carissa carandas Apocynaceae Shrub
13. Cassia fistula Fabaceae Tree
14. Celtisaustralis Ulmaceae Tree
15. Cissampelospareira Menispermaceae Climber
16. Cordia dichotoma Boraginaceae Tree
17. Cryptolepisbuchanani Asclepiadaceae Climber
18. Dalbergia sissoo Fabaceae Tree
19. Datura stramonium Solanaceae Shrub
20. Diclipterabupleuroides Acanthaceae Herb
21. Dodonaeaviscosa Sapindaceae Shrub
22. Eucalyptus sp. Myrtaceae Tree
23. Eupatorium sp. Asteraceae Herb
24. Euphorbia royleana Euphorbiaceae Shrub
25. Ficusbenghalensis Moraceae Tree
26. Ficuspalmata Moraceae Tree
27. Ficus religiosa Moraceae Tree
28. Ficusrumphii Moraceae Tree
29. Jasminum dispermum Oleaceae Shrub
30. Lantana camara Verbenaceae Shrub
31. Mallotusphilippensis Euphorbiaceae Tree
32. Mangiferaindica Anacardiaceae Tree
33. Malva parviflora Malvaceae Shrub
34. Morus alba Moraceae Tree
35. Murrayakoenigii Anacardiaceae Shrub
36. Phoenix sylvestris Arecaceae Tree
37. Populusdeltoides Salicaceae Tree
38. Sidaacuta Malvaceae Herb
39. Solanum nigrum Solanaceae Herb
40. Terminalia arjuna Combretaceae Tree
41. Terminalia bellirica Combretaceae Tree
42. Terminalia chebula Combretaceae Tree
43. Tinosporacordifolia Menispermaceae Climber
44. Urenalobata Malvaceae Shrub
45. Xanthium strumarium Asteraceae Shrub
46. Ziziphusmauritiana Rhamnaceae Shrub
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 142
3.8.10 FAUNA OF THE STUDY AREA
Table 3-19: Fauna of the Core Zone
S.No Common Name Scientific Name Wildlife
schedule
IUCN Red
List Status
Avian fauna (Bird):
1. Common Myna Acridotherestristis IV LC
2. Indian roller Coracias benghalensis IV LC
3. House Crow Corvussplendens LC
4. Indian Cuckoo Cuculusmicropterus IV LC
5. Koel Eudynamysscolopacea IV NA
6. Little Green Bee Eater Meropsorientalis LC
7. Sparrow Passer domesticus IV LC
8. Rose-ringed Parakeet Psittaculakrameri IV LC
9. Pied Myna Sturnus contra IV LC
10. Hoopoe Upupa epopsceylonensis DD
11. Fork-tailed Drongo Dicrurusadsimilis IV LC
LC: Least Concern, NA: Not Assessed, DD: Data deficient.
Table 3-20: Fauna of the Buffer Zone
S.No Common Name Scientific name Wildlife Schedule
IUCN Red List Status
Mammals:
1. Field mouse Apodemussylvaticus - LC
2. Golden Jackal Canis aureus II LC
3. Indian Palm Squirrel Funambulus palmarum IV LC
4. Indian Grey
Mongoose
Herpestesedwardsii II LC
5. Indian hare Lepus nigricollis IV LC
6. Rhesus macaque Macaca mulatta II LC
7. Fruits bat Pteropusconspicillatus V LC
8. Rat Rattus rattus V DD
9. Wild pig Sus scrofa III LC
Domestic
10. Cow Bos indicus NA
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 143
11. Buffalo Bos bubalis DD
12. Goat Capra aegagrushircus DD
Avian fauna (Birds):
13. Jungle Myna Acridotheresfuscus IV LC
14. Common Myna Acridotherestristis IV LC
15. Spotted Owlet Athene brama IV LC
16. Cattle Egret Bubulcus ibis IV LC
17. Red-rumped Swallow Cecropisdaurica - DD
18. Pied kingfisher Cerylerudis IV DD
19. Blue Rock Pigeon Columba livia - LC
20. Oriental Magpie
Robin
Copsychussaularis IV LC
21. Indian roller Coracias benghalensis IV LC
22. House Crow Corvussplendens V LC
23. Common Cuckoo Cuculuscanorus IV LC
24. Ashy Drongo Dicrurusleucophaeus IV LC
25. Asian Koel Eudynamysscolopacea IV NA
26. White-breasted King fisher
Halcyon smyrnensis IV LC
27. Small Green Bee Eater
Meropsorientalis - LC
28. House Sparrow Passer domesticus IV LC
29. Rose ringed Parakeet Psittaculakrameri IV LC
30. Red vented Bulbul Pycnonotuscafer IV LC
31. Spotted Dove Streptopeliachinensis IV NA
32. Pied Myna Sturnus contra IV LC
33. Marsh Sandpiper Tringastagnatilis IV LC
34. Common Babbler Turdoidescaudatus IV NA
35. Hoopoe Upupa epopsceylonensis IV NA
Reptiles
36. Common Toad Bufomelanostictus IV LC
37. Skipping frog Bufostomaticus IV LC
38. Krait Bungarus caeruleus IV NA
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 144
39. Banded krait Bungarusmulticinctus - NA
40. Kashmir Rock Agama Laudakiatuberculata - NA
41. Bronze Grass Skink Eutropismacularia NA
42. Garden lizard Calotes versicolor - NA
43. House lizard Hemidactylusfrenatus - LC
44. India bull frog Hoplobatrachustigerinus - DD
45. Cobra Najanaja II LC
46. Rat snakes Ptyasmucosus - NA
LC: Least Concern, NA: Not Assessed, DD: Data deficient.
3.8.11 WASTE LAND:
Most of the areas nearby the Core zone are waste land. Commonly seen plant
species in such areas are Saccharum munja, Ipomoea aquatic, Dodonaeaviscosa,
Vitex negundo, Cenchrusciliaris, etc. These weeds are affecting the agricultural
productivity of the region due to fast growth, short life cycle and enormous
production of seeds.
*Source: Field Survey Report
3.8.12 CONCLUSION:
After site visit and survey around the 10 km buffer zone of the proposed Steel
project, it is observed that there are no RF, PF existing within the buffer zone. The
proposed project is located in the Tahliwala industrial area, surrounded by small
industrial units. The study area did not record presence of any
endangered/threatened/endemic flora and fauna species. No wildlife/bird
sanctuaries/national parks/ biospheres located within the 10-km study area from
the proposed project.
There are about species of 54 floral & 57 faunal species recorded from field studies
among them number of 34 species of aves, 12 mammals and 11 reptiles are
recorded from the site visits, communication with the locals and from the secondary
literatures. Vast anthropogenic activities are going on, due to the presence of
industrial hub, but as per survey no significant schedule I species has been
observed, therefore it can be concluded this project will not cause disturbance to
any wildlife for roosting, foraging and nesting.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 145
3.9 SOCIO ECONOMIC STUDY
Iron and Steel are highly important materials used in a wide range of products with
important contribution to the economic development. The processes for making Iron
and Steel are energy intensive and known to contribute to local pollution. This
metallurgical plant mainly uses electrical power for its Induction Furnaces,
continuous casting and rolling mills to meet its energy needs. All these operations
can disturb environment of the area in various ways, such as removal of mass, flora
and fauna of the area, surface drainage, and change in air, water and soil quality.
While for purpose of development and economic upliftment of people, there is need
for establishment of industries, but these have to be sustainable and environmental
friendly. Therefore, it is essential to assess the impacts of Metallurgical industry on
different environmental parameters before starting the industrial operations. The
likely impacts on different environmental parameters due to this metallurgical project
taking into consideration the kind of activities involved and mitigation are discussed.
Along with environmental impact social impact is also occurred due to any industrial
activity and for the same a strong social impact assessment is required.
General information about the project site: - Capacity Enhancement of Steel
Manufacturing Unit by Replacing Existing Induction Furnaces and Enhance
production capacity from 45,000 MTPA to 1,40,000 MTPA proposed by M/s
Vardhman Ispat Udyog. The total allotted area for the proposed project is 27078.0
Sq.m.in Tehsil & district Una, Himachal Pradesh-174303. The project is falling under
Category “A”according to the EIA notification 2006 and subsequent amendments
thereof. The proposed project has interstate boundary with Punjab within 1km from
project site. The proposed project is classified under category “A”. Himachal Pradesh
and Punjab interstate boundary are around 1.0 km from project site.
Nangal town has all facilities of many Schools, Colleges, Petrol pumps, Hospitals,
Temples, Hotels, ATMs, Cinema Theaters, Bus stops etc. The civil amenities and
civil institutions are falling within 10.66 km (Aerial distance) from project site. Una city
(H.P) is about 17.39 km from the project site.Nangal, Una, Nawanshahr are the
nearby Cities to Bathari.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 146
3.9.1 STUDY AREA
M/s Vardhman Ispat Udyog is located at Village- Bathri, Distt. Una, State Himachal
Pradesh of India. Nangal region is the nearby Localities to the site & pin code no of
Nangal is140124 and postal head office is also in Nangal.
The site is located at about 31°19'10.06"to 31°19'06.14"North Latitude and
76°17'25.38" to 76°17'37.02"East Longitude. Hindi and Punjabi are the Local
Languages here.
3.9.2 METHODOLOGY
The Demographic profile has been studied through random sample primary surveys
and secondary data. Proper care and weightage will be given to the local people in
employment and providing other amenities. Namely data was collected from local
villages. Accordingly; both qualitative and quantitative data was analyzed from
secondary sources. Primary Census Abstract 2011 is the main source of secondary
data. Collection and evaluation of baseline data for various socio-economic
parameters in and around the proposed sites has been done (within 10 km radius of
the study area from the lease boundary). Villages, within the study area are being
identified from survey of India Toposheet. Figure below is showing the location of
villages falling within10 km radius of boundary.
On the basis of a preliminary reconnaissance survey, a questionnaire was developed
to make it suitable to fulfill the objectives of the study. The data collected during the
above survey was analyzed to evaluate the prevailing socio-economic profile of the
area.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 147
Figure 3-14: Showing Location of Villages’within10 Km Radius of Boundary
3.9.3 BASELINE DATA
For impact assessment both primary and secondary data was collected. While
primary data was collected through census-cum sample survey in the core area and
sample survey in the buffer area, the secondary data was collected from
administrative records, published reports and websites.
According to the Census 2011, Una district is having total population 521,173
comprising 263,692 males and 257,481 females.. This population of the district
forms 8.44 per cent of the state population and ranks at 6th place among the
districts. Out of the total population of the district 91.38 per cent lives in rural areas
while 8.62 per cent lives in urban areas. Rural population of the district is distributed
among 5 sub-districts (previously known as tahsils/ sub-tahsil) and urban population
is spread over in equal number of towns.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 148
Of the total population of Una district total 44 villages are found in the radius of 10
km (including both region Punjab & H.P) from project site as per toposheet.
According to the 2011 census data, population of district Una Himachal Pradesh in
44 villages is 53591. The male population is 27342 and female population is 26249.
The sex ratios of Una district in 44 villages are 960 females per 1000 Male.
The majority of the people depend on Agriculture with the capacity enhancement of
the proposed project the occupational pattern of the people in the area will change
with more people getting engaged in industrial and business activities.
The study area is falling under the 10 Km buffer zone of Una, Tehsil Una and as well
as of Rupnagar District, Tehsil Nangal. So the details of both districts are presented
below.
Table 3-21: Demographic Profile of the Study Area within the Boundary of Two
Tehsils in Two Districts and States
Nam
e o
f th
e
Teh
sil &
Dis
tric
t
To
tal H
H
To
tal
Po
pu
lati
on
Male
Fem
ale
Po
pu
lati
on
belo
w 6
yrs
.
SC
Po
pu
lati
on
ST
Po
pu
lati
on
No
of
lite
rate
To
tal w
ork
er
Main
Wo
rker
Marg
inal
Wo
rker
No
n-w
ork
er
Una,
H. P
24694
118598
60226
58372
13179
22946
247
90855
46571
32059
14512
72027
Anandp
ur
Sahib,
Rupnag
ar,
Punjab
28270
144600
76624
67976
15540
43363
0 105961
47214
39988
7226 97386
*Source: - Census 2011
Baseline data refers to basic information collected before a project/scheme is
implemented. It is used later to provide a comparison for assessing actual impact of
the project. The present report is provided with the following base line data for the
study area as a whole. Table no. 33 presents the demographic profile of the villages
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 149
falling in District Una and Tehsil Haroliunder the state boundary of Himachal
Pradesh.
Table 3-22: Demographic Profile of the Study Area within 10 Km Radius from
the Project Site (Himachal Region)
S. No.
Tehsils/District
Name of the villages
No_HH
TOT_P
TOT_M
TOT_F
P_06
P_SC
P_ST
P_LIT
TOT_WORK_P
MAINWORK_P
MARGWORK_P
NON_WORK_P
1
Una Fatehpur (223)
193
963
483
480
106
255 0
743 295 285 10 668
2
CharatgarhUpperla (225)
410
1990
1008
982
215
741 0
1621 573 321 252 1417
3
Udheypur (224)
122
639
314
325
84
62 0
424 332 295 37 307
4
CharatgarhNichla (225) 76
381
181
200
49
71 0
287 140 80 60 241
5
Raipur Upperla (218)
553
2437
1195
1242
241
77 0
2016 678 637 41 1759
6
Raipur Nichla (218)
222
1208
627
581
153
401 0
923 366 355 11 842
7
Khanpur (226)
248
1283
633
650
142
53 1
948 606 369 237 677
8
Binnewal (243)
138
648
311
337
57
85 0
504 280 280 0 368
9 Haroli
Bhadauri (468)
264
1264
668
596
143
300 0
894 408 139 269 856
10
Palakwah (469)
401
1854
914
940
235
483 2
1408 545 471 74 1309
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 150
11
Karampur
189
1011
524
487
103
55 0
770 426 165 261 585
12
Bhadiaran
163
765
389
376
80 0 1
576 246 77 169 519
13
GoindpurTarf Bula (529)
248
1273
652
621
131
216 0
992 492 324 168 781
14
Bitan (528)
566
2976
1540
1436
371
819
1917
2009 1082 542 540 1894
15
Lalehri (470)
816
4242
2158
2084
485
545
12
3240 1668 708 960 2574
16
Nangal Khurd (471)
270
1498
760
738
188
304 0
1131 467 276 191 1031
17
Nangal Kalan (472)
217
1169
608
561
139
106 0
877 363 352 11 806
18
Bat Kalan (473)
142
752
397
355
87
27 0
519 257 235 22 495
19
Bat Khurd (474)
173
897
474
423
115 4 0
648 380 293 87 517
20
Bathu (475)
361
1862
931
931
215
278 0
1424 660 387 273 1202
21
Bathri (476)
539
2684
1383
1301
364
971
62
1770 962 575 387 1722
Total Villages = 21
6311
31796
16150
15646
3339
4882
1995
23724
11226 7166 4060
20570
*Source: - Census 2011
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 151
3.9.4 DEMOGRAPHIC DETAILS OF THE STUDY AREA IN HIMACHAL REGION
The total household in these 21 villages is 6311 and the total population is 31796.
The male population is 50.79 % and female population is 49.20%. Children’s
population is 10.50%. Literacy rate is around 74.61% which is considerably lower
than the overall state figure. The SC population is 15.35% and ST population is
6.27% which is found in only 6 villages. There are 15 villages having no Schedule
Tribes. The sex ratio of the study area in Himachal region is 969 females per 1000
males.
3.9.5 OCCUPATIONAL PATTERNS OF THE STUDY AREA IN HIMACHAL
REGION
Occupational details of the study area in Himachal Region; Total working population is
concerned 35.30%. Populations considered as main worker are 22.53% and Non
workers are 65% whereas marginal worker considered 12.76% within study area. These
21 villages are falling within the two Tehsils namely Una (8 villages) and Haroli (13
villages).
Table no. 34 presents the demographic profile of the villages falling under the state
boundary of Punjab, District Rupnagar, and Tehsil Anandpur Sahib.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 152
Table 3-23: Demographic Profile of the Study Area within 10 Km Radius from the Project Site (Punjab Region)
S. No.
Tehsil /Sub District
Name of the villages
No_HH
TOT_P TOT_M TOT_F P_06 P_SC P_ST P_LIT TOT_WORK_P MAINWORK_P
MARGWORK_P
NON_WORK_P
1
Tehsil Anandpur Sahib
Dholowal (307) 7 33 17 16 0 0 0 32 11 11 0 22
2 Majara (311) 92 484 259 225 59 156 0 356 132 71 61 352
3
Bhanam (271) 510 2667 1414 1253 279 286 0 1916 1038 901 137 1629
4
Pasiwal (268)
202 958 485 473 82 367 0 751 361 277 84 597
5 Majari (266) 212 1052 522 530 105 63 0 787 490 318 172 562
6
Daghaur (254) 174 841 414 427 103 241 0 664 224 192 32 617
7 Sukhsal(255) 374 1848 938 910 209 5 0 1342 560 500 60 1288
8 Diyapur (265) 94 484 236 248 54 180 0 373 134 130 4 350
9
Gohlani (263) 356 1668 879 789 148 147 0 1286 865 307 558 803
10 Kulgraon 206 941 459 482 80 143 0 749 248 191 57 693
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 153
(264)
11
Sangatpur (258) 138 754 385 369 74 70 0 569 128 100 28 626
12
Bhikhapur (256) 60 322 165 157 37 0 0 234 169 16 153 153
13 Melwan (257) 230 1008 513 495 109 116 0 730 344 173 171 664
14
Sehjowal (252) 364 1843 952 891 208 94 0 1298 781 666 115 1062
15
Bainspur (253) 64 294 147 147 33 0 0 191 94 94 0 200
16
Surewal (251) 129 614 297 317 64 116 0 451 297 241 56 317
17 Hazipur (250) 121 658 354 304 48 96 0 517 89 89 0 569
18
Chhotewal (259) 232 1087 568 519 95 69 0 818 474 378 96 613
19
Maujowal (260) 226 1129 562 567 144 351 0 854 330 314 16 799
20
MedhaMajra(238) (Part) 0 0 0 0 0 0 0 0 0 0 0 0
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 154
21 Bhaton (262) 120 577 297 280 75 71 0 354 180 178 2 397
22
NurpurBedi
Mehandpur (478) 222 1181 619 562 151 232 0 812 335 212 123 846
23
Bhangal (477) 267 1352 710 642 205 164 0 869 662 461 201 690
Total Villages = 23 4400 21795 11192 10603 2362 2803 0 15084 7946 5820 2126 13849
*Source: - Census 2011
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 155
3.9.6 DEMOGRAPHIC DETAILS OF THE STUDY AREA IN PUNJAB REGION
There are 23 villages located within 10 Km radius of the project area within the state
boundary of Punjab. All these villages are being considered as buffer area villages.
Socio-economic data of these villages are being compiled based on 2011 census
book. The total population is 21795, among which 51.35% male and 48.64% female.
Children’s are 10.83%. Literacy rate is 69.2%, a slightly lower than the overall state
figure. The sex ratio of the study area in Himachal region is 947 females per 1000
males. Sex ratio is comparatively lower than the H.P region. Cause of lower sex
ration in Punjab region is presence of Dowry system. Literacy rate within 10 Km
study area in Himachal Pradesh, Schedule caste Population is 12.86 % and
Schedule Tribe population is 0. There is no ST population in the study area in Punjab
region. There are also four villages namely Dholowal Bhikhapur, Bainspur, Medha
Majra where no Schedule Caste community found.
3.9.7 OCCUPATIONAL PATTERNS OF THE STUDY AREA IN PUNJAB REGION
Occupational details of the study area in Punjab Region; Total working population is
concerned 36.45%. Populations considered as main worker are 26.70% and Non
workers are 63.54% whereas marginal worker considered 9.75% within study area.
These 23 villages are falling within the two Tehsils namely Anandpur Sahib (21
villages) and NurpurBedi (2 villages).
Table 3-24: Demographic Profile of the Study Area (10km) In Tehsil & District
Una Himachal Pradesh
Nu
mb
er
of
the V
illa
ge
s
To
tal
Ho
us
eh
old
To
tal
Po
pu
lati
on
Male
Fem
ale
Po
pu
lati
on
belo
w 6
yrs
.
SC
Po
pu
lati
on
ST
Po
pu
lati
on
No
of
lite
rate
To
tal w
ork
er
Main
Wo
rke
r
Marg
inal W
ork
er
No
n w
ork
er
SUM
TOTAL
of 44
Villages
10711 53591 27342 26249 5701 7685 1995 38808 19172 12986 6186 34419
*Source: - Census 2011
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 156
Table no. 3-24 presents the demographic profile of the 44 villages located within 10
km radius of the project area in district Una Himachal Pradesh. All these villages are
falling within two States, Himachal Pradesh where the project is situated, and
another is Punjab state due to interstate boundary.
The total Household in these 44 villages is 10711 and the total population is 53591. The
male population is 51% and female population is 48.98%. Children’s population is
10.63%. Literacy rate is around 72.41% which is considerably lower than the overall
state figure that is 83.78%. The SC population is 14.34% and ST population is 3.72%.
Total working population is concerned 35.77%. Populations considered as main worker
are 24.23% and Non workers are 64.22% whereas marginal worker considered 11.54%
within study area.
A) SOCIAL COMPOSITION
From the baseline data it has been found that the majority of populations in these
villages are Hindus. The people from Sikh community are staying there. There is
also Schedule Caste and Schedule Tribe. Local languages are
Himachali, Hindi and Punjabi. Punjabi with mixture of Himachali language is mostly
used in plain areas of Una City, Tehsil Ghanari and Haroli Tehsil. But in other areas
like Bangana, Amb and ChintpurniHimachali language is widely spoken.
B) CULTURE
Most of the population is Hindu and hence most people. The local language is Hindi
and Punjabi both. Punjabi with mixture of Himachali language is mostly used in plain
areas of Una City, tehsil Ghanari and Haroli Tehsil. But in other areas like Bangana,
Amb and ChintpurniHimachali language is widely spoken. Una had been a tehsil of
the Hoshiarpur district until the Punjab Reorganization Act, 1966 and Kangra
district until 1972. Due to religious contiguity and cultural affinity it was given
to Himachal Pradesh. Before 1966 Una was the part of Punjab. So, mixture of
culture (Himachali as well as Punjabi) is found in this district.
• People: - Population of Una district is predominantly Hindus and next come
Sikhs and third being the Mohammedans. There is considerable population of
Hindus.
• Caste/Race: - The Bhatti, Kashyaps, Khatri and Sood castes are the main
castes in this region. The Scheduled Castes communities and Scheduled
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 157
Tribes are found within the 10 km periphery from project site. But Punjab
region of the study area have not ST community.
• Dress: -Kurta and Pajama is the culturally accepted dress for men. Office-
going men wear shirts and pants. Women wear Salwar Kameez on most
casual and formal occasions. A Sari is also worn, especially to weddings.
Young people mostly wear western styled clothing, including jeans and
shirts. Unisex clothing is gaining acceptance, especially in the suburbs.
Shawl is worn in the winters. They can be plain or embroidered (especially for
women).
• Food and Drinks: -Maize and wheat are the staple food of the people. They
also take rice occasionally. People take three or four meals a day. In breakfast meal
Paratha is famous meal in this region. Butter milk and curds are always used. The
practice of taking tea in the morning and evening is gaining popularity.
C) ECONOMY
The local economy is mainly based on agriculture. The people of Una mainly earn their
livelihood through agriculture. Una is also becoming an industrial hub. Inrecent years,
there has been growth in various light industries including Rubber, Paper Computers
manufacturing, Pharmaceutical s industry and many other manufacturing firms in Una
region.
Potential for new MSMEs: Based on resources available in the district scope of small-
scale industries have been identified, care has been taken to identify those Industries
also for which there is a congenial climate condition in the district.
• Resource Based Industries: Cattle Feed, Pickles & Chutney, Wooden
Furniture etc.
• Skill Based Industries: Woolen carpets, Hosiery Products etc.
• Demand Based Industries: Atta Chakki, Spices grinding, Ice Cream/Ice, etc.
• Hosiery and Textiles: Canvas School Bags, Travel Bags, School Uniform etc.
• Paper Products: Corrugated paper boxes, Office File Covers/exercise books
etc.
• Leather and Rexine Products: Leather Shoes/Chappals/Belts, Rexine
Suitcase etc. Chemical Based: HDPE/IDPE Pipes, Insecticides/pesticides,
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 158
Paint & Varnish, etc. Mechanical and Allied Products: Steel Furniture, Spray
pumps, Gates and Grills etc.
• In addition of that there is cylinder factory named Him Cylinders and Steel Plant by
the name of Him Alloys. The International Cars and Motor has also one their plant
in the City. The Jeevan Market has many shops dealing in all types of products.
Nestle has set up a factory in nearby industrial area Tahliwal.[citation
needed] Cremica is already present there, some big industries are also moved in
like Inox Wind in Basal and some other industrial units in Dhamandari. The
economic growth of this region is depending upon the industries.
D) EMPLOYMENT
The project would be promoting employment and ancillary business opportunities of
local population. Because the project area is mainly fall in Una Industrial area. There
are many industries like Inox Wind, Catechu, Katha Udyog, Cylinder factory, Steel
Plant, International Cars and Motor Plant, Paper mill, Pharmaceuticals manufacture unit
and many more are within the Una district. So, there is a huge opportunity of various
industry-oriented jobs and a good opportunity of different workforce has been founded.
Most of the population is engaged in agricultural activities. So, the working population of
this region is only 35.77%. The Proposed capacity enhancement project shall improve
the socio-economic status of the area due to the people engaged in industrial activities.
There are around 184 people skilled and unskilled labour will be employed in this plant
(Existing 84 & Proposed 100). The area is considered as industrially upward. They also
depend on agriculture, which is seasonal.
E) ROAD, RAIL AND AIR CONNECTIVITY
Nangal city is at the distance (Aerial) of 10.66 km in NE direction from project site which
is well connected with Road and railway.
• Nearest Railway Station: -Nangal Railway station about 9 kmin the NE
direction(Aerial Distance).
• Nearest Airport: -Ludhiana Airport about 61 km away from project site in SW
Direction (Aerial Distance).
• Nearest Highway: -Project site is adjacent to MDR-41road and further
connected with NH-205 approx. 33 Km in the SE direction (Aerial Distance).
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 159
3.9.8 BASIC AMENITIES
• Educational
The Nangal has facility of all levels of schools and colleges and educational institutes
which is approx. 10.66 km from the project site; Village Bathari, District Una Himachal
Pradesh. Govt. School Gurpalaah- Bathu at About 1.0 Km in North direction. Govt.
College Beetan about 5.87 Km in NW direction from the project site.
• Medical
The Nangal has all types of medical facilities like Nursing Homes, Health Centers,
Fertility Centers, Multispecialty Hospitals, Ayurvedic Hospital, Dental Care Center
and Civil Hospitals besides many private clinics at Nangal which is about 10.66 km
(Aerial distance) from the project site. Govt Hospital Binewal Punjab is about 5 km in
SW direction & Civil Hospital Una Haroli is about 14 km from NW direction from the
project site.
• Electricity
Electricity is available in all small villages of study area.
• Housing and drinking water
A major part of the houses in the study area is pucca houses. All villages in the study
area have water supply for domestic purposes. The sources of water supply in most of
the villages are through private bore wells, pipe line however people have preference
for ground water. The water source to the project site is from the District Industries
Centre connection.
• Transport
The main mode of transportation is by road. A network of both paved (Pucca) and
unpaved (Kucha) roads exist in the study area, both are suitably inter connected.
Private vehicles and private bus services share the major responsibility of the
Transport in the study area. Numbers of buses, private and state Govt. of Himachal
Road Transport Corporation (HRTC) are operating on state highway. The existing
local transport facility is, appears to be sufficient.
• Post and Telegraph
The Post office facility, telegraph office and telephone office and telephone, FAX, STD,
ISD etc.is located in nearest villages. The study area is connected through mobile
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 160
network. The Nangal city with all modern facility is at distance (aerial) of approx. 10.66
Km from the project site.
• Place of Historical or Archaeological Interest
No place of Historical or Archaeological importance exists near the project site. But
Chintpurni is the most visited temple in Una by Hindus and Sikhs, especially on
weekends and on special religious days. The Hindu genealogy registers at
Chintpurni, Himachal Pradesh are kept at Chintpurni. Una is one of the industrial
destinations in the Himachal Pradesh. Una shares its border with
the Hoshiarpur districand Rupnagar district of Punjab and Kangra, Hamirpur and Bila
spur district of Himachal Pradesh. The terrain is generally semi-hilly with low hills.
Una has been identified as a main industrial hub and has become a transit town for
travelers going to the city of Dharamshala or locations within the Himalayas such
as Kullu, Manali, Jawalamukhi, and Chintpurni.
• Prominent industries in Una
It is a prominent town in the Micro/Small/Medium Enterprises. Una district is one the
industrial hub in Himachal Pradesh. Since past few years, Steel industries, Inox
Wind, Catechu, Katha Udyog, Cylinder factory, Steel Plant, International Cars and
Motor Plant, Paper mill, Pharmaceuticals manufacture related business has been
booming in the region. Prominent Industries of the area are as follows: -
• Luminous Power Technologies Pvt. Ltd., Ram Nagar Gagret
• Him Cylinder Ltd., Plot No. 1 to 4, Indl. Area, Amb
• Swiss Garnier life Science, I.A Mehatpur, Distt. Una
• International Car & Motors ltd., Indl. Area, Amb
• Him Alloys & Steel Pvt. Ltd., VPO, Nehrian Road Amb
• Inox Wind Ltd. Plot No. 1, Indl. Area, Basal
Gagret is the fastest-developing town in Himachal Pradesh, as many companies
have established their manufacturing units in Gagret: Fewa Electrical Corporation
(Fine Group), Tigaksha Metallics Pvt. Ltd. (Supermax Personal Care Pvt. Ltd.),
Luminous India, MBD Group, Accurate Metals. to name a few. Gagret is also known
for its wholesale steel market. Nestle has set up a factory in nearby industrial
area Tahliwal.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 161
3.9.9 SOCIAL IMPACT ASSESSMENT & CONCLUSION:
The project has provided a direct job opportunity to the locals as both technical and
non-technical workers. Right now there are workers from local village and town. With
the growth of other industries in this area the workload and scope of job opportunity is
increasing by day. A major part of this labour force is mainly from local villagers who are
expected to engage themselves both in agriculture and project activities. This enhances
their income and lead to overall economic growth of the area. The following socio-
economic changes are expected due to project activities:-
• There will be positive effect on livelihood of people living in this area. It creates a
great impact on education and literacy. Because a fixed income helps to lead a
better life and give a better future for next generation too.
• The project has brought about changes in the pattern of demand from food to
non-food items as sufficient income is being generated.
• People located in the project area and in close vicinity, enjoying positive
changes in life style and better quality of life.
• Approximately 84 local people are already employed in existing plant & 100
would be proposed due to capacity enhancement in production out of which
14 will be residing within the project premises.
• The no of labours will increase in near future to cater more services in
surrounding areas.
• The employment shall be in the form of skilled, semiskilled as well as
unskilled workers.
• Due to production activities by proposed project will be help to meet the market
demand of metallic material for various engineering works.
3.10 REHABILITATION &RESETTLEMENT (R&R) ACTION PLAN
No Rehabilitation & Resettlement (R&R) is involved as mostly the local people are
employed in the project and they will be coming from the nearby villages. A few
employees will stay within the plant complex itself.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 162
CHAPTER-4: ANTICIPATED ENVIRONMENTAL IMPACTS &
MITIGATION MEASURES
4.1 INTRODUCTION
Identification and evaluation of various potential impacts due to the proposed
Expansion and augmentation project on the surroundings and the mitigation
measures in respect of each of the environmental parameters are presented in this
chapter.
Generally, the environmental impacts can be categorized as either adverse or
beneficial. Almost all the potential impacts that are temporary and short termed might
occur during the construction phase, whereas potential impacts during operational
phase might have long term effects. The potential impacts have been identified for
the whole of study area (10 km impact zone) with respect to air, noise & vibration,
water, soil, biological and socio-economic environment. The mitigation measures
that are required to negate the adverse impacts are also discussed in this chapter
environmental aspect wise.
The impact identification and prediction process aims to:
❖ Identify potential source or cause of impact throughout the life of project
❖ Characterize the potential impacts affecting the social, economic and
environmental attributes.
❖ Assess the potential of changing likelihood of impact through Environmental
Management Plan (EMP).
❖ Prediction of the impacts due to the development, construction and functional
activities encompass the developmental processes to be undertaken during
construction and functional phases.
In following sub sections, the potential impacts and magnitude of the impacts from
the project have been assessed and discussed in detail.
4.2 IMPACTS ON LAND ENVIRONMENT
The land use pattern of the project not change as land is already developed for
industrial purposes. The proposed project is for expansion and augmentation of
integrating melting and rolling facility within the existing plant premises only.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 163
4.2.1 IMPACTS DURING CONSTRUCTION PHASE
Minor site excavation will be envisaged during construction of the expansion unit.
The activities causing potential impact during construction phase on land use
includes leveling of site, construction of related structures and installation of
equipment’s/heavy machineries. No significant adverse impact on the surrounding
land use during the construction period is envisaged. The construction activities will
result in top soil displacement to some extent in the plant area. Apart from localized
construction impacts at the plant site, no adverse impacts on soil in the surrounding
areas are anticipated.
4.2.2 IMPACTS DURING OPERATIONAL PHASE
During operation phase, the activities of proposed plant will not change the soil
quality. There is no generation and dumping of industrial process wastes/solid
wastes from the plant operations and whatever solid wastes are generated are
disposed either in recovery or for further use in manufacture or recycling.
4.2.3 MITIGATION MEASURES
Excavated soil during construction phase will be suitably used for land filling in low
lying areas. The top soil will be preserved and used for landscaping purposes and
whatever solid wastes get generated will be disposed of as either in recovery of iron
or used as sand in road construction or recovery of precious/ more valuable metals.
Other solid wastes are sold to market as low value products.
4.3 IMPACTS ON AIR ENVIRONMENT
4.3.1 IMPACTS DURING CONSTRUCTION PHASE
During the construction phase, dust (particulate matter) is expected to be the main
pollutant to be emitted from the haul roads, stockpiles and material handling. In this
case, pollution emission sources shall be distributed throughout the project site and
will fall under the category of area source. The land is already developed for
industrial work so extensive site formation work is not required. Vehicular emission of
SO2, NO2, CO will add onto the air pollution. Movement of vehicles on unpaved
roads will also add onto the dust emission. Operation of DG sets will also generate
air pollutants like SO2, NO2, CO. Fugitive emissions are envisaged such as dust in
construction phase only.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 164
4.3.2 IMPACTS DURING OPERATION PHASE
Raw material will be transported in lump form by trucks, with covered tarpaulin, and
finished product will be transported likewise. Hence, no emission is envisaged.
Particulate and fugitive emissions might arise from activities like grinding and
screening of scrap, DG set activity, and by the movement of vehicle.
During the operation phase, there are four major categories of sources of air
pollutants, they are:
❖ Emissions from manufacturing processes
❖ Fugitive emissions from material handling
❖ Emissions (NOx, CO, and PM) from vehicular movement
❖ Emissions (NOx, CO, & PM) from Diesel Generator Set
4.3.3 MITIGATION MEASURES
The impact during construction phase will be reversible, marginal and temporary in
nature. Proper maintenance of vehicles and construction equipment will help in
controlling the gaseous emissions. Water sprinkling on roads and construction site
will prevent fugitive dust. Green belt development along the road side and in the
plant premises will be useful in dust suppression. Over loading of the trucks will be
avoided. Haulage roads, which are used for transportation of material, will be
maintained properly. Utmost care and regular inspection schedule will be made to
prevent any fugitive emission of dust during transportation of material. People
working in and around the dust generating area, will be provided with Personal
Protective Equipment (PPE) like dust mask to prevent inhalation of dust particles,
and use of the same will be strictly enforced during working hours.
During operation phase, air pollution control equipment’s will be used, paved roads
will be laid to prevent dust emission during vehicular movement. Adequate greenbelt
is also proposed, which will control the dust. Regular water sprinkling arrangement
will be provided at the loading and unloading areas. Workers working near the dust
generating area will be provided with dust masks, which will be made as mandatory
to wear during working hours. Following mitigation measures will be taken to reduce
ambient air pollution.
❖ The proposed stacks to comply with the applicable emission norms.
❖ Adequate stack height to be provided as per norms.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 165
❖ APCD system will be provided to minimize the emissions of dust and to maintain
the emissions within the prescribed limits.
❖ The suction hood provided with the Induction Furnace will be of adequate size
and design which would ensure suction of major emissions from both the IF and
metal/slag tapping.
❖ Regular monitoring of emissions from all stacks and ambient air quality to be
carried out as per norms.
❖ All air pollution control devices shall be well maintained to keep them running
efficiently.
❖ The stack attached to the DG set will have stack of height which will go 3m above
the nearby roof.
❖ Environmental management cell equipped with adequate manpower and
provided with budgetary funds allocation will be entrusted with the responsibility
of ensuring the efficient working of all environmental control devices.
❖ Post commissioning monitoring and submission of half yearly report on
compliance to the Regional office of MoEF&CC in Dehradun, Uttrakhand.
M/S VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 166
Figure 4-1: Induction Furnace and Its Air Pollution Control Device
M/S VARDHMAN ISPAT UDYOG `
167
TREATMENT PROCESS
The unit is designed keeping in view the worst operating conditions. Following
equipments are provided with their different functions.
SUCTION HOOD
The furnace is fitted with Movable Suction Hood of capacities adequate enough for
efficient suction of the total volume of flue gases generated from the furnace either
located on top of the induction furnace or around its sides suitable for suction from
both the furnace and from the ladle while tapping of slag or tapping of molten steel.
DUCTING
Ducting has been provided in the system not only for conveyance of gases at
appropriate velocities so that there is no major build up dust in them, but also to
reduce the temperature by natural convection. Periodical inspection of inside of
ducts and cleaning thereof of any settled dust in them will be carried out, which will
also form a part of regular reporting of half yearly reports to the regional office of
MoEF.
ID FAN
They have been provided for creating an adequate negative pressure in the system
for efficient suction of gases. They are so chosen that it ensures suction of entire
generated gases evolved from the mouth of IFs and ctapping point of Slag and
metal.
BAG HOUSE
The Bag filter Unit is a pulse type system where dust gets collected on the outer side
of the bags when dust-laden gas passes from the outside of the bags to the inside of
bags. Time set sequentially passed pulses of compressed air from the top releases
the collected dust on bags to the hopper below. The Bag House removes fine
particles and gases are fed to chimney. The entire mobility to the air from the suction
hood throughout the system up to release of gas to the chimney is provided by
induced draft centrifugal fan.
M/S VARDHMAN ISPAT UDYOG `
168
EQUIPMENT SPECIFICATIONS ARE GIVEN BELOW:
M/S VARDHMAN ISPAT UDYOG `
169
4.4 PROCESS AND FUGITIVE EMISSION AND CONTROL MEASURES
The plant will install air pollution control equipments to control particulate matter
emissions from process. For this, both primary and secondary emission control
M/S VARDHMAN ISPAT UDYOG `
170
system is envisaged. Primary system will consist of water cooled suction hood on the
cover of the furnace, hot duct, gas cooler and the cooled waste gases with
temperature not exceeding 150 degree Celsius will be taken to a pulse jet bag filter.
An induced draft fan will discharge the cleaned gas to atmosphere. For secondary
emission arising a hood near tapping will be provided and the gases will be taken to
the same bag filter system connected after gas cooler, which is connected to the
primary hood. Hydraulic dampers to control opening and closing of hoods will control
the suction. The collected dust of bag filter will be used in backfilling and leveling
purpose or for removal of precious metal, depending upon availability.
Fugitive emissions from the proposed plant would be significant due to activities like
material handling, transfer points of materials, loading of product and movement of
vehicles. These operations generate large quantity of dust. Specific instances of
fugitive dust generation may include dust caused by vehicular traffic within the
factory, Good housekeeping, proper maintenance, wetting of dusty areas, use of
enclosed storage wherever feasible etc., would considerably reduce fugitive dust.
For the purpose of effective prevention and control of fugitive emissions, the
proposed project shall be implementing the following:
❖ Water shall be sprayed on the Paved Road and surrounding of loading
&unloading area.
❖ Where facilities for metal extraction from the slag generated from IF are
provided, all the transfer points shall be fully enclosed and provided with dust
suppression systems
❖ All roads shall be paved within the plant, on which movement of raw materials
or products will take place.
❖ Preventive measures shall be employed to minimize dust build up on road.
❖ Conveyors shall be provided with conveyor covers
❖ Maintenance of air pollution control equipment shall be done regularly.
❖ All the workers shall be provided with disposable dust mask.
❖ Green belt will be developed around the plant boundary to arrest the fugitive
emissions.
M/S VARDHMAN ISPAT UDYOG `
171
4.4.1 IMPACT OF THE TRANSPORTATION AND MITIGATION MEASURES
The transportation of raw materials and finished product is likely to create impact on
surrounding environment. The following point identifies the possible impacts and the
mitigation measures to be adopted.
I. IMPACT OF THE TRANSPORTATION ON AIR ENVIRONMENT
❖ The movement of heavy vehicles due to transportation of raw material causes
re-suspension of loose dust particles in air
❖ Increase in PM10, SO2, CO and NO2 levels due to burning of fossil fuels.
MITIGATION MEASURES:
❖ Sprinkling of water to reduce fugitive particulate matter concentration.
❖ Vehicle shall be thoroughly covered to prevent release of fine particulate in
case of accidental leakage.
❖ Vehicle used for transportation shall comply with environmental standards and
only vehicles having Pollution under Control certificate will be put into use.
❖ Occasional levelling by bulldozing of road to fill up the ditches and to even out
the roads for smooth movement of vehicles , to reduce noise, to prolong the
length of vehicles by preventing frequent damage and to improve maintenance
of transporting vehicles
II. IMPACT OF THE TRANSPORTATION ON LAND ENVIRONMENT:
❖ During accidental leakage due to puncture of carry bags, containers, deposition
of material on top soil, land is probable.
MITIGATION MEASURE:
❖ Vehicles shall be covered to prevent accidental leakage.
❖ The area contaminated shall be remediated through scrapping or other
remediation measures.
III. IMPACT AND MITIGATION ON TRAFFIC DENSITY:
4.4.2 TRAFFIC ANALYSIS
The Material will be loaded directly into trucks and transported to the concerned
market/end users and the raw materials will be transported through tarpaulin covered
trucks only.
District Road-41 is located along the plant which is used for the transportation
purpose only.
M/S VARDHMAN ISPAT UDYOG `
172
Existing Traffic Scenario & LOS
ROAD V C EXISTING
V/C RATIO LOS
MDR-39 533 5,700 0.09 A
MDR-41 146 1,800 0.08 A
Source: Capacity as per IRC: 64-1990
V= Volume of Vehicles in PCU’s/day & C= Capacity of Road in PCU’s/day
The existing Level of Service (LOS) is “A” i.e. excellent.
V/C LOS PERFORMANCE
0.0 - 0.2 A Excellent
0.2 - 0.4 B Very Good
0.4 - 0.6 C Good / Average / Fair
0.6 - 0.8 D Poor
0.8 - 1.0 E Very Poor
Reference: ENVIS Technical Report, IISc, Bangalore
DURING PLANT OPERATION
S. NO. TYPE OF
VEHICLE
ADDITIONAL
VEHICLE PER
DAY
PCU TOTAL NUMBER OF
VEHICLE IN PCU/DAY
1. Truck 110 3 330
2. 2-Wheeler 34 0.5 17
3. Bus 5 3 15
4. Car 08 1 08
Total 370
MODIFIED TRAFFIC SCENARIO & LOS
ROAD INCREASED
PCU’S V C
MODIFIED
V/C
RATIO
LOS
MDR-39 533+370 903 5,700 0.15 A
MDR-41 146+370 516 1,800 0.28 B
M/S VARDHMAN ISPAT UDYOG `
173
RESULTS
From the traffic study it is observed that there is not much of impact on LOS of the
two main district roads. The LOS on MDR 39 continues to be excellent whereas on
MDR 41 it has just entered from the excellent to the Very Good range.
4.4.3 AIR QUALITY MODELING
AIR QUALITY MODELS
U.S. EPA AERMOD dispersion model, 1996 – 2018 Lakes Environmental Software,
Version 9.5.0 has been used for this report.
STACK DETAILS
Impacts on ambient air during operation phase would be due to emissions from flue
gas stacks (3 DG sets) and 2 Induction furnaces.
Emissions were analyzed for their impacts on the GLC for various distances using
the dispersion modelling guidelines given by the Central Pollution Control Board,
New Delhi and the dispersion modelling software AREMOD of the United States
Environment Protection Agency (USEPA).
Stack
No.
Stack Attached
to
PM10
(g/s)
PM2.5
(g/s)
SO2
(g/s) NO2 (g/s)
1 2 * Induction
Furnace 0.11 0.044 0.019 0.057
5 DG (2*125KVA) 0.0004 0.0002 0.0101 0.001
6 DG (250 KVA) 0.0006 0.0003 0.0161 0.0011
METEOROLOGICAL DATA
The meteorology of the project area plays very important role in dispersion of
pollutants and build-up of pollution within the atmosphere. In the present study, one
season meteorological data has been taken to find the dispersion of pollutant
concentration. The mixing height for study period, which is an important parameter to
express the dispersive potential of atmosphere, has been taken from the atlas of
hourly mixing height and assimilative capacity of atmosphere in India (S.D. Attri et
al., 2008).
RESULTS
• The maximum cumulative GLC concentration of PM10 when Furnaces and
M/S VARDHMAN ISPAT UDYOG `
174
DG sets are in working condition wiz. 99.038 ug/m3 was predicted inside
the study area. As the distance from source increases, the incremental
concentration of PM10 drops drastically due to settling of PM10 particles
under gravity.
• The maximum cumulative GLC concentration of PM2.5 when Furnaces and
DG sets are in working condition wiz. 62.80 ug/m3 was predicted inside the
study area.
• The maximum cumulative GLC concentration of SO2 when Furnaces and
DG sets are in working condition wiz. 13.516 ug/m3 was predicted inside
the study area.
• The maximum cumulative GLC concentration of NOx when Furnaces and
DG sets are in working condition wiz. 30.116 ug/m3 was predicted inside
the study area.
Table 1 – Predicted GLC of PM10 at Ambient Air Quality Monitoring Stations
Locat
ion Village
Max Baseline
Concentrations
Predicted GLC –
AERMOD Cumulative GLC
PM1
0
PM2
.5 NO2 SO2
PM1
0
PM2.
5 NO2 SO2
PM1
0
PM2.
5 NO2 SO2
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
(µg/
m3)
A1 Project
Site 99 62.3 24.2 10.9
0.03
846
0.02
419
0.14
43
0.40
51
99.0
385
62.3
242
24.6
051
11.3
051
A2 Bhangal 92 57.4 23.5 10.6 0.00
572
0.00
33
0.01
822
0.08
962
92.0
057
57.4
033
23.5
896
10.6
896
A3 Sapalwa
n 95 59.1 25.3 11.4
0.00
447
0.00
227
0.01
066
0.09
211
95.0
018
59.1
023
25.3
921
11.4
921
A4 Nangal
Khurad 98.9 58.6 24.8 11.1
0.00
178
0.00
119
0.00
759
0.03
55
98.9
009
58.6
012
24.8
355
11.1
355
A5 Bhawan
pur 94.5 62.8 26.5 11.9
0.00
091
0.00
055
0.00
305
0.01
397
94.5
008
62.8
006
26.5
140
11.9
140
A6 Santokh
garh 91 62 30.1 13.5
0.00
081
0.00
042
0.00
252
0.01
612
91.0
011
62.0
004
30.1
161
13.5
161
A7 Kokowal 86 56.7 22 9.9 0.00
11
0.00
055
0.00
26
0.02
3
86.0
032
56.7
006
22.0
230
9.92
30
A8 Beetan 88 55 22.7 10.2 0.00 0.00 0.00 0.06 88.0 55.0 22.7 10.2
M/S VARDHMAN ISPAT UDYOG `
175
315 157 898 668 023 016 667 667
A9 Suskal 94 60.3 23.5 10.6 0.00
229
0.00
116
0.00
504
0.04
713
94.0
000
60.3
012
23.5
471
10.6
471
The contour maps showing the predicted concentration levels of PM10, PM2.5,SO2,
NOx are presented in Figure 4.2, Figure 4.3, Figure4.4 and Figure 4.5
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 176
Figure 4-2Spatial distribution of predicted GLCs of PM10
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 177
Figure 4-3Spatial distribution of predicted GLCs of PM2.5
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 178
Figure 4-4Spatial distribution of predicted GLCs of SO2
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 179
Figure 4-5Spatial distribution of predicted GLCs of NO2
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 180
IMPACTS
During the construction phase the activities that can cause potential impacts on air
quality are as follows:
• Dust and air emission particularly due to the excavation, construction of
production facility and movement of vehicles.
• Particulate emission due to machinery and instrument operation for cleaning
and construction works.
• Fumes and gases near the work area due to welding & cutting activities.
MITIGATION MEASURES
• The flue gas from the Plant is being sent to Bag Filter before discharging to
the atmosphere to comply with particulate emission limit. All the dust collected
in the Pollution Control Equipment is being recycled in the process.
• As per MoEF guidelines, regular monitoring of air emissions and ambient air
quality will be carried out through MoEF&CC approved laboratories. Green
belt in around 33% area will be developed which will acts like adsorbent of air
pollutants.
• To combat fugitive emissions roads are paved and regularly swept. Water
sprinklers are provided for suppression of dust. Vehicular exhaust is being
maintained by providing regular maintenance and servicing of vehicles. Same
will be continued for future also.
4.5 IMPACTS OF NOISE AND VIBRATION DURING CONSTRUCTION PHASE
Noise generated during the construction period from operation of machineries like
compressor, compactors, concrete mixing plant, cranes and transportation materials
will be of short term in nature, and it will be controlled by using machines equipped
with silencers and regular maintenance of the same. Similarly, the vibrations
produced during this phase will be of low intensity, short term and of intermittent
nature. This is not expected to cause significant impact on the environment and
residents around the site.
4.5.1 NOISE EXPECTED DURING OPERATION PHASE
Noise would be an inevitable byproduct of the operationM/s Vardhman IspatUdyog,
the noise that would be generated from the unit would be from rollers, furnace and
transporting vehicles, DG set, compressors, fans and pumps available in the
company.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 181
4.5.2 NOISE IMPACT ASSESSMENT ANDMITIGATION MEASURE
Noise would be aninevitable in an industrial unit and some methods of noise
pollution control have been outlined in Table given below.
Noise
sources
Impact and Evaluation Mitigation Measures
During
Construction
activity
The labours could get
annoyance and can lose
concentration during
construction work. It can
cause disturbance during
working. The eardrums of
labours can get damage. In
long exposure, labours can
get nervous system affected
due to noise and very likely
face sleep disturbance
• Selection of quieter tools/ machines.
Equipment
• Enclose the noise sources
• Hearing protection by ear mufflers
• Reduction of noise by placing
temporary noise barriers
• Employees exposed to hand
vibration while handling/operating
heavy machineries will compulsorily
wear anti-vibration gloves made up
of visco-elastic material.
During
Operation
The workers could get
annoyance and can lose
concentration during
operation. It can cause
disturbance during working.
The ear of workers can get
damage. In long exposure,
workers can get nervous
system affected due to noise.
.
• Ensure hand-held concrete breakers
are muffled
• Maintain machines regularly - they
will be quieter
• Locate noisy machines away from
main areas of activity.
• Fit silencers to combustion engines.
Ensure they are in good condition
and work effectively
• Keep machinery covers and panels
closed and well fitted.
Bolts/fasteners done up tightly to
avoid rattles
• Enclose the DG sets with acoustic
enclosures so that noise shall not
dissipate.
• Hearing protection by ear mufflers
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 182
• Check for noise problems.
• Switch off engines or reduce to idle
when not in use
• Employees exposed to hand
vibration while handling/operating
heavy machineries will compulsorily
wear anti vibration gloves made up
of visco-elastic material.
Operation of machineries like conveyor, rotating machines during operation and DG
sets will result in generation of noise and vibration. The vibration arising out of
generator will not have significant impact though it is proposed to shield the
generator area with noise and vibration absorbing walls. Movement of vehicles will
also contribute to noise though the generated noise will be insignificant.
4.5.3 OTHER MEASURES
Noise could cause serious health hazard and could damage ear of workers.
The following precautionary measures are to be adopted in the proposed
project.
• Proper care will be taken at the time of installation to insulate/enclose all the noise
sources to avoid occupational exposure to the workers and also to minimize the
generation of excess noise level.
• Monitor the ambient noise level and work zone noise level as per the monitoring
schedules to conform to the stipulated norms.
• Noise attenuation devices such as ear mufflers must be provided to the workers in
the high noise exposure areas
• Regular health and hearing check to be made.
4.6 IMPACTS ON WATER ENVIRONMENT
4.6.1 IMPACTS DURING CONSTRUCTION PHASE
No major impacts will occur as the capacity enhancement will occur in the existing
site. Water during the construction phase will be met from the pipeline water and
through tankers.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 183
4.6.2 IMPACTS DURING OPERATION PHASE
Approximately 31 KLD of water will be used during operational phase for industrial and
domestic uses of which 21 KLD will be for industrial use and 10 KLD for domestic
purposes. This water will be used as makeup water for cooling tower to compensate for
evaporation loss. Domestic waste water generated will be sent to sewage treatment
plant. The treated water from STP will be used for green belt development whereas
blow down water from the cooling tower will be first sent to ion exchange and the
water from it will be used for sprinkling on road or for dust suppression in slag metal
recovery system or for product cooling. Thus, the net consumption of water will be
less and that no industrial effluent will be discharged outside the plant.
4.6.3 MITIGATION MEASURES
The sewage generated during the construction and operation phases on treatment in
STP will be used for green belt development whereas blow down water from the
cooling tower will be first sent to ion exchange and the water from it will be used for
sprinkling on road or for dust suppression in slag metal recovery system or for
product cooling.
4.7 SOLID WASTE GENERATION AND ITS IMPACT
Taking into consideration the raw material input and production parameters; mass
balancing shows possible quantum of solid waste generation in various forms.
The proposed melting, rolling mill section and details of raw material is already
tabulated in Chapter-2.The production of solid waste and their management is as
follows:
Table 4-1: Solid and Hazardous Wastes Management Plan
Solid
Waste
Generation Utilization Sold Remarks
Slag 21MT/day
11MT/day
(after Slag
Processing)
10MT/day
The Slag will be sold to
Paver Industry for Interlock
block making
Mill scale 12 MT/day -- 12MT/day Sold in Open Market.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 184
APCD
Dust
1MT/day -- 1MT/day
Given to recyclers for
recovery of valuable metal
and rest will be sent to TSDF
Site for disposal.
Trimming
& Cutting
Loss
9 MT/day 9 MT/day Reused as raw material in
process
Dust generation possibility is minimum as raw material will be transported in the form
of scrap, drums, boxes by trucks with covered tarpaulin and finished product will be
transported in trucks as bundled rolled products. Recyclable materials will also be
transported in trucks packed in HDPE bags. Strict implementation of Hazardous
Waste (Management, Handling and Trans-boundary Movement) Rules 2008 while
storage/handling/transportation of hazardous substances, Regular monitoring of
emissions.
4.8 IMPACT ON SOCIO-ECONOMIC ENVIRONMENT
Critically analyzing the existing environmental status of the socio-economic profile
and visualizing the scenario with the project, the impacts of the project would be
varied and may generate both positive and negative impacts of the proposed project
in the region that are stated below.
4.8.1 POSITIVE IMPACTS
A) NO REHABILITATION
As per detail provided by the proponent, the proposed project will not require
additional land. Backward integration will take place within existing plant area of 2.70
Ha (15.0 Bigha). No additional land shall be required for the project. Hence,
Resettlement & Rehabilitation is not required as there is no land acquisition or
displacement of any houses, habitation or livestock.
B) INCREASE IN JOB OPPORTUNITIES
The project in general will help to reduce the unemployment level as it may provide
direct and indirect job opportunities for auxiliary and ancillary works etc. The
proposed project will provide direct employment to 184 skilled and unskilled
personnel.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 185
C) MINIMAL BURDEN IN THE EXISTING INFRASTRUCTURE FACILITIES
As the labour will mostly be employed from Local work force and first preference will
be given to them, the activity will reduce the influx of the outsiders. Thus, there will
not be the necessity of provision of housing facility for the local workers.
D) IMPROVEMENT IN INFRASTRUCTURE
As the project authority is working towards the welfare of village community it will
definitely benefit the local people by providing more infrastructural facilities.
4.8.2 ADVERSE IMPACTS:
A) IMPACTS ON HUMAN HEALTH
The project may have impact due to air pollution on the villages in Core zone near to
the Project site. The impact from the air emissions are controlled efficiently using air
pollution control equipment and designed in such a manner that after implementation
of the project, the air emissions will be well within the prescribed ambient air quality
limits set forth by CPCB. The proponents of this facility will adopt effective control
systems at all the identified sources of emission.
b) IMPACTS ON PUBLIC HEALTH AND SAFETY
The discharge of waste materials (stack emission, wastewater and solid wastes)
from process operations can have potential impact on public safety and health. The
impact from the discharge of waste products is not expected to be significant since,
the adverse impacts on ambient air, water and soil quality are predicted to be low. It
is predicted that the impacts on public safety will be very low, due to the effective
safety system and safety management available in the plant.
4.8.3 MITIGATION MEASURES OF SOCIO ECONOMIC ENVIRONMENT
• Adequate measures have been envisaged in the project design to control air &
noise pollution. Proposed adequate & effective control measures will be
provided which include dust suppression.
• Awareness programs shall be arranged on health, hygiene and sanitation.
• Periodic health checkup camps, distribution of medical aid and medicines shall
be organized by project authority for villagers, contract labourers, employees
and their family.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 186
• Apart from the normal health check-up, emphasis shall also be given to prevent
specific diseases originating due to emission of different pollutants such as
respiratory ailments, skin problems, water borne diseases, hearing abilities etc.
• Job oriented training courses must be organized through industrial / technical
training institutions for educated youth like electrical, tailoring, plumbing, type
writing, shorthand and machine repairing, welding fabrication, and other skill
developing trades.
• Awareness programs will be taken to make people aware about the
environmental protection, need of water conservation etc.
• At the work place, first aid facilities shall be maintained at a readily accessible
place with necessary appliances including sterilized cotton wool etc. Ambulance
facility shall also be provided during emergency.
• Sufficient supply of water fit for drinking shall be provided at suitable places.
• Sanitary facilities shall be provided at accessible place within the work zone and
kept in a good condition.
4.9 IMPACTS ON BIOLOGICAL ENVIRONMENT
Construction activities at the site involving human and vehicular movement will
disturb aril and wild animals in the area.
IMPACTS ON TERRESTRIAL ECOLOGY
• The impact on terrestrial ecology may be due to gaseous pollutants likely to emit
i.e. particulate matter, Sulphur dioxide (SO2), Oxides of nitrogen (NOx), etc.
Increase in concentration of PM in the ambient air will cause the deposition of
dust on surface of leaves, leading to increase in pH of leaves as well as clog the
stomata aperture and reduce the chlorophyll content. The increased
concentration levels of particulate matter, SO2, NOx, in the atmosphere will,
lead to decline in the rate of photosynthesis, thus retarding the growth of plant.
However, air quality modelling outputs study revealed that, the resultant
concentrations of particulate matter, Sulphur di-oxide and oxides of nitrogen are
well within the prescribed limits, there is hardly any incremental increase. The
impact due to proposed project would be minimal as project activity will be
carried out within the plant boundary limit with proper control measures.
• Terrestrial micro flora and fauna at the site are also affected. However, the
adverse effect are reduced by shortening the construction phase period and
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 187
simultaneous development of greenery in the site along with construction of
project. Further, there are no sensitive locations within the study area. Hence, no
significant adverse impacts are expected on biological environment.
There are no endangered flora and fauna species in the region. Vehicular
movement during night will be restricted to avoid adverse sound related impacts to
birds and wild animals in the region. Plantation is carried out to attenuate the dust
pollution in the area. The project activities are restricted to the project site except
the transportation of raw material and finished products. There is no discharge of
solid or liquid wastes to the environment. Green belt and greenery will be
developed in the premise covering more than 33% of area. The plantation will
comprise of fruiting trees, soil improving and air pollution abatement tress. No eco
sensitive receivers or rare / endangered species of fauna were observed in the
study area. Thus, the impacts on flora and fauna will be insignificant.
4.10 RECOMMENDED PLANTS FOR GREEN BELT DEVELOPMENT
Greenbelts are an effective mode of control of air and noise 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, absorbs pollutants on their
surface, and thus effectively reduce pollutant concentration in the ambient air.
Often the adsorbed pollutants get 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 sinks 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.
SELECTION OF PLANTS FOR GREEN BELTS
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,
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 188
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;
1. For absorption of Gases:
• Tolerance towards pollutants in question, at concentration, that is 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 stomata apertures.
2. For Removal of Suspended Particular matter
• Height and spread of crown.
• Leaves supported on firm petiole.
• Abundance of surface on bark and foliage.
• Roughness of bark.
• Abundance of axillaries hairs.
• Hairs or scales on laminar surface.
• Protected Stomata
PLANTATION ALONG ROAD SIDES:
Automobiles are the source of pollution of gaseous and particulate pollutants.
Component of green belt on road side hence should be with both absorbers of gases
as well as of dust particles. The choice of plants for road side should include shrubs
of height 1 to 1.5 meter and trees of 3-5 meter height. Medium sized trees,
alternating with shrubs are ideal for sorption of particulates and gases.
Table 4-2: Recommended Plant Species for Green Belt Development
Plant species Common Name Habit
Acacia auriculiformis Earleaf Acacia Tree
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 189
Azadirachtaindica Neem Tree
Bougainvillea spectabilis Booganbel Shrub
Delonixregia Gulmohur Tree
Euphorbia tirucalli Indian tree spurge Shrub
Hibiscus rosa-sinensis China rose Small tree
Ixora arborea Jilpai Small tree
Ixora rosea Jungle flame Small tree
Lawsoniainermis Henna tree Shrub
Mangiferaindica Aam Tree
Melia azadirachta Bakain Tree
Nerium indicum Kaner Shrub
Peltophorumpterocarpum Yellow flametree Tree
Polyalthialongifolia Ashoka Tree
Sesbaniasesban Jayanti Shrub
Tamarindusindica Imli Tree
Tectonagrandis Sagun Tree
Terminalia alata Asan Tree
Thevetia peruviana Indian tulip tree Shrub
4.11 RAIN WATER HARVESTING
Depending upon the available contours at detailed engineering stage, the number of
drainage outfall and extent of open drains etc. will be designed so as to discharge
the water to the rainwater harvesting pond for reuse in dust suppression & greenbelt
development. A rainwater harvesting pond of capacity 12849 Cubic meters will be
made to collect rainwater. The calculation of rainwater endowment is presented here
which shows the total rain water harvesting potential of the plant.
4.11.1 RAIN WATER HARVESTING POTENTIAL OF THE AREA
S.No Details Values
1 Roof top Area (m2) 12830.57
2 Green/Open Land Area (m2) 11234.72
3 Road/Paved area(m2) 3012.71
4 Average Annual rainfall District 1.040 m
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 190
5 Co-efficient of evaporation, spillage and first
flush wastage
0.8
6 Runoff coefficient for roof top (0.7-0.9) 0.8
7 Runoff coefficient for paved area (0.5-0.7) 0.6
8 Runoff coefficient for open land(0.3-0.6) 0.3
9. Collection coefficient factor will be consider at rate of 80%
The rainwater harvesting will be done from the Rooftop area, Green Area, Paved Area.
S.
No
.
Details Calculation Rainfall Runoff
(m3/Annum)
Rainfall
Harvested
@80% Fraction
(m3)
1 Roof top Area 12830.57x1.040x0.8 10675.03 8540.02
2 Paved/Road Area 3012.71x 1.040x0.6 1879.93 1503.95
3 Green/Open land
Area
11234.72 x
1.040x0.3
3505.23 2804.19
TOTAL 12848.15
12848.15 m3water will be harvested in plant premises as per diagram given below.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 191
Figure 4-6Rain Water Harvesting Pit Design
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 192
CHAPTER-5: ANALYSIS OF ALTERNATIVE TECHNOLOGY AND
SITE
5.1 ALTERNATE TECHNOLOGY
The project involves changing of low capacity induction furnaces from 4MT/heat and
6 MT/heat to 10 MT/heat each with good controls on parameters and quality of
products to be erected within the same project area therefore no alternate
technology has been considered.
5.2 TECHNOLOGY
For the selection of technology, M/s Vardhman Ispat Udyog has considered less
environmental polluting, less energy consuming, higher productive and competing
cost technology like continuous casting of molten steel into red hot billets even in
such a small plant.
5.3 SITE ALTERNATIVES
Land is already available with M/s Vardhman Ispat Udyog at Village- Bathri, Distt.
Una, State-Himachal Pradesh hence no alternative site has been considered. The
plant site is located in an area marked for setting up of industries
Land Documents are attached as Annexure 3.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 193
CHAPTER-6: ENVIRONMENT MONITORING PLAN
6.1 INTRODUCTION
An environmental monitoring plan provides a delivery mechanism to address the
adverse environmental impacts of the project during replacement of two existing IFs
with addition of two Induction furnaces of 10 MT/heat each, producing a total of
1,40,000 MT/annum of finished rolled products, to enhance project benefits and to
introduce standards of good practices. An environmental monitoring plan is important
as it provides useful information and helps to:
❖ Assist in detecting the development of any unwanted environmental situation, and
thus, provides opportunities for adopting appropriate control measures.
❖ Define the responsibilities of the project proponents, contractors and
environmental monitors and provides a means of effective communication of
environmental issues among them.
❖ Define monitoring mechanism and identify monitoring parameters.
❖ Evaluate the performance and effectiveness of mitigation measures proposed
in the Environment Management Plan (EMP) and suggest improvements in
management plan, if required.
From the monitoring point of view, the important components are soil, water, air,
noiseand occupational health and safety. The suggested monitoring details are
outlined in the following sections. All monitoring will be carried out through Ministry
of Environment and Forest (MoEF) approved and/or National Accreditation Board
for Testing and Calibration Laboratories (NABL) accredited laboratory.
6.2 ENVIRONMENTAL MONITORING
A comprehensive monitoring programme is given as under. This environmental
monitoring will be entrusted to a third party. The following parameters shall be
monitored after proposed expansion of plant.
• Soil Quality Monitoring
• Air Quality Monitoring
• Noise Quality Monitoring
• Water Quality Monitoring
• Stack Emission
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 194
• Performance of Pollution Control Equipment
• Green belt development (monitoring carried out by the Environmental cell itself).
6.2.1 SOIL QUALITY MONITORING
The soil quality monitoring is carried out to assess the soil characteristics. The soil
quality will be analyzed as per CPCB norms. The green belt development acts as
pollution sink and bio indicators. Afforestation will also check soil erosion, make the
ecosystem functionally stable and make the microclimate more conducive.
During the operation phase, soil quality will be monitored in the green belt and plant
area for pH, texture, nitrogen, phosphorous, potassium and fluoride. This monitoring
shall be done annually except monsoon season and the results shall be shown to
competent agriculture expert to assess the need for remedial measures, if required.
Condition of the plant species planted shall be recorded once in two years by visual
observations with respect to vegetative growth, flowering etc.
6.2.2 AIR QUALITY MONITORING
Presently ambient air quality is being monitored regularly in accordance with
CPCB/HPPCB guidelines. It is necessary to monitor the air quality at the boundary
of the steel worksspecifically with respect to particulate matters. It is proposed that
continuousparticulate matter monitoring stations be established at one location on
thedownwind of the annual predominant wind direction of the steel works.
Theequipment shall have facilities to monitor PM10, PM2.5,SO2,NOxand CO.
Himachal Pradesh Pollution Control Board (HPPCB) will do ambient air quality
monitoring in and around the premises as per direction. Theparameters monitored
include the parameters as per National Ambient Air Quality Standard, 2009.
Table 6-1: Ambient Air Quality Frequency and Parameters
Description No. of Monitoring Stations Frequency
Ambient Air Quality 3 quarterly
Parameters – PM10, PM2.5, SO2, NOx & CO,
Parameters Technique Technical Protocol
PM 2.5 Gravimetric method CPCB Guidelines
PM 10 Gravimetric method IS 5182 (Part-23)
Sulphur Dioxide (SO2) Improved West and Geake
method
IS-5182 (Part-2)
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 195
Nitrogen Dioxides (NO2) Modified Jacob &Hochheiser
method
IS-5182 (Part-6)
Carbon Monoxide (CO) CO Analyzer (NDIR
technology)
CPCB Guidelines
6.2.2.1 STACK EMISSIONS
Periodical monitoring of stack for SPM, SO2, NOx& CO in case of process stacks of
Induction Furnace and DG Set shall be done to assess the performance of pollution
control facilities installed at the unit. Incase emissions are found to exceed the
norms; the ‘on duty’ personnel shall check the relevant process parameters and
appropriate corrective action will be taken. Emissions from all the stacks shall be
monitored once in a quarter using the manually operated stacks emissions
monitoring equipment.
However, the frequency of monitoring may be increased if required in accordance
with the stipulations of HPPCB or other statutory authorities.
Table 6-2: Stacks to Be Monitored After the Implementation of the Expansion
Plan
S. No. Unit No. of Stack Frequency
1 Induction Furnaces 2 Quarterly (Other than monsoon)
2 DG set 3 Quarterly
6.2.3 NOISE QUALITY MONITORING
In the construction phase, the equivalent noise level during day time and night time
will be monitored at three representative locations in the construction area
seasonally.
Similarly, in operation phase, Day time and Night time equivalent noise level will be
monitored at three locations i.e. within 100 – 200 m of the project site, one location
at each of the production units and near DG set. Monitoring will be carried outfor a
period of 24 hr and at an interval of one hour for the given season.
6.2.4 WATER QUALITY MONITORING
6.2.4.1 GROUND WATER QUALITY MONITORING
In construction phase ground water quality at three locations within the plant area
will be monitored every season as per the parameters given in IS 10500: 2012.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 196
During operation phase, water quality will be monitored at the following locations -
Physico-chemical characteristics of the ground water (Three locations – two within
plant area and one nearest well outside plant area) will be monitored once in every
season. The parameters are to be monitored as per IS 10500: 2012 drinking water
standards.
6.2.4.2 EFFLUENT QUALITY
There will be no effluent generation, as the proposed plant has adopted zero liquid
discharge (ZLD) approach. Domestic water generated will be treated in 10 KLD
capacities STP and treated water will used in horticulture.
Blow-down water from Cooling Tower after treated in Ion Exchange shall be used
for dust suppression and in hot product cooling.
Table 6-3: Monitoring of Effluent Quality
Unit Point of Measurement of Effluent quality
Frequency
Treated water analysis of STP
At the outlet
(For MLSS)
monthly
6.2.5 GREENBELT DEVELOPMENT
Greenbelt in and around the plant will be monitored for survival rates for taking the
steps like gap filling.
6.2.6 OCCUPATIONAL HEALTH
Statutory Health Checkup will be conducted every six months for employees and
contract workers in plant.
6.2.7 REPORTING SCHEDULE
After completion of analysis, copies of all the analysis reports will be sent to the
regional office of the Ministry of Environment, Forest & Climate Change and SPCB
periodically. Copies of the reports will be maintained in the plant and will be made
available to the concerned inspecting authorities as and when required.
6.2.8 MONITORING OF POLLUTION CONTROL EQUIPMENT
It should be ensured that pollution monitoring equipment is effectively working. A
detailed maintenance schedule shall be drawn for all pollution control systems. The
maintenance shall be done strictly as per schedule and guidelines furnished by plant
manufacturer. All pollution control, monitoring and safety equipment shall be
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 197
periodically checked and calibrated. Adequate quantity of spare parts will be
maintained within the plant.
6.3 ENVIRONMENTAL MANAGEMENT
Considering the importance of the pollution control and environmental protection, a
group of personnel will be identified for the existing plant, which will take care of future
requirement also with suitable technical and support staff. Further, to meet the
additional requirement, if any, manpower from operations and maintenance wing is
engaged. Organization structure of environmental management department for the
existing plant is shown in Figure 6-1, which will be suitably augmented by employing
relevant subject/discipline experts at an appropriate time.
The company has a full-fledged safety department to look after the safety issues of
the plant. The same shall be followed in future expansion also.
Table 6-4: Environmental Monitoring (Operation Phase)
Attribute Location & Frequency
Frequency Parameter
Air At 3locations, one within the plant and two in the predominant wind direction
Quarterly PM10, PM2.5, SO2 and NOx
Noise Near working area and generator set.
Quarterly Equivalent noise level
Ground Water
Three locations –within plant area and nearest well outside plant area
Seasonal
Except monsoon
Parameters as per CPCB standards
Soil Three locations - one location within plant area and two locations around the project site within 200 m distance from the unit.
Annually pH, texture, nitrogen, phosphorous, potassium and fluoride
Storm Water One location Once in monsoon season at the charging point of water being charged to
Parameters as per CPCB standards
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 198
aquifer to ensure it is of drinking water quality
Occupational Health
Health Checkup Half yearly General and respiratory and liver ailments’ check up
Figure 6-1: Organization Structure of Environmental Management
6.3.1 OPERATION AND MAINTENANCE OF POLLUTION CONTROL SYSTEM
Normally persons engaged in production are also entrusted with operation and
maintenance of pollution control systems. This may result in neglect of these
systems as priority is given to production equipment. In view of this and the
requirement of ensuring emission and ambient air and water standards, an officer
of the plant shallbe made responsible for the effective functioning of all pollution
control systems. He will report to the Head of the Maintenance Department.
Whenever required, he will draw crew from the main plant maintenance team for
maintenance of pollution control system.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 199
6.3.2 BUDGET FOR ENVIRONMENTAL MONITORING PROGRAM
Monitoring may include socio-economic interaction, through local liaison activities or
even assessment of complaints. Regular Monitoring of all the environmental
parameters viz., air, water, noise and soil as per the formulated program based on
CPCB and MoEF&CC guidelines will be carried out every year as per schedule. The
budgetary allocation for Environmental monitoring is Rs. 6.00 Lakhs/Annum. A third
party will be engaged to monitor all the environmental parameters as per CPCB /
SPCB norms once the expansion project comes into operation.
TABLE 6-5: Cost Of Environmental Monitoring Program
S. No. Item Cost (in Lakhs)
Per Year
1. Cost of monitoring of environmental parameters for Air, Water and Noise
3.50
2. Occupational Health & Safety (Monitoring) 1.00
3. Greenbelt Development 1.00
4. Monitoring of Performance of Pollution Control Equipment
0.50
Total 6.00
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 200
CHAPTER-7: ADDITIONAL STUDIES
7.1 INTRODUCTION
The outline of the proposed project, the baseline environmental status and the
impact assessment along with proper mitigation measures have been duly
addressed in the previous Chapters. This Chapter briefly encompasses the
additional aspects that were also dealt upon while conducting EIA study for the
proposed new project. These include:
1. Public Consultation
2. Environmental Risk Assessment, Environmental Risk Evaluation and
Risk Management Measures
3. Identification of Hazards
4. Occupational and Safety Hazards and Preventive Measures
5. Exposure control and Personal Protection
6. Occupational Health & Safety
7. Disaster Management Plan
8. Resettlement & Rehabilitation
7.2 PUBLIC CONSULTATION
Public hearing for the “capacity enhancement of manufacturing unit by
replacing existing induction furnace (4 T & 6 T to 2x10 T each), Rolling Mill and
enhance production capacity 45,000 MTPA to 1, 40,000 MTPA at Village-
Bathri, Distt. Una, State-Himachal Pradesh by M/s Vardhman Ispat Udyog” was
conducted on 11th December 2019 by HPPCB. The hearing was conducted at
Rajiv Gandhi Common Facility Center HPSIDC at VPO Bathu. Firstly, Sh.
Parveen Kumar, Regional officer, HPSPCB welcomed President, representative
of various departments, project proponent, Environmental consultant and public
present. After that representative of the consultant from Shivalik Solid Waste
Management Limited, Mr. Sandeep Garg described the details of the project.
Approximately 50 people attended public hearing, 4 people spoke during the
hearing and raised some issues and made suggestions. The proceedings of
public hearing and other documents in original shared by HPPCB with MoEF&CC
are enclosed as Annexure13.Summary of the complaints/queries raised by public
hearing and action plan are given below in Table.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 201
7.2.1 Advertisement OF Public Hearing
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 202
SUMMARY OF PUBLIC HEARING PROCEEDINGS
Sr. No Name of the person
Detail of query/ statement/ information/clarification sought by the person present at the venue of hearing
Reply of the query/ statement/ information/clarification given by the project proponent
Time bound action plan.
1. Sh. Ravinder Sharma, Village Bathu, Tehsil Haroli, District Una (HP)
He expressed his concern about pollution due to existing industries and its impact on the health of people and said proposed industry can increase the level of pollution in the area.
He asked how proposed industry will control pollution generated by their activities.
Environment Consultant of proposed Project Dr. Sandeep Garg answered this question that steel industry is mainly air polluting; the air pollutants are discharged into air through stack.
As per guidelines of Govt. of India, stack height should be 30 m. Stack of 120 ft height with Pulse Jet Beg House Filter has been installed to maintain emission level to 150 mg/m3. Pulse Jet Bag Filter is used to remove dust particle from smoke to maintain emission level within prescribed limits and online air monitoring system will be provided which will be visible to concerned department in case level of pollution is above prescribed standards.
Project proponent has already provided air pollution control device in the form of side suction hood followed by Pulse Jet Beg House Filter on one induction furnace and same will be provided on second furnace also based on latest technology and there will be no impact on the environment.
clearl2. Sh. Ramesh Chand Sharma, Aazad Nagar Arniyala Road Una,Tehsil&Dist
He asked Project Proponent that how fund under CSR will be used and who will audit. What is the mechanism for auditing this
Environment Consultant of proposed project agreed to the audit of budget allocated under CSR activities.
• Project Proponent assured that CER Committee will be constituted. Pradhan of village panchayat
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 203
rict Una (HP) expenditure?
He suggested that fund could be used for water harvesting in the nearby area forirrigation and for constructing building in local schools.
He said that 25 lacs will be utilized in the development of area and its utilization will be decided after discussion with local administration and people.
He also gave assurance that 100% fund will be utilized for the development of area and expenditure details will be displayed on company’s web site.
He also suggested that fund can be utilized for constructing toilets in Girl’s school and also constructing cremation shed.
Bathu will be member of this committee and expenditure details will be displayed on company’s web site.
• Project proponent assured thatRs. 25 lakhs will be utilized in the development of area; Out of which, funds will be utilized for constructing toilets in Girl’s school and constructing cremation shed.
3. Sh. K.K Rana, Pradhan Village Bathu, Tehsil Haroli, District Una (H.P)
He welcomed setting up proposed project. He expressed his concern regarding pollution caused by various industries in the area; he said area is not suitable to live due to pollution; local people are suffering adverse impact due to pollution. He showed dissatisfaction toward action taken by the Pollution Control Board in controlling the pollution generated by the industries.
He raised the question regarding
DC,Una and President informed Sh. K.K. Rana to ask question related to project only.
Environmental Consultant of proposed project requested people to raise question related to proposed project only as requested by DC, consult his office regarding other administrative matter.
Environmental Consultant of proposed project answered the query raised by K.K. Rana that 25 lacs will
-
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 204
unauthorized settlement along the side of industrial area and said this area is turning into slum area where open defecation is a normal practice. He said local people expect from administration not to convert this area into slum and to take appropriate measures for rehabilitation of the contractor’s laborers. He asked to take necessary step to make this area from defecation free.
He further said CSR budget from the existing industries is not still being utilized for development activities and it should be ensured that CSR budget from proposed industry should be utilized for the development of local area only.
The existing industries employ local people as laborer only not as staff for office work. Migratory workers are preferred for laborer. He asked project proponent to give employment to local people based on qualification.
He further said that the proposed project should establish after completing of all statutory
be utilized in the development of area and he assured on the behalf of company’s management that Pradhan of village panchayat Bathu will be nominated as member of CSR Committee of the company. As per his suggestions fund will be utilized, in this way he can keep viewing the expenditure done under CSR activities.
Environmental Consultant of proposed project said that 100 people will get employment and local will be preferred as per their qualification.
Environment Consultant of proposed project explained that three month’s Base line monitoring has been done for proposed project and found that only 1% pollution will be increased. Sufficient air pollution control equipments like pulse jet beg house filters will be used. Thus pollution level shall not increase.
He further said that 14 employees will reside within the company’s premises and company management will ensure that contractor’s laborers will take appropriate measures to
Project Proponent assured that CER Committee will be constituted. Pradhan of village panchayat Bathu will also be member of this committee. CSR activities depicting detailed given in report.
Company has assured to provide additional 100 nos. of employment in the project for expansion and preference will be given to local villagers.
The Project proponent assured that they will provide the air pollution control devices based on latest technology and there will be no impact on the environment and expansion project will be established after completing all the statutory guidelines and
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 205
guidelines and norms.
He said that administration should increase supply of cement to local panchayat by government and to ban illegal mining.
mitigate pollution in their settlement area.
President of industrial area, Una said that a hostel has been already constructed in this area so workers can stay there instead of slum.
norms.
4. Sh. Sunil Kumar, Village Santoshgarh, Tehsil and DisttUna (HP)
He asked how local workers will be benefited by proposed project and how many people will get employment?
Environment Consultant of proposed project said that 100 people will get employment and as already said local will be preferred as per their qualification.
Company committed to provide additional 100 nos. of employment in the project after expansion and preference will be given to local villagers based on their qualification.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 206
PUBLIC HEARING PHOTOGRAPHS
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 207
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 208
7.3 ENVIRONMENTAL RISK ASSESSMENT
The safety and protection of people, equipment and the environment are a
serious concern in the manufacturing industries. Steel Plants have also
recognized the significance of safe working environment and are progressively
trying to prevent hazardous events, avoid production & manpower losses and
other fallouts associated with industrial accidents by conducting risk assessment,
onsite & off-site management plan and adopting the safety measures as
proposed. This also assists industries to enhance employee knowledge of
operations, improve technical procedures, maintain accurate process safety
information and increase overall facility productivity. This Chapter, accordingly,
gives an outline of the associated environmental and other risk prone hazards,
their assessment and remedial measures. It also describes an approach to
emergency planning to be adopted by the Plant management.
The objectives of environmental risk assessment are governed by the following
which excludes for measure.
❖ Identifying the potentially hazardous areas so that adequate design safety
measures can be adopted to reduce the likelihood of accidental events.
❖ Identifying the stakeholders and evaluating their risk along with proposing
adequate control techniques.
❖ Identifying the probable areas of environmental disaster which can be prevented
by appropriate design of the installation and its controlled operation.
❖ Managing emergency or a disastrous event if any, during the plant operation.
Environmental risk assessment is a systematic approach for identification,
evaluation, mitigation and control of hazards that could occur as a result of failures
in process, procedures, or equipment. Increasing industrial accidents, loss of life
&property, public scrutiny, statutory requirements and intense industrial processes,
all contribute to a growing need to ensure that risk management is conducted and
implemented.
Managing a disastrous event would require prompt action by deployment of area
specific emergency plans by the operators and plant emergency staff using all their
existing resources like deployment of firefighting equipment, operation of emergency
shut off valves, water sprays etc. Minimizing the immediate consequences of a
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 209
hazardous event include cordoning off, evacuation, medical assistance and providing
correct information to the families of the affected persons and local public to avoid
rumors and panic.
The following terms related to environmental risks are defined before reviewing the
environmental risks.
Terms Environmental Risk
Harm Damage to person, property or environment
Hazard Situation that poses a level of threat to life, health property or environment. A hazardous situation that has come to pass is called incident. Hazard and possibility interact together to create risk. An environmentalhazard is thus going to be a set of circumstances which leads to direct or indirect degradation of environment and damage to the life and property.
Risk The probability of harm or likelihood of harmful occurrence and its severity. Environmental risk is a measure of the potential threats to the environment, life and property.
Consequence Effect due to occurrence of the event which may endanger the environment permanently or temporarily and, or, loss of life and property.
Environmental Disaster
The consequence is so severe that it can extensively damage any one or all the four components of the environments of the environment, namely
(a) Physicochemical, (b) Biological, (c) Human, and (d) aesthetics.
7.4 IDENTIFICATION OF HAZARDS
This is an early check of major hazards, which are of high-risk potential - including
the potential for disastrous interactions of the various plant operational activities.
The checklist, though not strictly speaking a Hazard and Operability Study
(HAZOP) but would facilitate a full-scale HAZOP Study for final drawing up of risk
management measures when the ‘design-freeze’ stage commences. Hazard is the
associated term with material, which is a measure or the likely hood of the human
working with or studying the material in question.
The entire probable potential hazard is classified under different heads.
• Fire hazards
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 210
• Toxic gas release hazards
• Explosion hazards
• Corrosion hazards
Fire Hazards
Since the Stone Age term, fire‟ is associated with fear. It is very dangerous if occurs
in uncontrolled manner. It should be clearly understood that when a liquid is used
having flash point below the normal ambient temperature, it could, in suitable
circumstances, liberate a sufficient quantity of vapour to give rise to flammable with
air.
Toxic Hazards
Toxic substances affect in three ways by ingestion, adsorption & inhalation which are
describe below.
Corrosion Hazards
Corrosion is a chemical reaction-taking place at the surface of metal.
POTENTIAL HEALTH EFFECTS:
Eye Contact:
Airborne dust may cause immediate or delayed irritation or inflammation. Eye
contact with large amounts of clinker dust and dry cement powder can cause
moderate eye irritation, chemical burns and blindness. Eye contact with large
amounts of gypsum can cause moderate eye irritation, redness, and abrasions. Eye
exposures require immediate first aid and medical attention to prevent significant
damage to the eye.
Skin Contact:
Dust of clinker, gypsum and cement may cause dry skin, discomfort, irritation, severe
burns and dermatitis. Clinker dust and cement dust are capable of causing dermatitis
by irritation. Skin affected by dermatitis may include symptoms such as, redness,
itching, rash, scaling and cracking. Irritant dermatitis is caused by the physical
properties of clinker dust including alkalinity and abrasion.
Inhalation (chronic):
Risk of injury depends on duration and level of exposure. This product contains
crystalline silica. Prolonged or repeated inhalation of respirable crystalline silica from
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 211
this product can cause silicosis, a seriously disabling and fatal lung disease. Some
studies show that exposure to respirable crystalline silica (without silicosis) or that
the disease silicosis may be associated with the increased incidence of several
autoimmune disorders such as scleroderma (thickening of the skin), systemic lupus
erythematous, rheumatoid arthritis and diseases affecting the kidneys. Silicosis
increases the risk of tuberculosis.
Ingestion:
Internal discomfort or ill effects are possible if large quantities are as allowed.
Explosion Hazards:
Release of energy in rapid and uncontrolled manner gives rise to explosion
7.5 ENVIRONMENTAL RISK EVALUATION
From environmental hazards point of view, risk analysis (RA) acts as a scrutinizing
vehicle for establishing the priority in risk management that concerns human health
and environmental quality in general. Though the proposed facilities are not
manufacturing, storing or handling any potentially hazardous/toxic chemicals as
scheduled in the Manufacture, Storage and Import of Hazardous Chemicals (MSHC)
Rules, 1989 and its amendments thereof, the proposed facility would have
installations, such as, storage and handling of coal, fuel oil, and fuel gases. An
Environmental Qualitative Risk Analysis Flow Chart Procedure is given below.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 212
Figure 7-1 : Environmental Risk Qualitative Analysis Flow Sheet
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 213
7.6 RISK MANAGEMENT MEASURES
The risk management measures for the proposed project activities require the
adoption of best safety practice at respective construction zones within the Works
boundary. In addition, the design and engineering of the proposed facilities will take
into consideration proposed protection measures for releases to air, land and water
environment as outlined in earlier Chapter.
Electrical safety: Adequately rated quick-response circuit breakers, aided by
reliable, selective digital/microprocessor-based electro-magnetic protective relays
would be incorporated in the electrical system design for the proposed Project. The
metering instruments would be of proper accuracy class and scale dimensions.
Appropriate use of ELCBs shall be ensured for all construction related low voltage
work.
Fire Prevention: In addition to the yard fire hydrant system, each individual shop
and offices are provided with fire and smoke detection alarm system along with the
portable fire extinguishers. Fire detection system would be interlocked with
automated water sprinklers. M/s Vardhman Ispat Udyog will has an on-site full-
fledged fire brigade department with 13 fire tenders which also provide the services
to the town in emergency situations.
CO detection and prevention: M/s Vardhman Ispat Udyog will install more than
1000 carbon monoxide detectors/alarms to detect the presence of carbon monoxide
(CO) and sound an alarm to alert personnel in case there is CO concentration
beyond 50 ppm. The plant personnel always carry a portable CO detector as part of
their personal protective equipment.
7.6.1 ON-SITE EMERGENCY PLAN
Emergency planning is an integral part of the environment and safety management
of TSL. Emergencies may arise due to manmade reasons and/or natural causes
resulting in fire, explosion, failure of critical control system, etc. It is crucial for
effective management of an accident to minimize the losses to the people and
property, both in and around the facility, termed as on-site and off-site emergency
plan.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 214
Accident Statistics: The safety and ergonomics department deal with emergency
records, events of both minor and major accidents, listing all the details such as
place, date & time, duration, probable cause, extent of damage, personnel affected,
man-hours lost, medical assistance provided etc to analyze these data for drawing
up necessary corrective measures.
Safety Inspections: The respective Department carries out monthly safety
inspection of all departments. Additionally, half-yearly Environmental, Health and
Safety Audit will be performed including all aspects of Environment, Occupational
Health & Safety for all the areas.
7.6.2 OFF-SITE EMERGENCY PLANNING
The off-site emergency plan is also an integral part of any major hazard control
system. This particular plan relates to only those accidental events, which could
affect people and the environment outside the plant boundary. Incidents, which
would have very severe consequences, yet have a small probability of occurrence,
would be in this category.
Emergency preparedness and disaster management plan covers the following:
❖ Identification of local authorities like civil defence, police, district commissioner,
their names, addresses and communication links.
❖ Details of availability and location of heavy-duty equipment like bull dozers, fire-
fighting equipment etc.
❖ Details of specialist agencies, and stakeholders upon whom it may be
necessary to call.
❖ Details of voluntary organization.
❖ Meteorological information.
❖ Humanitarian arrangements like transport, evacuation centers, first aid,
ambulance, community kitchen etc.
❖ Public information and communication through media, informing relatives,
public address system etc.
7.7 OCCUPATIONAL AND SAFETY HAZARDS AND PREVENTIVE MEASURES
7.7.1 FIRST AID MEASURES
Following first aid measures shall be taken:
❖ Eye Contact
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 215
Rinse eyes thoroughly with water for at least 15 minutes, including under lids, to
remove all particles. Seek medical attention for abrasions and burns
❖ Skin Contact:
Wash with cool water and a pH neutral soap or a milk skin detergent. Seek medical
attention for rash, burns, irritation and dermatitis.
❖ Inhalation:
Move person to fresh air. Seek medical attention for discomfort or if coughing or
other symptoms.
❖ Ingestion:
Do not induce vomiting. If conscious, have person drink plenty of water. Seek
medical attention.
7.8 EXPOSURE CONTROLS AND PERSONAL PROTECTION
7.8.1 EXPOSURE CONTROLS
❖ Control of dust through implementation of good housekeeping and
maintenance;
❖ Proper fume and dust extraction system to control fume/dust emission in work
zone.
❖ Use of PPE, as appropriate (e.g. masks and respirators)
❖ Use of mobile vacuum cleaning systems to prevent dust build up on paved
areas;
7.8.2 PERSONAL PROTECTIVE EQUIPMENT (PPE)
As a supplementary protection against exposure to hazardous conditions in the
production of iron and steel where the safety of workers cannot be ensured by other
means, such as eliminating the hazard, controlling the risk at source or minimizing
the risk, suitable and sufficient PPE, having regard to the type of work and risks, and
in consultation with workers and their representatives, shall be procured and used by
the workers and provided and maintained by the employer, without cost to the
workers.
• Items of PPE provided shall comply with the relevant BIS standards and criteria
approved or recognized by the competent authority. Where BIS standards are
not available, PPEs meeting international standards may be procured
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 216
• Those responsible for the management and operation of the personal protection
programme shall be trained in the selection of the proper equipment, in assuring
that it is correctly fitted to the people who use it, in the nature of the hazards the
equipment is intended to protect against, and provide adequate comfort, and in
the consequences of poor performance or equipment failure.
• PPE shall be selected considering the characteristics of the wearer and
additional physiological load or other harmful effects caused by the PPE. It shall
be used, maintained, stored and replaced in accordance with the standards or
guidance for each hazard identified at the facility and according to the
information given by the manufacturer.
• PPE shall be examined periodically to ensure that it is in good condition.
• Different PPE & their components shall be compatible with each other when
worn together.
• It shall be ensured that the procured PPEs are ergonomically designed and, to
the extent practicable, should not restrict the user’s mobility or field of vision,
hearing or other sensory functions.
• Employers shall ensure that the workers who are required to wear PPE are fully
informed of the requirements and of the reasons for them, and are given
adequate training in the selection, wearing, maintenance and storage of this
equipment
• When workers have been informed accordingly, they shall use the equipment
provided throughout the time they may be exposed to the risk that requires the
use of PPE for protection
• Items of special PPE for use in proximity to molten metal shall be so procured
that they should protect the wearer from heat and should withstand splashes of
molten metal. It should be possible to remove these items easily if molten
matter gets between the body and the protective clothing.
• The PPE shall not be used for longer than the time indicated by the
manufacturer
• Workers shall make proper use of the PPE provided, and maintain it in good
condition, consistent with their training and be provided with the proper means
for doing so.
• Respiratory Protection: When the dust level is beyond exposure limits or when
dust causes irritation or discomfort use Respirator.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 217
• Eye Protection: Wear Safety goggles to avoid dust contact with the eyes.
Contact lenses should not be worn when handling the materials.
• Skin Protection: Wear impervious abrasion and alkali resistant gloves, boots,
long sleeved shirt, long pants or other protective clothing to prevent skin contact.
7.8.3 FIRE FIGHTING FACILITIES
Keeping in view the nature of fire and vulnerability of the equipment and the
premises, following fire protection facilities have been envisaged for the plant.
❖ Safety training to the workers will be given.
❖ PPE will be provided to the workers.
❖ The maintenance and cleaning of bag filters will be carried out regularly.
❖ The dust removal efficiency of bag filters will be check regularly.
❖ Work place environment monitoring will be carried out regularly and records will
be maintained. The monitoring of dust in the work place will be carried out.
❖ Good housekeeping will be implemented in the plant.
❖ First aid box will be provided.
❖ The industry will provide adequate lighting facility inside the plant premises.
❖ General dilution ventilation will be provided to control dust levels below
applicable exposure limits.
❖ Fire extinguishers will be provided to withstand the fire or explosion condition.
❖ Pre-employment and periodical medical examination of workers will be done by
government approved medical practitioners and the details will be recorded as
per the Regulations.
❖ The industry will prepare on-site emergency plan.
❖ In case any emergency, arrangement of ambulance van will be done from
nearest Hospital.
❖ Two main gates will be provided for entry and exit of the workers.
7.9 OCCUPATIONAL HEALTH& SAFETY
M/s Vardhman Ispat Udyog believes in Safety First and is concerned with protecting
safety, health & welfare of the people engaged in work or employment.
The following safety measures for the employees shall be implemented:
❖ Safety training is provided to the employees.
❖ Manual call bell in case of emergency are provided.
❖ Fire alarms are provided.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 218
❖ First aid facility and trainings are provided.
❖ Personal protective gears and equipment’s are provided to the employees.
❖ Health check-ups are organized at regular intervals and records are maintained.
❖ Fire Protection System by means of providing Fire hydrants, Fire Extinguisher at
vulnerable points within the plant has been envisaged.
❖ Cleanliness facilities, rest room, plenty Plant Lightning is also envisaged for the
proposed project.
7.9.1 MAJOR HAZARDS
INDUCTION FURNACE:
• Cooling water meeting molten metal or slag causing explosion
• Moist scrap being charged causing explosion
• Radioactive scrap being charged spreading radio activity
• Scraps having explosive materials like abandoned bombs being charged causing
explosions.
CONTINUOUS CASTING MACHINES:
• Strand is hardened only superficially and is still liquid inside
• Spillage of molten metal can occur with damage by radiant heat to mechanical
and civil structures, electric cables and hydraulic equipment etc.
PREVENTING FIRES & EXPLOSIONS
• Fires & explosions in induction furnaces most often result from water coming into
contact with molten metal. The water may be present in scrap material, damp
moulds, from leaks in the furnace cooling systems or leaks in the building
• Fires & explosions in can also result from the ignition of volatile materials and
fuels. The most hazardous procedures are during the firing- up and shutting-
down procedures
• Operators shall be trained in safe systems of work. The building shall be
designed to be non-combustible, with automatic fire suppression engineered or
designed into the process where appropriate.
• Risk assessments shall be carried out to consider the potential dispersal of toxic
chemicals from non-furnace processes & combustion products, and the potential
impact of an explosion on the surrounding areas
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 219
• Regular safety audits shall be undertaken to ensure that hazards are clearly
identified, and risk-control measures maintained at an optimum level
• Refractories (e.g. crucibles, troughs, ladles) and tools shall be preheated and
dried before use to minimize the risk of explosion Refractory linings should be
regularly inspected for wear.
• Furnaces shall not be operated beyond their safe lives
A budget of Rs.2.00 Lakhs has been kept for occupational health & safety.
7.10 DISASTER MANAGEMENT PLAN (DMP)
A disaster is a catastrophic event that causes serious injuries, loss of life & extensive
damage to plant & property. It is a situation that goes beyond the control of the
available resource of any authority or organization. Several factors could trigger
accidents leading to a disaster, e.g. process and safety system failures (technical
errors, human errors), natural calamities (earthquake, tsunami etc.) The DMP is
formulated with an aim of taking precautionary measures to control the hazard
propagation and to take such action that the damage following a disaster is
minimized and controlled.
The objective of the DMP is to make use of the combined resources of the plant and
the outside services to achieve the following:
• Effective rescue and medical treatment of casualties.
• Safeguard other people.
• Minimize damage to property and the environment.
• Initially contain and ultimately bring the incident under control.
• Identify any dead.
• Provide for the needs of relatives.
• Provide authoritative information to the news media
• Secure the safe rehabilitation of affected area
• Preserve relevant records and equipment for the subsequent inquiry into the
cause and circumstances of the emergency.
In effect, DMP helps to optimize operational efficiency to rescue rehabilitation and
render medical help and to restore normalcy.
The following hazards for disaster management have been considered:
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 220
• Fire
• Explosion & Toxic release
• Oil spillage/liquid metal spillage
• Electrocution
• Accident
These hazards and potential causes have already been discussed in the preceding
sections. A selective disaster management measures to prevent disaster due to the
above-mentioned hazards are as follows:
• Design, manufacture, operation and maintenance of all plant machineries/
structures as per applicable national and international standards as laid down by
statutory authority,
• Intelligent formulation of layout to provide ‘Assembly Point’ and safe access way
for personnel in case of a hazardous event/disaster, as can be inferred from Risk
& Consequence modelling.
• Proper emergency (both on site & off-site) preparedness plan, emergency
response team, emergency communication, emergency responsibilities,
emergency facilities, and emergency actions shall be developed.
• Proper Alarm system and training the personnel for appropriate response during
disastrous situation.
• Complete fire protection coverage for the entire plant as per regulatory
stipulations.
• Creation and maintenance of Disaster Management cell with adequately trained
personnel who can handle all sorts of emergency.
• Provision of funds for prevention of disaster, mitigation, capacity-building and
preparedness.
7.10.1 OBJECTIVES
Objectives of the disaster control/management plan for the proposed plant are:
• To identify type of major disasters this may occur in the plant
• To collect data on type of disasters this has happened already in other iron &
steel plants.
• An action plan to handle disaster.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 221
Identification of Hazardous Process/Area
• Induction Furnace/Ladle Refining Furnace: Hot metal spillage, steam explosion,
Fire & Electrocution
• Continuous Casting Plant: Hot metal spillage
• Re-heating Furnace: Fire and explosion
• Rolling Mills: Hot metal spillage
• Fuel Oil tanks: Fire & Spillage
• Electrical Rooms: Fire & Electrocution
• Transformer area: Fire & Electrocution
7.10.2 LEVEL OF ACCIDENTS
If there is any disaster in any part of the plant/work place due to any reason, the
area, which may be affected, can be classified in the following four classes:
1. Level I - Operator level
2. Level II - Local/community level
3. Level III - Regional/ national level
4. Level IV - International level
Level I, II and III class of accidents have been considered for the plant.
Level I
Under this level, disasters may happen due to fire, explosion, oil spillage and
spontaneous ignition of inflammable materials. This level has probability of
occurrence affecting persons inside the plant. The various shops, which have been
mentioned as potential hazard areas, will be affected during this level of accident.
Level II
In case of sabotage/complete failure of all automatic control/warning systems; fuel
oil storage area (the oil kept in tanks and covered by tank bund) which may leak
out. However, the probability of this is very low due to adequate instrumentation,
security and training of persons of the plant operating such system.
Level III
In case of sabotage/complete failure of all automatic control/warning systems,
undetected leakage from the furnace; the resultant leakage of the flammable gases
is a potential threat that can affect the region. However, with the proposed
instrumentation, gas detection and alarm system, security and training of persons
such a situation is unlikely.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 222
7.11 RESETTLEMENT & REHABILITATION (R&R)
No dislocation of people is involved in any of the villages, the industry is located
within an existing industrial area, properly earmarked for this purpose namely
Tahliwal Industrial area. More over this is an existing industrial unit being expanded
and its capacity being enhanced for more efficient use.
The manpower is mainly drawn from nearby villages and employment exchanges. As
such no rehabilitation and resettlement is involved.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 223
CHAPTER-8: PROJECT BENEFITS
8.1 PHYSICAL INFRASTRUCTURE
The beneficial impact of the proposed project on the civic amenities will be
substantial after the commencement of the project activities. The basic requirement
of the community needs will be strengthened which will help in uplifting the living
standards of local communities.
8.2 EMPLOYMENT OPPORTUNITIES
The project will create extra opportunities of 100 persons’ direct and indirect
employment for which skilled and unskilled manpower will be needed. Secondary
jobs are day-to-day needs and services to the work force. This will also increase the
demand for essential daily utilities in the local market.
8.2.1 INDIRECT EMPLOYMENT
Due to the proposed modernization project indirect employments will be generated.
Indirect employments like; Primary requirements, Grocery Shops, Residential
Requirements, Garments Requirements, Transportation Facilities, Health Care
Facilities, etc. These kinds of requirements will increase the prevailing scenario,
which will generate the indirect employment.
Local villagers of the project will get its benefits more by giving preference to them in
relation to direct employment associated with the various project activities.
Construction and operation phase of the proposed replacement project will involve a
certain number of laborers, contractors and construction workers. Local people will
be engaged more for this purpose. Presently84 employees are present. For the
expansion unit 100 more employees (both permanent and temporary) will be
required for different works.
8.2.2 INDUSTRIES
The Industries will require raw materials, skilled and unskilled laborers. It will be
available from the local area. Due to increasing industrial activities, it will boost the
commercial and economic status of the locality, to some positive extent.
In brief it can be concluded that, the proposed activities will not produce adverse
impact on sanitation, communication and community health, as sufficient measures
have been proposed to be taken under the EMP. The proposed project is expected
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 224
to make any significant positive change in the existing status of the socio - economic
environment of this region.
8.3 SOCIAL INFRASTRUCTURE
With the implementation of the proposed expansion plant, the increasing industrial
activity will boost up the commercial and economic status of the locality, significant
positive change in the existing status of the socio - economic environment of this
region.
The required skilled and unskilled laborers will be utilized maximum from the local
area. In brief it can be concluded that, the proposed activities will not produce
adverse impact on sanitation, communication and community health, as sufficient
measures have been proposed to be taken under the Environmental Management
Plan.
Due to proposed project, the surrounding environment will not face any problems
related to the pollution because all kind of wastes, be it solid, liquid or gaseous will
be handled properly and No alteration in transport routes will be required.
The land rates in the area will improve in the nearby areas due to the proposed
activity. This will help in upliftment of the social status of the people in the area.
Educational institutions will also come-up and will lead to improvement of
educational status of the people in the area. Primary health and the medical facilities
will certainly improve due to the proposed project.
8.4 CORPORATE ENVIRONMENT RESPONSIBILITY (CER)
Corporate Environment Responsibility (CER) Budget towards capital expenditure in
accordance to the MoEF&CC’s Office Memorandum F.No. 22-65/2017-IA.III dated
01.05.2018 for Social Welfare.
1% of project cost i.e. 25 lakhs has been earmarked for the corporate environment
responsibility (CER) to meet expenditures for the commitments made to the stake
holders during the Public Hearing or as a part of company’s commitment towards the
welfare for all.
The details of activities to be undertaken and the budget allocated are given in Table
below:
S. No.
Description Amount to be spent Total Rs. in Lakhs
1st Year Rs.in Lakhs
2nd Year Rs.in Lakhs
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 225
1. Employment (Vocational Training for Skill development for self employment like Sewing, Pickle making, Craft making for Women Empowerment of village Balyana)
7.00 3.00 10.00
2. Educational Facility I. (Construction of 4 No’s of Toilets
for Boy & Girl separately) II. Donation of books to the School
Library.
4.00 2.00 6.00
3. Community Development I. Providing 4 No’s of Solar Light to
Gram Panchayat Bhawan. II. Construction of Rain Water
Harvesting Structure at Gram Panchayat Bhawan.
4.00 2.00 6.00
4. Construction of Shed for Cremation Ground
2.00 1.00 3.00
Total (1st Year +2nd Year) 17.00 8.00 25.00
8.5 CONCLUSION
The proposed project will provide direct employment to 184 people of the area and
thousands will get business opportunity to feed the demand of project and the people
working for the project. Small market will get developed to feed daily demand of the
people working for the proposed project. There is provision of separate allocation of
fund under CER and 1% of the project cost will be invested for the infrastructure
development of the local people of the area under CER activity. People will get
medical, education and business opportunities. Proposed project will make need-
based survey in the area under supervision of local panchayat and district
administration. The needy person will be supported as per his requirement. This will
improve infrastructure and economic status of the people living in the area. Other
project proponent will take advantage of developed infrastructure of the area to set
up industry which will further improve infrastructure and economy of the area.
Proposed project will change infrastructure scenario of the area.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 226
CHAPTER-9: ENVIRONMENTAL COST BENEFIT ANALYSIS
9.1 ENVIRONMENTAL COST BENEFIT ANALYSIS
As per EIA Notification dated 14thSeptember, 2006 as amended from time to time; this
chapter on “Environmental Cost Benefit Analysis” is applicable only, if the same is
recommended at the Scoping Stage.
As per the ToR issued by MoEF&CC for the project, vide letter no. IA-J-
11011/187/2019-IA. (II) (I) dated 17thSeptember, 2019the Environmental Cost Benefit
Analysis is not required.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 227
CHAPTER-10: ENVIRONMENTAL MANAGEMENT PLAN
10.1 INTRODUCTION
Environmental Management Plan (EMP) is the key to ensure a safe and clean
environment. The desired results from the environmental mitigation measures
proposed in the project may not be obtained without a management plan to assure
its proper implementation & function, without an organizational set up, without an
implementation of scheduled monitoring program, without a proper assessment to
review and corrective action thereby and without a timely reporting of compliance to
the authorities. The EMP envisages the plans for the proper implementation of
mitigation measures to reduce the adverse impacts arising out of the project
activities simultaneously with the construction planning and execution of the project
right from the beginning. This chapter includes following aspects:
❖ Pollution control/mitigation measures for abatement of the undesirable impacts
caused during the construction and operation phase in respect of air, water,
noise, soil and others.
❖ Details of management plans (Greenbelt development plan, Waste
management plan, Solids and hazardous waste management plan.)
❖ Institutional set up identified/recommended for implementation of the EMP.
❖ Post project environmental monitoring programme to be undertaken.
❖ Budget provisions and allocation of funds, Expenditures for EMP
10.2 PROPOSED ENVIRONMENTAL MITIGATION MEASURES
The major impacts due to different project activities and their mitigation measures
together constitute part of Environmental Management Plan (EMP). The
environmental mitigation measures for construction and operation phases have been
given in Table10-1.
Figure 10-1:Proposed Environmental Mitigation Measures
S. No Component Impact Mitigation Measures
Construction Phase
1 Air Generation of Dust CO2, NOx,
SOx.
Mainly as a result of transport
activity, excavation and
installation of machines and
Use of water sprinklers.
Personal Protective equipment
for laborers.
Proposed project site is inside
Tahliwal Industrial premises. No
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 228
structures on foundations
erected on excavated earth
impact on general public.
2 Noise and
Vibration
Increase in the noise levels due
to movement of vehicle and
construction activities. Vibration
due to movement of vehicles
and construction activities.
Noise due to working of
machineries compactors,
concrete plant, cranes and
transportation materials.
Proper service and maintenance
of vehicles to control noise.
Personal protective equipment’s
for laborers. Construction
activity will be carried out in day
time only. Proposed project site
is inside Tahliwal industrial
premises, hence no impact on
general public.
3 Water Water pollution due to disposal
of untreated sewage. No
change is land use pattern as
project site is inside the existing
industrial complex.
Sewage water treated in
proposed STP no waste water
will be discharged from the
plant.
4 Land Land is already developed for
industrial use. Pollution of land
due to discharge of untreated
sewage and solid wastes.
Land use of the project site will
not change as proposed
expansion is done inside the
existing premises and project
site also comes in Tahliwal
Industrial Area.
5 Biological
Flora ,
Fauna
Disturbance due to increase in
noise
A thick 2 tier Green Belt will be
developed around the boundary
of project to minimize the noise
due to machinery operation.
6 Socio
Economic
Employment of construction of
workers.
People from the study area to be
hired for employed as far as
possible for construction.
7 Occupational
Health &
Safety
Auditory ailment due to noise.
Respiratory ailment due to dust
emission inhalation.
The use of personal protective
equipments will be made
stringent. Water sprinkling
system for dust generating
areas.
Operational Phase
1 Air Increase in the air pollutant
concentration due to operation
of Induction furnaces. Dust
generation possibility is
minimum as raw material will
be transported in the form of
scrap, drums, boxes by trucks
with covered tarpaulin and
finished product will be
Solids red-hot particles along
with hot gases emitted in
process will first be captured by
adequately designed side and
top hoods, coarse and heavy
particles will first get cleaned in
baffle house, cyclones, get
cooled prior to cleaning in pulse-
type bag filters. Use of stacks
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 229
transported in trucks as
bundled rolled products.
Recyclable materials will also
be transported in trucks packed
in HDPE bags.
with adequate height, for
dispersion in air, with provisions
of monitoring ports and platform,
stairs for installing continuous or
manual when as per monitoring
program decided, complying to
stack emissions of 50mg/Nm3
will be kept.
Personal protective equipment’s
for employees.
Strict implementation of
Hazardous Waste
(Management, Handling and
Trans-boundary Movement)
Rules 2008 while
storage/handling/transportation
of hazardous substances.
Regular monitoring of emissions.
2 Noise and
Vibration
Increase in the noise levels due
to operation of Equipment such
as compressors, Centrifugal
fans, DG sets and gas cutting
machines for red hot billets.
Vibration during milling,
grinding, screening and
operation of manufacturing
unit.
Equipment’s with noise level
below 80dB (A) only will be
used. Proper service and
maintenance of machines to
control noise. Personal
Protective equipment’s for
employees like anti vibration
gloves and ear plug. Project site
is inside industrial complex. No
impact on general public. Use of
low noise equipment. Isolation of
the noise prone unit from the
employee area to avoid
continuous exposures of working
personal to noise, use of
vibration damping devices for
vibrating machines and isolation
of stationary devices from the
rotating devices by flexible
insertions.
3 Water Impact on ground water due to
abstraction will be minimum as
ground water will either be
used for domestic purposes or
for process cooling.
No industrial effluent will be
Fresh ground water used for
domestic and in the cooling
water recirculation system is the
minimum requirement, which is
used for recirculation through
cooling tower is reused. The
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 230
discharged, which makes this
production process a Zero
Discharge Production Process.
sludge from washing cradles is
pumped in a settling.
Water used for cooling of coils,
moulds or for solidification of
inner hot molten metal in red hot
billets will be recirculated after
getting it cooled in Cooling
towers, the blow down water will
be passed through ion exchange
system before reutilization for
dust suppression and sprinkling
on roads, STP waste water and
dried manure will be put to use
for green belt development. The
only evaporation loss of
continuous recirculated water for
cooling in Cooling tower will be
made up, which the minimum
most. The entire process
ensures ZLD.
4 Land Pollution due to discharge of
sewage waste.
Raw material will be
transported in lump from by
trucks with covered tarpaulin
and finished product will be
transported in recycled HDPE
bag.
Domestic sewage effluent
generated will be treated in STP.
Process solid wastes generated
are completely reused for
ancillary activities. Slag from the
IFs is first subjected to metal
recovery, recovered metal is
used as raw material as scrap,
waste slag is used by recyclers
for manufacture of paver blocks,
mill scales from both continuous
casting and rolling mills are sold
to authorized recyclers, crop
ends from rolling mills are used
directly back in Ifs.
All raw materials and end use
products will be transported in
tarpaulin covered trucks which
ensure that no materials will
throw out during transportation.
5 Biological
Flora, Fauna
Disturbance due to increase in
noise.
Operational activities of heavy
machineries and transportation
only in daytime. Green belt
development in one-third of plant
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 231
occupied land with choicest
trees, shrubs, bushes and
creepers. Taking it as a
simultaneous measure along
with plant construction activity.
6 Socio
Economic
Employment to local people. People from the local area to be
employed as far as possible.
Plant involves no resettlement
and rehabilitation activity,
adequate funds kept to the
extent of 1% of project cost for
the social upliftment, which
provides for putting toilet blocks
in the Govt. Girls Sr. Secondary
School and community
development and skill training for
youth.
7 Occupational
Health &
Safety
Auditory ailment due to noise
generated from the production
unit. Accidents due to handling/
storage/ transportation of
hazardous materials.
Equipments with noise level
below 80dB (A) only will be
used. Wearing of personal
protective equipments like gas
masks, ear muffs etc. will be
strictly enforced. Enclosures of
high noise generating machines
will be part of noise suppression
and reducing propagation plan.
Training/ awareness programme
about the handling/ storage/
transportation of hazardous
materials. First aid training for
chemical/ fire hazard related
accidents. Maintaining proper
records and review will be part of
overall planning and protection.
Programmed periodical Medical
checkup and providing
medicines to the needy.
10.3 DETAILS OF MANAGEMENT PLAN
10.3.1 AIR ENVIRONMENT
The major pollutants emitted from the plants are Particulate Matter (PM10/ PM2.5),
Sulphur dioxide (SO2), Nitrogen dioxide (NO2), Carbon Monoxide (CO) and
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 232
Hydrocarbons (HC). The major sources of pollutants are vehicular movement,
material handling, crushing, grinding and the dust emission from operation.
During the ambient air quality monitoring, it is observed that the baseline
concentration of air pollutants, namely PM10, PM2.5, NO2, SO2, CO are well
below the National Ambient Air Quality Standards (NAAQS), 2009. It is anticipated
that the plant activity will not cause any adverse effect on the existing baseline
status.
PM10 ranges from 55 to 99 µg/m3 in the study area with the maximum value
recorded at the project location. However mass levels of PM10 during few sampling
days approaches to prescribed limits. The project site is situated in the downwind
direction of industrial area of Tahliwal as well as industrial areas of Una & Gagret,
which adds up to the PM10 values. Main sources of PM10 in the study area are
industrial, construction, mining and anthropogenic activities in the region. Apart
from local and regional sources, transboundary migration from one place to another
could be anticipated as external sources, as respirable dust can remain in air from
hours to days and can move from meters to hundreds of kilometres. Hot and
turbulent winds in summer season leads wind storms and dusty conditions in the
region.
Fugitive emissions will be controlled with the following recommended measures:
❖ Development of green belt in the plant area.
❖ Use of water sprinkling system in haulage roads for dust suppression.
❖ Proper maintenance of haulage roads, which are being used for transportation
of material.
In addition to the above, the following additional measures are also recommended:
❖ Dust mask will be provided to all workers working in dust generating area.
❖ Overloading of trucks will be avoided.
❖ Utmost care and regular inspection schedule will be carried out to prevent any
fugitive emission of dust during manufacturing process and transportation of
material from one place to another.
❖ Industry will be providing Bag filters based on latest technology, paved area
inside the premises so that no dust is generated due to truck movement, tree
plantation on 33% of the plot area which all will help in reducing the PM10
values.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 233
10.3.2 AIR POLLUTION CONTROL EQUIPMENTS
Increase in the air pollutant concentration due to operation of Induction furnaces.
Dust generation possibility is minimum as raw material will be transported in the form
of scrap, drums, and boxes by trucks with covered tarpaulin and finished product will
be transported in trucks as bundled rolled products. Recyclable materials will also be
transported in trucks packed in HDPE bags.
MITIGATION MEASURES
➢ Solids red-hot particles along with hot gases emitted in process will first be
captured by adequately designed side and top hoods, coarse and heavy
particles will first get cleaned in baffle house, cyclones, get cooled prior to
cleaning in pulse-type bag filters. Use of stacks with adequate height, for
dispersion in air, with provisions of monitoring ports and platform, stairs for
installing continuous or manual when as per monitoring program decided,
complying to stack emissions of 30mg/Nm3 will be kept.
➢ Personal protective equipment’s for employees.
➢ Strict implementation of Hazardous Waste (Management, Handling and
Trans-boundary Movement) Rules 2008 while storage/handling/transportation
of hazardous substances. Regular monitoring of emissions.
10.3.3 NOISE ENVIRONMENT
Noise exposure level will be maintained within 85 dB (A) in the work zone (for 8
hours exposure). The main sources of noise in plant activity are crushing,
screening, grinding, material handling machinery, loading equipment, etc. and
noise level are expected to increase at work zone with commencement of project
and other allied activities. The following precautionary measures will be taken to
control noise pollution:
❖ Ear muffs, ear plugs, etc. will be provided to workers when the noise levels
exceed 85 dB (A).
❖ The silencers and acoustic enclosures are incorporated for equipment’s and
machineries, which emit high noise levels.
❖ Regular maintenance will be carried out for equipment’s and various machines.
❖ Plantation will be carried out.
❖ Sufficient green belt is proposed to control noise level.
❖ PUC certified vehicles will only be used
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 234
❖ Occasional leveling of Katchcha haul roads by bulldozing for smooth of
vehicles movement
10.3.4 WATER ENVIRONMENT
Fresh ground water used for domestic and in the cooling water recirculation system
is the minimum requirement, which is used for recirculation through cooling tower is
reused. The sludge from washing cradles is pumped in a settling.
No industrial effluent will be discharged, which makes this production process a Zero
Discharge Production Process.
Proper sanitation facilities the plant area, all the spent water from washing of scrap is
collected in settling tank and is recycled. The waste water from quenching is
collected in tanks and passed through cooling towers and is reused. The sludge from
washing cradles is pumped in a settling.
Water used for cooling of coils, moulds or for solidification of inner hot molten metal
in red hot billets will be recirculated after getting it cooled in Cooling towers, the blow
down water will be passed through ion exchange system before reutilization for dust
suppression and sprinkling on roads, STP waste water and dried manure will be put
to use for green belt development. The only evaporation loss of continuous
recirculated water for cooling in Cooling tower will be made up, which the minimum
most. The entire process ensures ZLD.
10.3.5 GREENBELT DEVELOPMENT
Development of a greenbelt around the proposed facility mitigates to a certain extent
the potential negative impact on the environment due to dust, air emissions, fugitive
emission and noise. A green cover itself acts as containment for dust. Presence of a
green belt, will lead to micro-climate and soil quality balancing, by retaining soil
moisture, recharge of ground water as well as self-control of micro- climate of that
area. It also improves the aesthetic value of the area. Later on, it becomes the
natural habitat of various bird species. Development of a green belt around the
proposed project site will also help to contain noise generated during construction
and operational phases.
There are two types of approaches recognized for development of green belts i.e.
Source oriented approach and Receptor oriented approach. Both source and
receptor-oriented approaches are similar i.e. it requires development of green belt.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 235
The only difference is the manner in which the plantation is being done. In source-
oriented approach green belt is located around the pollution source whereas in
receptor-oriented approach the receptor is protected against pollution by
development of green belt nearer to the receptor. In this project the plantation will be
source oriented, i.e., the plant site will be covered at the boundary with green belt.
Green belt will be developed over 33% area of the total plant area. Out of 2.70 Ha
plant area 0.894 Ha (8947 sq.mtr.) will be developed as green belt. Out of 0.89 ha
area earmarked for greenbelt development, at present 1451 nos. of plants
hasalready been planted in plant area as a part of prior environment planning.
Additionally, 370 no. of trees at a distance of (10mx10m) &505 no. of shrubs at a
distance of (4mx4m) will be planted. Hence, total number of plants planted after
expansion will be 875.
Calculation of Cost for Green belt Development
Expenditure per plant Rs. 60/-
Total Numbers of Plant=875/-
Expenditure=875x60=52,500/-
Remuneration to gardener for maintenance= 3, 00,000/-
Total Expenditure = Rs.3, 52,500/- say Rs. 3, 55,000
The general considerations involved while developing the green belt are:
• Generally local/native fast-growing trees should be planted.
• Planting of trees should be undertaken in appropriate encircling rows around the
project site.
The trees should be protected by plantation of non-palatable shrub species to avoid
browsing by animals.
Plantation comprising of pollutant resistant species which exists in and around the
Plant facility will serve as not only pollution sink but also as noise barrier.
Figure 10-2 List of plant species for green belt development
S.No. Botanical Name Local Name Trees/Shrubs
1 Terminalia arjuna Arjun Trees
2 Acacia nilotica Kikar Trees
3 Albizzia procera Siri Trees
4 Ziziphus sp. Ber Trees
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 236
5 Mangiferaindica Mango Trees
6 Melia azedarach Bana/ American dek Trees
7 Toonaciliata Tuni Trees
8 Morus alba Toot Trees
9 Syzygiumcumini Jamun Trees
10 Psidium guajava Gauva Trees
11 Ficus religiosa Peepal Trees
12 Pithecellobium dulce Jungle jalebi Shrub
13 Carissa carandas Karanda Shrub
14 Jasminum
dispermum
Pink Jasmine Shrub
15 Nerium indicum Kaner Shrub
16 Cascabelathevetia Maxican oleander Shrub
10.4 HEALTH AND SAFETY
The Health and Safety of the employees shall be given priority during the plant
operation. Provision of rest shelters for workers with amenities like drinking water,
fans etc. First aid facility shall be provided at project site. Training programme
organized on First Aid. Periodical medical checkup camp shall be organized for
worker and staff.
Anticipated Occupational Health Impacts of the Project Construction
The occupational health problems envisaged at this stage can mainly be due to
accidents during construction activities and noise. To overcome these hazards, in
addition to arrangements to reduce it within Threshold Limiting Values (TLV),
properly slanted foundation pits excavated required personal protective equipment
(PPE) like helmet, dust masks, earmuffs etc. will also be supplied to workers.
Operation and Maintenance:
Noise is the major occupational hazard during operation stage apart from chemical
and accidental hazards. Suitable personnel protective equipment will be given to
employees. The working personnel shall be given the following appropriate
personal protective equipment’s.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 237
❖ Industrial safety helmet.
❖ Welders equipment for eye and face protection.
❖ Cylindrical type earplug.
❖ Ear muffs.
❖ Safety belt/line man's safety belt.
❖ Leather hand gloves.
❖ High temperature protection gloves
❖ Asbestos hand gloves.
❖ Canvas cum leather hand gloves with leather palm.
❖ Electrical resistance hand gloves.
❖ Industrial safety shoes with steel toe.
❖ Electrical safety shoes without steel toe and gum boots.
❖ Vibration protective hand gloves
First aid facility will be made available round the clock for attending to emergency in
case of any accident, if any. All working personnel shall be medically examined at
least once in every six months and at the end of his term of employment.
Health and Safety Monitoring Plan
All the potential occupational hazardous work places such as fuel storage area will
be monitored regularly. The health of employees working in these areas will be
monitored once in six months for early detection of any ailment.
A medical care center will be established with the following responsibilities:
❖ Examination of workers’ health in relation to work.
❖ Surveillance of working environments.
❖ Identification and evaluation of environmental factors which may affect the
workers’ health.
❖ Assessment of conditions of occupational workers’ health.
❖ Observance of safety norms and reduce/eliminate exposure to hazardous
environment.
Company will take up monitoring activities periodically to assess hazards due to
gases, dusts, etc.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 238
10.5 IMPLEMENTATION OF EMP AND MONITORING
A large part of the sampling and measurement activities will be concerned with long
term monitoring aimed at providing an early warning of any undesirable changes or
trends in the natural environment that can be associated with beneficiation and
associated activities. Monitoring strategy is required to ensure that all
environmental resources, which may be subjected to contamination, are kept under
review. Monitoring of the individual elements of the environment is necessary. To
meet the above objective an Environment Management Cell shall be formed under
supervision of consultant and involve Pollution Control Board for their valuable
suggestion and guidance. The following items will be considered under the
monitoring schedule:
❖ Re-Vegetation & Green Belt development
❖ Washing
❖ Loading
❖ Air Quality Monitoring
❖ Water Quality Monitoring
❖ Occupational Health
❖ Socio-Economic Development.
The monitoring and disaster management plans as given in the previous sections will
be followed.
10.6 ENVIRONMENT MANAGEMENT CELL
An Environment Management Cell (EMC) will be responsible for implementation of
the aforesaid post project monitoring/management plan. The composition of the
Environment Management Cell and responsibilities of its various members are given
in Table 10-3.
Table 10-1: Environment Management Cell
Designation Proposed Responsibility
Senior Director Environmental policy and directions.
Advisor
Environment
Overall responsibility for environment management and
decision making for all environmental issues.
Director In-charge of operation of environment management facilities.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 239
Ensuring legal compliance and interaction with regulatory
agencies.
Manager Secondary responsibilities for environment management and
decision making for all environmental issues.
Site In charge Ensure environmental monitoring as per appropriate
procedures.
The Company is aware of its responsibility in protecting the Environment. Thus,
various mitigation measures as given in the report shall be taken-up and effort will be
made to nullify the effect of the Project on the Environment, if any. Any action or
effort remains incomplete, if it is not monitored properly at regular intervals and
corrective measures not taken, wherever necessary. Regular monitoring has thus,
been provided. The Company has a well-defined policy to keep the Environment
clean. The management has decided that all effective steps shall be taken to prevent
deterioration of the existing Environment. The company makes a well-defined
Environment Policy and the main aims under the said Policy are to:
• Integrate sound environmental management practices in all our activities.
• Conduct our operations in an environmentally responsible manner to comply with
applicable legal and other requirements related to its environmental aspects and
strive to go beyond.
• Progressively adopt cleaner and energy efficient technologies.
• Minimize waste generation and promote recovery, recycle and reuse.
• Increase greenery in and around the plant.
• Company shall ensure that deviations from this policy and cases of violations,
if any, shall be reported to the Board of Directors and shall identify designate
responsible person for ensuring compliance with the environmental Laws and
Regulations.
• Strive for continual improvement in our environmental performance by setting
challenging targets, measuring progress, taking corrective action and
communicating environmental information to all concerned.
• Enhance environmental awareness amongst employees working for and on
behalf of us and the general populace around working areas.
• Encourage our business associates to adopt similar approach for environmental
protection.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 240
10.6.1 MONITORING & RESPONSIBILITY
The cell responsible for monitoring of the plant environment related requirements
include:
Interaction with the State pollution Control Board
EMC shall be in regular touch with HPPCB and shall send them environmental
monitoring reports regularly in the prescribed format, as per the prevailing practice.
Any new regulations considered by State/Central Pollution Control Board for the
Industry shall be taken care of by EMC.
Provide Training
EMC would be responsible for the implementation of the EMP, needs to be trained
on the effective implementation of the environmental issues. To ensure the success
of the implementation set up proposed, there is a high requirement of training and
skill up-gradation. For the proposed expansion project, additional training facilities
will be developed for environmental control. For proper implementation of the EMP,
the officials responsible for EMP implementation will be trained accordingly.
To achieve the overall objective of pollution control it is essential not only to provide
latest pollution control and monitoring systems but also to provide trained man power
resources to operate and maintain the same. So far, the practice with many plants is
to utilize the plant operations and maintenance crew for operation of systems. This
has shown adverse results due to lack of specialized knowledge in addition to priority
selection. Therefore, apart from the ECD, specific training will be provided to
personnel handling the operation and maintenance of different pollution control
equipment.
OTHER RESPONSIBILITIES OF THE CELL WILL INCLUDE:
• A HPSPCB registered agency will be retained to generate the environment
quality data in respect of air, water, noise, soil and meteorology and prepare the
Environmental report.
• Timely renewal of Consents & Authorization will be taken care of.
• Submitting environmental monitoring report to HPSPCB. The cell wills also
mitigative or corrective measures as required or suggested by the Board.
• Conduct and submit annual Environmental Statement to HPSPCB.
• Submit six monthly compliance to stipulated EC commitments report to the
Regional office of MoEF&CC
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 241
• Prepare and submit six monthly reports on the compliance with the conditions of
the environmental clearance.
• Keeping the management updated on regular basis about the findings / results
of monitoring activities and proposes measures to improve environmental
performance.
• Conducting regular safety drills and training programs to educate employees on
safety practices. A qualified and experienced safety officer will be responsible for
the identification of the hazardous conditions and unsafe acts of workers and
advise on corrective actions, organize training programs and provide
professional expert advice on various issues related to occupational safety and
health.
• Conducting safety and health audits to ensure that recommended safety and
health measures are followed.
10.7 BUDGETARY PROVISION FOR EMP IMPLEMENTATION
In order to respond to evolving management needs, a contingency budget will be
required. The cost required for the Environmental Management Plan for the
proposed expansion is Rs. 137 lakhs as capital cost and Rs. 35 lakhs/Annnum as
recurring cost and detail are given in Table10-4.
Table 10-2: EMP Budget
S. No.
Particulars Capital Cost
(in lacs)
Recurring Cost per annum (in
lacs)
1. Air Pollution Control Devices (Bag Filters, online continuous emission monitoring system etc.)
100 20
2. Water Pollution Control Measures 20 04
3. Noise Pollution Control Measures 05 01
4. Environment Monitoring and Management --- 06
5. Occupational Health 2 01
6. Green Belt Development 3.5 01
7. Rain Water Harvesting 7.5 02
Total 137 35
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 242
CHAPTER-11: SUMMARY AND CONCLUSIONS
11.1 SUMMARY
M/s Vardhman Ispat Udyog (VIU), established in 2005 is a Partnership firm promoted
by Mr. Pradeep Garg and Mr. Subodh Kumar. VIU is an authorized distributor of
Kamdhenu Ispat Limited’s (KIL) steel product in Punjab. It also supplies the products
in Himachal Pradesh. The firm has a dealer network of 400 dealers through which
the distribution is done. As per the arrangement between VIU & Kamdhenu, any sale
of Kamdhenu TMT (retail or institutional) is being routed through VIU only in Punjab.
M/s Vardhman Ispat Udyog acquired by purchase M/s H.N Steel Castings & M/s
S.R. Steel along with Mr. Rakesh Kumar’s land (10199 sq.m) in the village Bathri
and formed a new unit. M/s. H. N. steel has two induction furnaces of capacity of 4T
&6T respectively and M/s. SR Steel has only rolling mill, both these units were
located adjacent to each other at Village Bathri district Una Himachal Pradesh. M/s
Vardhman Ispat Udyog proposes to install a new manufacturing unit of Steel at
Village Bathri, Distt. Una (HP).
Project falls under Category A due to interstate boundary of Punjab within 10
Km as Metallurgical Industries (secondary metallurgical processing) Item 3(a) of the
schedule of EIA notification of Sept 14, 2006 issued by MOEF & CC.
Water for construction and domestic purpose will be drawn from bore well.
Approximately 31 KLD (21 KLD + 10 KLD) water will be used for industrial and
domestic purposes respectively. The project adopts Zero Liquid Discharge. Total
Power loads around 9,925 KW to run the additional plant & machinery during
Construction and Operational Phase. Expected source is Himachal Pradesh Power
Corporation Ltd. DG set power is provided for running essential machinery to prevent
any blocking and for illumination.
Total Project Cost will beRs. 3038 Lacs. Total Plot Area is around 27078.0 Sq. m.
Domestic wastewater will be generated as liquid effluent that will be further sent to
the STP and treated water will be used for horticulture. About 10-15 % of the total
raw material used will get converted into slag and Dust from APCD devices are
hazardous materials generated on site will be stored and transported to TSDF site or
considered for zinc metal recovery in future. The generated APCD dust will be
disposed of in the authorized TSDF site for the present.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 243
11.2 CONCLUSIONS
Certain levels of impacts are observed in the proposed project. These impacts are
reduced by mitigative measures implemented in the project area. Apart from these
impacts’ certain beneficial effects in terms of providing employment opportunities
and development of surrounding plant area is foreseen. This will produce multiple
effects on the life and economy of the local people.
The project activities involved in the construction and operation phase are identified.
For identification of impacts, the interaction between the project activities and
different components of environment were detailed and are classified phase wise.
In the constructional phase, the transportation of construction material could have
an impact, especially on air, noise, vibration. However, since the proposed project is
surrounded with industries and well-maintained infrastructure facilities exist, even
this impact is minimal and temporary. The noxious emission arising out of the
various systems will be taken care by a bag filters and waste water generated if any
will be recycled in the manufacturing process.
During the operational phase, there could be minor change in air quality.
Transportation of raw material, storage and handling of material and the production
process could cause a temporary disturbance to environment variables, which will
be prevented with the proposed mitigation measures proposed in Chapter 4.
With respect to occupational health, minimal impacts are anticipated on the health of
the employees during operation phase. As the project site is already established
there are no issues related to Resettlement and Rehabilitation. The company has
proposed to create green belt inside the project area premises along with
development of rainwater harvesting system inside the plant premises.
The project will generate employment opportunities among the local peoples which
will provide a handsome support in improving the living standard.
Thus, it can be concluded that with the judicious and proper implementation of the
pollution control and mitigation measures, the proposed project will be beneficial to
the society and will help reduce the demand-supply gap of steel and will contribute
to the economic development of the region and country in general.
M/s VARDHMAN ISPAT UDYOG
FINAL EIA REPORT PREPARED BY: SHIVALIK SOLID WASTE MANAGEMENT LTD Page 244
CHAPTER-12: DISCLOSURE OF CONSULTANTS
M/s Shivalik Solid Waste Management Limited (SSWML) has been appointed as
Consultant to carry out Environmental Impact Assessment study of the proposed
metallurgical project M/s Vardhman Ispat UdyogPvt. Ltd.
Brief profile of SSWML is as below:
Name of the Consultancy Company
M/s. Shivalik Solid Waste Management Ltd.
Address Registered Office: Village-Majra, P.O. Dabhota, Tehsil Nalagarh, Distt. Solan, Himachal Pradesh - 174101 Phone/Telefax: 01795-260427, 260227 Zirakpur Office: SCO 20-21, 1st Floor, Near Hotel Dolphin, Baltana, Zirakpur Punjab- 140604 Phone/Telefax : 01762 – 509496
E-mail Address [email protected] [email protected]
Website www.sswml.net
Nature of Services Treatment, Storage & Disposal Facility, EIA Consultancy, Environmental, Health & Safety Auditing, EMS, Environmental Monitoring & Laboratory Analytical Services, Waste water Management, Energy Audit Greens Concept Development, etc.
Shivalik Solid Waste Management Limited (SSWML) is offering high quality technical
services in the field of EIA, Environment, Health & Safety (EHS), and Environmental
Monitoring & Laboratory Analytical Services etc.
SSWML is supported by distinguished professionals, engineers, scientists etc.
SSWML Professionals have excellent experience in executing EIA and other
environmental projects.
For Environmental Monitoring related work, we have our in-house laboratory
approved by NABL. Following experts are associated with SSWML for EIA and
Environmental projects.