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EIA Report

ENVIRONMENTAL IMPACT ASSESSMENT REPORT

For Refinery Capacity Expansion from Existing 15 MMTPA to 25 MMTPA within the existing Refinery Complex

At

IOCL Panipat Refinery & Complex, Panipat Village:Baholi Taluk: : Panipat State:

[Project termed under Schedule 4(a) Category „A‟ – Petroleum Refining Industries as per EIA Notification 2006 and its Amendments]

Submitted by:

M/s. LIMITED, PANIPAT REFINERY

EIA CONSULTANT:

M/s. Hubert Enviro Care Systems (p) Limited

July 2021

1 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Declaration by the Head of the Accredited Consultant Organization I, Dr. J. R Moses hereby, confirm that the below mentioned experts prepared the EIA/EMP for the “Panipat Refinery Capacity Expansion from Existing 15 MMTPA to 25 MMTPA within the existing Refinery Complex” at Baholi village, Panipat District, Haryana state by M/s. Indian Oil Corporation Limited also confirms that I shall be fully accountable for any misleading information mentioned in this statement.

Signature:

Date: 17.07.2021

Name: Dr. J.R Moses

Designation: CEO

Name of the EIA Consultant Organization: Hubert Enviro Care Systems Pvt. Ltd., Chennai.

NABET Certificate No & Validity: NABET/EIA/1922/RA 0172 & 13.10.2022.

2 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Declaration of Experts contributing to the EIA I hereby certify that I was involved in the preparation of EIA/EMP for the “Panipat Refinery Capacity Expansion from Existing 15 MMTPA to 25 MMTPA within the existing refinery ” at Baholi village, Panipat District, Haryana state by M/s. Indian Oil Corporation Limited as EIA Coordinator with the support of the following Functional Area Experts.

EIA Co-ordinator

Name: Dr. J R Moses

Signature: Date:17.07.2021

Contact Information: Hubert Enviro Care Systems Pvt. Ltd., # A-21, Phase III, Behind Lions Club School, Thiru-vi-ka Industrial Area, Guindy, Chennai –600032. , . Email: [email protected] Website: www.hecs.in

Functional Area Experts (FAEs): S. Functional Duration of Name of the Expert Signature No. Areas Involvement Jan 2019 till Dr. J R Moses date 1. AP FAE Jan 2019 till Mr. Vamsee Krishna Navooru date Jan 2019 till 2. AQ FAE Dr. J R Moses date Jan 2019 till Dr. J R Moses date FAE Jan 2019 till 3. WP Mr. Vamsee Krishna Navooru date Jan 2019 till FAA Mr. Chengalvarayan date Jan 2019 till Mr. A. Manoharan March 2021 4. SHW FAE Jan 2019 till Mr. Vamsee Krishna Navooru date

3 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Functional Duration of Name of the Expert Signature No. Areas Involvement Jan 2019 till 5. SE FAE Mr. V. Dhivakar date Jan 2019 till Dr.. Sundararajan date 6. EB FAE Jan 2019 till Dr. Rajkumar Samuel date Jan 2019 till 7. HG FAE Mr. MallikarjunaRao date Jan 2019 till 8. Geo FAE Mr. MallikarjunaRao date Jan 2019 till Mr. Vivek P. Navare date 9. NV FAE Jan 2019 till Mr. Vamsee Krishna Navooru date Jan 2019 till 10. LU FAE Mr. VenkateswarluRachala date Jan 2019 till 11. RH FAE Dr. J R Moses date Jan 2019 till Mr. A. Manoharan March 2021 12. SC FAE Feb 2020 till Dr.B.C.Nagaraja date

AP - Air pollution monitoring, prevention and control AQ - Meteorology, air quality modelling and prediction EB - Ecology and biodiversity HG - Hydrology, ground water and water conservation LU - Land use N&V - Noise & Vibrations RH - Risk assessment and hazards management SC - Soil Conservation SE - Socio-Economics SHW - Solid and hazardous waste management WP - Water pollution monitoring, prevention and control Geo -Geology

4 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Acknowledgement The following personnel are gratefully acknowledged for their fullest support in collection, compilation of needful data regarding the project and kind cooperation in fulfilling the report on Environmental Impact Assessment (EIA)/EMP for “Panipat Refinery Capacity Expansion from existing 15 MMTPA to 25 MMTPA within the existing Refinery Complex” at Baholi village, Panipat District, Haryana state by M/s. Indian Oil Corporation Limited

M/s. Indian Oil Corporation Limited

1) Mr. Hitesh R Shah CGM(TS) 2) Mr. Ashish Bhushan GM(HSE) 3) Mr. Biju Shah CM(TS) 4) Mr. Dharmendra Kumar SM(HSE) 5) Mr. Tilak Singh M(HSE)

M/s Hubert Enviro Care System Private Limited 1) Dr. J R Moses (CEO and EIA Coordinator) 2) Mr. Vamsee Krishna Navooru (Consultancy Head) 3) Mr. Manoj Kumar (Risk Engineer) 4) Ms. Rekha (Trainee Engineer) 5) Mr. Rabik Raja (Trainee Engineer) 6) Mr. Praveen kumar (Trainee Engineer) 7) Ms. Mahadevi (Trainee Engineer)

5 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Certificate of Plagiarism check Title of EIA report Panipat Refinery Capacity Expansion from Existing 15MMTPA to 25 MMTPA within the existing Refinery Complex

Name of Accredited Consultant Hubert Enviro Care Systems (P) Ltd Organisation

Unique identification number HECS/EIA/IOCL Panipat/Final/17.07.2021/1063

Name of EIA Coordinator Dr. J R Moses

Name of Software Plagiarism Checker X

Date of check 13.07.2021

Time of check 10:15am

Declaration by the head of accredited consultant Organisation/ authorised person

I hereby certify that, this EIA report has been evaluated using online/in house software Plagiarism Checker X. The report produced has been analysed by the system and based on it, I certify that the EIA report produced is in accordance with good scientific practice.

Date and sign of EIA Coordinator:

Name: Dr. J R Moses

Designation: CEO

Date and sign of Head of Accredited Organisation:

Name of the EIA Consultant organisation: Hubert Enviro Care Systems (P) Ltd

NABET certificate No and issue date: NABET/EIA/1922/RA0172 & 13.10.2022

6 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Contents CHAPTER 1 ...... 19 1 INTRODUCTION ...... 20 1.1 Introduction to project & Project Proponent ...... 20 1.2 Purpose of the EIA report...... 22 1.3 Brief description of the Project ...... 23 1.4 EIA cost ...... 23 1.5 Scope of study & Methodology adopted ...... 23 1.5.1 Objectives of the EIA Report ...... 24 1.5.2 Scope of Work ...... 24 1.5.3 EIA Process ...... 26 1.6 Objectives of the Study ...... 28 1.7 Applicable Regulatory Framework ...... 28 1.8 ToR Compliance ...... 33 CHAPTER 2 ...... 117 2 PROJECT DESCRIPTION ...... 118 2.1 Project Description ...... 118 2.1.1 Type of Project ...... 119 2.2 Need of the project ...... 119 2.3 Site Location ...... 120 2.4 Existing Environmental Setup ...... 126 2.5 Project Cost ...... 134 2.6 Proposed Schedule for Approval and Implementation ...... 134 2.7 Project Details ...... 134 2.7.1 Existing Facility Description ...... 134 2.7.1.1 Size & magnitude of operation ...... 135 2.7.1.2 Dispatch of Products ...... 136 2.7.1.3 Auxiliary Facilities ...... 136 2.7.1.4 Other Auxiliary Facilities ...... 137 2.7.1.5 Existing Utilities ...... 139 2.7.1.6 Existing Fire and Gas Monitoring System ...... 140 2.7.2 Proposed Facility ...... 141 2.7.2.1 Process Description ...... 141

7 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.7.2.2 Crude Distillation Unit ...... 141 2.7.2.3 Naphtha Stabilizer ...... 142 2.7.2.4 Vacuum Distillation Unit...... 143 2.7.2.5 Product Rundown section ...... 144 2.7.2.6 Steam Generation Section ...... 145 2.7.2.7 VGO HDT ...... 146 2.7.2.8 INDMAX FCC with Propylene Recovery Unit ...... 147 2.7.2.9 Diesel Hydro treater ...... 150 2.7.2.10 Naphtha Hydrotreater Unit ...... 151 2.7.2.11 Resid Hydro processing Unit ...... 153 2.7.2.12 Amine Regeneration Unit...... 156 2.7.2.13 Sulphur Recovery Unit ...... 157 2.7.2.14 Tail Gas Treating Unit...... 158 2.7.3 Raw Material and Mode of Transportation ...... 162 2.7.4 Proposed Utilities ...... 164 2.7.5 Sulphur Balance ...... 166 2.8 Plot area ...... 167 2.8.1 Site Photographs ...... 167 2.8.2 Land Area Breakup ...... 172 2.9 Water requirements ...... 174 2.10 Air Pollution Control Measures ...... 178 2.11 Green Belt ...... 178 2.11.1 Existing ...... 178 2.11.2 Proposed ...... 179 2.11.3 After Expansion ...... 179 2.11.4 Detail of Species Planted ...... 179 2.11.5 Eco-Park in ETPs area ...... 180 2.11.6 Maintenance of planted tree in township / refinery ...... 180 2.12 Power and Fuel Requirements...... 184 2.13 Manpower...... 184 2.14 Water Pollution Control Measures ...... 185 2.15 Solid waste Management ...... 190 2.16 Hazardous Waste Management ...... 191

8 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report CHAPTER 3 ...... 195 3 DESCRIPTION OF ENVIRONMENT ...... 196 3.1 Preamble ...... 196 3.2 Study area ...... 196 3.3 Description of the Study Area ...... 197 3.4 Environmentally/Ecologically Sensitive areas ...... 200 3.5 Physical Conditions of PIA district ...... 216 3.5.1 PIA District Profile ...... 216 3.5.2 Climatic Conditions ...... 216 3.5.3 Natural Resources ofPIA District ...... 216 3.5.4 Land Use & Land Cover ...... 222 3.5.5 Topography ...... 228 3.5.6 Geomorphology of PIA District...... 231 3.5.7 Hydrogeology of PIA District ...... 234 3.5.8 Drainage Pattern in PIA District ...... 234 3.5.9 Soils in PIA District ...... 236 3.6 Seismicity ...... 236 3.7 Air Environment ...... 238 3.7.1 Meteorological Conditions...... 238 3.7.2 Meteorological Data Collection ...... 238 3.7.3 General Meteorological Scenario based on IMD Data ...... 238 3.7.4 Meteorological data during Study Period ...... 240 3.7.5 Atmospheric Inversion ...... 241 3.8 Ambient Air Quality...... 241 3.8.1 Ambient Air Quality Monitoring Stations ...... 242 3.8.2 Ambient Air Quality Monitoring Techniques and Frequency ...... 244 3.9 Noise Environment ...... 250 3.9.1 Results and Discussions ...... 250 3.10 Water Environment ...... 253 3.10.1 Surface Water Resources ...... 253 3.10.2 Surface Water Quality Assessment ...... 253 3.10.3 Groundwater resources ...... 261 3.11 Soil Quality ...... 267

9 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.12 Biological Environment ...... 271 3.13 Socio Economic profile ...... 283 3.13.1 Socio Economic Aspects...... 284 3.13.2 Social Economic Profile of the study area ...... 286 3.13.3 Summary ...... 296 CHAPTER 4 ...... 297 4 Anticipated environmental impacts & mitigation measures ...... 298 4.1 Introduction ...... 298 4.2 Proposed Project Activities ...... 298 4.3 Construction Phase ...... 298 4.3.1 Impacts During Construction Phase ...... 299 4.3.2 Mitigation Measures for Construction Phase ...... 299 4.3.3 Land environment ...... 300 4.3.4 Air environment ...... 301 4.3.5 Water environment ...... 302 4.3.6 Noise environment ...... 303 4.3.7 Waste generation ...... 303 4.3.8 Ecology ...... 304 4.3.9 Social environment ...... 304 4.4 Operation Phase...... 305 4.4.1 Impacts During Operational Phase ...... 305 4.5 Air Environment ...... 305 4.5.1 Meteorological data ...... 306 4.5.2 AERMET Process ...... 307 4.5.3 AERMOD Process ...... 307 4.5.4 Emissions-Point Source ...... 309 4.5.5 Emissions-Line Source ...... 314 4.5.6 Emissions-Cumulative Source ...... 319 4.5.7 Impacts due to Traffic and Transportation ...... 324 4.6 Noise Environment ...... 325 4.7 Water Environment ...... 327 4.7.1 Impacts On Surface Water Bodies ...... 331 4.7.2 Mitigation measures on Grownd Water ...... 331

10 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 4.7.3 Impacts Due to Wastewater Generation ...... 331 4.7.4 Mitigation Measures to Wastewater Generation ...... 332 4.8 Effluent Water Quality, Quantity and Treatment Method ...... 332 4.8.1 Process Description ...... 333 4.8.2 Sanitary Sewage Treatment ...... 334 4.8.3 VOC Control System ...... 334 4.8.4 Slop & Sludge Handling ...... 334 4.9 Land Environment ...... 336 4.9.1 Potential Impact Due to Location ...... 336 4.9.2 Impacts Due to Changes in Land Use Pattern ...... 336 4.9.3 Mitigation Measures ...... 336 4.10 Solid Waste Management...... 336 4.10.1 Impact Due to Solid Waste Generation ...... 336 4.10.2 RO Rejects Treatment Facility ...... 336 4.10.3 Evaporation Section ...... 337 4.10.4 Dryer Section ...... 337 CHAPTER 5 ...... 339 5 ANALYSIS OF ALTERNATIVES ...... 340 5.1 Introduction ...... 340 5.2 Site Alternative ...... 340 5.3 Water Supply Alternative ...... 340 5.4 Technology Alternative ...... 340 CHAPTER 6 ...... 342 6 ENVIRONMENTAL MONITORING PROGRAM ...... 343 6.1 Introduction ...... 343 6.2 Environmental Effects Monitoring in EIA ...... 343 6.2.1 Post Project Environment Monitoring Program ...... 344 6.2.2 Monitoring Methodologies ...... 344 6.3 Reporting & Documentation ...... 345 6.4 Budget for Environmental Monitoring Plan...... 345 CHAPTER 7 ...... 347 7 ADDITIONAL STUDIES ...... 348 7.1 Public Consultation ...... 348

11 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 7.1.1 Reply to the issues raised by the public during Public Hearing on 06.04.2021 352 7.2 Risk Assessment ...... 356 7.3 Applicability of Environmental Clearance ...... 356 7.4 Consent for Existing Operation ...... 356 7.5 ToR Issued by MoEF&CC ...... 357 7.6 Copy of Standard ToR...... 358 CHAPTER 8 ...... 365 8 PROJECT BENEFITS ...... 366 8.1 Project Benefits ...... 366 CHAPTER 9 ...... 367 9 ENVIRONMENTAL COST BENEFIT ANALYSIS ...... 368 CHAPTER 10 ...... 369 10 ENVIRONMENTAL MANAGEMENT PLAN...... 370 10.1 Introduction ...... 370 10.2 Objectives of EMP ...... 370 10.3 EMP Structure and Organization ...... 371 10.4 EMP/EHS Roles and Responsibilities ...... 372 10.5 Environmental Management Plan for Construction Phase ...... 373 10.5.1 Air Quality ...... 373 10.5.2 Noise Environment ...... 374 10.5.3 Water Quality and Water Resources ...... 374 10.5.4 Solid Waste ...... 375 10.5.5 Land Environment ...... 375 10.5.6 Material Handling Storage and Transportation...... 375 10.5.7 Ecology ...... 375 10.5.8 Socio Economic ...... 376 10.6 Environmental Management Plan for Operation Phase ...... 376 10.6.1 Air Quality Management ...... 376 10.6.2 Noise Monitoring ...... 379 10.6.3 Water and waste water management ...... 379 10.6.4 Land Environment ...... 382 10.7 Cumulative EMP ...... 383 10.7.1 Construction Phase...... 383

12 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 10.7.2 Operation and Maintenance Phase ...... 383 10.8 Occupational Health and Safety ...... 385 10.8.1 Construction Phase...... 386 10.8.2 Operational phase...... 386 10.8.3 First aid Boxes ...... 386 10.8.4 Eye Wash Fountain and Safety Shower ...... 388 10.8.5 Existing Safety System ...... 388 10.8.6 Fire Extinguisher ...... 388 10.8.7 Emergency Equipment‟s and PPEs ...... 389 10.8.8 Occupational Health Monitoring ...... 389 10.9 Environmental Management Cell...... 390 10.10 Corporate Environmental Policy ...... 390 10.11 Budgetary Provision for Environmental Management Plan ...... 392 10.12 Corporate Social Responsibility ...... 392 10.13 Corporate Environmental Responsibility (CER) ...... 392 CHAPTER 11 ...... 393 11 SUMMARY & CONCLUSION ...... 394 CHAPTER 12 ...... 396 12 DISCLOSURE OF CONSULTANTS ...... 397 12.1 Brief Profile of Hubert Enviro Care Systems (P) Limited (HECS) ...... 397 12.2 QCI-NABET - EIA Accreditation...... 399 12.3 Copy of QCI NABET Accreditation ...... 400

13 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report List of Tables Table 1-1 Chronology of Environmental clearances ...... 22 Table 1-2 Applicable Acts and Rules for the proposed Refinery project ...... 29 Table 2-1 Geographical coordinates of the project site ...... 121 Table 2-2 Existing Environmental Setup of the study region ...... 126 Table 2-3 List of major Industries within 10km Radius from the project site ...... 131 Table 2-4 Project Cost ...... 134 Table 2-5 Time Schedule for proposed project...... 134 Table 2-6 Plant Description ...... 134 Table 2-7 Existing Units in the refinery ...... 135 Table 2-8 Existing Storage Tanks ...... 139 Table 2-9 List of fire hydrants ...... 140 Table 2-10 Process Units with Proposed Capacity ...... 161 Table 2-11 Raw Materials ...... 163 Table 2-12 Material Balance ...... 163 Table 2-13 Proposed Utilities ...... 164 Table 2-14 Sulphur Balance...... 166 Table 2-15 Land use planning of the Project Site ...... 172 Table 2-16 Existing and Proposed Water Requirements ...... 175 Table 2-17 No. of trees planted from FY 2014-15 onwards ...... 180 Table 2-18 Power and Fuel Requirement ...... 184 Table 2-19 Manpower requirements ...... 184 Table 2-20 Water Pollution Treatment Methods ...... 186 Table 2-21 Characteristics of Effluent Generated ...... 190 Table 2-22 Solid Waste Management ...... 191 Table 2-23 Hazardous Waste Management ...... 191 Table 3-1Environmentally Sensitive Areas within 15 Km from Project Boundary ...... 200 Table 3-2Production details of the district (Panipat) during the year 2011-12 ...... 219 Table 3-3 Land use/Land cover statistics for Panipat district (2015-16) ...... 222 Table 3-4Land use pattern of the Study Area ...... 225 Table 3-5Geomorphology pattern of the study area ...... 231 Table 3-6Climatological Summary – (1971-1999) ...... 239 Table 3-7Meteorology Data for the Study Period (March - May 2019)...... 240 Table 3-8Details of Ambient Air Quality Monitoring Locations ...... 242 Table 3-9Analytical Methods for Analysis of Ambient Air Quality Parameters (NAAQ) ... 244 Table 3-10Summary of the average baseline concentrations of pollutants ...... 246 Table 3-11Day and Night Equivalent Noise Levels ...... 250 Table 3-12Test methods used for the analysis of water quality parameters ...... 253 Table 3-13Details of Surface water sampling locations ...... 254 Table 3-14 Physicochemical Parameters of Surface water samples from the study area...... 257 Table 3-15 Surface water Standards (IS 2296:1992) ...... 260 Table 3-16 Details of Groundwater Quality Monitoring Locations ...... 262 Table 3-17Physico chemical analysis of Ground water samples from study area ...... 264

14 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 3-18Soil & Sediment Quality Monitoring Locations ...... 267 Table 3-19Physico Chemical parameters of soil samples from the study area ...... 269 Table 3-20List of Flora recorded from Secondary source ...... 271 Table 3-21List of bird species recorded from Secondary source ...... 277 Table 3-22Social Indicators ...... 284 Table 3-23Education Infrastructures in Panipat district ...... 285 Table 3-24Socio Economic analysis: Health care ...... 286 Table 3-25List of villages in the study area ...... 287 Table 3-26Summary of Socio-economic indicators within the study area ...... 288 Table 3-27 Summary of Employment and Livelihood within the study area ...... 288 Table 3-28Details of Education facilities within study area ...... 289 Table 3-29 Literates population and the percentage within the study area ...... 289 Table 3-30 Health facility within the study area ...... 291 Table 3-31 Drinking water sources of Villages in the study area ...... 293 Table 4-1 Proposed Stack Emission details ...... 309 Table 4-2 Estimated Top 10 Highest Concentrations of Particulate Matter obtained through Modeling ...... 310 Table 4-3 Estimated Top 10 Highest Concentrations of Sulphur Dioxide Obtained Through Modeling ...... 311 Table 4-4 Estimated Top 10 Highest Concentrations of oxide of Nitrogen Obtained through Modeling ...... 312 Table 4-5 Estimated Top 10 Highest Concentrations of Carbon Monoxide Obtained through Modeling ...... 313 Table 4-6 Total Maximum GLCs from the Stack Emissions ...... 314 Table 4-7 Existing & Proposed Vehicular movement per Peak hour ...... 324 Table 4-8 Traffic Volume after Implementation of the Project ...... 325 Table 4-9 Characteristics of the treated effluent ...... 335 Table 6-1 Post Project Environmental Monitoring Plan ...... 344 Table 6-2Budgetary allocation for Environmental Monitoring ...... 345 Table 10-1 Responsibility for EMP/EHS Implementation ...... 372 Table 10-2 Water Management ...... 381 Table 10-3 Waste Water Management...... 381 Table 10-4 Existing Safety Equipment‟s ...... 388 Table 10-5 Suitability of Extinguishing Media for Different Fires ...... 388 Table 10-6 Expenditure on Environmental measures ...... 392

15 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report List of Figures Figure 1-1 EIA Process ...... 27 Figure 2-1 Market Potential ...... 120 Figure 2-2 Index map of the project site ...... 122 Figure 2-3 Google image showing salient features within 0- 1 km radius ...... 123 Figure 2-4 Google image showing salient features within 0- 5 km radius ...... 124 Figure 2-5 Google image showing salient features 0- 10 km Radius Map around the study region ...... 125 Figure 2-6 Existing Block flow diagram ...... 138 Figure 2-7 Over view of admin green belt from top of the admin building ...... 168 Figure 2-8 Photographs of Existing Unit ...... 169 Figure 2-9 Treated Effluent Discharge Fall Out Point...... 170 Figure 2-10 Site Photographs of Existing and Proposed Facilities...... 171 Figure 2-11 Existing and Proposed Refinery Layout ...... 173 Figure 2-12 Water Balance of Existing Refinery (Source: IOCL Panipat) ...... 176 Figure 2-13 Total Proposed Water Balance (Source: IOCL Panipat) ...... 177 Figure 2-14 A view of Eco-park located besides ETP-2 ...... 181 Figure 2-15 Herbal park located in Township ...... 181 Figure 2-16 A view of Green Belt ...... 182 Figure 2-17 Green Belt between PR &PNC ...... 182 Figure 2-18 Tree plantation – village Gwalara ...... 183 Figure 2-19 Effluent Treatment plant 1 & 2 and PX/PTA...... 187 Figure 2-20 Flow Diagram of Proposed ETP plant ...... 188 Figure 2-21 Proposed ETP plant Layout ...... 189 Figure 3-1 Map showing the Satellite Image of the study area ...... 198 Figure 3-2 Topo Map of Study area ...... 199 Figure 3-3 Environmental sensitive areas covering within 15 Km from project boundary ... 214 Figure 3-4 Environmental sensitive areas covering within 15 Km from project boundary ... 215 Figure 3-5Mineral Map of Haryana ...... 221 Figure 3-6Land use/Land cover pattern for Panipat district ...... 223 Figure 3-7 Land use/Land cover Map of Panipat district ...... 224 Figure 3-8Land use pattern of the Study Area ...... 226 Figure 3-9Land use map of the Study Area ...... 227 Figure 3-10 Physical map of Haryana State ...... 229 Figure 3-11 Contour map of the Study Area ...... 230 Figure 3-12 Geomorphology pattern of the study area ...... 232 Figure 3-13 Geomorphology Map of Study Area ...... 233 Figure 3-14Drainage map of the study area ...... 235 Figure 3-15Seismicity Map of India ...... 237 Figure 3-16Wind Rose during (March - May 2019)...... 240 Figure 3-17Atmospheric inversion level at the project site ...... 241 Figure 3-18Map showing the Ambient Air Quality monitoring locations ...... 243 Figure 3-19 Map showing the noise monitoring locations ...... 252

16 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Figure 3-20 Map showing the surface water monitoring locations ...... 256 Figure 3-21Depth to water level during Pre-Monsoon& Post Monsoon in Panipat District . 262 Figure 3-22Map showing the groundwater monitoring locations...... 263 Figure 3-23Map showing the soil monitoring location...... 268 Figure 4-1 Wind rose diagram of Meteorological data considered for Modelling (March to May 2019) ...... 307 Figure 4-2 Predicted 24-Hrs GLC‟s of Particulate matter within 10 km Radius of the Study Area ...... 310

Figure 4-3 Predicted 24-Hrs‟ GLC‟s of SO2 within 10 km Radius of the Study Area ...... 311 Figure 4-4 Predicted 24-Hrs‟ GLC‟s of NOx within 10 km Radius of the Study Area ...... 312 Figure 4-5 Predicted 1-Hr‟ GLC‟s of CO within 10 km Radius of the Study Area ...... 313 Figure 4-6 Predicted 24-Hrs GLC‟s of Particulate matter within 10 km Radius of the Study Area ...... 315

Figure 4-7 Predicted 24-Hrs‟ GLC‟s of NOx within 10 km Radius of the Study Area ...... 316 Figure 4-8 Predicted 1-Hrs‟ GLC‟s of CO within 10 km Radius of the Study Area ...... 317 Figure 4-9 Predicted 24-Hrs GLC‟s of Particulate matter within 10 km Radius of the Study Area ...... 320

Figure 4-10 Predicted 24-Hrs‟ GLC‟s of SO2 within 10 km Radius of the Study Area ...... 321 Figure 4-11 Predicted 24-Hrs‟ GLC‟s of NOx within 10 km Radius of the Study Area ...... 322 Figure 4-12 Predicted 1-Hrs‟ GLC‟s of CO within 10 km Radius of the Study Area ...... 323 Figure 4-13 Existing & Proposed ETP block diagram ...... 335 Figure 7-1 Public Hearing Advertisements () ...... 349 Figure 7-2 Public Hearing Advertisements (English) ...... 350 Figure 7-3 Public Hearing photographs...... 351 Figure 10-1 Typical HSE Department Organogram ...... 371 Figure 10-2 Rain Water Harvesting Pits ...... 380 Figure 10-3 Organogram for OHC ...... 387 Figure 10-4 EHS Policy ...... 391

17 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Abbreviation

MMTPA-Million Metric Tonnes Per Annum PX/PTA-Para Xylene /Purified Terephthalic Acid KTPA-Kilo Tonnes Per Annum PREP- Panipat Refinery Expansion Project CDU -Crude Distillation Unit VDU- Vacuum Distillation Unit HGU- Hydrogen Generation Unit NHDT- Naphtha Hydro treating unit AVU-Atmospheric & Vacuum Unit VBU- Visbreaker Unit CCRU- Continuous Catalytic Reforming Unit OHCU- Once through Hydrocracker Unit RFCCU- Resid Fluidized Catalytic Cracking Unit BBU- Bitumen Blowing Unit SRU- Sulphur Recovery Unit DHDT- Diesel Hydrotreating Unit ARU- Amine Regeneration Unit PAREX -Paraxylene Extraction unit SWS- Sour Water Stripper CPP- Captive power plant PSA- Pressure Swing Adsorption TGTU- Tail Gas Treating Unit SMPL- Salaya Pipeline MPPL- Mundra-Panipat Pipeline PIA -Project Impact/Influence Area CGWB-Central Ground Water Board IMD- Indian Meteorological Department BIS- Bureau of Indian Standards NAAQS- National Ambient Air Quality Standards GLC- Ground Level Concentration OSHA- Occupational Safety and Health Administration ZLD-Zero Liquid Discharge EMP- Environmental Management Plan PPE-Personal Protective Equipments VOC- Volatile Organic compounds

18 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

CHAPTER 1 INTRODUCTION

19 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 1 INTRODUCTION

1.1 Introduction to project & Project Proponent

Indian Oil Corporation Limited (IOCL) is India's largest commercial enterprise engaging in the business of refining, pipeline transportation, marketing of petroleum products and also involving in exploration production of crude oil gas, marketing of natural gas and .

Panipat Refinery site with downstream PX-PTA units is located North West of Panipat City about 5.18 km, IOCL owned a land of 491.6 Acres at Baholi village, Panipat District- 132140, Haryana. Land documents enclosed as Annexure 1

Panipat Refinery (PR) was commissioned in 1997-98 with crude oil processing capacity of 6.0 MMTPA. The refinery capacity was raised in 2008-09 to 12.0 MMTPA with the addition of another crude unit and a full conversion hydrocracker as the secondary processing unit and Delayed Coker unit for bottom upgradation (PREP- Panipat Refinery Expansion Project). Further through revamps and addition of process units the refining capacity has been brought to the present operating capacity of 15.0 MMTPA (PRAEP- Panipat Refinery Additional Expansion Project).

Panipat Refinery is integrated with Aromatic Complex and Naphtha Cracker Complex. Aromatic complex consists of Paraxylene (PX) unit with production capacity of 360 KTPA & Purified Terephthalic Acid (PTA) unit with production capacity of 550 KTPA which were commissioned in 2006. Naphtha Cracker Complex with Ethylene production capacity of 857 KTPA was commissioned in 2010. At present revamping of PX, PTA and Naphtha Cracker complex are under implementation.

Motor Spirit Quality Upgradation project with Naphtha Hydrotreating unit (NHDT), Isomerization (ISOM), FCC Gasoline Desulphurization unit (Prime G) was commissioned in 2010 for production of BS-IV quality compliant MS.

At present Panipat refinery has been upgraded to BS-VI grade fuel completely since 1st April 2020. Accordingly, EIL was asked to make a configuration study for 100% BS VI auto fuels from existing 15 MMTPA Refinery. Stage-1 approval was accorded for production of BS-VI compliant products with crude processing capacity of 15 MMTPA. In order to produce BS-VI quality fuel, following units such as new DHDT (2.2 MMTPA), new HGU (44 KTPA), new

20 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report SRU (225 TPD), new ARU (189 m3/hr), new SWS (57 m3/hr) are envisaged in BS-VI project that has been commissioned. Crude oil is received from two pipelines originating from Coast. The first one is SMPL(salaya Mathura pipeline), which supplies crude to Gujarat (Koyali refinery), Mathura refinery and Panipat refinery. 2nd pipeline is MPPL(mundra Panipat pieline) 1194km long and capacity is 8.4 MMTPA.

The existing refinery obtained several Environmental Clearances since 1992 with latest EC obtained from MoEF&CC vide: J-11011/177/2016-IA-II(I) dated 26-03-2018 enclosed as Annexure-2. The earlier EC‟s are enclosed as Annexure-3. The certified Post EC compliance is enclosed as Annexure 4. The existing plant is under operation with HSPCB consent obtained vide: HSPCB/Consent/: 313105620PITCTO7559304 dated 04.05.2020 valid till 30.09.2021, copy enclosed as Annexure 5. The Earlier CTO and CTE are enclosed in Annexure 6. The CTO compliance is enclosed in Annexure 7. PESO license obtained is listed in below table and the documents are enclosed as Annexure-8.

S. Date of Valid Licence Number Description No issue upto G / NC / HN / 06/728 31-08- 30-09- 1 Chlorine - 36 Nos. (G26114) 2020 2030

G / NC / HN / 06/730 31-08- 30-09- 2 (G26116) Chlorine - 24 Nos. 2020 2030 G / NC / HN / 06/1099 Storage of 58 Nos- CARBON 28-01- 30-09- 3 (G36172) MONOXIDE in cylinders 2015 2023 G / NC / HN / 06/1090 02-12- 30-09- 4 (G35401) Storage of chlorine in cylinders 2014 2024 P / HQ / HN / 15/2085 Existing Petroloeum class A, B, C 13-12- 31-12- 5 (P135610) Installation 2019 2024 G / NC / HN / 06/1091 02-12- 30-09- 6 (G35402) Storage of chlorine in cylinders 2014 2021 G / NC / HN / 06/656 Storage of AMMONIA gas -100 Nos. 18-09- 30-09- 7 (G18981) in cylinders 2017 2022 G/NC/HN/06/ Storage of Chlorine gas -15 Nos. in 27-09- 30-09- 8 7(G21134) cylinders 2017 2022 P / HQ / HN / 15/861 Existing Petroloeum class B 19-12- 31-12- 9 (P180609) Installation 2019 2024 P / HQ / HN / 15/534 Existing Petroloeum class A, B, C 19-12- 31-12- 10 (P3090) Installation 2019 2024 S / HO / HN / 03/69 Storage of HYDROGEN gas in 31-03- 30-09- 11 (S4221) pressure vessels 2017 2021 S / HO / HN / 03/70 31-05- 30-09- 12 (S4223) Storage of LPG gas in pressure vessels 2017 2021

21 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Date of Valid Licence Number Description No issue upto S / HO / HN / 03/71 26-05- 30-09- 13 (S4226) Storage of LPG gas in pressure vessels 2017 2021 S / HO / HN / 03/81 Storage of PROPYLENE gas in 25-05- 30-09- 14 (S4246) pressure vessels 2018 2022 S / HO / HN / 03/192 Storage of NITROGEN gas in pressure 25-05- 30-09- 15 (S24863) vessels 2018 2022 S / HO / HN / 03/211 16-05- 30-09- 16 (S31340) Storage of LPG gas in pressure vessels 2018 2021 24-08- 17 No. P-5(2) 158/ Commissioning of ' Additional clay - Refinery/XX filter at Old ATF MEROX Unit' 2020 14.12.20 31-12- 18 PPT/T-2506 Renewal of Factory licence 20 2021

Mr.Hitish.R. Shah, CGM TS,HS&E of IOCL Panipat Refinery is the Project Proponent with the registered office address: IOCL Panipat Refinery PR 42-128 Gram Panchayat Baholi Village, PO: Panipat Refinery. Panipat 132-140, Haryana. Table 1-1 Chronology of Environmental clearances S. Date of Status of MoEF&CC File No Units No issue Project Setting up Grassroot 1 J-11011/27/91-IA-II(I) 16-07-1992 Commissioned refinery Expansion of Refinery 2 J-11011/60/2000-IA-II from 6 MMTPA to 12 09-04-2001 Commissioned MMTPA Integrated PX & PTA 3 J-11011/52/2000-IA-II 30-04-2001 Commissioned project J-11011/9/2001-IA- 4 MS quality upgradation 06-12-2001 Commissioned II(I) J-11011/52/2000-IA- Modification in Plant 5 20-01-2003 Commissioned II(I) Layout Expansion of Refinery J-11011/7/2004-IA- 6 from 12 MMTPA to 15 09-08-2004 Commissioned II(I) MMTPA BS-VI upgradation and J-11011/177/2016-IA- PX/PTA Plant, 7 26-03-2018 Commissioned II(I) Petrochemical Complex expansion EC for Panipat Refinery J-11011/177/2016-IA 8 Capacity Expansion from - Applied Now II(I) 15 MMTPA to 25 MMTPA

1.2 Purpose of the EIA report

The Government of India, Ministry of Environment Forest and Climate Change (MoEF&CC), New , vide notification no. S. O. 1533 dated 14th September, 2006, and

22 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report its amendments, has made it mandatory to obtain „Prior Environmental Clearance (EC)‟ for New projects listed in the schedule, Expansion and Modernization of existing projects listed in the schedule, any change in product mix in the existing manufacturing unit falling within the schedule to that notification from MoEF&CC (for Category A projects).

The EIA submission at MoEF&CC pertains to “Panipat Refinery Capacity Expansion from existing 15 MMTPA to 25 MMTPA within the existing refinery complex”. The Project is considered under Schedule 4(a) – Petroleum Refining Industries Category A, since all the projects under this schedule falls under “A” category.

1.3 Brief description of the Project

Nature: M/s. IOCL, Panipat Refinery and Petrochemical Complex as a part of the compliance to the regulatory requirement i.e., to obtain Environmental Clearance from MoEF& CC has appointed M/s. Hubert Enviro Care Systems Private Limited, as EIA Consultant who is accredited by National Accreditation Board for Education and Training (NABET)-Quality Council of India (QCI), for Schedule 4(a) – Petroleum Refining Industries Category A, since all the projects under this schedule falls under “A” category. Size: Panipat Refinery (PR) was commissioned in 1997-98 with crude oil processing capacity of 6.0 MMTPA. The refinery capacity was raised in 2008-09 to 12.0 MMTPA with the addition of another crude unit and a full conversion hydrocracker as the secondary processing unit and Delayed Coker unit for bottom up gradation (PREP- Panipat Refinery Expansion Project). Further through revamps and addition of process units the refining capacity has been brought to the present operating capacity of 15.0 MMTPA (PRAEP- Panipat Refinery Additional Expansion Project). Location: The existing complex is located at Baholi Village, Panipat District, Haryana State. The site is located 5.18 km from Panipat city towards NW.

1.4 EIA cost

EIA study was undertaken by HECS for an amount of Rs.13,48,043.25 (Exclusive of GST).

1.5 Scope of study & Methodology adopted

EIA is the process of identifying, predicting, evaluating and mitigating the biophysical, social and other relevant effects of development proposals prior to major decisions being taken and

23 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report commitments made. These studies integrate the environmental concerns of developmental activities into the process of decision – making.

An Environmental Impact Assessment (EIA) is an assessment of the possible impact, whether positive or negative, that a proposed project may have on the environment, together consisting of the natural, social and economic aspects, i.e., aiming at “Sustainable Development” due to the project activities

1.5.1 Objectives of the EIA Report

 To ensure environmental considerations are explicitly addressed and incorporated into the development decision-making process.  To anticipate and avoid, minimize or offset the adverse significant biophysical, social and other relevant effects of the above project proposal.  To protect the productivity and capacity of natural systems and the ecological processes which maintain their respective functions.  To promote development that is sustainable and optimizes resource use as well as management opportunities.  To fully recognize the scope and requirements of the ToR and comply with the same.

1.5.2 Scope of Work

The scope of the work mentioned includes an assessment study of proposed expansion of refinery unit and their impact on the region. This study puts forward the most effective ways to protect the environment from increasing pollution caused by the burgeoning industrial development and recommendations for environmental-friendly development initiatives in the region.

An Environmental Impact Assessment (EIA) is an assessment of the possible impact, whether positive or negative, that a proposed project may have on the environment, together consisting of the natural, social and economic aspects, i.e., aiming at “Sustainable Development” due to the project activities.

This EIA report presents the existing baseline scenario and the assessment and evaluation of the environmental impacts that may rise during the construction and operational phases of the project. This report also highlights the Environmental Monitoring Program during the construction and operation phases of the project and the post-project monitoring program. In

24 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report terms of the EIA Notification of the MoEF&CC dated 14th September 2006 and subsequent amendments the generic structure of the EIA document will be as under

Chapter 1: Introduction

Introductory information is present in this Chapter. The introduction chapter provides background of the project, project proponent and describes the objective of this document. The purpose and organization of the report is present in this chapter. Chapter 2: Project Description

This Chapter includes existing and proposed expansion project description and infrastructure facilities delineating all the industrial and environmental aspects of Panipat Refinery project as well as process details of proposed products. Chapter 3: Description of the Environment

This Chapter provides baseline environmental status of Environmental Components (Primary data) delineating meteorological details of the project site and surrounding area. Chapter 4: Anticipated Environmental Impacts & Mitigation Measures

This Chapter presents the analysis of impacts on the environmental and social aspects of the project as a result of establishment of plan and thereby suggesting the mitigation measures. Chapter 5: Analysis of Alternatives (Technology and Sites)

This chapter includes the justification for the selection of the project site or technology from Environmental point of view as well as from economic point of view.

Chapter 6: Environmental Monitoring Program

This chapter will include the technical aspects of monitoring, the effectiveness of mitigation measures which will include the measurement methodologies, frequency, location, data analysis, reporting schedules etc. Chapter 7: Additional Studies

This chapter will detail about the Public Consultation sought regarding the project. It will also identify the risks of the Project in relation to the public and the surrounding environment during construction and operation phases of the refinery expansion project and thereby presents Disaster Management Plan, Social impact assessment and R&R action plans.

25 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Chapter 8: Project Benefits

This chapter deals with improvement in physical and social infrastructures, employment potential and other tangible benefits. Chapter 9: Environmental Cost Benefit Analysis This chapter summarizes the cost benefit analysis if it is available in scoping stage.

Chapter 10: Environmental Management Plan

This is the key Chapter of the report and presents the mitigation plan, covers the institutional and monitoring requirements to implement environmental mitigation measures and to assess their adequacy during project implementation. Chapter 11: Summary and Conclusion

This chapter summarizes the information given in Chapters in this EIA/EMP report and the conclusion based on the environmental study, impact identification, mitigation measures and the environmental management plan. Chapter 12: Disclosure of the Consultant

Names of consultants engaged in the preparation of the EIA/EMP report along with their brief resume and nature of Consultancy rendered are included in this Chapter.

1.5.3 EIA Process

The EIA process followed for this EIA report is composed of the following stages: 1. Study of project information 2. Screening & Scoping environmental pre-feasibility study & application for approval of ToR 3. Collection of detailed project management plan/report 4. Baseline data collection 5. Impact identification, Prediction & Evaluation 6. Mitigation measures & delineation of EMP 7. Risk assessment and safety & disaster management plan 8. Review & finalization of EIA Report based on the ToR requirements Submission of EIA report for implementation of mitigation measures & EMP as well as necessary clearances from relevant Authority

26 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report The EIA Cycle based on the above stages has been illustrated as per the ToR dated 24-08- 2018, in Figure 1-1

Figure 1-1 EIA Process

27 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 1.6 Objectives of the Study The major objective of this study is to prepare a detailed Environmental Impact Assessment Study within the study area i.e. 10 km radius from the project.

1.7 Applicable Regulatory Framework The following are some of the acts and rules related to environment that are applicable for the proposed project:

1. EIA Notification 2006 and its amendments 2. Manufacture Storage and Import of Hazardous Chemicals Rules,1989 and its amendments 3. Water (Prevention and Control of Pollution) Act,1974 and its amendments 4. Air (Prevention and Control of Pollution) Act,1981 and its amendments

5. Hazardous Waste (Management, Handling and Transboundary movement) Rules,2008

and its amendments 6. Public Liability InsuranceAct,1991 and its amendments 7. Environmental (Protection)Rules,1986 and its amendments 8. The Noise Pollution (Regulation and control) rules, 2000 9. Factories Rules 1950 and its amendments 10. Petroleum Act, 1934 11. Explosive Act,1884

The details of applicable Acts and Rules and the applicability to the project is given in Table 1-2

28 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 1-2 Applicable Acts and Rules for the proposed Refinery project

S. Act and Rules Purpose Objective Applicability No applicable 1. EIA Notification New projects, Protection and As the proposal is for 2006 and its Expansion Improvement of compliance to amendments. modernization, the Environment petroleum refining change of industry, product mix of Environmental the existing clearance from project Ministry of Environment, Forest and Climate Change (MoEF&CC) is applicable 2. The Manufacture, Handling of Regulate the Preparation/ update of Storage and Import Hazardous manufacture, On-site Emergency of Hazardous Chemicals storage and Preparedness Plan and Chemicals Rules, import of submission to Factory 1989 and its Hazardous inspectorate. amendments Chemicals Preparation/ update of Safety Report and submit to Factory inspectorate. Preparation of Material Safety Data Sheet. 3. The Water New projects, Prevention, Consent to Establish (Prevention and Expansion control and and Consent to Control of Pollution) modernization, abatement of Operate from State Act, 1974 and its change of water pollution Pollution Control amendments. product mix of Board to be obtained the existing for expansion project, Existing plants

29 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Act and Rules Purpose Objective Applicability No applicable 4. The Air (Prevention New projects, Prevention, Consent to Establish and Control of Expansion control and and Consent to Pollution) Act, 1981 /modernization, abatement of air Operate from State and its amendments. change of pollution Pollution Control product mix of Board to be obtained the existing for expansion project, Existing industries 5. The Hazardous and Management, Prevention, Hazardous waste other wastes Handling and Control and Authorization from (Management, Transboundary abatement of State Pollution Control Handling and Movement of pollution Board to be obtained Transboundary Hazardous waste for expansion Movement Rules) 2016 and Solid Waste Management Rules 2016. 6. The Environmental New projects, Protection and Environmental (Protection) Expansion/ Improvement of Standards as specified Rules,1986 and its modernization the Environment are to be complied. Amendments change of Submission of product mix of Environment the existing Statement on yearly project, Existing basis to PCB industries

30 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Act and Rules Purpose Objective Applicability No applicable 7. The Noise Pollution New projects, To protect the Noise control measure. (Regulation and Expansion/mode workers and Comply with Noise Control) Rules, 2000 rnization change public from standards and of product mix noise related submission of of the existing problems Quarterly report to project, Existing PCB industries 8. The Public Liability Transportation of To provide Provision of Liability Insurance Act, 1991 Hazardous immediate relief Insurance Policy. and its amendments Substance. to persons affected by accident involving hazardous substances and also for Establishing an Environmental Relief fund 9. Factories Rules 1950 New projects, Control of Factory License from and its amendments. Expansion/mode workplace Factory inspectorate. rnization change environment, of product mix and providing of the existing for good health project, Existing and safety of industries. workers.

31 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Act and Rules Purpose Objective Applicability No applicable 10. The Petroleum Act, New projects, Production, License to be acquired 1934 Expansion/mode Storage and for storage and rnization change import of adequate safety of product mix petroleum and measures are in place. of the existing provides the project, Existing regulations for industries the safety and environmental measures 11. The Explosive Act, New projects, Production, Safety measures are to 1884 Expansion/ Storage and be complied for the modernization import of storage of chemicals in change of explosive the plant as per PESO product mix of substance in and guidelines. the existing around the project, Existing project and industries provides the regulations for the safety and environmental measures

32 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 1.8 ToR Compliance

S. No Terms of Reference Compliance STANDARD TERMS OF REFERENCE FOR CONDUCTING ENVIRONMENT IMPACT ASSESSMENT STUDY FOR 4(a) PETROLEUM REFINING INDUSTRIES PROJECTS AND INFORMATION TO BE INCLUDED IN EIA/EMP REPORT A. Standard TOR 1 Executive Summary Brief executive summary is provided as a Separate booklet which is enclosed as Annexure 26. 2 Introduction i. Details of the EIA Consultant M/s. Hubert Enviro Care Systems (P) Ltd., Chennai including NABET accreditation NABET Accredited Number:NABET/EIA/1922/RA 0172 Valid up to 13/10/2022 ii. Information about the Project M/s. INDIAN OIL CORPORATION LIMITED Proponent IOCL Panipat Refinery, Baholi Village, Panipat District- 132140, Haryana State. iii. Importance and Benefits of the Project  Meeting the demand for distillate products & Petrochemicals needs nationwide and particularly in the Northern Capital Region (NCR).  It will also give the Opportunity to increase and improve refining margin.  Conversion of low value, low octane naphtha streams into high value high octane reformate.  The plant will require approx. 300 permanent manpower for operation and maintenance of the proposed plant. Besides, a contractual worker also will be required for regular maintenance works in the plant.  Since the project is big in nature it will affect the socio-economic status of the region due to capital investment. There will be cascading effects on economic status and avenues in the area as well as in the buffer zone where in, there will be a growth in employment scenario.  People at large in the nearby villages will get advantage by getting more employment opportunities and getting better living standards. 3 Project Description i. Cost of project and Time of The cost of the project is Rs.32946 crores. completion Note: In Form-1 the project cost is being mentioned as 25600 crores. Time of completion is expected in FY 2024-25. ii. Products with capacities for the S. No Name of the Unit Units Proposed Capacity proposed project 1 AVU MMTPA 10 2 State Run LPG treatment unit (SR-LPGT) MMTPA 0.152 3 VGO Hydrotreater unit MMTPA 3.6 4 Diesel hydrotreater unit MMTPA 5.0 5 Propylene Recovery unit MMTPA 1.15

33 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance 6 Resid Hydrocracker unit- RHCU MMTPA 2.5 7 INDMAX MMTPA 2.5 8 NHT/ CCR/ ISOM MMTPA 0.95/0.625/0.205 9 HGU MMTPA 0.081 10 ALKYLATION MMTPA 0.67 11 SARU MTPD 185 12 CDW/LOBS MMTPA 0.56 13 SRU-I/II/ TGTU TPD 2x465 /930 14 SWS-I/II TPH 252+180 15 ARU TPH 1256 16 MUG Compressor MMTPA 0.17

iii. If expansion project, details of existing products with capacities and whether S.No Name of Unit Units Existing Capacity adequate land is available for 1 CDU 1 MMTPA 7.5 expansion, reference of earlier EC if 2 VDU 1 MMTPA 3.75 any. 3 Resid Fluidized Catalytic Cracking Unit (RDCCU) MMTPA 0.85 4 Propylene Separation Unit (PSU) MMTPA 0.225 5 Once Thru Hydrocracker Unit MMTPA 1.9 6 Continuous Catalytic Reforming Unit (CCRU) MMTPA 0.65 7 Hydrogen Generation Unit (HGU) TMTPA 38 8 VisbreakerUnit (VBU) MMTPA 0.4 9 Diesel Hydro Desulphurisation Unit (DHDS) TMTPA 0.77 10 Bitumen Blowing Unit (BBU) MMTPA 0.5 11 SulphurRecovery Units (SRU/SSRU) TPD 2 *115 12 Amine Regeneration Unit m3/hr 400 13 Sour Water Strippers I (Refinery) m3/hr 71.8 14 Sour Water Strippers II (OHCU) m3/hr 16 15 SR LPG treatment MMTPA 0.142 16 Merox: TPA 190000 1.FCCGasoline 200000+100000 2.CrackedLPG(FCC+DCU) 1150000 3.ATF/KERO 17 Crude Distillation Unit (CDU‐ II) MMTPA 7.5 18 Vacuum Distillation Unit (VDU‐ II) MMTPA 3.75 19 Hydrocracker Unit MMTPA 1.8 1.7

34 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance 20 Delayed Coker Unit MMTPA 3.0 21 Hydrogen Generation Unit (HGU –2&3) MTPA 2*70 22 Sulphur Recovery Units SRU (3,4 &5) TPD 3 *225 23 Coker LPG Merox unit MMTPA 0.1 24 Straight Run LPG Merox unit MMTPA 0.142 25 Diesel Hydrotreating Unit (DHDT) TMTPA 3.5 26 Amine Regeneration Unit (ARU-II) m3/hr 410 27 Sour Water Stripper (SWS-III) m3/hr 170 28 Hydrocracker Sour Water Stripper m3/hr 40 (SWS‐ IV) 29 NSU‐ II TPA 0.75 30 Naptha oxygen stripping unit MTPA 400,000 31 Naphtha hydrotreating MTPA 500,000 32 Continuous catalyst (Platforming + Regeneration) MTPA 500,000 33 Shell sulfolane extraction unit MTPA 152,200 34 Benzene Toluene fractionation unit MTPA 379,800 35 Paraxylene Extraction unit (PAREX) MTPA 2,025,400 36 Xylene fractionation unit MTPA 481,700 37 Trans alkylation Disproportionate(Tatoray) MTPA 360,200 unit 38 Isomerisation unit (Isomar) MTPA 1,656,500 39 PTA UNITS MTPA 553000 40 PX feed unit(NSU‐ I) MMTPA (BH) 1.3 41 NHT TMTPA 410 42 PENEX TMTPA 400 43 RSU TMTPA 470 44 FCCGDU TMTPA 370

Unit Configuration as per Latest EC- J-11011/177/2016-IA-II(I) dated 26-03-2018 S. No. Plant/Unit Unit Capacity Remarks 1 Diesel hydro desulphurization (DHDS) KTA 1000 Deferred 2 Prime-G KTA 445 Commissioned 3 Diesel Hydro-Treater (DHDT) KTA 2200 Commissioned

35 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance 4 Hydrogen generation unit (HGU) KTA 44 Commissioned 5 Tertiary Amyl Methyl Ether (TAME) KTA 36 To be Commissioned 6 OCTOMAX KTA 116 Deferred 7 Sulphur Recovery Unit (SRU) Tail gas 225 Commissioned TPD treating unit 8 Amine Regeneration Unit TPH 188.9 Commissioned 9 Para Xylene Unit 460 Existing 360 KTA and post Revamp 460 KTA KTA 10 Purified Terephthalic Acid Unit 700 Existing 550 KTA and post Revamp 700 KTA KTA 11 Sour Water Stripper(SWS) TPH 56.7 Commissioned

S. No. Proposed tanks as per Latest EC Unit Capacity Remarks 1 TAME feed tank m3 5500 Constructed but yet to be commissioned 2 TAME product tank m3 2x3600 Constructed but yet to be commissioned 3 Methanol tank m3 2x500 Constructed but yet to be commissioned

Panipat refinery owned a land of 491.6 Acres.Adequate land is available for expansion & Land document attached as Annexure 1. iv. List of Raw materials and their source with mode of transportation Raw Mode of S. No. Quantity Unit Source Material Transport IOCL Crude basket for proposed plant will be Crude 10 MMTPA Pipeline 1 selected at the time of processing of crude..

v. Other chemicals and materials required S. Existing Proposed Chemical Storage Capacity with quantities and storage capacities No. (MT/annum) (MT/annum) 1 MDEA 370.8 160.2 Use on a continuous basis, no

36 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance requirement of storage 2 Hydrazine 3.97 2.27 Use on a continuous basis, no requirement of storage 3 Morpholine 51 32.72 Use on a continuous basis, no requirement of storage 4 Multi- 131.2 84.56 Use on a continuous basis, no functional requirement of storage additive 5 Orange dye 5.98 4.18 Use on a continuous basis, no requirement of storage 6 Anti-static agent 1.6 0.92 Use on a continuous basis, no requirement of storage

vi. Details of emission, effluents, 1. Emission: hazardous waste generation and their a. Existing: management Emission(g/s) S.n Process Stack Exit Gas Volume PM SO2 NOx CO o (Nm3/Hr) @ 25C (g/sec) (g/sec) (g/sec) (g/sec) A Panipat refining unit

1 RFCC Heater 10702.17 0.0380 0.1479 0.4250 0.0851 2 RFCC Boiler 77661.33 0.2431 1.1861 3.0435 0.7904 3 AVU- 1 335341.24 1.2370 4.8774 9.8125 1.9198 B MCR

4 OHCU- Recycle gas Heater 23609.14 0.1097 0.3090 0.8758 0.1427 5 OHCU LP Section 78410.6 0.3004 1.3114 2.9498 0.5985 6 DHDS- Furnace 24562.62 0.0721 0.3572 0.8727 0.2031 CCRU stack- FF101, FF 102 7 73167.78 0.2833 1.2237 2.5233 0.5120 FF 204 CCRU Stack- FF 201, FF 202 8 36088.83 0.1536 0.7611 1.2068 0.2640 FF 203 9 CCRU Stack- FF 205 21186.13 0.0816 0.3543 0.8081 0.1685 10 VBU 21385.69 0.0766 0.4044 0.6146 0.1837 11 HGU 101595.74 0.5576 1.7731 4.0875 0.8401 C PR Expansion Unit

12 HCU Unit 42215.04 0.1867 0.5833 1.1249 0.2148 13 AVU- 2 341972.09 1.4230 5.9684 11.0780 2.7196

37 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance D Hydrogen Generation Unit

14 HGU-PDS 38499.52 0.1766 0.5039 1.2673 0.2694 15 HGU-76 140182.48 0.5775 1.9369 5.0540 1.2484 16 HGU-77 155111.13 0.7316 2.2560 5.1867 1.0362 E Diesel Hydrotreater Unit

17 DHDT-72 Heater 01 44393.26 0.1599 0.6780 1.5773 0.4095 18 DHDT-72 Heater 02 45833.96 0.1892 0.8666 1.7721 0.4956 F Paraxylene Aromatic Section

19 CCR-Heater 47019.04 0.1614 0.6839 1.2775 0.2842 20 NHT Heater 12715.52 0.0377 0.2127 0.3521 0.0809 21 Xylene Charge Heater 52943.5 0.1610 0.6546 1.5215 0.3200 22 Isomer Charge Heater 18592.5 0.0525 0.2839 0.6412 0.0710 23 Tatoray charge Heater 18392.82 0.0580 0.2407 0.6150 0.1287 G Thermal Power Station

24 HRSG 01 146887.37 0.6218 2.0295 6.3700 0.6541 25 HRSG 02 148251.99 0.5819 1.9405 6.6619 0.6132 26 HRSG 03 159843.57 0.5093 2.6734 7.0993 0.7628 27 HRSG 04 151283.04 0.5429 2.2003 6.8771 0.6736 28 HRSG 05 158248.86 0.5495 1.9566 6.7801 0.5033 29 VHP Boiler 01 130260.73 0.5142 1.9894 5.1728 0.6629 30 VHP Boiler 02 134520.21 0.6681 2.3478 5.4824 0.6420 31 Utility Boiler 02 163531.04 0.7359 3.0921 6.5794 0.7282 Pur. Teraphthalic AC-Aromatic H section 32 Fired combustion preHeater 72693.78 0.3354 0.9515 2.7727 0.2312 33 Hot oil heater 73286.64 0.2463 0.7994 2.2975 0.4662 34 thermal Oxidizer 16642.03 0.0733 0.1573 0.5739 0.0794 I Delayed Coker Unit

35 DCU 13826.97 0.0679 0.2413 0.3974 0.1012 J MS Quality Unit

36 HDS (303 Heater 201) (MSQ) 63025.7 0.2495 0.7792 1.6795 0.4410 37 NHT (301 H101) - - - - - 38 Old SRU-22/44 126752.64 - - - - 39 CPP VHP-3 149983.92 - - - - 40 SRU-26 126752.54 - - - - 41 New SRU -57 151935.71 - - - -

38 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance 42 UB-1 146307.28 - - - - 43 BBU Heater - - - - - 44 BBU incinerator - - - - - 45 NSRU - - - - - K BS-VI - - - - - 46 Prime G - - - - - 47 DHDT - - - - - 48 HGU 180000 - - - - Note: Item no.37 to 48 are idle.So the emissions are not mentioned.

b. Proposed:

S.No Stack connected to Flue gas Flow Emission per stack (g/s)

Rate (Nm3/hr) PM SO2 NOx CO 1. AVU (CDU/VDU) 257400 0.751 50.8 13.829 8.297 2. VGO - HDT 89750 0.125 0.306 4.778 1.972 3. Diesel Hydrotreater Unit 41430 0.058 0.142 2.208 0.908 4. MS Block_Charge Heater 92520 0.129 0.319 4.931 2.031 5. NHT Charge Heater 25380 0.035 0.086 1.353 0.556 6. Naphtha Stripper reboiler Heater 17260 0.024 0.058 0.919 0.378 7. CDWU_HCR Reactor Feed Heater 5700 0.008 0.019 0.297 0.131 8. CDWU_DW Reactor feed Heater 4150 0.006 0.014 0.217 0.094 9. CDWU_Vaccum Column Feed 18300 0.025 0.064 0.975 0.403 Furnace 10. Resid Hydrocracking Unit 53160 0.074 0.183 2.833 1.167 (RHCU) 11. Resid Hydrocracking Unit 8630 0.012 0.031 0.469 0.206 (RHCU)_Vaccum Heater 12. IndmaxFCC_Fresh Feed Furnace 38500 0.053 0.133 2.050 0.844 13. IndmaxFCC_Flue Gas cooler 260750 3.622 3.711 6.084 7.189 14. Sulpur recovery unit (SRU) 216570 0.037 17.889 5.464 4.925 15. Spent Acid Recovery unit 3850 0.005 0.047 0.233 0.094 (SARU)_APH System & Stack

39 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance 16. Spent Acid Recovery unit (SARU)_Decomposition furnace 18790 0.159 2.000 0.778 0.467 burner 17. Hydrogen Generation Unit 155111.13 0.732 2.256 5.186 1.036 18. CPP Stack 871660 11.555 101.795 78.190 22.303 Total(g/s) 17.41 179.853 130.794 53.001 Total (kg/hr) 62.676 647.4708 470.8584 190.8036 Further details on emissions & sources are provided in chapter 4, Section 4.5 of EIA report

2. Effluent Details:

a. Existing water balance:

EXISTING (m3/hr)

used

Treated

Loss

ffluent

Outlet

water used

Rejects

Sewage

Description

Condensate

E

FreshWater

generated generated

(a)+(b)+(c )

TotalWater Use of Use Outlets

S.No. (a) (b) (c ) of Reuse Rejects

1 Cooling Tower 1200 590 460 150 0 0 90 0 0 0 1110

2 Service Water 230 230 0 0 0 0 80 0 0 0 0 Domestic 3 Water 130 130 0 0 0 0 110 0 0 110 20 PNC Township Domestic 4 Water 125 125 0 0 0 0 125 0 0 125 0 PPMC 5 Consumption 60 60 0 0 0 0 0 0 0 0 0 Process Steam 6 Generation 0 0 0 0 0 0 0 0 0 0 0 Green Belt/ 7 Horticulture 0 0 0 0 0 0 0 125 0 0 0

40 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance Fire Water 8 Makeup 0 0 0 0 0 0 10 35 0 0 25 Refinery Units, 9 PX/PTA, CPP 1055 0 1055 0 0 0 100 1245 1030 0 115

10 Storm Water 0 0 0 0 0 160 35 200 0 0 5

11 ETP-1/2 0 0 0 0 0 0 630 0 0 0 5

12 ETP-PTA 0 0 0 0 0 0 255 0 0 0 0

13 ETP- new 0 0 0 0 0 0 0 0 0 0 0

14 RO/DM Plant 585 585 0 0 160 0 1055 630 0 0 0

15 MEE 0 0 0 0 0 0 0 0 0 0 0

16 ATFD 0 0 0 0 0 0 0 0 0 0 0

TOTAL 3385 1720 1515 150 160 160 2490 2235 1030 235 1280

b. Proposed water balance:

PROPOSED (m3/hr)

Treated

Loss

Outlet

water used

Rejects

Sewage

Description

Effluent

FreshWater

Condensate used

generated generated

se se of Outlets

(a)+(b)+(c )

TotalWater U

S.No. (a) (b) (c ) of Reuse Rejects

1 Cooling Tower 1847 1847 0 0 0 0 287 0 0 0 1560

2 Service Water 112 112 0 0 0 0 13 0 0 0 99

41 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance

3 Domestic Water 10 10 0 0 0 0 0 0 0 9 1 PNC Township 4 Domestic Water 0 0 0 0 0 0 0 0 0 0 0 PPMC 5 Consumption 0 0 0 0 0 0 0 0 0 0 0 Process Steam 6 Generation 850 18 832 0 0 0 0 0 362 0 488 Green Belt/ 7 Horticulture 10 1 9 0 0 0 0 0 0 0 0 Fire Water 8 Makeup 250 250 0 0 0 0 14 0 0 0 236 Refinery Units, 9 PX/PTA, CPP 0 0 0 0 0 0 0 0 0 0 0

10 Storm Water 0 0 0 0 0 0 0 0 0 0 0

11 ETP-1/2 0 0 0 0 0 0 0 0 0 0 0

12 ETP-PTA 0 0 0 0 0 0 0 0 0 0 0

13 ETP- new 0 0 0 0 0 0 360 0 0 0 2

14 RO/DM Plant 162 162 0 0 48 0 0 674 0 0 0

15 MEE 0 0 0 0 0 48 10 0 0 0 0

16 ATFD 0 0 0 0 0 0 0 10 0 0 0

TOTAL 3241 2400 841 0 48 48 684 684 362 9 2386

3.Hazardous waste management

Hazardous waste materials will be properly disposed as per the Hazardous Wastes (Management, Handling and Transboundary Movement) Rules 2016; Hazardous waste authorization has been made with SPCB, Haryana is enclosed

42 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance as Annexure-9.Hazardous waste generated and disposal given in chapter 2, Section 2.16 of EIA report.

a.Existing and proposed:

S. Quantity (MTPA) Source of Waste Mode of Plant Waste category No. Existing Proposed generation Disposal/Facility Disposed to 1 DHDT Spent Catalyst 134 175 DHDT SPCB authorised dealer CCR Catalyst Fines from Disposed to Spent Catalyst 2 Regeneration 0.85 1.58 Spent Catalyst Fines SPCB authorised Fines Section Collection Pot dealer CCR Disposed to Spent catalyst from 3 Platforming Spent Catalyst 7.25 4.173 SPCB authorised Reactors Process Unit dealer CCR Net GAS Chloride 4 Platforming Spent Adsorbent 0.6 31.2 To TSDF Treaters Adsorbents Process Unit CCR Fuel gas Chloride 5 Platforming Spent Adsorbent 4.25 1.8 To TSDF Adsorbent Process Unit CCR LPG Chloride 6 Platforming Spent adsorbent 0.05 1.26 To TSDF Treatment Adsorbent Process Unit CCR Debutanizer feed 7 Platforming Spent Adsorbent 10.2 33.26 To TSDF Chloride Treater Process Unit Indmax equilibrium INDMAX catalyst (E-cat) is 8 Spent Catalyst 50 839.5 To TSDF FCC withdrawn from Indmax FCC unit. Propylene Adsorbents from 9 Spent adsorbent 10 20 To TSDF Recovery unit Propylene Driers Propylene Adsorbent from Arsine 10 Spent adsorbent 20 11 To TSDF Recovery unit Guard Bed HCU/RHCU Spent catalyst 11 Spent Catalyst 136.5 5.256 To TSDF Reaction withdrawn from the

43 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance Section reactors UOP Naphtha Spent Catalyst from 12 Hydrotreating Spent Catalyst 1.4 4.5 To TSDF Reactor Process Unit Disposed to Spent Catalyst From 13 PENEX Spent Catalyst 1.4 2.96 SPCB authorised Reactor A dealer Disposed to Spent Catalyst From 14 PENEX Spent Catalyst 10.25 1.48 SPCB authorised Reactor B dealer Disposed to Spent Catalyst From 15 PENEX Spent Catalyst 5.125 0.987 SPCB authorised Reactor C dealer Disposed to Spent Catalyst from 16 PENEX Spent Catalyst 4 0.312 SPCB authorised Methanator Reactor dealer Makeup Gas Chloride 17 PENEX Spent Adsorbent 4 0.45 To TSDF Treater Spent Molecular 18 PENEX 7 3.25 Makeup Gas Driers To TSDF Sieve Spent Molecular 19 PENEX 1.19 0.595 Penex Feed Driers To TSDF Sieve VGO REACTOR/ REACTOR DIESEL 20 VGOHDT SPENT NA 500 To TSDF OPOLISHING CATALYST REACTOR Disposed to 21 CDWU Spent Catalyst NA 3.762 HCR Reactor SPCB authorised dealer Disposed to 22 CDWU Spent Catalyst NA 3.864 DW Reactor SPCB authorised dealer Disposed to 23 CDWU Spent Catalyst NA 3.621 HDF Reactor SPCB authorised dealer SR LPG Spent Catalyst from 24 Spent Catalyst NA 3.250 To TSDF Treater Reactor

44 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance SR LPG Spent Grading Bed Spent Grading Bed 25 NA 0.15 To TSDF Treater Catalyst Catalyst from Reactor Spent Catalyst from 26 HGU (Note-1) Spent Catalyst 4.5 1.583 To TSDF Hydrogenation Reactor Spent Catalyst from Predesuffurization 27 HGU (Note-1) Spent Catalyst 63 21 To TSDF Reactor A/B (Dechlorination) Spent Catalyst from Predesuffurization 28 HGU (Note-1) Spent Catalyst 18.12 505.2 To TSDF Reactor A/B (Removal of Sulfur compound) Spent Catalyst from Desuffurization 29 HGU (Note-1) Spent Catalyst 19 6.387 To TSDF Reactor (Removal of Sulfur compound) Spent Catalyst from Desuffurization 30 HGU (Note-1) Spent Catalyst 8 2.667 To TSDF Reactor (Deep Desuffurization) Spent Catalyst from 31 HGU (Note-1) Spent Catalyst 25 9.4 To TSDF Prereformer A/B Spent Catalyst from 32 HGU (Note-1) Spent Catalyst 8 5.883 To TSDF Reformer Spent Catalyst from 33 HGU (Note-1) Spent Catalyst 30 10.107 High Temp Shift To TSDF Reactor Spent Catalyst from 34 HGU (Note-1) Spent Catalyst 24 16.883 Low Temp Shift To TSDF Reactor Spent Support Material Catalyst Support from 35 HGU (Note-1) Material (Ceramic 16 5.6 Reactors,Prereformer, To TSDF balls) Reformer & Shift Reactors Catalyst Support Spent Support Material 36 HGU (Note-1) 28 9.79 To TSDF Material from

45 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No Terms of Reference Compliance (Aluminium balls) Reactors,Prereformer, Reformer & Shift Reactors HGU /PSA Spent Adsorbent from 37 Spent Adsorbent 250 51.938 To TSDF (Note-1) PSA 38 SRU Spent Catalyst 36.8 53.5 Claus reactors To TSDF 39 TGTU Spent Catalyst 15 11.34 Reactor To TSDF Catalyst Support Material Claus and TGTU 40 SRU/TGTU 8 11.4 To TSDF (Ceramic/alumina reactors balls)

Note-1: All data for HGU are preliminary for proposed case. Data given has been prorated from BS VI Panipat HGU data. Data shall be confirmed after getting data from the selected

vii. Requirement of water, power, with a. Requirement of fresh water source of supply, status of approval, 3 water balance diagram, man-power S. Water Source Required Quantity (m /hr) Extraction Approval No Existing Proposed After Expansion requirement (regular and contract) . Governor of Haryana acting through Executive Engineer, Panipat Water Service Division, Panipat made a agreement with IOCL PR & PNC on 1.04.2020 for providing fresh water from Western canal of quantity round the clock supply of Western 1 1720 2400 4120 water @30cusec (3058.2m3/hr).is attached Yamuna Canal as Annexure 10. Application has been submitted for additional fresh water requirement of 2400m3/hr to Executive engineer, Panipat Water services Division which is enclosed along with the Annexure 10 Details of Existing and Proposed Water requirement, given in Chapter 2, Section 2.9 of EIA report.

46 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report b.Water balance diagram

Existing Water Balance Diagrams

47 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Proposed Water Balance Diagrams

48 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report c.Requirement of power

Required Quantity (MW/hr) Extraction Approval Power Source Existing Proposed After Expansion Uttar Haryana Bijili Vitran Nigam Limites‟s Provisionally acceptance Import of power from grid 175 222.513 397.513 of extension of load from 70000KW to 288000KW is attached as Annexure 11 Power and Fuel requirement details provided in Chapter 2, Section 2.12

d.Requirement of manpower

Operational Phase

S. No Description Regular Contractual Total 1 Existing (Nos) 1007 720 1727 2 Proposed (Nos) 300 480 780 3 After Expansion (Nos) 1307 1200 2507 Construction phase :10,080 Nos.

viii. Process description along with a.Process description major equipment‟s and machineries, Crude oil is heated and fed into a distillation column. As the temperature of the crude oil in the distillation column rises, process flow sheet (quantitative) from the crude oil separates itself into different components, called “fractions.” The fractions are then captured separately. Each raw material to products to be provided fraction corresponds to a different type of petroleum product, depending on the temperature at which that fraction boils off the crude oil mixture. Further detailed process description in given in Chapter 2, Section 2.7 of EIA report

b.Process flow diagram

Existing:

49 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

50 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Proposed:

List of major Equipment‟s and machineries are enclosed as Annexure 12. The proposed block flow diagram in quantitative manner is enclosed as Annexure 27. Hazard identification and details of Hazard identification is the process used to identify all the possible situations in the workplace where people proposed safety systems may be exposed to injury, illness or disease. Identification of causes and type of hazards is the primary task for planning for risk assessment.

A preliminary hazard analysis is carried out initially to identify the major hazards associated with storages and

51 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report the processes of the plant. This is followed by consequence analysis to quantify these hazards.

Hazardous chemicals:

In a refinery, hazardous chemicals can come from many sources and in many forms. In crude oil, there are not only the components sought for processing, but impurities such as sulphur, vanadium, and arsenic compounds. The oil is split into many component streams that are further altered and refined to produce the final product range. Most, if not all, of these component stream chemicals are inherently hazardous to humans, as are the other chemicals added during processing. Hazards include fire, explosion, toxicity, corrosiveness, and asphyxiation. Information on hazardous materials manufactured or stored in a refinery should be supplied by the client's representative when a work permit is issued

Health and hygiene hazards

Major potential air contaminants which can escape from a typical refinery operation and their major sources. It does not attempt to identify all such possible hazards.

Parameters Major sources

Hydrocarbon Vapours –  Transfer and loading operations Compounds of Carbon  Storage tanks (C) and Hydrogen  Crude unit, atmospheric, and vacuum towers  Cracking units  Rearranging and combining processes such as Reformers and alkylation units  Treating Operations  Cracking Unit Regeneration  Heat Exchangers  Boilers & Heaters

52 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

 Pumps, Valves Cooling Towers Sulphur dioxide  Boilers  Cracking Unit Regeneration  Treating Operations  Flares Carbon monoxide (CO)  Rearranging and combining processes such as reformers and alkylation units  Catalyst Regeneration  Flares  Boiler  Furnaces Nitrogen dioxide (NO2)  flares  boilers Hydrogen sulphide (H2S)  Sour Crudes  Liquid Wastes  Pumps  Crude Tower  Cracking Operations  Re-arranging and combining processes such as reformers and alkylation unit  Hydro generation Particulates  Catalyst dusts – Cracking unit, Catalyst regeneration and rearranging and combining processes such as reformers and alkylation units  Petroleum Coke Dust – Cracking units Chlorine (Cl or Cl2)  Caustic Unit Ammonia (NH3)  Compressors

Common hazardous chemicals and chemical groups typically present and their most significant hazards to workers. MATERIAL DOMINANT HAZARD Additives – usually skin irritants Ammonia – toxic on inhalation Asbestos – designated substance under construction regulations. See chapter on asbestos in this manual. Asphalt – dermatitis (can be photosensitizer)

53 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Benzene – designated substance under industrial regulations

Carbon monoxide – toxic on inhalation Caustic soda – corrosive to skin and eyes Chlorine – corrosive to skin and tissue on contact or inhalation HBAHs (high boiling aromatic – potential carcinogens hydrocarbons) Hydrofluoric acid – corrosive to skin and tissue on contact or inhalation Hydrogen sulphide – toxic on inhalation MEK (methyl ethyl ketone) – corrosive to skin

Nitrogen – asphyxiant PAHs (polynuclear aromatic – potential carcinogens hydrocarbons) Phenol-acid – corrosive to skin and tissue Silica – designated substance under industrial regulations

Sulphuric acid – corrosive to skin and tissue on contact or inhalation Sulphur dioxide – toxic on inhalation

Care should be exercised at all times to avoid inhaling solvent vapours, toxic gases, and other respiratory contaminants. Because of the many hazards from burns and skin contact, most plants require that you wear long- sleeved shirts or coveralls

Confined spaces

On most jobsites there are potential confined space hazards. These hazards are multiplied, however, on a refinery site because of the complex collection of tanks, reactors, vessels, and ducts combined with a wide variety of hazardous chemicals and emissions, often in enclosed areas. Many of these chemicals can produce oxygen- deficient, toxic, or explosive atmospheres. Knowledge of general confined space procedures and specific in-plant requirements are both critical in refinery work. For more information, refer to the chapter on

54 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Confined Spaces in this manual.

a.Hazard identification – LPG: Liquefied petroleum gas (LPG), is a flammable mixture of hydrocarbon gases such as propane and butane

Health hazards:

Routes of entry Effects of Exposure/Symptoms Effects w.r.t concentration

Inhalation can cause headache, disorientation, dizziness, i) Concentration in air greater drowsiness and possibly than 10% causes dizziness in unconsciousness at concentrations few minutes. Inhalation & Skin that cause oxygen deficiency and ii) 1% conc. gives the same asphyxiation. symptoms in 10 metres. Rapidly expanding gas or iii) High concentration causes vaporized liquid may cause asphyxiation. frostbite to skin and eyes.

Fire hazards: Eliminate all sources of ignition, since motor spirit is highly inflammable. Keep the containers cool by spraying water if exposed to fire or heat. If the container is not sufficiently cooled it will explode in fire.

Use CO2, Dry Chemical Powder or Water Spray to extinguish fire.

Hazard ratings:

HAZARD RATING NFPA

Flammability 4 Health 1 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe

55 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

b.Hazard identification – Naphtha:

Naphtha is a flammable oil containing various hydrocarbons, obtained by the dry distillation of organic substances such as coal, shale, or petroleum.

Hazard summary: Extremely flammable. Irritating to eyes and respiratory system. Affects central nervous system. Harmful or fatal if swallowed. Aspiration Hazard.

Symptoms:

Dizziness, Discomfort, Headache, Nausea, Kidney disorders, Liver Disorders.

Health hazards:

Contact Effects

Eyes High vapor concentration or contact may cause irritation and discomfort. Brief contact may cause slight irritation. Skin irritation leading to dermatitis may occur upon Skin prolonged or repeated contact. Can be absorbed through skin. Aspiration hazard if liquid is inhaled into lungs, particularly from vomiting after ingestion. Ingestion Aspiration may result in chemical pneumonia, severe lung damage, respiratory failure and even death. Vapors or mists from this material can irritate the nose, throat, and lungs, and can cause signs and symptoms of central nervous system depression, depending on the concentration and Inhalation duration of exposure. Inhalation of high concentrations may cause central nervous system depression such as dizziness, drowsiness, headache, and similar narcotic symptoms, but no long- term effects.

56 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Long-term exposure may cause effects to specific organs, such as to the liver, kidneys, blood, Chronic nervous system, and skin. Contains benzene, which can cause blood disease, including anemia Exposure and leukemia.

Target Skin, Central nervous system, Liver, Kidney, Blood. Organs

Fire hazards:  Keep away from fire, sparks and heated surfaces because it can easily ignite with small ignition sources.  Use water spray, alcohol-resistant foam, dry chemical or carbon dioxide Do not use a solid water stream as it may scatter and spread fire. Hazard ratings:

HAZARD RATING NFPA Flammability 3 Health 1 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe

c.Hazard identification – MS:

Motor Spirit also known as Gasoline, or petrol, is a transparent, petroleum-derived liquid that is used primarily as a fuel in internal combustion engines.

Health hazards

Routes of entry Effects of Exposure/Symptoms

57 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Inhalation & Excessive inhalation Vapours cause rapid breathing, excitability, staggering, headache, Ingestion fatigue, nausea and vomiting, dizziness, drowsiness, narcosis convulsions, coma.

Skin absorption Skin-dryness, cracking, irritation eyes watering, stinging and inflammation.

Fire hazards:

 MS catches fire with any sparks or ignition sources, once it makes contact with it.  Use Foam, Carbon dioxide, Dry Chemical Powder as Extinguishers and Water is used to cool down the containers. Hazard ratings:

HAZARD RATING NFPA Flammability 3 Health 0 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe

d.Hazard identification – HSD:

HSD is normally used as a fuel in medium and high speed compression ignition engines in commercial vehicles, stationary diesel engines, locomotives and pumps etc.

Health hazards:

Routes of entry Effects of Exposure/Symptoms

Excessive inhalation Vapours cause rapid breathing, excitability, staggering, Inhalation & Ingestion headache, fatigue, nausea and vomiting, dizziness, drowsiness, narcosis convulsions, coma.

Skin absorption Skin-dryness, cracking, irritation eyes watering, stinging and inflammation.

58 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Fire hazards: HSD ignites in contact with fire, so keep the ignition sources away from it. Use Foam, Carbon dioxide, Dry Chemical Powder as Extinguishers and Water is used to cool down the containers. On fire it will be liberate some amount carbon monoxide, Sulphur dioxide Nitrogen Oxide and other aromatic hydrocarbons.

Hazard ratings:

Hazard rating NFPA

Flammability 2 Health 1 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe

Following are the proposed safety measures in the plant  Emergency isolation valves are to be provided/online monitoring via SCADA (Supervisory Control And Data Acquisition) that will closely monitor the process flow and parameters in a safe place and auto mode through gas/fire detector system.  Passive fire protection such as fire proofing shall be recommended.  Appropriate detection measures such as fire and gas detectors are recommended and the same to be deep-rooted throughout the plant area

The detailed Risk Assessment Report is enclosed as Annexure 13.

ix. Expansion/ modernization proposals Expansion (a) Copy of all Environmental Clearance(s) including Status of Status of S. No MoEF&CC File No Units Date of issue amendments thereto obtaining for Project compliance the project from MoEF&CC/SEIAA shall be 1 J-11011/27/91-IA-II(I) Setting up grassroot refinery 16-07-1992 Commissioned Complied attached as an Annexure. A

59 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report certified copy of the latest Expansion of Refinery from 2 J-11011/60/2000-IA-II 09-04-2001 Commissioned Complied monitoring report of the Regional 6 MMTPA to 12 MMTPA office of the Ministry of Integrated PX & PTA Partially 3 J-11011/52/2000-IA-II 30-04-2001 Commissioned Environment and Forests as per project complied th circular dated 30 May, 2012 on 4 Complied the status of compliance of J-11011/9/2001-IA-II(I) MS quality upgradation 06-12-2001 Commissioned conditions stipulated in all Partially existing environmental clearances complied- including Amendments shall be same as J-11011/52/2000-IA- provided. In addition, status of 5 Modification in Plant Layout 20-01-2003 Commissioned condition of II(I) compliance of Consent to Operate EC‟s obtained on 9.4.2001 & for the ongoing existing operation 30.4.2001 of the project from SPCB shall be attached with the EIA-EMP Expansion of Refinery from Partially 6 J-11011/7/2004-IA-II(I) 09-08-2004 Commissioned report 12 MMTPA to 15 MMTPA complied (b) In case the existing project has not obtained environmental BS-VI upgradation and J-11011/177/2016-IA- PX/PTA Plant, Partially 7 26-03-2018 Commissioned clearance, reasons for not taking II(I) Petrochemical Complex complied EC under the provisions of the expansion EIA notification 1994 and/or EIA EC for Panipat Refinery J-11011/177/2016-IA notification 2006 shall be 8 Capacity Expansion from 15 Ongoing Applied Now II(I) provided. Copies of Consent to MMTPA to 25 MMTPA Establish / No objection certificate and Consent to Operate (in case of units operating in prior Earlier EC‟s Attached as Annexure 3 to EIA notification 2006, CTE and CTO of FY 2005-2006) Latest EC- J-11011/177/2016-IA-II(I)dated 26-03-2018 Attached as Annexure 2 obtained from the SPCB shall be Certified Latest EC‟s Compliance report with the Action Attached along with Annexure 4 submitted. Further compliance taken report. report to the conditions of Consents from the SPCB shall be S. No Latest CTO No. Date of issue Valid till Status of compliance submitted. 1 HSPCB/Consent/: 04.05.2020 30.09.2021 Complied 313105620PITCTO7559304

60 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Latest CTO- HSPCB/Consent/: Latest CTO is attached as Annexure 5. 313105620PITCTO7559304 dated 04.05.2020 valid till Earlier CTO&CTE is attached as Annexure 6. 30.09.2021 with all CTO‟s and CTE‟s Self-certified compliance report of latest CTO submitted Attached along with Annexure 7. to HSPCB –Ref No:PR/HSE/3 dated 21.06.2021

4 Site Details i. Location of the project site The project site is situated at IOCL Panipat Refinery, PR 42-128 Gram Panchayat Baholi, Baholi Village, Panipat District, covering village, Taluka/Tehsil, District Haryana-132140. and State, justification for selecting the site. Whether other sites were considered Alternate sites were not considered since the proposed expansion is within the existing refinery complex. Adequate land is available with IOCL Panipat refinery for the proposed expansion ii. A Topo sheet of the study area of radius of 10Km and site location on 1:50,000/ 1:25,000 scale on an A3/A2 sheet (including al eco-sensitive areas and environmentally sensitive places)

No notified Eco-sensitive areas and environmentally sensitive places within 10km radius from the project boundary.

61 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Topo map in 1:50,000 scale for the study area on an A3 sheet including environmental sensitive areas/ eco-sensitive areas is given in Chapter 3, Section 3.4 of EIA report. iii. Details w.r.t option analysis for Alternate sites were not considered since the proposed expansion is within the existing refinery complex. Adequate land is selection of site available with IOCL Panipat Refinery for the proposed expansion.

iv. Co-ordinates (lat-long) of all four Co-ordinates of all four corners of the site S. No corners of the site Latitude Longitude 1 29°29'14.20"N 76°51'31.41"E

2 29°29'21.06"N 76°52'58.10"E 3 29°28'31.54"N 76°51'25.01"E

4 29°27'29.93"N 76°53'31.14"E

v. Google map Earth downloaded of Google map Earth downloaded of the project site the project site

62 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

vi. Layout maps including existing The layout indicating storage area, plant area, greenbelt area, utilities etc is appended in Chapter 2, Section 2.8, Figure unit as well as proposed unit indicating 2-8of EIA report. storage area, plant area, greenbelt area, utilities etc. If located within an industrial area/Estate/Complex, layout The project site is situated outsideindustrial area/Estate/Complex of Industrial indicating location of unit within the Industrial area/Estate. vii. Photographs of the proposed and Photographs of the proposed and existing plant site are appended inChapter 2, Section 2.8.1, Figure 2-7 of EIA report. existing (if applicable) plant site,

63 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report existing, show photographs of Green Belt Photographs are given in Chapter 2, Section 2.11, Figure 2-11 to Figure 2-15of EIA report. plantations/greenbelt, in particular viii. Land use break-up of total land of Classification of landuse of Project Site: Builtup, Urban (As per Bhuvan 2011-12) the project site (indicate and acquired), government/ private- agriculture, forest, After Proposed(Ac Percent S. No Description Existing(Acres) expansion(Acr wasteland, water bodies, settlements, etc res) (%) shall be included (not required for es) 1. Built up area 943 industrial area) 491.6 1551.6 99.36 2. Roads 117 Green belt within 3 10 0 10 0.64 premises Total 1070 491.6 1561.6 100

Details given in Chapter 2, Section 2.8.2of EIA report. ix. A list of major industries with List of major industries within the study area (10 km radius) name and type within the study area (10 km radius) shall be incorporated. Land S.No Industries Distance(~km) Direction use details of the study area) 1 HPCL Depot Adjacent to site 2 Smartchem Technologies Limited 0.22 E 3 Depot 0.3 N 4 IOCL Panipat Petrochemical Plant 0.75 SSW 5 Ambadi Enterprises Ltd 1.44 E 6 Tinna Rubber and Infrastructure Limited 1.89 E 7 Shree Ganesh Cot Spin 2.38 ESE 8 IVL Dhunseri Petrochem Industries Pvt Ltd 2.4 NNE 9 Fieldking Unit 3 2.69 ENE 10 Karnal LPG Bottling Plant IOCL 3.56 ENE 11 Dev Overseas 4.32 SE 12 Dr.Sandhu Feeds and Hatcheries 5.24 N 13 Gurdev feeds India pvt Ltd 5.36 SE 14 Birmi Industries Private Limited 6 SW 15 LC woollen mill 6.07 SE

x. Geological features and Geo- a.Geological features hydrological status of the study area The geological formation of the study area is entirely alluvium. shall be included. b.Geo-hydrological status The Geo-hydrological formation of study area in which the ground water is alkaline in nature and is fresh to moderately

64 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report saline

Further detailed Geological features and Geo-hydrological status is provided in Chapter 3, Section 3.5.6 ,Section3.5.7of EIA report.

xi. Details of drainage of the project upto 5km radius of the study area. If the site is within 1Km radius of any major river, peak and lean season river discharge as well as flood occurrence frequency based on peak rainfall data of the past 30 years. Details of Flood Level of the project site and maximum of Flood of the river shall also be provided (mega green field projects)

Drainage Map showing the study area

is one of the major canal running from NE to SE of the project site at a distance of 0.05km(S). Its start at (originally Barrage) and its source is Yamuna River. Main purpose of the canal is drinking water, irrigation & hydel power generations.  Munak Drain is running inside the refinery complex which ends at Main Drain No 2 canal.  Main Drain No 2 canal which is running adjacent to eastern side of the refinery complex leading into Yamuna River.  Canals like Thirana Minor, Khandra Drain, Madlauda Minor, Joshi Drain, Rer Kalan Minor, Goli Distributary, Munak Canal, Untala Minor are sub distributaries of Western Yamuna Canal.

65 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Details of drainage of the project upto 5km radius of the study area S.No Description Distance (~km) Direction 1 Munak Drain Adjacent to Site W 2 New Delhi Branch (Western Yamuna Canal) 0.05 S 3 Main Drain No 2/Indri Drain 0.05 E New Delhi Parallel Branch (Western Yamuna 0.1 S 4 Canal) 5 Gohana Distributary 0.1 S 6 Nahar Kuna Hansi/HanalNadi 0.19 N 7 Madlauda Minor 0.22 S 8 Thirana Minor 0.23 S 9 Khandra Drain 0.67 S 10 Begampur Minor 0.8 N 11 Joshi Drain 0.82 W 12 Untala Minor 1.78 S 13 Phurlak Drain 2.14 N 14 Tributary Drain No 1 2.32 SSW 15 Gagsina East Drain 2.62 N 16 RerKalan Minor 2.67 WNW 17 Kabir Branch/Bazida Distributary 2.7 E 18 Munak Minor 2.76 N 19 Hansi Branch(Western Yamuna Canal) 4.31 NW 20 Munak Canal 4.46 NNW 21 Goli Distributary 4.88 NNW

Details of waterbody present within 1Km radius of the study area S.No Description Distance (~Km) Direction 1 Munak Drain Adjacent to Site W 2 New Delhi Branch (Western Yamuna Canal) 0.05 S 3 Main Drain No 2/Indri Drain 0.05 E New Delhi Parallel Branch (Western Yamuna 0.1 S 4 Canal)

66 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 5 Gohana Distributary 0.1 S 6 Nahar Kuna Hansi/HanalNadi 0.19 N 7 Madlauda Minor 0.22 S 8 Thirana Minor 0.23 S 9 Khandra Drain 0.67 S 10 Begampur Minor 0.8 N 11 Joshi Drain 0.82 W

There is no major river present within the study area.

xii. Status of acquisition of land. If Land acquisition is not required as the proposed expansion is within the existing facility. acquisition is not complete, stage of the Land Documents are enclosed as Annexure 1 acquisition process and expected time of complete procession of the land. xiii. R&R details in respect of land in Not applicable. line with state Government policy The project site is located in existing refinery land area.

5 Forest and wildlife related issues (if applicable): i. Permission and approvals for the Not Applicable, since no forest land involved. use of forest land (forestry clearance), if any, and recommendations of the State Forest Department (if applicable) ii. Land use map based on High Not Applicable, since no forest land involved. resolution satellite imagery (GPS) of the proposed site delineating the forest land (in case of projects involving forest land more than 40 Ha) iii. Status of application submitted Not Applicable, since no forest land involved. for obtaining the stage I Forestry Clearance along with latest status shall be submitted iv. The projects to be located within Not Applicable since no National parks, Sanctuaries, Biosphere Reserves, Migratory Corridors of Wild Animals in 10km 10 Km of the National parks, Sanctuaries, radius from the project boundary.

67 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Biosphere Reserves, Migratory Corridors of Wild Animals, 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. v. Wildlife Conservation Plan duly Not Applicable authenticated by the Chief Wildlife Warden of the State Government for conservation of schedule I fauna, if any exists in the study area. vi. Copy of application submitted for No notified Sanctuaries/ National Parks/ Eco-sensitive zones within the 15km radius from the project boundary. clearance under the Wildlife (Protection) Not Applicable Act, 1972 to the Standing Committee of the National Board for Wildlife. 6 Environmental Status i. Determination of atmospheric The Peak inversion level at the project site varies from 50 to 4000m during 6 AM to 5 PM, the maximum recorded at 5 inversion level at the project site and PM, April 2019. Details given in Chapter 3, Section 3.7.5of EIA report. site-specific micrometeorological date using temperature, relative humidity, Meteorological Data for the Study Period (March - May 2019) hourly wind speed and direction and S. No Parameter Observation 0 rainfall 1. Temperature Max Temperature: 45 C Min Temperature: 100C Avg Temperature: 31.280C 2. Average Relative Humidity 43.91% 3. Average Wind Speed 2.8 m/s 4. Predominant Wind Direction North West

ii. AAQ data (except monsoon) at 8 The ambient air quality have been monitored at 8 locations for 14 parameters as per NAAQS/CPCB guidelines within the

locations for PM10, PM2.5, SO2, NOX, study area.

CO and other parameters relevant to The average baseline levels of PM10 (83.59 – 128µg/m³), PM2.5 (42.7 – 64.98µg/m³), SO2(14.92 – 22.83µg/m³), the project shall be collected. The NO2(27.89 – 43.71µg/m³) and CO (610 – 780µg/m³). monitoring stations shall be based on The nearest HSPCB AAQ monitoring station is Sector-18, Panipat in which the maximum and minimum levels for the

68 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

CPCB guidelines and take into period March to May 2019 is PM10 (487.59 and 29.52µg/m³), PM2.5 (131.87 and 15.96 µg/m³), SO2 (148.33 and 5.82 account the pre-dominant wind µg/m³), NOx (120.5 and 11.87 ppb) and CO (77.44 and 0.14 mg/m³). The average values of same station for the above direction, population zone, sensitive period is PM10 (169.49µg/m³), PM2.5 (47.27µg/m³), SO2 (30.56 µg/m³), NO2 (48.86ppb) and CO (11.13 mg/m³).

receptors including reserved forests. All the parameters are well within the National Ambient Air Quality Standards for during the study period from March 2019 - May 2019 except PM10 and PM2.5 .

AAQ locations detail is provided in the Chapter 3, Section 3.8.1and monitoring results are provided in the Section 3.8.2of EIA report.

iii. Raw data of all AAQ measurement for Raw data of all AAQ measurement for 12 weeks of all stations as per frequency given in the NAAQM notification of 12 weeks of all stations as per Nov. 2009 along with- min-max, average and 98% values for each of the AAQ parameters from data of all AAQ stations frequency given in the NAAQM are provided as Annexure 14. 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 iv. Surface water quality of nearby River Surface water sampling locations (100m upstream and downstream of discharge point) and other surface S. No Location Location Code Distance in ~Km Direction 1 Main drain no 2 u/s near project site SW1 0.09 NE drains at eight locations as per CPCB/ 2. Main drain no 2 d/s near Razapur SW2 2.31 E MoEF&CC guidelines. 3 Western Yamuna canal d/s near Sithana SW3 0.98 SE 4 Pond near Khukrana SW4 6.82 S 5 Pond near Assan kalan SW5 5.61 S 6 Western Yamuna canal u/s SW6 0.42 W 7 Pond near Paban Hasanpur SW7 7.66 NW 8 Pond near Gagsina SW8 7.25 N

69 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Surface water quality results of nearby River

Surface water Standard Limit Parameter sample Class A Class B Class C Class D Class E pH 7.05 to 7.73 8.5 8.5 8.5 8.5 8.5 Total Dissolved Solids 203 to 1279 mg/l 500 - 1500 - 2100 (TDS) Hardness 115.1 – 554.2 mg/l. 300 - - - - BOD 1.4 - 10mg/l 2 3 3 - - COD 4 to 56 mg/l - - - - -

Class A- Drinking water without conventional treatment but after disinfection. Class B-Water for outdoor bathing. Class C- Drinking water with conventional treatment followed by disinfection. Class D-Water for fish culture and wild life propagation. Class E-Water for irrigation, industrial cooling and controlled waste disposal

Surface water quality of nearby River and other surface drains at eight locations as per CPCB/ MoEF&CC guidelines are collected & analyzed and the details are provided in the Chapter 3, Section 3.10.2ofEIA report.

v. Whether the site falls near to polluted No Polluted stretch of river identified as per CPCB within 10km radius from the project site. stretch of river identified by the CPCB/MoEF& CC, if yes give details vi. Ground water monitoring at minimum Ground water monitoring results at 8 locations 8 locations shall be included Standard Limit Parameter Range of Results Acceptable Limit Permissible Limit pH 7.35 to 8.01 6.5-8.5 No Relaxation Total Dissolved Solids (TDS) 386 mg/l –820 mg/l 500mg/l 2000 mg/l Fluoride 0.17 mg/l – 1.30 mg/l 1mg/l 1.5 mg/l Hardness 220 mg/l – 470mg/l 200mg/l 600 mg/l  Total alkalinity as calcium carbonate, Magnesium and Chloride are well within the limits  The heavy metals concentrations are below detection limits and all are well within the limits

Ground water monitoring at minimum 8 locations are collected & analyzed. Futher detailed Ground water monitoring

70 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report results were provided in theChapter 3, Section 3.10.3of EIA report.

vii. Noise levels monitoring at 8 locations Noise levels monitoring results at 8 locations within the study area within the study area. Day Time (dB(A)) Night Time (dB(A)) Site Results Standards Re ults Standards Industrial areas (Project site) 69.4 75 60.5 70 Residential area (Dharamgarh, Barauli, Razapur, New 47.5 to 41.5 to 55 45 Bahauli, Madlauda, Panipat, Munak) 54.8 44.7

Noise levels monitoring at 8 locations within the study area are collected &analysed. Further detailed Noise level monitoring results were provided in the Chapter 3, Section 3.9of EIA report.

viii. Soil characteristics as per CPCB Soil characteristics as per CPCB guidelines guidelines  The pH of the soil samples ranged from 7.19 to 7.96, indicating the soils are neutral to moderately alkaline in nature.  Conductivity of the soil samples ranged from 280 to 4410µmho/cm.  Nitrogen content ranged from 733.4 mg/kg to 953 mg/kg.  Phosphorous ranged from 2.2 mg/kg to 15.7 mg/kg.  Potassium content ranges from 9.92 mg/kg to 97.60mg/kg.

Further detailed Soil characteristicsare analysed as per CPCB guidelines are provided in theChapter 3, Section 3.11 of EIA report.

ix. Traffic study of the area, type of Existing & Proposed Vehicular movement per peak hour vehicles, frequency of vehicles for Total vehicles PCU Total PCU transportation of materials, additional Propose S. Type of Existing Existing Propose after Factors after project traffic due to proposed project, parking d No Vehicle vehicles PCU d PCU project IRC (SP implementati arrangement etc. vehicles implementa 41) on tion 1 2 wheeler 97 72.75 0 0 97 0.75 72.75 2 3 wheelers 11 13.2 0 0 11 1.2 13.2

71 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 4 3 82 82 40 40 122 1 122 wheelers/cars 4 truck/Lorry 21 77.7 20 74 41 3.7 151.7 agricultural 5 46 230 0 0 46 5 230 tractor light emission 6 10 14 0 0 10 1.4 14 vehicle 267 489.65 60 114 327 603.65

Traffic Volume after Implementation of the Project Road Volume of Volume LOS Traffic For the Road Capacity V/C Ratio Traffic (V) Category* Classification (C) Existing 267 489.65 3600 0.14 “A” Free Flow Traffic After 357 603.65 3600 0.17 “A” Free Flow Traffic implementation

*LOS (Level of Service) categories are A-Free Flow, B- Reasonably Free Flow, C-Stable Flow, D-Approaching unstable flow, E- Unstable flow, F- Forced or breakdown flow. Due to propose project there will be slight increment in the vehicle movement but the level of service (LOS) anticipated will be Free Flow Traffic.

x. Detailed description of flora and fauna a.Flora (terrestrial and aquatic) existing in the study area shall be given with special  A total 173 species under 58 families observed based on secondary source. reference to rare, endemic and  No endangered species are found in the study area endangered species. If Schedule-I b.Fauna fauna and found within the study area, There are four near threatened bird in the study area i.e., named Mycteria leucocephala, Ephippiorhynchus asiaticus, a Wildlife Conservation plan shall be Threskiornis melanocephalus and Psittacula eupatria prepared and furnished . Flora and Fauna study is carried out found within the 10km radius study area and the details are provided inChapter 3, Section 3.12

xi. Socio-economic status of the study Socio-economic status of the study area area S.No Particulars Study area Unit

72 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 1 Number of villages in the Study Area 59 Nos. 2 Number of Towns in the Study Area 7 Nos. 3 Total Households 124375 Nos. 4 Total Population 624417 Nos. 5 Children Population (<6 Years Old) 47188 Nos. 6 SC Population 108599 Nos. 7 ST Population 0 Nos. 8 Total Working Population 210197 Nos. 9 Main Workers 180839 Nos. 10 Marginal Workers 29358 Nos. 11 Cultivators 22601 Nos. 12 Agricultural labours 25826 Nos. 13 Household Industries 9144 Nos. 14 Other Workers 152626 Nos. 15 Literates 425334 Nos.

Further detailed socio-economic status of the study area is provided in the Chapter 3, Section 3.13 of EIA report.

7 Impact and Environmental Management Plan

i. Assessment of ground level The ground level concentration of pollutants (PM10, PM2.5, SO2&NOx) using AERMOD software were assessed and concentration of pollutants from the presented in Chapter 4 Section 4.5 of EIA report. stack emission based on site-specific meteorological features. In case the AERMOD Software Version 8.0.5 was used for air dispersion modeling and is applicable to a wide range of buoyant or project is located on a hilly terrain, neutrally buoyant emissions up to a range of 10 km. The air quality contours shall be plotted on a location map showing AQIP modeling shall be done using the location of the project site are shown in GLCs for proposed is given in Chapter 4 Section 4.5 of EIA report inputs of the specific terrain characteristics for determining the Total Maximum GLCs from the Stack Emissions potential impacts of the project on the Pollutant Max. Base Estimated Incremental Total Conc. (µg/m3) NAAQ % increase AAQ. Cumulative impact of all line Conc. Conc. (µg/m3) standard sources of emissions (including (µg/m3) (µg/m3) transportation) on the AAQ of the PM 128 2.89 130.89 100 2.26 area shall be assessed. Details of the SO2 22.83 30.52 53.35 80 133.68 model used and the input data used NOx 43.71 22.29 66 80 51.00 for modelling shall also be provided. CO 780 30.66 810.66 4000 3.93 The air quality contours shall be

73 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report plotted on a location map showing Total Maximum GLCs from the Line Emissions the location of project site, habitation Pollutant Max. Base Estimated Incremental Total Conc. (µg/m3) NAAQ % increase nearby, sensitive receptors, if any. line Conc. Conc. (µg/m3) standard (µg/m3) (µg/m3) PM 128 0.12 128.12 100 0.09

NOx 43.71 4.88 48.59 80 11.16 CO 780 500.68 1280.68 4000 64.19

Total Maximum GLCs from the Cumulative Emissions Max. Base NAAQ Estimated Incremental Pollutant line Conc. Total Conc. (µg/m3) standard % increase Conc. (µg/m3) (µg/m3) (µg/m3) PM 128 2.90 130.9 100 2.27 SO2 22.83 30.52 53.35 80 133.68 NOx 43.71 22.29 66 80 51.00 CO 780 501.68 1281.68 4000 64.32

ii. Water Quality modelling - in case of Treated effluent from PTA ETP is discharged in Thirana drain which have a valid CTO- discharge in water body. No.HSPCB/Consent/313105620PITCTO7559304 for discharge quantity of 255m3/hr, meeting the quality parameters as per the standards. The logbook of daily discharge into Thirana Drain and the treated effluent test report from NABL & MoEF accredited lab- Nitya Laboratories is attached as Annexure 28.

The effluent disposing into the Thirana drain is coming from the PX-PTA plant. However under this proposed project the treated effluent followed by RO treatment, MEE and ATFD and reused in process steam generation. iii. Impact of the transport of raw Material Handling, Storage and Transportation material and end products on the  Hazardous chemicals will be stored in closed tanks and drums with appropriate blanketing systems. surrounding environment shall be  All transfers from drums / tanks will be done through pumps in closed pipelines. assessed and provided. In this regard,  The loading of finished products to trucks and drums will be done through automated filling systems with options for transport of raw materials overflow protections.

74 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report and finished products and wastes  All key raw materials will be charged to the reactors through closed pipeline systems including pneumatic (large quantities) by rail or rail-cum systems for solid handling. road transport or conveyor-cum-rail  Raw materials/ intermediates/ products will be stored in closed tanks/drums provided with breather arrangements transport shall be examined. to avoid fugitive emissions.

Further details are given in Chapter 10 Section10.5.6 of EIA report. iv. A note on treatment of waste water a.Wastewater management: from different plant operations, extent recycled and reused for Unit Existing (m3/hr) Proposed (m3/hr) After expansion (m3/hr) different purposes shall be included. Effluent generation 1030 362 1392 Complete scheme of effluent Treated water Reused 1515 841 2356 treatment, characteristics of untreated

and treated effluent to meet the Existing prescribed standards of discharge Approx. 1030 m3/hr of effluent and 235 m3/hr of sewage is generated in the existing facility which is reused back in RO under E(P) rules. plant and Cooling tower. The quantity of 775 m3/hr is treated in ETP-1 and 2 and being completely reused in RO plant and Cooling tower. Remaining 255m3/hr is treated in the PTA-ETP and Treated effluent from PTA ETP is discharged in Thirana drain (vide permission- No.HSPCB/Consent/:313105620PITCTO7559304 dated 04-05-2020). The 235 m3/hr of sewage is generated in which 125 m3/hr is sent to horticulture and balance is sent to ETP for treatment. Proposed Due to the proposed expansion Approx. 362 m3/hr of effluent and 9 m3/hr of sewage are generated in the existing facility. The Effluent of 360m3/hr is reused back for process steam generation, 2m3/hr of sludge is generated which will be disposed off in scientific manner and sewage of 9 m3/hr is reused back for Green Belt. Rejects of 48 m3/hr effluents from RO/DM is directed to MEE and to ATFD, finally remaining 4 m3/hr of effluent as salt from ATFD is discharged to Disposal Facilities.

b.Characteristics of effluent being generated

S. No. Parameter units ETP-1 ETP-2 PTA-ETP 1 Oil % 0.1 0.1 NA 2 COD mg/L 1000 1000 6800 3 BOD mg/L 500 500 4700 4 TSS mg/L 150 150 1800 5 Phenol mg/L 30 30 -- 6 Sulfide mg/L 60 60 --

75 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 7 Cyanide mg/L 5 5 --

c.Characteristics of the treated effluent

S. No. Parameter units ETP-1 ETP-2 PTA-ETP 1 PH -- 6-8.5 6-8.5 6.5-8.5 2 Oil mg/L 5.0 5.0 NA 3 COD mg/L 125.0 125.0 250 4 BOD mg/L 15.0 15.0 30 5 TSS mg/L 20.0 20.0 100 6 Phenol mg/L 0.35 0.35 1.0 7 Sulfide mg/L 0.5 0.5 2.0 8 Cyanide mg/L 0.2 0.2 0.20

Note: 1. Treated water from ETP- 1&2 is going to the DM-RO Plant which has tertiary facilities along with UF& RO

2. PTA-ETP outlet water is discharging in Thirana Drain which have a valid CTO- No.HSPCB/Consent/313105620PITCTO7559304 for discharge quantity of 255m3/hr. The logbook of daily discharge into Thirana Drain and the treated effluent test report from NABL & MoEF accredited lab- M/s. Nitya Laboratories is attached as Annexure 28.

The effluent treatment scheme is given in Chapter 2 Section 2.14, Figure 2-17 and Figure 2-18of EIA report.

Wastewater treatment and disposal details are provided in the Chapter 4, Section 4.7of EIA report.

v. Details of stack emission and action Existing stack emission plan for control of emissions to meet Emission(g/s) S.no Existing Stack details standards. PM (g/sec) SO2 (g/sec) NOx (g/sec) CO (g/sec) A Panipat refining unit

1 RFCC Heater 0.0380 0.1479 0.4250 0.0851 2 RFCC Boiler 0.2431 1.1861 3.0435 0.7904 3 AVU- 1 1.2370 4.8774 9.8125 1.9198 B MCR

4 OHCU- Recycle gas Heater 0.1097 0.3090 0.8758 0.1427 5 OHCU LP Section 0.3004 1.3114 2.9498 0.5985 6 DHDS- Furnace 0.0721 0.3572 0.8727 0.2031

76 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 7 CCRU stack- FF101, FF 102 FF 204 0.2833 1.2237 2.5233 0.5120 8 CCRU Stack- FF 201, FF 202 FF 203 0.1536 0.7611 1.2068 0.2640 9 CCRU Stack- FF 205 0.0816 0.3543 0.8081 0.1685 10 VBU 0.0766 0.4044 0.6146 0.1837 11 HGU 0.5576 1.7731 4.0875 0.8401 C PR Expansion Unit

12 HCU Unit 0.1867 0.5833 1.1249 0.2148 13 AVU- 2 1.4230 5.9684 11.0780 2.7196 D Hydrogen Generation Unit

14 HGU-PDS 0.1766 0.5039 1.2673 0.2694 15 HGU-76 0.5775 1.9369 5.0540 1.2484 16 HGU-77 0.7316 2.2560 5.1867 1.0362 E Diesel Hydrotreater Unit

17 DHDT-72 Heater 01 0.1599 0.6780 1.5773 0.4095 18 DHDT-72 Heater 02 0.1892 0.8666 1.7721 0.4956 F Paraxylene Aromatic Section

19 CCR-Heater 0.1614 0.6839 1.2775 0.2842 20 NHT Heater 0.0377 0.2127 0.3521 0.0809 21 Xylene Charge Heater 0.1610 0.6546 1.5215 0.3200 22 Isomer Charge Heater 0.0525 0.2839 0.6412 0.0710 23 Tatoray charge Heater 0.0580 0.2407 0.6150 0.1287 G Thermal Power Station

24 HRSG 01 0.6218 2.0295 6.3700 0.6541 25 HRSG 02 0.5819 1.9405 6.6619 0.6132 26 HRSG 03 0.5093 2.6734 7.0993 0.7628 27 HRSG 04 0.5429 2.2003 6.8771 0.6736 28 HRSG 05 0.5495 1.9566 6.7801 0.5033 29 VHP Boiler 01 0.5142 1.9894 5.1728 0.6629 30 VHP Boiler 02 0.6681 2.3478 5.4824 0.6420 31 Utility Boiler 02 0.7359 3.0921 6.5794 0.7282 H Pur. Teraphthalic AC-Aromatic section

32 Fired combustion preHeater 0.3354 0.9515 2.7727 0.2312 33 Hot oil heater 0.2463 0.7994 2.2975 0.4662 34 thermal Oxidizer 0.0733 0.1573 0.5739 0.0794 I Delayed Coker Unit

35 DCU 0.0679 0.2413 0.3974 0.1012 J MS Quality Unit

77 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 36 HDS (303 Heater 201) (MSQ) 0.2495 0.7792 1.6795 0.4410 37 NHT (301 H101) - - - - 38 Old SRU-22/44 - - - - 39 CPP VHP-3 - - - - 40 SRU-26 - - - - 41 New SRU -57 - - - - 42 UB-1 - - - - 43 BBU Heater - - - - 44 BBU incinerator - - - - 45 NSRU - - - - K BS-VI - - - - 46 Prime G - - - - 47 DHDT - - - - 48 HGU - - - -

Proposed Stack emission S.No Stack connected to Flue gas Flow Emission per stack (g/s)

Rate (Nm3/hr) PM SO2 NOx CO 19. AVU (CDU/VDU) 257400 0.751 50.8 13.829 8.297 20. VGO - HDT 89750 0.125 0.306 4.778 1.972 21. Diesel Hydrotreater Unit 41430 0.058 0.142 2.208 0.908 22. MS Block_Charge Heater 92520 0.129 0.319 4.931 2.031 23. NHT Charge Heater 25380 0.035 0.086 1.353 0.556 24. Naphtha Stripper reboiler Heater 17260 0.024 0.058 0.919 0.378 25. CDWU_HCR Reactor Feed Heater 5700 0.008 0.019 0.297 0.131 26. CDWU_DW Reactor feed Heater 4150 0.006 0.014 0.217 0.094 27. CDWU_Vaccum Column Feed 18300 0.025 0.064 0.975 0.403 Furnace 28. Resid Hydrocracking Unit 53160 0.074 0.183 2.833 1.167 (RHCU) 29. Resid Hydrocracking Unit 8630 0.012 0.031 0.469 0.206 (RHCU)_Vaccum Heater 30. IndmaxFCC_Fresh Feed Furnace 38500 0.053 0.133 2.050 0.844 31. IndmaxFCC_Flue Gas cooler 260750 3.622 3.711 6.084 7.189

78 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 32. Sulpur recovery unit (SRU) 216570 0.037 17.889 5.464 4.925 33. Spent Acid Recovery unit 3850 0.005 0.047 0.233 0.094 (SARU)_APH System & Stack 34. Spent Acid Recovery unit (SARU)_Decomposition furnace 18790 0.159 2.000 0.778 0.467 burner 35. Hydrogen Generation Unit 155111.13 0.732 2.256 5.186 1.036 36. CPP Stack 871660 11.555 101.795 78.190 22.303 Total(g/s) 17.41 179.853 130.794 53.001 Total (kg/hr) 62.676 647.4708 470.8584 190.8036

Further details of stack emission are provided in theChapter 4 Section4.5.4 of EIA report.

Details of action plan for control of emissions:

 Low sulphur fuels will be used for internal fuel purpose.  Heaters/furnaces will be provided with well proven Low NOx burners to reduce the emissions of Nitrogen Oxides (NOx).  Under normal circumstances, there will be no continuous/intermittent point releases of volatile hydrocarbon streams. However, if during startup/shut down or an emergency situation any hydrocarbon streams are released, they will be directed to an elevated flare for complete combustion. This will eliminate the possibility of forming an explosive mixture due to sudden release of unburned hydrocarbons to the atmosphere.  The flares elevation will be such that there will be no impact of thermal radiation on the operating personnel in the refinery.Further, to ensure smokeless and non-luminous flaring, the steam provision at the flare tip is also envisaged..  The refinery complex is designed in such a way that the total emissions from the refinery complex will meet all the applicable standards/stipulations. vi. Measures for fugitive emission Details of action plan for control of emissions control  Minimum number of flanges, valves, etc.  High grade gasket material for packing.  Usage of state-of-the-art low leakage valves preferably with bellow seals.  Usage of pumps with Double Mechanical seals for light hydrocarbon services.  Provisions of floating roof storage tanks.

79 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report  Provisions of double seal in some of storage tanks.  Provision of covering the oil-water separation units in ETP.  Provision of seals in the drains and manholes. IOCL Panipat Refinery has VOC Monitoring system in Existing Refinery and VOC facility in proposed Effluent Treatment Plant will be installed in Proposed expansion.

vii. Details of hazardous waste Hazardous waste management: generation and their storage, Hazardous waste materials will be properly disposed as per the Hazardous Wastes (Management, Handling and utilization and management, Copies Transboundary Movement) Rules 2016; Hazardous waste authorization has been made with SPCB, Haryana is enclosed of MOU regarding utilization of solid as Annexure-9.Hazardous waste generated and disposal given in chapter 2, Section 2.16 of EIA report and hazardous waste in cement plant also be included. EMP shall include S. Quantity (MTPA) Source of Waste Mode of Plant Waste category the concept of waste-minimization, No. Existing Proposed generation Disposal/Facility recycle/ reuse/recover techniques, Disposed to Energy conservation, and natural 1 DHDT Spent Catalyst 134 175 DHDT SPCB authorised resource conservation. dealer CCR Catalyst Fines from Disposed to Spent Catalyst 2 Regeneration 0.85 1.58 Spent Catalyst Fines SPCB authorised Fines Section Collection Pot dealer CCR Disposed to Spent catalyst from 3 Platforming Spent Catalyst 7.25 4.173 SPCB authorised Reactors Process Unit dealer CCR Net GAS Chloride 4 Platforming Spent Adsorbent 0.6 31.2 To TSDF Treaters Adsorbents Process Unit CCR Fuel gas Chloride 5 Platforming Spent Adsorbent 4.25 1.8 To TSDF Adsorbent Process Unit CCR LPG Chloride 6 Platforming Spent adsorbent 0.05 1.26 To TSDF Treatment Adsorbent Process Unit CCR Debutanizer feed 7 Platforming Spent Adsorbent 10.2 33.26 To TSDF Chloride Treater Process Unit Indmax equilibrium INDMAX 8 Spent Catalyst 50 839.5 catalyst (E-cat) is To TSDF FCC withdrawn from

80 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Indmax FCC unit. Propylene Adsorbents from 9 Spent adsorbent 10 20 To TSDF Recovery unit Propylene Driers Propylene Adsorbent from Arsine 10 Spent adsorbent 20 11 To TSDF Recovery unit Guard Bed HCU/RHCU Spent catalyst 11 Reaction Spent Catalyst 136.5 5.256 withdrawn from the To TSDF Section reactors UOP Naphtha Spent Catalyst from 12 Hydrotreating Spent Catalyst 1.4 4.5 To TSDF Reactor Process Unit Disposed to Spent Catalyst From 13 PENEX Spent Catalyst 1.4 2.96 SPCB authorised Reactor A dealer Disposed to Spent Catalyst From 14 PENEX Spent Catalyst 10.25 1.48 SPCB authorised Reactor B dealer Disposed to Spent Catalyst From 15 PENEX Spent Catalyst 5.125 0.987 SPCB authorised Reactor C dealer Disposed to Spent Catalyst from 16 PENEX Spent Catalyst 4 0.312 SPCB authorised Methanator Reactor dealer Makeup Gas Chloride 17 PENEX Spent Adsorbent 4 0.45 To TSDF Treater Spent Molecular 18 PENEX 7 3.25 Makeup Gas Driers To TSDF Sieve Spent Molecular 19 PENEX 1.19 0.595 Penex Feed Driers To TSDF Sieve VGO REACTOR/ REACTOR DIESEL 20 VGOHDT SPENT NA 500 To TSDF OPOLISHING CATALYST REACTOR Disposed to 21 CDWU Spent Catalyst NA 3.762 HCR Reactor SPCB authorised dealer Disposed to 22 CDWU Spent Catalyst NA 3.864 DW Reactor SPCB authorised

81 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report dealer Disposed to 23 CDWU Spent Catalyst NA 3.621 HDF Reactor SPCB authorised dealer SR LPG Spent Catalyst from 24 Spent Catalyst NA 3.250 To TSDF Treater Reactor SR LPG Spent Grading Bed Spent Grading Bed 25 NA 0.15 To TSDF Treater Catalyst Catalyst from Reactor Spent Catalyst from 26 HGU (Note-1) Spent Catalyst 4.5 1.583 To TSDF Hydrogenation Reactor Spent Catalyst from Predesuffurization 27 HGU (Note-1) Spent Catalyst 63 21 To TSDF Reactor A/B (Dechlorination) Spent Catalyst from Predesuffurization 28 HGU (Note-1) Spent Catalyst 18.12 505.2 To TSDF Reactor A/B (Removal of Sulfur compound) Spent Catalyst from Desuffurization 29 HGU (Note-1) Spent Catalyst 19 6.387 To TSDF Reactor (Removal of Sulfur compound) Spent Catalyst from Desuffurization 30 HGU (Note-1) Spent Catalyst 8 2.667 To TSDF Reactor (Deep Desuffurization) Spent Catalyst from 31 HGU (Note-1) Spent Catalyst 25 9.4 To TSDF Prereformer A/B Spent Catalyst from 32 HGU (Note-1) Spent Catalyst 8 5.883 To TSDF Reformer Spent Catalyst from 33 HGU (Note-1) Spent Catalyst 30 10.107 High Temp Shift To TSDF Reactor Spent Catalyst from 34 HGU (Note-1) Spent Catalyst 24 16.883 Low Temp Shift To TSDF Reactor Catalyst Support Spent Support Material 35 HGU (Note-1) 16 5.6 To TSDF Material (Ceramic from

82 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report balls) Reactors,Prereformer, Reformer & Shift Reactors Spent Support Material Catalyst Support from 36 HGU (Note-1) Material 28 9.79 Reactors,Prereformer, To TSDF (Aluminium balls) Reformer & Shift Reactors HGU /PSA Spent Adsorbent from 37 Spent Adsorbent 250 51.938 To TSDF (Note-1) PSA 38 SRU Spent Catalyst 36.8 53.5 Claus reactors To TSDF 39 TGTU Spent Catalyst 15 11.34 Reactor To TSDF Catalyst Support Material Claus and TGTU 40 SRU/TGTU 8 11.4 To TSDF (Ceramic/alumina reactors balls)

Note-1: All data for HGU are preliminary for proposed case. Data given has been prorated from BS VI Panipat HGU data. Data shall be confirmed after getting data from the selected

viii. Proper utilization of fly ash shall be Furnace oil/ Natural Gas is used as fuel in the boiler; hence there is no fly ash generation ensured as per Fly Ash notification, 2009. A detailed plan of action shall be provided. ix. Acton plan for the green belt Existing: development plan in 33% area i.e., S. No Location Acres land with not less than 1500 trees per Ha. Giving details of Species, width 1 Polishing Pond+Eco park 92 of plantation, planning schedule etc. 2 Green Belt between PR and PNC 358 shall be included. The green belt shall be around the project boundary and a 3 RWTP Old 10 scheme for greening of the roads 4 Refinery Boundary 79 used for the project shall also be Total 539 incorporated. Note: RWTP OLD Green belt is within PR Boundary and others are adjacent of PR.

83 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Proposed:

S. No Location Acres 1 Gwalara (Avenue plantation)*(~25.68km, S from the project boundary) 86 Total 86

After expansion:

S.No Description Acres

1 Existing 539

2 Proposed 86

3 Total After expansion 625 (40% of 1561.6 acres)

Note:

Total Land area =1561.6 Acres (625 acres (40%)have been provided for green belt including avenue plantation)

Existing & Proposed Green belt species:

S.No Description S.No Description 1 Kaijici 20 Alestonia 2 Legestovia 21 Nimboo 3 Jaerenda 22 Aeralvpornis 4 Legestonia 23 Amal Tas 5 Shisham 24 Amrud 6 Papri 25 Benjamin 7 Anaar 26 Kadavb 8 Neem 27 Cassia galuca 9 Chukresia 28 Cassia shamia

84 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 10 Budr 29 Kussum 11 Kaehvav 30 Safeda 12 Aovla 31 Toon 13 Pipal 32 Poplar 14 Jamun / Jamoa 33 Bail Patthar 15 Gulmohar 34 Guddal 16 Kauair 35 Casuarinas 17 Arjun 36 Chandni 18 Bottle bram 37 Siros 19 Bogan bail

SNO Description Existing Proposed Total 1 Total area of Green 539 86 625 Belt (Acre) 2 Percentage of total 34.5 5.5 40 project area (%) 3 No. of Plants (nos.) 6,50,000 34,400 6,84,400 4 Funds allocated 1820 96.32 1916.32 (Lakhs)

Further details of Green Belt data is given in Chapter 2, Section 2.11of EIA report. The existing and proposed green belt layout is enclosed as Annexure 16

x. Action plan for rain water harvesting Rainwater Harvesting will be implemented at project site to conserve rainwater. Roof top area, greenbelt/ green area, measures at plant site shall be road/paved area and open areas proposed in the project site are considered for rainwater which can be harvested. There are submitted to harvest rainwater from 21nos. of rainwater harvesting pits available within the IOCL Panipat Refinery township and 8nos of rainwater harvesting the roof tops and storm water drains pit available in refinery complex. Additionally 34 nos of rainwater harvesting pits completed in IOCL Panipat refinery to recharge the ground water and also complex. The total catchement area on roof top is 78087 m2. to use for the various activities at the Rain water harvesting facilities are attached as Annexure 18. project site to conserve fresh water and reduce the water requirement from other sources. xi. Total capital cost and recurring cost Capital cost and Recurring cost /annum for environmental pollution control measures /annum for environmental pollution control measures shall be included. S. No. Activity Capital Cost(Lakhs) Recurring Cost(Lakhs)

85 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 1 Air Pollution i.Stack 400 126.76 ii.APC equipment 50 2 Water Pollution i.ETP 26925 2269.15 ii.STP 500 3 Noise Pollution i.Acoustic Enclosure 10 - 4 Solid waste management 80 331.14 5 Storm Water management/ Rain water harvesting 100 2 6 Greenbelt Development 96.32 13.69 28161.32 2742.74

xii. Action plan for Post-project Action plan for Post-project environmental monitoring environmental monitoring shall be submitted S. Particulars Frequency of Parameters for Monitoring No monitoring 1. Air pollution monitoring Ambient air quality within the Continuous PM, SOX, NOX, CO, HC, VOC premises (CAAQMS) Ambient air quality within the Twice in week All 12 parameters as given in NAAQS premises Ambient air quality at 1 location in Twice in week All 12 parameters as given in NAAQS Prevalent Down Wind Direction Ambient air quality at 1 location in Twice in week All 12 parameters as given in NAAQS Up Wind Direction Stack monitoring Once in two months PM, SOX, NOX, CO for all the stacks and monthly for SRU as per CPCB norms 2. Noise monitoring

86 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report At four locations within the Once in a month Noise Levels in dB(A) premises

3. Ground water quality monitoring Three locations at site and two Quarterly Physicochemical properties, Heavy location outside site metals 4. Soil Quality monitoring Two locations at site and two Half yearly Physicochemical properties, Nutrients, location outside site Heavy metals 5. Effluent Quality Monitoring Inlet and outlet of ETP Once a month As per MINAS Standard Inlet and out let of STP No STP Sewage is Biologically treated as a part of the CETP and standards are met. 6. Work place Monitoring Quarterly Noise, VOC, Lux levels

xiii. Onsite and offsite Disaster (natural The Risk Assessment has been carried out by using the PHAST software . Risk Assessment report and is attached as and Man-made) preparedness and Annexure 13. Emergency Management Plan On-site emergency plans and offsite Disaster management with ERDMP enclosed as Annexure 19. including Risk Assessment and damage control. Disaster Management Plan should be linked with District Disaster Management Plan. 8 Occupational Health i. Plan and fund allocation to ensure the All the occupational health related expenditure of casual & contract workers incorporated in the scope of contractor and occupational health & safety of all compliance to the statutory rules in this regard is ensured. Approximate cost for OHC checkup is Rs. 5764 per person. contract and casual workers IOCL PR has no tie up with any hospital for their OHC.

M/s IOCL, PR, Safety, Health and Environment Policy (SHE) provided in Chapter 10, Section 10.10 of EIA report. ii. Details of exposure specific health The specific health status evaluation of worker‟s medical report is enclosed as Annexure 21.. status evaluation of worker. If the worker‟s health is being evaluated by

87 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report pre-designed format, chest x-rays, Audiometry, Spirometry, Vision testing (Far and near vision, color vision and any other ocular defect), ECG, during pre-placement and periodical examinations give the details of the same. Details regarding last month analyzed data of above mentioned parameters as per age, sex, duration of exposure and department wise. iii. Details of existing Occupational & Main Hazards identified within the refinery complex are Safety Hazards. What are the 1.Fire Hazard exposure levels of hazards and 2.Electrical Hazards 3.Thermal Hazard whether they are Permissible 4.Occupational Hazards Exposure level (PEL) if these are not 5. Chemical Hazards etc., within PEL, what measures the Environmental monitoring is being carried out within the refinery shop floors and the parameters are mainly VOCs, H2S, company has adopted to keep them CO and HCs. within PEL. So that health of the In addition to the above Noise and illumination levels are also being carried out on regular intervals. Same will be workers can be preserved. continued even after expansion

Details of existing Occupational & Safety Hazards for which the employees take treatments has attached in Annexure 21.. iv. Annual report of health status of Periodic medical examination is the same as the pre-employment screening and may be modified according to current workers with special reference to conditions, such as changes in the employee's symptoms, site hazards or exposures. Medical reports of few Employees of Occupational Health and Safety IOCL Panipat Refinery are attached asAnnexure 21. 9 Corporate Environment Policy i. Does the company have a well laid Yes, the company have a well laid down Environmental Policy approved by its Board of Directors. down Environmental Policy M/s IOCL, PR, Safety, Health and Environment Policy (SHE) areprovided in Chapter 10, Section 10.8of EIA report. approved by its Board of Directors? If so, it may be detailed in the EIA report ii. Does the Environment Policy A dedicated Environmental Management Cell (EMC) will be in force to bring into focus of any infringement/ deviation/ prescribe for standard operating violation of the environment. Details provided in Chapter 10 and Section 10.9of EIA report.

88 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report process/procedures to bring into focus any infringement/ deviation/ violation of the environemnt or forest norms/ conditions? If so, it may be detailed in the EIA iii. What is the hierarchical system or Hierarchical system or Administrative order of the company to deal with the environmental issues and for ensuring Administrative order of the company compliance is provided in Chapter 10, Section 10.3of EIA report. to deal with the environmental issues and for ensuring compliance with the environmental clearance conditions? Details of this system may be given. iv. Does the company have system of System of reporting of non-compliances/ violations of environemntal norms & the Board Hierarchical system or reporting of non-compliances/ Administrative order of the company to deal with the environmental issues and for ensuring compliance is provided in violations of environemntal norms to Reporting mechanism detailed inChapter 10, Section 10.3of EIA report. The daily report on safety and environmental the Board of Directors of the parameters on reporting the non-compkiance is enclosed in Annexure 29. company and/or Stakeholders or stakeholders at large? This reporting mechanism shall be detailed in the EIA report 10 Details regarding infrastructure facilities The site layout indicating all the facilities is enclosed as Annexure 15. such as sanitation, fuel, restroom etc. to Infrastructure facilities such as sanitation, restroom etc. shall be provided to the labour force during construction as well be provided to the labour force during as to the casual workers including truck drivers during operation phase. construction as well as to the casual workers including truck drivers during operation phase. 11 Enterprise Social Commitment (ESC) i. Adequate funds (at least 2.5% of the The 2.5% of the project cost (32946 Cr.) = 823.65 Cr. project cost) shall be earmarked towards the Enterprise Social Public hearing was conducted by HSPCB on 06-04-2021 at 12.30pm at at near the project site Baholi village, Post office Commitment based on public Panipat-132140. Hearing issues and item-wise details along with the bound action plan The total fund allotted for the commitment made on the requirement of public during public hearing is INR 45.51Cr. shall be included. Socio-Economic

89 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report development activities need to be S. No. Activity based on public hearing isuues Fund allocation (Crores) Time bound elaborated upon. 1 Brick wall construction around whole green 9.3 March 2023 belt area of IOCL PRPC to avoid the surrounding damaged by neel gaye 2 Creating gallery type way to pit dargah for 0.05 FY-2022-23 public usage. 3 Labour quarters with necessary arrangements 36 December 2022 for the waste generated from the residential area of labours disposal area. 4 5 rooms of school building construction for 0.16 August 2022. GovtSen Sec school, Kutana Total 45.51

As per OM F. No: 22-65/2017-IA.III dated 1st May 2018 M/s IOCL will Allocate 0.125% of the project cost (32946 Crores) towards CER i.e. 0.125% of 32946 Crores = 41.18 Crores. CER OM superseded by OM dated 30.09.2020.

CEPI value of Panipat is 83.54

As per CEPI compliance for CPA 2 times of slab to be allotted(2 * 41.18)=82.36 Crores. CER details will be provided later.

12 Any litigation pending against the project Case Details and/ or any direction/ order passed by any 1.Original Application No. 738/2018 With report dated 15.02.2021- Case dissolved dtd. 22.03.2021 Court of Law against the project, if so, 2.Original Application No. 67/2020 With report dated 5.03.2021- Case dissolved dtd. 09.04.2021 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 The detailed order detailswith action plan and recommendations are attached in Annexure 22. compliance /ATR to the notice(s) and present status of the case. 13 A tabular chart with index for point wise Point wise ToR compliance is provided in provided in Chapter 1 & Section 1.8 of EIA report. compliance of above TOR A. SPECIFIC TERMS OF REFERENCE FOR EIA STUDIES FOR PETROLEUM REFINING INDUSTRY

90 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 1 Complete process flow diagram describing Complete process flow diagram describing each unitis given in Chapter 2, Section 2.7.2.1, Figure 2-6 of EIA report. each unit, its capacity along-with material and energy balance. 2 Details of intermediate product, their a.Existing intermediate and final Product storage details. storages and final products to be manufactured. S. Material Capacity (KL) No of Dia HT Class of No. Tanks (M) (M) Material Product Tanks/ Spheres/ Bullets in Refinery 1 LPG Spheres 1500 7 14.5 -- - 2 LPG Mounded Bullets 2873 4 70 7 - 3 Propylene Spheres 950 2 12 -- A 4 80 MT Gasoline Bullet 200 1 13.2 4.40 A 5 Naphtha 5000 4 25.50 11 A 6 Naphtha/ Heart Cut Naphtha 5000 2 25.5 11 A 7 Naphtha 19200 1 45.4 13.4 A 8 Naphtha/ GT Naphtha 20000 1 45 14.2 A 9 MS/ Naphtha 19200 1 45.4 13.4 A 10 MS 15000 4 40 13.4 A 11 MS/ Isomerate 4000 1 20 14 A 12 MS/ Isomerate 10000 1 30 14.5 A 13 Naphtha/ GT Naphtha 2000 2 16.2 11.25 A 14 LBT 4000 1 20 14 15 ATF 15000 5 40 14.4 B 16 MTO 2000 2 16.2 11.25 B 17 Kerosene 20000 4 45 14.4 B 18 Kerosene 10000 1 14.4 14.5 B 19 Heavy Kero 1000 2 30 10 B 20 HSD 40000 8 13 14.4 B 21 E- III HSD 10000 1 62 10 B 22 FFS 5000 4 30 10 C 23 Bitumen 5000 4 25.5 10 -- 24 Bitumen (Dual) 5000 2 25.5 10 -- 25 Bitumen (Feed) 5000 3 25.5 10 -- 26 IFO 5000 4 25.5 10 C 27 SLOP Oil (Black) 5000 2 25.5 10 C 28 SLOP Oil (White) 5000 1 25.5 10 A

91 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 29 LDD/ Slop Oil (MKTG) 2000 2 16.2 10 C Unit Feed Tanks/ Intermediate Tanks 1 Hydrogen Feed 5000 3 25.5 11 A 2 Hydrogen Feed 10000 3 32.2 14 A 3 Reformer Feed 10000 4 34 14 A 4 DHDT Feed 30000 3 53 15.4 B 5 Hydrocracker/ FCC Feed 20000 2 45 13 C 6 Hydrocracker Feed 20000 2 45 13 C 7 FCC Feed 20000 2 45 13 C 8 FCC Feed 20000 1 45 14.2 C 9 VR (VBU Feed) 5000 1 25.5 10 C 10 VR (DBU Feed) 31100 4 44.5 20 C 11 VR/ CO (VBU/DCU Feed) 5000 2 25.5 10 C 12 High Sulphur NHT Feed 5000 2 24.1 11 A Naphtha 13 Low Sulphur NHT Feed 5000 2 26 11 A Naphtha 14 CCR Feed 1000 1 11.1 10.5 A 15 Reformate 5000 1 21.1 14.4 A 16 Tatoray Feed 4000 1 19 14.4 A 17 Benzene 1520 3 14.3 12 A 18 Para Xylene 10000 3 32.8 14.4 A

a.Proposed intermediate and final Product storage details.

S. No Description Capacity (m3) No of Dia HT (m) Class of Tanks (m) Material Intermediate Bullets 1 Propylene 3850 2 8 90 - 2 Alkylate Feed/LPG 3850 3 8 90 - Intermediate Tanks 3 NHT Feed 14000 2 34 20 A 4 Reformate 17454 1 35 20 A 5 Isomerate 7360 1 28 13 A 6 VGO Feed 30098 3 45 20 Excluded 7 INDMAX Feed 30098 2 45 20 Excluded 8 INDMAX Gasoline 17000 1 37 20 A

92 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 9 DHDT Feed 30000 4 49 20 B 10 RHCU Feed 30098 2 45 20 Excluded 11 Alkylate Product 20000 1 42 17.5 A 12 UCO 13630 1 32 18 Excluded Finished Product Bullets 13 LPG 3850 6 8 90 - Finished Product Tanks 14 Naphtha 14000 1 34 20 A 15 MS 15000 7 36 16.6 A 16 HSD 40000 4 55 18.8 B LOBS TANKS 17 API GRADE II LOBS (P 6315 2 24 15 Excluded 60) 18 API GRADE II LOBS (2 6315 2 24 15 Excluded Cst) 19 API GRADE II LOBS (3 6315 2 24 15 Excluded Cst) 20 API GRADE II LOBS (P 9515 2 24 15 Excluded 150) 21 API GRADE II LOBS (P 6315 2 24 15 Excluded 230) 22 API GRADE II LOBS (P 6315 2 24 15 Excluded 500) 23 API Grade III LOBS (4 CST/ 6315 2 24 15 Excluded Light Lobs) 24 API Grade III LOBS (6 CST/ 9515 2 24 15 Excluded Light Lobs) 25 API Grade III LOBS (8 CST/ 6315 2 24 15 Excluded Light Lobs)

3 Sulphur balance giving input from crude, Sulphur Balance refinery fuel (if used) and any other outside fuel and output in various products S.No. Feed Stream Sulphur(ppmw) Feed (TPD) Sulphur(TPD) and emissions. 1 Crude Blend 30000 75000 1650 2 RLNG 30 4343 0.1 3 C7-C8 from PNCP 0.2 684 0

93 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 4 C9+ Stream from PNCP 250 300 0.1 5 IFO from PNCP 400 336 0.1 6 C4 from PNCP 0 600 0 7 C5 from PNCP 0 510 0 8 Surplus H2 available 0 20 0 9 Mathura Ref. Naptha 500 450 0.2 Total feed Sulfur 1650.56 Product Stream Sulphur(ppmw) Product (TPD) Sulphur(TPD) 10 Mixed LPG‟s 0.85 2176 0 11 RFCC Propylene 0 332 0 12 Poly Propylene 0 1350 0 13 Polymer grade Propylene 0 0 0 14 Fuel gas from RFCC and DCU 30 254 0.01 15 E-VI regular gasoline 8 10546 0.08 16 Premium gasoline 8 854 0.01 17 Benzene 0 74 0 18 PTA 0 2100 0 19 Total naptha to PNCP 500 8208 4.10 20 ATF 1067.1587 6000 6.40 21 BS VI Sulfur diesel 8 38270 0.31 22 Bitumen 46053.4492 1080 49.74 23 DCU Coke 138.84 Total Product sulfur 199.49 Total Sulfur as Refinery Sox 13.09 Total Sulphur in Feed, TPD 1650.56 Total Sulphur in Products, TPD 199.49 Total Sulphur in Refinery Sox, TPD 13.09 Sulfur Capacity in terms of Sulfur Product, TPD 1437.98 SRU PR 115 SRU PREP+PRAEP 450 SRU BS-VI 225 Total SRU Capacity available, TPD 790 New SRU Capacity required, TPD 648 No. of Trains Proposed 2 nos. Each train capacity(TPD) 465

4 Details of proposed source-specific pollution control schemes and equipment Following to be indicated for Air pollution control measures:

94 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report to meet the national standards for  Low sulphur fuels will be used for internal fuel purpose. petroleum refinery.  Heaters/furnaces will be provided with well proven Low NOx burners to reduce the emissions of Nitrogen Oxides (NOx).  Under normal circumstances, there will be no continuous/intermittent point releases of volatile hydrocarbon streams. However, if during startup/shut down or an emergency situation any hydrocarbon streams are released, they will be directed to an elevated flare for complete combustion. This will eliminate the possibility of forming an explosive mixture due to sudden release of unburned hydrocarbons to the atmosphere.  The flares elevation will be such that there will be no impact of thermal radiation on the operating personnel in the refinery.Further, to ensure smokeless and non-luminous flaring, the steam provision at the flare tip is also envisaged.. The refinery complex is designed in such a way that the total emissions from the refinery complex will meet all the applicable standards/stipulations.

5 Details of emissions from all the stacks 1. Emission: including volumetric flow rate. a. Existing:

Emission(g/s) S.n Process Stack Exit Gas Volume PM SO2 NOx CO o (Nm3/Hr) @ 25C (g/sec) (g/sec) (g/sec) (g/sec) A Panipat refining unit

1 RFCC Heater 10702.17 0.0380 0.1479 0.4250 0.0851 2 RFCC Boiler 77661.33 0.2431 1.1861 3.0435 0.7904 3 AVU- 1 335341.24 1.2370 4.8774 9.8125 1.9198 B MCR

4 OHCU- Recycle gas Heater 23609.14 0.1097 0.3090 0.8758 0.1427 5 OHCU LP Section 78410.6 0.3004 1.3114 2.9498 0.5985 6 DHDS- Furnace 24562.62 0.0721 0.3572 0.8727 0.2031 CCRU stack- FF101, FF 102 7 73167.78 0.2833 1.2237 2.5233 0.5120 FF 204 CCRU Stack- FF 201, FF 202 8 36088.83 0.1536 0.7611 1.2068 0.2640 FF 203 9 CCRU Stack- FF 205 21186.13 0.0816 0.3543 0.8081 0.1685 10 VBU 21385.69 0.0766 0.4044 0.6146 0.1837 11 HGU 101595.74 0.5576 1.7731 4.0875 0.8401 C PR Expansion Unit

95 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 12 HCU Unit 42215.04 0.1867 0.5833 1.1249 0.2148 13 AVU- 2 341972.09 1.4230 5.9684 11.0780 2.7196 D Hydrogen Generation Unit

14 HGU-PDS 38499.52 0.1766 0.5039 1.2673 0.2694 15 HGU-76 140182.48 0.5775 1.9369 5.0540 1.2484 16 HGU-77 155111.13 0.7316 2.2560 5.1867 1.0362 E Diesel Hydrotreater Unit

17 DHDT-72 Heater 01 44393.26 0.1599 0.6780 1.5773 0.4095 18 DHDT-72 Heater 02 45833.96 0.1892 0.8666 1.7721 0.4956 F Paraxylene Aromatic Section

19 CCR-Heater 47019.04 0.1614 0.6839 1.2775 0.2842 20 NHT Heater 12715.52 0.0377 0.2127 0.3521 0.0809 21 Xylene Charge Heater 52943.5 0.1610 0.6546 1.5215 0.3200 22 Isomer Charge Heater 18592.5 0.0525 0.2839 0.6412 0.0710 23 Tatoray charge Heater 18392.82 0.0580 0.2407 0.6150 0.1287 G Thermal Power Station

24 HRSG 01 146887.37 0.6218 2.0295 6.3700 0.6541 25 HRSG 02 148251.99 0.5819 1.9405 6.6619 0.6132 26 HRSG 03 159843.57 0.5093 2.6734 7.0993 0.7628 27 HRSG 04 151283.04 0.5429 2.2003 6.8771 0.6736 28 HRSG 05 158248.86 0.5495 1.9566 6.7801 0.5033 29 VHP Boiler 01 130260.73 0.5142 1.9894 5.1728 0.6629 30 VHP Boiler 02 134520.21 0.6681 2.3478 5.4824 0.6420 31 Utility Boiler 02 163531.04 0.7359 3.0921 6.5794 0.7282 Pur. Teraphthalic AC-Aromatic H section 32 Fired combustion preHeater 72693.78 0.3354 0.9515 2.7727 0.2312 33 Hot oil heater 73286.64 0.2463 0.7994 2.2975 0.4662 34 thermal Oxidizer 16642.03 0.0733 0.1573 0.5739 0.0794 I Delayed Coker Unit

35 DCU 13826.97 0.0679 0.2413 0.3974 0.1012 J MS Quality Unit

36 HDS (303 Heater 201) (MSQ) 63025.7 0.2495 0.7792 1.6795 0.4410 37 NHT (301 H101) - - - - - 38 Old SRU-22/44 126752.64 - - - - 39 CPP VHP-3 149983.92 - - - - 40 SRU-26 126752.54 - - - -

96 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 41 New SRU -57 151935.71 - - - - 42 UB-1 146307.28 - - - - 43 BBU Heater - - - - - 44 BBU incinerator - - - - - 45 NSRU - - - - - K BS-VI - - - - - 46 Prime G - - - - - 47 DHDT - - - - - 48 HGU 180000 - - - - Note: Item no.37 to 48 are idle.So the emissions are not mentioned

b. Proposed:

S.No Stack details Flue gas Flow Emission per stack (g/s)

Rate (Nm3/hr) PM SO2 NOx CO 1. AVU (CDU/VDU) 257400 0.751 50.8 13.829 8.297 2. VGO - HDT 89750 0.125 0.306 4.778 1.972 3. Diesel Hydrotreater Unit 41430 0.058 0.142 2.208 0.908 4. MS Block_Charge Heater 92520 0.129 0.319 4.931 2.031 5. NHT Charge Heater 25380 0.035 0.086 1.353 0.556 6. Naphtha Stripper reboiler Heater 17260 0.024 0.058 0.919 0.378 7. CDWU_HCR Reactor Feed Heater 5700 0.008 0.019 0.297 0.131 8. CDWU_DW Reactor feed Heater 4150 0.006 0.014 0.217 0.094 9. CDWU_Vaccum Column Feed 18300 0.025 0.064 0.975 0.403 Furnace 10. Resid Hydrocracking Unit 53160 0.074 0.183 2.833 1.167 (RHCU) 11. Resid Hydrocracking Unit 8630 0.012 0.031 0.469 0.206 (RHCU)_Vaccum Heater 12. IndmaxFCC_Fresh Feed Furnace 38500 0.053 0.133 2.050 0.844 13. IndmaxFCC_Flue Gas cooler 260750 3.622 3.711 6.084 7.189 14. Sulpur recovery unit (SRU) 216570 0.037 17.889 5.464 4.925 15. Spent Acid Recovery unit 3850 0.005 0.047 0.233 0.094 (SARU)_APH System & Stack

97 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 16. Spent Acid Recovery unit (SARU)_Decomposition furnace 18790 0.159 2.000 0.778 0.467 burner 17. Hydrogen Generation Unit 155111.13 0.732 2.256 5.186 1.036 18. CPP Stack 871660 11.555 101.795 78.190 22.303 Total(g/s) 17.41 179.853 130.794 53.001 Total(kg/hr) 62.676 647.4708 470.8584 190.8036 Further details on emissions & sources are provided in chapter 4, Section 4.5 of EIA report

6 Details on availability of raw materials (crude oil, natural gas, chemicals, etc.), its S. Raw Mode of Storage Quantity Unit Source source and storage at the plant. No. Material Storage Capacity (KL) IOCL Crude basket for proposed plant will be MS storage Crude 10 MMTPA 1,58,000 1 selected at the time of Tanks processing of crude

Details of raw materials given in Chapter 2 Section 2.7.3. 7 Details on mode of transportation of crude a.Existing mode of transportation of crude and products. and products. S. No. Products Existing, TMTPA Mode of Transport 1 Crude 15 MMTPA Pipeline 2 Propylene 123 Pipeline 3 LPG 438 Pipeline 4 Naphtha 1435 Pipeline 5 MS BS-VI 1965 Pipeline 6 ATF 1751 Pipeline 7 HSD BS-VI 6932 Pipeline 8 Bitumen 449 Pipeline 9 RPC 884 Truck 10 Sulphur 200 Truck 11 LOBS 0 Truck

98 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report b.Proposed mode of transportation of crude and products. S. No. Products Proposed, TMTPA Mode of Transport 1 Crude 10 MMTPA Pipeline 2 Propylene 554 Pipeline 3 LPG 752 Pipeline 4 Naphtha 407 Pipeline 5 MS BS-VI 1483 Pipeline 6 ATF 500 Pipeline 7 HSD BS-VI 5074 Pipeline 8 Bitumen 41 Pipeline 9 RPC 0 Truck 10 Sulphur 187 Truck 11 LOBS 526 Truck

8 Details of storage capacity of crude and a.Existing storage capacity of crude and products. products. S. Material Capacity (KL) No of Dia HT Class of No. Tanks (M) (M) Material Crude oil storage 1 Crude 50000 7 70 14.4 A 2 Crude 38000 2 62 14.1 A 3 Crude 40000 2 62 14.575 A 4 Crude 30000 2 54 14.1 A Product Tanks/ Spheres/ Bullets in Refinery 1 LPG Spheres 1500 7 14.5 -- - 2 LPG Mounded Bullets 2873 4 70 7 - 3 Propylene Spheres 950 2 12 -- A 4 80 MT Gasoline Bullet 200 1 13.2 4.40 A 5 Naphtha 5000 4 25.50 11 A 6 Naphtha/ Heart Cut Naphtha 5000 2 25.5 11 A 7 Naphtha 19200 1 45.4 13.4 A 8 Naphtha/ GT Naphtha 20000 1 45 14.2 A 9 MS/ Naphtha 19200 1 45.4 13.4 A 10 MS 15000 4 40 13.4 A 11 MS/ Isomerate 4000 1 20 14 A

99 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 12 MS/ Isomerate 10000 1 30 14.5 A 13 Naphtha/ GT Naphtha 2000 2 16.2 11.25 A 14 LBT 4000 1 20 14 15 ATF 15000 5 40 14.4 B 16 MTO 2000 2 16.2 11.25 B 17 Kerosene 20000 4 45 14.4 B 18 Kerosene 10000 1 14.4 14.5 B 19 Heavy Kero 1000 2 30 10 B 20 HSD 40000 8 13 14.4 B 21 E- III HSD 10000 1 62 10 B 22 FFS 5000 4 30 10 C 23 Bitumen 5000 4 25.5 10 -- 24 Bitumen (Dual) 5000 2 25.5 10 -- 25 Bitumen (Feed) 5000 3 25.5 10 -- 26 IFO 5000 4 25.5 10 C 27 SLOP Oil (Black) 5000 2 25.5 10 C 28 SLOP Oil (White) 5000 1 25.5 10 A 29 LDD/ Slop Oil (MKTG) 2000 2 16.2 10 C 30 Benzene 1520 3 14.3 12 A 31 Para Xylene 10000 3 32.8 14.4 A

a.Proposed storage capacity of crude and products..

S. No Description Capacity No of Dia HT (M) Class of (m3) Tanks (M) Material Crude Oil storage Existing crude oil storage facility will be used for the proposed crude oil storage Product Bullets & Tanks Finished Product Bullets 1 LPG 3850 6 8 90 - Finished Product Tanks 2 Naphtha 14000 1 34 20 A 3 MS 15000 7 36 16.6 A 4 HSD 40000 4 55 18.8 B

9 Ambient air quality data should include Raw data of all AAQ measurement is provided as Annexure 14. hydrocarbon (methane and non-methane), AAQ locations detail is provided in the Chapter 3, Section 3.8.1 and monitoring results include hydrocarbon (methane

100 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report VOC, Ni & V etc. and non-methane), VOC, Ni & V are provided in the Chapter 3,Section 3.8.2.1, Table 3-10 of EIA report. 10 Efforts to minimize water consumption, a.Efforts on minimizing the water consumption: effluent discharge and to maintain quality of receiving water body. No Requirement Existing Proposed after expansion 1 Fresh water (m3/hr) 1720 2400 4120 2 Reuse of treated 1515 841 2356 effluent/Sewage/RO(m3/hr)

b.Efforts on minimizing the effluent discharge:

Liquid waste (m3/hr) After Unit Existin Additi Disposal Method Facility Details (m3/hr) expansio g onal n Effluent 1030 362 1392 Existing: 255m3/hr of Existing: Combined ETP-1 of treated effluent discharged to capacity 400m3/hr, Combined ETP-2 Thirana Drain and remaining of capacity 400m3/hr and Combined reused in the plant PX/PTA ETP of capacity 275m3/hr Sewage 235 9 244 Proposed: 4 m3/hr of salt is Proposed: ETP of capacity discharged to TSDF and 450m3/hr.Sewage will be combined remaining reused in the into the proposed ETP for treatment. plant

To maintain quality of receiving water body(Thirana drain): 1. Monthly Testing through external agency (NABL accredited agency) and internally through IOCL PRPC Lab on daily basis 2. Treated effluent meets the MINAS standards 3. Continuous online monitoring system The logbook of daily discharge into Thirana Drain and the treated effluent test report from NABL & MoEF accredited lab is attached as Annexure 28.

11 Details of effluent treatment plant, inlet a.Details of Effluent Treatment Plant

101 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report and treated water quality with specific S. No. List of units in ETP Efficiency on reduction in respect to all environmental parameters efficiency of each treatment unit in ETP-1- Capacity: 400m3/hr reduction in respect of all con corned/ 1 TPI Separator Free Oil(>60 micron): minimum 90% TSS: 80% regulated environmental parameters. Also, 2 DAF Oil Removal efficiency: 95 % TSS: 70 % Sulphide Removal Efficiency: 82 % include treatment details such as primary 3 Bio-tower BOD Removal Efficiency: 50% COD Removal Efficiency: 55% (physico-chemical), secondary (biological) 4 Aeration Tank BOD Removal Efficiency: 92.5 and tertiary (Activated carbon filters) COD Removal Efficiency: 62% treatment systems. 5 Clarifier TSS: 98 % ETP-2- Capacity: 400m3/hr 1 TPI Separator Free Oil(>60 micron): minimum 90% TSS: 70% 2 DAF Oil Removal efficiency: 96 % TSS: 90 % Sulphide Removal Efficiency: 96.8 % 3 Bio-tower BOD Removal Efficiency: 70-75% COD Removal Efficiency: 50-55% 4 Aeration Tank BOD Removal Efficiency: 95% COD Removal Efficiency: 78.6% 5 Clarifier TSS: 98 % PX/PTA ETP – Capacity: 275m3/hr 1 DAF Oil Removal efficiency: 9 % TSS>70 % 2 AHR (An-aerobic COD Removal Efficiency: 70% hybrid reactor) 3 Aeration Tank BOD Removal Efficiency: 93.5% 4 Clarifier TSS: 98 %

b.Characteristics of inlet effluent into ETP

S. No. Parameter units ETP-1 ETP-2 PTA-ETP 1 Oil % 0.1 0.1 NA 2 COD mg/L 1000 1000 6800 3 BOD mg/L 500 500 4700 4 TSS mg/L 150 150 1800 5 Phenol mg/L 30 30 -- 6 Sulfide mg/L 60 60 -- 7 Cyanide mg/L 5 5 --

102 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report c.Characteristics of outlet effluent

S. No. Parameter units ETP-1 ETP-2 PTA-ETP 1 PH -- 6-8.5 6-8.5 6.5-8.5 2 Oil mg/L 5.0 5.0 NA 3 COD mg/L 125.0 125.0 250 4 BOD mg/L 15.0 15.0 30 5 TSS mg/L 20.0 20.0 100 6 Phenol mg/L 0.35 0.35 1.0 7 Sulfide mg/L 0.5 0.5 2.0 8 Cyanide mg/L 0.2 0.2 0.20

The treatment scheme is broadly divided into five sections as follows:

a) Physico-Chemical treatment, for removal of Hydrocarbons, Sulphides and Total suspended solids. b) Biological treatment system incorporating activated sludge system for oxidizing the organic matters. c) Tertiary treatment system comprising of pressure sand filters and activated carbon filters for removal of TSS, Odour, Colour and Organics. d) Sludge processing section comprising of Oily & Chemical Sludge Processing and disposal as a solid waste biodegradable material. e) Chemical dosing system comprising of storage facilities of various chemicals and preparations of chemical solutions of standard concentration for injection at various stages during effluent treatment. The effluent treatment scheme is given in Chapter 2 Section 2.14, Figure 2-17 and Figure 2-18 of EIA report.

Wastewater treatment and disposal details are provided in the Chapter 4, Section 4.7of EIA report. The logbook of daily discharge into Thirana Drain and the treated effluent test report from NABL & MoEF accredited lab is attached as Annexure 28.

12 Storm water management plan. There will be two numbers of Main drain having total capacity upto last culvert is 52.037 m3/s. Total storm water discharge in the plant area will be 35.85 m3/s. Further the detailed storm water management planis attached in Annexure 23.

13 Estimation SO2 and NOx emissions load. Proposed: Pollutant Emission load (g/s) Emission load (Kg/hr)

103 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

SO2 179.853 647.471

NOx 130.893 471.215

Max. Base NAAQ Estimated Incremental Pollutant line Conc. Total Conc. (µg/m3) standard % increase Conc. (µg/m3) (µg/m3) (µg/m3)

SO2 22.83 34.23 57.06 80 149.93

NOx 43.71 22.29 66 80 51.00

14 Details on flaring system. S.No. Utility Units Capacity

1 Flare Kg/hr 2191374

104 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report The flares elevation will be such that there will be no impact of thermal radiation on the operating personnel in the refinery. To ensure complete combustion of released hydrocarbons through flares, a pilot burner shall always be burning with the aid of fuel gas. Further, to ensure smokeless and non-luminous flaring, the steam provision at the flare tip is also envisaged. All the Safety valves are connected to the flare gas system (FGS). In the event of pop-up of the safety valves, flare gas recovery system (FGRS) is in place to recover gas back in the fuel gas header 15 Details of VOC recovery devices in the To control VOC emission from the Storage Tanks: storage tanks.  Heavier products have fixed roof tanks, whose Vapor pressure lower than the atmospheric pressure, results in no emissions to atmosphere from the tanks.  All Floating roof tanks have provision of primary and secondary seals to prevent emissions from the tanks. IOCL Panipat Refinery has VOC Monitoring system in Existing Refinery and VOC facility in proposed Effluent Treatment Plant will be installed in Proposed expansion 16 Arrangement for spill management. Oil Spill Management Hay filters are installed along both the open channels running through Panipat Refinery to prevent spilled oil from escaping out of the Refinery premises with the open channel water. Also oil traps have been installed at strategic locations to arrest oil spillage. 17 Oily sludge management plan. Oily sludge generated from ETP shall be recovered for oil through oil recovery module. The residual sludge shall be bio remediated using Confined Bioremediation as shown below:

105 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

18 Risk Assessment & Disaster Management The Risk Assessment has been carried out by using the PHAST software. Risk Assessment report and is attached as Plan Annexure 13 and the Disaster Management Plan as Annexure 19.

106 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report i. Identification of hazards ii. Consequence Analysis i.Identification of hazards iii. Risk assessment should also Hazard identification is the process used to identify all the possible situations in the workplace where people may be include leakages and location exposed to injury, illness or disease. Identification of causes and type of hazards is the primary task for planning for risk near to refinery & proposed assessment. measures for risk reduction. iv. Arrangement for fire protection A preliminary hazard analysis is carried out initially to identify the major hazards associated with storages and the and control. processes of the plant. This is followed by consequence analysis to quantify these hazards.

Hazardous chemicals:

In a refinery, hazardous chemicals can come from many sources and in many forms. In crude oil, there are not only the components sought for processing, but impurities such as sulphur, vanadium, and arsenic compounds. The oil is split into many component streams that are further altered and refined to produce the final product range. Most, if not all, of these component stream chemicals are inherently hazardous to humans, as are the other chemicals added during processing. Hazards include fire, explosion, toxicity, corrosiveness, and asphyxiation. Information on hazardous materials manufactured or stored in a refinery should be supplied by the client's representative when a work permit is issued

Health and hygiene hazards

Major potential air contaminants which can escape from a typical refinery operation and their major sources. It does not attempt to identify all such possible hazards. Parameters Major sources Hydrocarbon Vapours –  Transfer and loading operations Compounds of Carbon  Storage tanks (C) and Hydrogen  Crude unit, atmospheric, and vacuum towers  Cracking units  Rearranging and combining processes such as Reformers and alkylation units  Treating Operations  Cracking Unit Regeneration  Heat Exchangers  Boilers & Heaters  Pumps, Valves Cooling Towers

107 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Sulphur dioxide  Boilers  Cracking Unit Regeneration  Treating Operations  Flares Carbon monoxide (CO)  Rearranging and combining processes such as reformers and alkylation units  Catalyst Regeneration  Flares  Boiler  Furnaces Nitrogen dioxide (NO2)  flares  boilers Hydrogen sulphide (H2S)  Sour Crudes  Liquid Wastes  Pumps  Crude Tower  Cracking Operations  Re-arranging and combining processes such as reformers and alkylation unit  Hydro generation Particulates  Catalyst dusts – Cracking unit, Catalyst regeneration and rearranging and combining processes such as reformers and alkylation units  Petroleum Coke Dust – Cracking units Chlorine (Cl or Cl2)  Caustic Unit Ammonia (NH3)  Compressors

Common hazardous chemicals and chemical groups typically present and their most significant hazards to workers. MATERIAL DOMINANT HAZARD Additives – usually skin irritants Ammonia – toxic on inhalation Asbestos – designated substance under construction regulations. See chapter on asbestos in this manual. Asphalt – dermatitis (can be photosensitizer)

108 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Benzene – designated substance under industrial regulations

Carbon monoxide – toxic on inhalation Caustic soda – corrosive to skin and eyes Chlorine – corrosive to skin and tissue on contact or inhalation HBAHs (high boiling aromatic – potential carcinogens hydrocarbons) Hydrofluoric acid – corrosive to skin and tissue on contact or inhalation Hydrogen sulphide – toxic on inhalation MEK (methyl ethyl ketone) – corrosive to skin

Nitrogen – asphyxiant PAHs (polynuclear aromatic – potential carcinogens hydrocarbons) Phenol-acid – corrosive to skin and tissue Silica – designated substance under industrial regulations

Sulphuric acid – corrosive to skin and tissue on contact or inhalation Sulphur dioxide – toxic on inhalation

Care should be exercised at all times to avoid inhaling solvent vapours, toxic gases, and other respiratory contaminants. Because of the many hazards from burns and skin contact, most plants require that you wear long- sleeved shirts or coveralls

Confined spaces

On most jobsites there are potential confined space hazards. These hazards are multiplied, however, on a refinery site because of the complex collection of tanks, reactors, vessels, and ducts combined with a wide variety of hazardous chemicals and emissions, often in enclosed areas. Many of these chemicals can produce oxygen- deficient, toxic, or explosive atmospheres. Knowledge of general confined space procedures and specific in-plant requirements are both critical in refinery work. For more information, refer to the chapter on Confined Spaces in this manual.

109 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report a.Hazard identification – LPG:

Liquefied petroleum gas (LPG), is a flammable mixture of hydrocarbon gases such as propane and butane

Health hazards:

Routes of entry Effects of Exposure/Symptoms Effects w.r.t concentration

Inhalation can cause headache, disorientation, dizziness, iv) Concentration in air greater drowsiness and possibly than 10% causes dizziness in unconsciousness at concentrations few minutes. Inhalation & Skin that cause oxygen deficiency and v) 1% conc. gives the same asphyxiation. symptoms in 10 metres. Rapidly expanding gas or vi) High concentration causes vaporized liquid may cause asphyxiation. frostbite to skin and eyes.

Fire hazards:  Eliminate all sources of ignition, since motor spirit is highly inflammable.  Keep the containers cool by spraying water if exposed to fire or heat. If the container is not sufficiently cooled it will explode in fire.  Use CO2, Dry Chemical Powder or Water Spray to extinguish fire.

Hazard ratings:

HAZARD RATING NFPA Flammability 4 Health 1 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe

b.Hazard identification – Naphtha:

Naphtha is a flammable oil containing various hydrocarbons, obtained by the dry distillation of organic substances such as coal, shale, or petroleum.

110 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Hazard summary: Extremely flammable. Irritating to eyes and respiratory system. Affects central nervous system. Harmful or fatal if swallowed. Aspiration Hazard.

Symptoms:

Dizziness, Discomfort, Headache, Nausea, Kidney disorders, Liver Disorders.

Health hazards:

Contact Effects

High vapor concentration or contact may cause irritation and Eyes discomfort. Brief contact may cause slight irritation. Skin irritation leading to Skin dermatitis may occur upon prolonged or repeated contact. Can be absorbed through skin. Aspiration hazard if liquid is inhaled into lungs, particularly from vomiting after ingestion. Aspiration may result in chemical Ingestion pneumonia, severe lung damage, respiratory failure and even death. Vapors or mists from this material can irritate the nose, throat, and lungs, and can cause signs and symptoms of central nervous system depression, depending on the concentration and duration of Inhalation exposure. Inhalation of high concentrations may cause central nervous system depression such as dizziness, drowsiness, headache, and similar narcotic symptoms, but no long-term effects.

111 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Long-term exposure may cause effects to specific organs, such as Chronic to the liver, kidneys, blood, nervous system, and skin. Contains Exposure benzene, which can cause blood disease, including anemia and leukemia.

Target Skin, Central nervous system, Liver, Kidney, Blood. Organs

Fire hazards:  Keep away from fire, sparks and heated surfaces because it can easily ignite with small ignition sources.  Use water spray, alcohol-resistant foam, dry chemical or carbon dioxide Do not use a solid water stream as it may scatter and spread fire. Hazard ratings: HAZARD RATING NFPA Flammability 3 Health 1 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe c.Hazard identification – MS: Motor Spirit also known as Gasoline, or petrol, is a transparent, petroleum-derived liquid that is used primarily as a fuel in internal combustion engines.

Health hazards

Routes of entry Effects of Exposure/Symptoms

Inhalation & Excessive inhalation Vapours cause rapid breathing, excitability, staggering, headache, Ingestion fatigue, nausea and vomiting, dizziness, drowsiness, narcosis convulsions, coma.

Skin absorption Skin-dryness, cracking, irritation eyes watering, stinging and inflammation.

Fire hazards:  MS catches fire with any sparks or ignition sources, once it makes contact with it.  Use Foam, Carbon dioxide, Dry Chemical Powder as Extinguishers and Water is used to cool down the containers.

112 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Hazard ratings: HAZARD RATING NFPA Flammability 3 Health 0 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe d.Hazard identification – HSD: HSD is normally used as a fuel in medium and high speed compression ignition engines in commercial vehicles, stationary diesel engines, locomotives and pumps etc.

Health hazards:

Routes of entry Effects of Exposure/Symptoms

Excessive inhalation Vapours cause rapid breathing, excitability, staggering, Inhalation & Ingestion headache, fatigue, nausea and vomiting, dizziness, drowsiness, narcosis convulsions, coma.

Skin absorption Skin-dryness, cracking, irritation eyes watering, stinging and inflammation.

Fire hazards:  HSD ignites in contact with fire, so keep the ignition sources away from it.  Use Foam, Carbon dioxide, Dry Chemical Powder as Extinguishers and Water is used to cool down the containers.  On fire it will be liberate some amount carbon monoxide, Sulphur dioxide Nitrogen Oxide and other aromatic hydrocarbons. Hazard ratings: Hazard rating NFPA Flammability 2 Health 1 Reactivity 0 Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe ii.Consequence Analysis

The Risk Assessment has been carried out by using the PHAST software. Consequence Analysis of the Risk Assessment is attached as Annexure 13 - in the below following APPENDIX's

113 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report APPENDIX – II –CONSEQUENCE ANALYSIS FOR PROCESS UNITS LISTED BELOW

 AVU  VGO  DHDT  PRU  SRU  INDMAX  MS BLOCK (NHT,CCR,ISOM)  HGU  CDWU  SR-LPGT  RHCU  SWS 1 & 2  ARU

iii.a.Leakages in refinery

Leak Category Leak Size (mm) Remarks Small Leak (S) 7 Representative of 0 to 10 mm Medium Leak (M) 22 Representative of 10 to 50 mm Large Leak (L) 70 Representative of 50 to 150 mm Full Bore Leak Representative of all leaks exceeding 150 mm including full (FBR) / Catastrophic 150 bore & rupture Rupture

iii.b.Locations near to refinery

Munak Village and Kutana Village adjacent to boundary of the refinery. iii.c.Proposed measures for risk reduction

Following are the proposed safety measures in the plant.  Emergency isolation valves are to be provided/online monitoring via SCADA (Supervisory Control And Data Acquisition) that will closely monitor the process flow and parameters in a safe place and auto mode through gas/fire detector system.  Passive fire protection such as fire proofing shall be recommended. Appropriate detection measures such as fire and gas detectors are recommended and the same to be deep-rooted

114 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report throughout the plant area.

Flammable release from crude oil pipelines /Fire Station contributes multiplefatalities (which is in ALARP region), therefore it is recommended to consider thefollowing measures to reduce the risk further to Broadly acceptable region:

1. Ensure that escape routes from Admin. Building, Fire station and Individual Process Refinery Units. 2. Ensure specific Emergency Response plan is developed for Admin. Building, Fire station and Individual Process Refinery Units addressing the response foran oil leak event resulting in fire from crude oil pipelines.  It is recommended to evaluate the adequacy of escape, muster, evacuation and rescue arrangements and ensure that adequate provisions are made for the safe escape, mustering and evacuation of personnel following major accident hazardscenario.  To reduce the risk from hydrocarbon release in process units/Pipelines, Risk Based Inspection (RBI) program to be implemented in order to reduce the frequency of leaks within the facility.  Personnel at Panipat Refinery facility shall be trained regularly on Emergency response and preparedness. Ensure that emergency handling and mitigation systems are adequate. Mock drills based on emergency scenarios shall be conducted at regular intervals to review emergency preparedness

iv.Arrangement for fire protection and control

 Alert Fire Brigade and tell them location and Nature of hazard.  Wearing breathing apparatus plus protective gloves.  Flammable liquid and VAPOUR. Use dry chemical, foam, or carbon dioxide to extinguish the fire.  Consult foam manufacturer for appropriate media, application rates and water/foam ratio.  Water spray may be used to disperse vapors and/or flush spills away from source of ignition.  Water spray can be used to cool tanks and exposures.  Vapour suppressing foam may be used to suppress vaporsCut off "fuel"; depending on circumstances, either allows the fire to burn out under controlled conditions or use foam or dry chemical powder to extinguish the fire.

The following general points shall be noted: i. All documents shall be properly indexed, page numbered. Accepted and Noted ii. Period/date of data collection shall be clearly indicated. Accepted and Noted

iii. Authenticated English translation of all material in Regional languages shall be provided. Accepted and Noted iv. The letter/application for environmental clearance shall quote the MOEF&CC file No. and also attach a copy of the Accepted and Noted

115 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report letter. v. The copy of the letter received from the Ministry shall be also attached as an annexure to the final EIA-EMP Report. Accepted and Noted vi. The index of the final EIA-EMP report must indicate the specific chapter and page no. of the EIA- EMP Report Accepted and Noted vii. While preparing the EIA report, the instructions for the proponents and instructions for the consultants issued by MOEF&CC vide O.M. No. J-11013/41/2006-IA.II (I) dated 4th August, 2009, which are available on the website of Accepted and Noted this Ministry shall also be followed. viii. The consultants involved in the preparation of EIA-EMP report after accreditation with Quality Council of India (QCl) /National Accreditation Board of Education and Training (NABET) would need to include a certificate in this regard in the EIA-EMP reports prepared by them and data provided by other organization/ Laboratories including Accepted and Noted their status of approvals etc. Name of the Consultant and the Accreditation details shall be posted on the EIA-EMP Report as well as on the cover of the Hard Copy of the Presentation material for EC presentation.

ix. TOR prescribed by the Expert Appraisal Committee (Industry) shall be considered for preparation of EIA-EMP report for the project in addition to all the relevant information as per the 'Generic Structure of EIA' given in Appendix III and IIIA in the EIA Notification, 2006. Where the documents provided are in a language other than English, an English translation shall be provided. The draft EIA-EMP report shall be submitted to the State Pollution Control Board of the concerned State for conduct of Public Hearing. The SPCB shall conduct the Public Hearing/public Accepted and Noted consultation, district wise, as per the provisions of EIA notification, 2006. The Public Hearing shall be chaired by an Officer not below the rank of Additional District Magistrate. The issues raised in the Public Hearing and during the consultation process and the commitments made by the project proponent on the same shall be included separately in EIA-EMP Report in a separate chapter and summarised in a tabular chart with financial budget (capital and revenue) along with time-schedule of implementation for complying with the commitments made. The final EIA report shall be submitted to the Ministry for obtaining environmental clearance.

116 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

CHAPTER 2 PROJECT DESCRIPTION

117 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2 PROJECT DESCRIPTION

2.1 Project Description

Panipat Refinery (PR) was commissioned in 1997-98 with crude oil processing capacity of 6.0 MMTPA. The refinery capacity was raised in 2008-09 to 12.0 MMTPA with the addition of another crude unit and a full conversion hydrocracker as the secondary processing unit and Delayed Coker unit for bottom up gradation (PREP- Panipat Refinery Expansion Project). Further through revamps and addition of process units the refining capacity has been brought to the present operating capacity of 15.0 MMTPA (PRAEP- Panipat Refinery Additional Expansion Project).

Panipat Refinery is integrated with Aromatic Complex and Naphtha Cracker Complex. Aromatic complex consists of Paraxylene (PX) unit with production capacity of 360 KTPA & Purified Terephthalic Acid (PTA) unit with production capacity of 550 KTPA which were commissioned in 2006. Naphtha Cracker Complex with Ethylene production capacity of 857 KTPA was commissioned in 2010. At present revamping of PX, PTA and Naphtha Cracker complex are under implementation.

Motor Spirit Quality Upgradation project with Naphtha Hydro treating unit (NHDT), Isomerization (ISOM), FCC Gasoline Desulphurization unit (Prime G) was commissioned in 2010 for production of BS-IV quality compliant MS.

At present Panipat refinery has been upgraded to BS-VI grade fuel completely since 1st April 2020. Accordingly, EIL was asked to make a configuration study for 100% BS VI auto fuels from existing 15 MMTPA Refinery. Stage-1 approval was accorded for production of BS-VI compliant products with crude processing capacity of 15 MMTPA. In order to produce BS-VI quality fuel, following units such as new DHDT (2.2 MMTPA), new HGU (44 KTPA), new SRU (225 TPD), new ARU (189 m3/hr), new SWS (57 m3/hr) are envisaged in BS-VI project has been commisioned. Crude oil is received from two pipelines originating from Gujarat Coast. The first one is SMPL(salaya Mathura pipeline), which supplies crude to Gujarat (Koyali refinery), Mathura refinery and Panipat refinery. 2nd pipeline is MPPL(mundra Panipat pieline) 1194km long and capacity is 8.4 MMTPA.

118 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.1.1 Type of Project

M/s Indian Oil Corporation limited, Panipat Refinery proposes “Panipat Refinery Capacity expansion from 15MMTPA to 25MMTPA” falls under Schedule 4(a)–“Petroleum Refining Industries” Category „A‟, since all the projects under this schedule falls under “A” category.

2.2 Need of the project

Panipat Refinery is strategically located to cater the increase in demand of Northern part of India as compared to meeting the demand by sourcing of products from Refineries situated in western part of India. Logistically, it will be more economical to cater the product demand from Panipat Refinery.

There is adequate land available for expansion of Panipat Refinery facilitating smooth execution of the expansion project.

There is wide network of Pipeline connectivity catering to large area and adequate facilities at Marketing Terminal to facilitate evacuation of products at minimal cost.

There is reliable availability of other associated infrastructure like water and power from the site. Availability of other in-house infrastructure for refinery operation, storage & dispatch facilities of Petroleum Products at minimal cost.

In the above as per study carried out to expand the Refinery from existing 15.0 MMTPA to 25.0 MMTPA capacities with an objective to obtain viable configuration with economically acceptable MIRR.

Industrial Demand under scenarios along with CAGR for intermediate years as provided by PPAC is summarized below

119 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-1 Market Potential 2.3 Site Location

The existing complex is located at Baholi Village, Panipat District, Haryana State. The site is located 5.18 km from Panipat city towards NW. Index map of the project site is given in Figure 2-2. Base map showing area within 15km, 10km (Figure 2-5), 5km (Figure 2-4) and 1 Km (Figure 2-3). Geographical coordinates of the project site given below in Table 2-1.

120 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 2-1 Geographical coordinates of the project site

S. No Location Latitude (N) Longitude (E) 1 C1 29°29'12.960"N 76°51'36.943"E 2 29°29'12.840"N C2 76°52'43.074"E 3 C3 29°29'18.231"N 76°52'50.985"E 4 29°29'19.426"N C4 76°52'57.413"E 5 C5 29°29'20.112"N 76°52'58.947"E 6 29°29'17.817"N C6 76°52'58.600"E 7 C7 29°29'16.488"N 76°53'1.9304"E 8 29°29'15.670"N C8 76°53'1.7831"E 9 C9 29°29'12.324"N 76°53'2.3166"E 10 29°28'54.457"N C10 76°53'5.5915"E 11 29°28'53.157"N C11 76°53'7.8166"E 12 C12 29°28'49.694"N 76°53'16.852"E 13 29°28'49.874"N C13 76°53'31.789"E 14 C14 29°28'23.493"N 76°53'44.174"E 15 29°28'20.281"N C15 76°53'40.061"E 16 C16 29°28'14.653"N 76°53'37.463"E 17 29°27'43.436"N C17 76°53'37.803"E 18 C18 29°27'42.603"N 76°53'24.407"E 19 29°27'42.603"N C19 76°53'24.407"E 20 C20 29°27'45.269"N 76°52'59.533"E 21 29°27'52.928"N C21 76°52'43.858"E 22 29°28'32.887"N C22 76°51'32.932"E 23 C23 29°28'59.621"N 76°51'31.435"E 24 29°28'59.408"N C24 76°51'29.580"E 25 C25 29°29'0.0235"N 76°51'31.438"E 26 29°29'13.748"N C26 76°51'32.980"E

121 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-2 Index map of the project site

122 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-3 Google image showing salient features within 0- 1 km radius

123 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-4 Google image showing salient features within 0- 5 km radius

124 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-5 Google image showing salient features 0- 10 km Radius Map around the study region

125 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.4 Existing Environmental Setup

The site details and the surrounding features are summarized in Table 2-2 Table 2-2 Existing Environmental Setup of the study region

S. No Particulars Details 1. Geographical Location 29°28'27.97"N, 76°52'35.83"E 2. Elevation above Mean Sea 238-250 m Level 3. Present Land Use Industrial 4. Nearest Railway Station Distance Description Direction (~km) Babarpur RS 7.3 E 5. Nearest Airport 28.85 NNE Indira Gandhi International Airport Delhi 99.6 SSE 6. Nearest Highway SH -14 (Panipat--) 7.07 S NH -44 (Srinagar-Panipat-Kanyakumari) 7.39 E Nearest Railway jn - Panipat Jn 10.12 SE Nearest Railway Station (Asan) 6.68 S 7. Nearest habitation /Village Baholi Refinery present within the village Bal Jattan 1.90 SSW Rer Kalan 2.23 W Kutana 1.22 N Dadlana 0.92 ENE Sithana 0.98 SE 8. Nearest Port Dahej Port 963.4 SSW 9. Nearest Town Panipat ~5.18 SE 10 Nearest City Panipat ~5.18 SE 11. Densely populated area Distance Description Population (Nos.) Direction (~km)

126 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Panipat 791634 ~5.18 SE 12. Inland water bodies S. Distance Direct S. Distance Direct Description Description No (~Km) ion No (~Km) ion Adjacent Mor Majra Munak Drain W 6.81 W 1 to Site 30 Drain New Delhi Branch (Western 0.05 S Ganda Nala 7.11 E 2 Yamuna Canal) 31 Main Drain No Jind 0.05 E 7.13 W 3 2/Indri Drain 32 Distributary New Delhi Parallel Branch Khukrana 0.1 S 7.21 S (Western Branch Canal 4 Yamuna Canal) 33 Gohana 0.1 S Bhalsi Minor 7.87 SSW 5 Distributary 34 Nahar Kuna Lift Irrigation Hansi/Hanal 0.19 N 9.7 N Channel 6 Nadi 35 7 Madlauda Minor 0.22 S 36 Drain 9.91 S Gagsina Thirana Minor 0.23 S 10.12 N 8 37 Subminor 9 Khandra Drain 0.67 S 38 Lohari Minor 10.13 S Left Branch Begampur Minor 0.8 N Gohana 10.13 S 10 39 Distributary 11 Joshi Drain 0.82 W 40 Jundla Drain 10.14 N 12 Untala Minor 1.78 S 41 Rasin Minor 10.38 NNE 13 Phurlak Drain 2.14 N 42 Bansa Drain 10.86 NNW

127 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Tributary Drain 2.32 SSW Pundri Drain 10.95 ESE 14 No 1 43 Gagsina East Augmentation 2.62 N 11.06 N 15 Drain 44 Canal Branch No 1 Rer Kalan Minor 2.67 11.26 W 16 WNW 45 Canal Kabir Bansa Branch/Bazida 2.7 E 11.7 NNW Subminor 17 Distributary 46 Munak Minor 2.76 N 12.05 SSE 18 47 Distributary Hansi Hulana Branch(Western 4.31 NW 12.18 SSE Distributary 19 Yamuna Canal) 48 Narayana Munak Canal 4.46 NNW 12.32 SSE 20 49 Distributary 21 Goli Distributary 4.88 NNW 50 Seori Minor 13.12 NW Bala Tributary Gudah Minor 5.34 E 13.26 22 51 Drain WSW 23 Binjhaul Minor 5.39 SE 52 Barauta Drain 13.55 NNE Jind Pabana/Pawana 5.47 Distributary 13.68 Drain WNW WSW 24 53 No 2 Nohra/Nauhra 5.68 SSE Naultha Minor 13.72 S 25 Drain 54 Ganda No 1R Israna Nala/Panipat 5.7 ESE 13.91 S Minor 26 Main Drain 55 Joshi Idyana 5.82 W 14.15 SSW 27 Distributary 56 Subminor 28 Kurian Minor 5.86 NW 57 Tributary Drain 14.84 S

128 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report No 2

29 Untala Drain 6.6 S

13. Reserved Forests/Protected Forests/Notified Wildlife Nil within 15km radius from the project boundary Sanctuary/Notified national

parks/Ecologically sensitive areas 14. Defense Installations Nil within 15 km radius from the project boundary

15. Archeologically Important Monuments places/sites S.N Distance Decription o (~km) Direction 1 Kohand 7.74 E 2 Kos Minar (South) 8.86 ENE 3 Kos Minar Taraf Unsar (Panipat) 9.82 SE 4 Gateway of old Moghul Sarai Gharaunda (North Gate) (South Gate) Gharaunda 9.85 NE 5 Site of 's tomb Panipat 9.96 SE 6 Bab-i-Faiz Gate on the north side of Panipat town Panipat 10.39 SE 7 Kos Minar (North) Gharaunda 11.41 NE 8 Kos Minar (Namaste Chowk) Karnal 11.44 NE 9 Kabuli Bagh with enclosure wall Panipat 11.6 SE

129 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 10 Kos Minar Taraf Afghan 13.04 SE 11 Obelisk commemorating the Third Battle of Panipat Kala Amb 14.15 ESE

16. Interstate/ National None within 15 km radius from the project boundary Boundaries 17. Hills/Valleys None within 15 km radius from the project boundary

130 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 2-3 List of major Industries within 10km Radius from the project site

S.No Industries Distance(~km) Direction 1 HPCL Depot Adjacent to site 2 Smartchem Technologies Limited 0.22 E 3 Bharat Petroleum Depot 0.3 N 4 IOCL Panipat Petrochemical Plant 0.75 SSW 5 Ambadi Enterprises Ltd 1.44 E 6 Tinna Rubber and Infrastructure Limited 1.89 E 7 Shree Ganesh Cot Spin 2.38 ESE 8 IVL Dhunseri Petrochem Industries Pvt Ltd 2.4 NNE 9 Fieldking Unit 3 2.69 ENE 10 Karnal LPG Bottling Plant IOCL 3.56 ENE 11 Dev Overseas 4.32 SE 12 Dr. Sandhu Feeds and Hatcheries 5.24 N 13 Gurdev feeds India pvt Ltd 5.36 SE 14 Birmi Industries Private Limited 6 SW 15 LC woollen mill 6.07 SE 16 Coozy Blankets 6.19 SE 17 Panipat Thermal Power Station 6.26 S 18 SHIV SHANKAR INDUSTRIES 6.41 SE 19 Prbhat Cop.Ltd 6.8 SE 20 Kasthuri Spinners 7.05 SE 21 Pepsi Plant 7.16 E 22 CSC Centre Faridpur 7.23 ESE 23 Varun Beverages ltd 7.26 E 24 Ambey Spinning Mills 7.31 SE 25 Jai Shree Radhey Woven Sacks 7.37 SE 26 BMC Spinners 7.54 ESE 27 Innovative Agro Pvt Ltd 7.65 E 28 Karan Automotives 7.67 E

131 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S.No Industries Distance(~km) Direction 29 Sunrise Woollen Mills kohand 7.87 E 30 Unnat Agrotech 8.18 ENE 31 Gargi Overseas 8.25 SE 32 Jai Jyoti Texo Fab 8.28 SE 33 Pachranga Foods 8.43 SE 34 Parkash Woollen Industries 8.52 SE 35 Aroma Agrotech Pvt Ltd 8.68 ENE 36 Maheya Mink Blankets 8.68 SE 37 M/S Saraswati Udyog 8.79 SE 38 Bagpoly International 8.92 E 39 Metal Tubes Private Limited 9.2 SE 40 Jindal Spinning Mills 9.2 SE 41 JRS Industries 9.22 E 42 Birmi International Pvt Ltd 9.44 SSW 43 Dream Home Carpets Pvt. Ltd 9.86 E 44 Bagpoly International Pvt. Ltd 9.89 E 45 Jai Hanuman and Gen Mills 9.91 ENE 46 Crystal Enterpise 9.93 ESE 47 Poly Bag Industries 10.03 ENE 48 Jatin Rice Industries 10.03 ENE 49 Mdj texco fab 10.07 E 50 Aakash Agrotech Private Limited 10.26 NE 51 Sugandha Textiles 10.3 ESE 52 Jai parkash solvent 10.47 SSW 53 Vaishno Rice Mills 10.54 ENE 54 Adinath Tradelinks 10.73 ESE 55 Shri Sham Wooltex 10.83 ESE 56 Mahaluxmi Enterprises 10.95 ESE 57 Laxmi Rice Mill 11.07 NE

132 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S.No Industries Distance(~km) Direction 58 Liberty Leathers Shoes Factory 11.07 NE 59 Panipat Cooperative Sugar Mills Limited 11.11 SE 60 G.R.International 11.46 SSW 61 Saanvi Steels 11.62 ESE 62 Shree Mahavir Trader 11.63 ESE 63 TANNA AGRO UNIT 2 11.79 NE 64 SRR Impex 11.88 NE 65 Pesticide Factory 11.94 SSW 66 Bansal Rice And General Mills Ghraunda 12.14 NE 67 Shree Jagdamba Agrico Exports Pvt. Ltd. 12.21 NE 68 Veer Rice and General Mill 12.3 ENE 69 Devgiri Overseas Pvt. Ltd 12.36 SSE 70 National Fertilizer Ltd 12.46 SSE 71 HPL Electric & Power Ltd 12.52 NE 72 Royal Star Agrotech Pvt Ltd 12.57 ENE 73 Sunrise Riceland Pvt Ld 12.81 NE 74 Sri Ganesh Agro Foods 12.83 ENE 75 TNR Roadways 13.23 SSE 76 Dhamu Textile Engg. Works 13.63 SE 77 Tanya Exim Pvt. Ltd 13.87 SE 78 Sandeep Textiles 14.07 SSE 79 Aalishan Exports India Pvt.Ltd 14.07 SSE 80 Nirmal Cotex Pvt ltd 14.12 SSE 81 Neelmani Factory 14.51 E 82 BB International 14.56 NE 83 Harbhole Enterprise 14.77 SSE 84 Mk spuntex Pvt Ltd 14.79 SSE 85 Liberty Shoes Kutail 14.11 NE

133 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.5 Project Cost

The estimated cost for the proposed expansion project in approx.as follows

Table 2-4 Project Cost

S. No. Proposed Project Project Cost (Crores) 1 Panipat Refinery Capacity expansion from existing 32946 15 MMTPA to 25MMTPA Total 32946 Note: In Form-1 the project cost is being mentioned as 25600 crores and the revised cost from proponent is given above.

2.6 Proposed Schedule for Approval and Implementation

The Time Schedule for completion of the proposed project is given in Table 2-5

Table 2-5 Time Schedule for proposed project S. No. Particulars Time Schedule 1 EC October 2021 2 Consent to Establish from PCB 2022 3 Civil Works 2023 4 Erection & Installation of Machinery 2023 5 Commissioning 2024 6 Consent to Operate from PCB 2024

2.7 Project Details

2.7.1 Existing Facility Description

Panipat Refinery has following Process Units besides associated facilities viz. tankages, Utilities Producing Centers (Thermal Power Station, Compressor Houses), Offsite, Effluent Treatment Plant etc. Brief description of these plants is given in Table 2-6. The Schematic diagram of Existing Facility is given in Figure 2-6

Table 2-6 Plant Description

S. No. Unit Purpose of the unit 1. Atmospheric & Vacuum Unit Refining of crude oil to produce various (AVU) petroleum fractions 2. Visbreaker Unit (VBU) Moderate cracking leading to viscosity reduction of heavy residue 3. Continuous Catalytic To produce motor spirit from naphtha by Reforming Unit (CCRU) catalytic reforming 4. Hydrogen unit To produce hydrogen by steam naphtha reforming process 5. Once through Hydrocracker To produce middle distillate from vacuum gas Unit(OHCU) oil by hydro cracking.

134 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 6. Resid Fluidized Catalytic Catalytic cracking leading to upgradation of Cracking Unit (RFCCU) residue to distillate products 7. Bitumen Blowing Unit (BBU) Bitumen production by oxidation process 8. Merox units Sulphur & Mercaptan removal 9. Sulphur Recovery Unit(SRU) Sulphur Recovery from refinery gases & SSRU

2.7.1.1 Size & magnitude of operation List of existing units with annual capacity is summarized in Table 2-7 Table 2-7 Existing Units in the refinery

S.No Name of Unit Units Existing Capacity 1 CDU 1 MMTPA 7.5 2 VDU 1 MMTPA 3.75 3 Resid Fluidized Catalytic Cracking Unit MMTPA 0.85 (RDCCU) 4 Propylene Separation Unit (PSU) MMTPA 0.225 5 Once Thru Hydrocracker Unit MMTPA 1.9 6 Continuous Catalytic Reforming Unit MMTPA 0.65 (CCRU) 7 Hydrogen Generation Unit (HGU) TMTPA 38 8 VisbreakerUnit (VBU) MMTPA 0.4 9 Diesel Hydro Desulphurisation Unit TMTPA 0.77 (DHDS) 10 Bitumen Blowing Unit (BBU) MMTPA 0.5 11 SulphurRecovery Units (SRU/SSRU) TPD 2 *115 12 Amine Regeneration Unit m3/hr 400 13 Sour Water Strippers I (Refinery) m3/hr 71.8 14 Sour Water Strippers II (OHCU) m3/hr 16 15 SR LPG treatment MMTPA 0.142 16 Merox: TPA 190000 1.FCCGasoline 200000+100000 2.CrackedLPG(FCC+DCU) 1150000 3.ATF/KERO 17 Crude Distillation Unit (CDU‐II) MMTPA 7.5 18 Vacuum Distillation Unit (VDU‐II) MMTPA 3.75 19 Hydrocracker Unit MMTPA 1.8 1.7 20 Delayed Coker Unit MMTPA 3.0 21 Hydrogen Generation Unit (HGU –2&3) MTPA 2*70 22 Sulphur Recovery Units SRU (3,4 &5) TPD 3 *225 23 Coker LPG Merox unit MMTPA 0.1 24 Straight Run LPG Merox unit MMTPA 0.142 25 Diesel Hydrotreating Unit (DHDT) TMTPA 3.5 26 Amine Regeneration Unit (ARU‐II) m3/hr 410 27 Sour Water Stripper (SWS‐III) m3/hr 170 28 Hydrocracker Sour Water Stripper m3/hr 40

135 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S.No Name of Unit Units Existing Capacity (SWS‐IV) 29 NSU‐II TPA 0.75 30 Naptha oxygen stripping unit MTPA 400,000 31 Naphtha hydrotreating MTPA 500,000 32 Continuous catalyst (Platforming + MTPA 500,000 Regeneration) 33 Shell sulfolane extraction unit MTPA 152,200 34 Benzene Toluene fractionation unit MTPA 379,800 35 Paraxylene Extraction unit (PAREX) MTPA 2,025,400 36 Xylene fractionation unit MTPA 481,700 37 Trans alkylation MTPA Disproportionate(Tatoray) 360,200 unit 38 Isomerisation unit (Isomar) MTPA 1,656,500 39 PTA UNITS MTPA 553000 40 PXFEEDUNIT(NSU‐I) MMTPA(BH) 1.3 41 NHT TMTPA 410 42 PENEX TMTPA 400 43 RSU TMTPA 470 44 FCCGDU TMTPA 370

BS-VI units

1) U-20 (SWS 40 m3/hr) 2) U-26 & U-57 (TGTU equivalent to 450 TPD of sulphur production) 3) BS-VI units (DHDT, HGU, SRU, TAME, ARU, SWS)

2.7.1.2 Dispatch of Products

Products of the refinery are dispatched through all three means of transportation, i.e. pipelines, road and rail. The major portion is transported by pipeline.

SMPL terminal is within the refinery battery area and in case of any emergency; all firefighting facilities and necessary assistance are being rendered by the refinery.

2.7.1.3 Auxiliary Facilities

The water requirement of the refinery is met from Western Yamuna canal . Two raw water reservoirs of 2,25,000 m3 capacity have been provided to stock water in the refinery. For treatment of water two water treatment plants have been provided.

136 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report To meet the steam and power requirement of the refinery, a Captive Thermal Power Plant has been provided. Compressed air requirement is met through air compressors and a distribution network of plant air and instrument air.

The Refinery site is having well designed &self-sufficient Fire Fighting facilities given in Annexure 19.(IOCL Panipat Refinery ERDMP Manual chapter 17.)

Products of the refinery are dispatched through all three means of transportation, i.e. pipelines, road and rail. A major portion is transported by pipeline. The different pipelines for product evacuation are:

1) Mathura‐ Pipeline with the following branches: a. Roorkee‐ Najibabad and b. Sonepat‐Meerut 2) Panipat‐ 3) Panipat‐Bhatinda Salaya Mathura Pipeline (SMPL) terminal is within the refinery battery area and in case of any emergency; all fire fighting facilities and necessary assistance are being rendered by the refinery.

2.7.1.4 Other Auxiliary Facilities

The water requirement of the refinery is met from western Yamuna canal which is at a distance of about 0.5km (S) from the refinery complex.

137 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Source: IOCL Panipat Figure 2-6 Existing Block flow diagram

138 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.7.1.5 Existing Utilities

(a) Raw Water treatment plant and Treated Water reservoir (b) RO based DM water plant (c) Circulating Cooling Water Systems (d) Captive power plant (CPP) for Steam & power

(e) N2/O2 plant (air Liquefaction type) on BOOT Basis f) Instrument Air& plant air systems The details of existing storage tanks are given in Table 2-8 Table 2-8 Existing Storage Tanks

S. Material Capacity No of Dia HT Class of No. (KL) Tanks (M) (M) Material Crude oil storage 1 Crude 50000 7 70 14.4 A 2 Crude 38000 2 62 14.1 A 3 Crude 40000 2 62 14.575 A 4 Crude 30000 2 54 14.1 A Product Tanks/ Spheres/ Bullets in Refinery 1 LPG Spheres 1500 7 14.5 -- - 2 LPG Mounded Bullets 2873 4 70 7 - 3nap Propylene Spheres 950 2 12 -- A th 4 80 MT Gasoline Bullet 200 1 13.2 4.40 A 5 Naphtha 5000 4 25.50 11 A 6 Naphtha/ Heart Cut Naphtha 5000 2 25.5 11 A 7 Naphtha 19200 1 45.4 13.4 A 8 Naphtha/ GT Naphtha 20000 1 45 14.2 A 9 MS/ Naphtha 19200 1 45.4 13.4 A 10 MS 15000 4 40 13.4 A 11 MS/ Isomerate 4000 1 20 14 A 12 MS/ Isomerate 10000 1 30 14.5 A 13 Naphtha/ GT Naphtha 2000 2 16.2 11.25 A 14 LBT 4000 1 20 14 15 ATF 15000 5 40 14.4 B 16 MTO 2000 2 16.2 11.25 B 17 Kerosene 20000 4 45 14.4 B 18 Kerosene 10000 1 14.4 14.5 B 19 Heavy Kero 1000 2 30 10 B 20 HSD 40000 8 13 14.4 B 21 E- III HSD 10000 1 62 10 B 22 FFS 5000 4 30 10 C 23 Bitumen 5000 4 25.5 10 -- 24 Bitumen (Dual) 5000 2 25.5 10 -- 25 Bitumen (Feed) 5000 3 25.5 10 -- 26 IFO 5000 4 25.5 10 C 27 SLOP Oil (Black) 5000 2 25.5 10 C 28 SLOP Oil (White) 5000 1 25.5 10 A 29 LDD/ Slop Oil (MKTG) 2000 2 16.2 10 C 30 Benzene 1520 3 14.3 12 A 31 Para Xylene 10000 3 32.8 14.4 A Source : IOCL Panipat

139 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.7.1.6 Existing Fire and Gas Monitoring System Fire hydrant pipelines used to supply water under pressure to various places within refinery and parking area.

The fire hydrant system consists of: (a) Double Fire hydrant posts and monitors (b) Diesel driven fire water pumps (c) Fire water storage tanks The fire hydrant mains cover the entire Refinery. The number of fire monitors and hydrant points provided in Table 2-9

Table 2-9 List of fire hydrants

Sr. Equipment/ System Quantity Frequency F&S/ARC No. Description

 Road Trial– Each shift FT‐5Nos.FN‐02Nos.DCP‐  Pump & 1 Fire Tender F&S 01 No.,TP‐02Nos. Equipment Checking‐ Weekly 2 Fire Hose 101 No. in Fire Tender Six‐Monthly F&S DCP‐4316 3 Fire Extinguishers CO2‐1141 Quarterly ARC CleanAgent‐20 4. Fire Hydrant 1979 Nos. Quarterly ARC 5 Fire Monitor 593 Nos. Quarterly ARC Monthly‐ HVLR Monitor F&S 6 306 Nos. Monthly/Quarterly (Remote/ Manual) Quarterly‐ ARC Water spray system 7. 129 Nos. Six Monthly F&S (offsite)

Floating– 8. Foam Pourer 137 Nos. Annually F&S Fixed –ARC

Multigas‐40 H2S‐219Nos. CO‐29Nos. Portable Gas 9. O ‐28Nos. Quarterly ARC Detector 2 NH3‐14Nos. H2‐22Nos. SO2‐25Nos.

140 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.7.2 Proposed Facility

2.7.2.1 Process Description A brief process description for each of the process unit as part of the selected refinery configuration is provided in this section. 2.7.2.2 Crude Distillation Unit a. Crude Charge and Preheat Train-I

Crude from offsite storage is received at CDU/VDU plant battery limit. The crude is subsequently heated in preheat exchangers by hot streams of CDU/VDU. Crude picks up heat in the preheat exchangers before being routed to Crude desalter. b. Desalter A 2-stage electrostatic Crude Desalter to be provided for removal of salt and water from the crude to desired level. The principle of desalting operation requires mixing of preheated wash water in a mixing valve with the crude under controlled conditions and to extract impurities. c. Crude Preheat Train-II and Preflash The crude from Desalter outlet is routed to the 2nd train of pre heat exchangers. Crude picks up heat from hot streams of CDU/VDU and routed to Preflash drum. The liquid separated in the Preflash drum is pumped to crude preheat train-III. d. Crude Preheat Train-III The pre flashed crude is heated in 3rd preheat train exchangers. Crude picks up heat from hot streams of CDU/VDU and finally routed to crude heater.

e. Crude Heater The preheated crude is fed to the crude heater and equally distributed to the heater passes through pass balancer control valve. The total crude flow to the unit signal is sent to the crude throughput controller, which sends signal to the furnace flow controllers. f. Crude Distillation Column Heated and partially vaporised crude enters crude column through feed nozzle. The column has five side draws, namely, Light Naphtha (SN), Heavy Naphtha (HN), Kerosene (Kero), Light Gas Oil (LGO) and Heavy Gas Oil (HGO). g. Crude Column Overhead Circuit The overhead system consists of a two stage condensing system with wash water circulation. Sour water separated in reflux drum is partly returned as wash water for atmospheric column overhead vapours. All the salt are dissolved in wash water and are purged out of the system

141 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report through sour water purge stream to sour water stripper unit. Additionally Filming Amine is also injected in the crude column overhead line in order to protect the overhead line. h. Light/Heavy Naphtha Section Naphtha is drawn as side product to side stripper. Stripper is provided with thermosiphonre boiler to knock off light ends from naphtha. The CDU hot stream is used as heating medium in reboiler. The bottom product of light/heavy naphtha stripper is pumped to naphtha product cooler. The cooled product ex-product cooler is finally routed to storage. The light hydrocarbon vapours leaving the naphtha stripper is returned to the crude column. Kero product from Kero Stripper bottom is pumped by Kero Product pump. After heat recovery, Kero product is further cooled in product coolers to required rundown temperature and routed to storage. i. LGO Product Circuit LGO Product from LGO Stripper is pumped by LGO product Pump for heat recovery, After Heat Recovery LGO product is further cooled in product coolers to required rundown temperature and routed to storage. j. HGO Product Circuit HGO Product from HGO Stripper is pumped by HGO Product Pump. After heat recovery, HGO product is further cooled in product coolers to required rundown temperature and routed to storage. k. RCO Product Circuit Normally, Reduced Crude Oil (Crude Column residue, RCO) from Crude Column is pumped to vacuum unit without any cooling. However, provision is kept to cool the hot RCO stream in crude preheat circuit and coolers to facilitate to operate Crude unit alone without Vacuum unit and route the RCO stream to storage. 2.7.2.3 Naphtha Stabilizer a. Naphtha Stabiliser Column The unstabilised naphtha consisting of all the fuel gas, LPG and Naphtha components is pumped to Naphtha stabiliser column after preheating in the stabiliser feed/bottom exchanger. The overhead products are partially condensed in the Stabiliser Overhead Condenser. Fuel gas and LPG are withdrawn from the overhead circuit. Fuel gas is routed to Fuel Gas ATU and LPG is routed to LPG Treater. Stabiliser column is a reboiled column using CDU hot stream as reboiling medium. Stabilised Naphtha is further cooled in the exchanger to required rundown temperature before routing the same to the storage.

142 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.7.2.4 Vacuum Distillation Unit a. Vacuum Heater Hot RCO from Crude column bottom is pumped by RCO pumps to Vacuum heater. Each coil outlet of vacuum heater joins the transfer line and is routed to Vacuum distillation column. The mixed vapour & liquid stream from the heater is introduced to the Flash zone of Vacuum column. b. Vacuum Distillation Column Heated & partially vaporised RCO from Vacuum Heater enters the Vacuum Column. An open ended tangential entry device and a large empty space above flash zone ensure optimal vapour liquid separation. c. Stripping section: The heavy hydrocarbons are stripped on valve trays. Subsequently the residue is quenched by the vacuum residue product (Quench) to prevent after cracking in the bottom compartment of the column. The various side streams taken out from Vacuum Column are Vacuum Diesel, LVGO, HVGO and Slop Distillate. d. Overhead Circuit: Overhead vapour from vacuum column goes to the vacuum system. The vacuum system is designed with a two stage ejector and a vacuum pump as the third stage. Sour water from Hotwell is pumped by Hotwell Sour water pumps. Sour water ex-Hotwell flows under interphase level-cascaded flow control for further treatment in sour water stripper unit. e. Vacuum Diesel Section: Vacuum Diesel is drawn and pumped by Vacuum Diesel Product + CR + IR Pump and is divided into 2 streams, namely, Vacuum Diesel IR, Vacuum Diesel CR + Product. Vacuum Diesel IR is returned back under flow control to the Vacuum Column. The product stream is cooled in the Vacuum Diesel Product + CR Trim Cooler f. Gas Oil Section: Gas oil is collected in collector tray and pumped by Gas oil IR pumps under level control along with LVGO CR through spray nozzle distributor. g. Light Vacuum Gas Oil Section (LVGO): LVGO from collector tray is pumped by LVGO Product + CR + IR Pump and is divided into 3 streams, namely, LVGO IR, LVGO CR and LVGO product. LVGO IR is returned back under flow control to the Vacuum Column LVGO CR is cooled in crude/LVGO CR Exchanger before returning back to the Vacuum Column along with Gas oil IR.

143 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report h. Heavy Vacuum Gas Oil section (HVGO): HVGO from Collector tray is pumped by HVGO Product pumps and HVGO CR + IR Pumps HVGO CR+ IR streams are split into two streams namely HVGO CR & HVGO IR. HVGO product after exchanging heat with crude in crude preheats exchangers is combined with LVGO and the combined VGO is cooled in tempered water cooler before being routed to storage. i. Wash section: Slop from bed collector tray flows by gravity to the Slop Drum. Slop from this drum is pumped by Slop Distillate Pump and is divided into 2 streams. Vapours rising from flash zone are condensed by HVGO IR and collected as slop in collector tray. This liquid provides the required washing in this section. j. Vacuum Residue Section (VR): (Vacuum Residue + Quench) from Vacuum Column bottom is pumped by VR + Quench Pump to crude preheat train for heat recovery in Crude/VR+Quench exchangers. TheVR + Quench stream is then split into two streams and one stream as VR quench is returned back to the Vacuum Column under flow control cascaded with vacuum column bottom stream temperature controller.

2.7.2.5 Product Rundown section a. Hot well vacuum slop oil: Hot well vacuum slop oil from Hot well is pumped by hot well Slop Oil Pumps through a coalescer and routed to downstream unit for further processing. Sour water from coalescer is routed to sour water rundown line. b. Vacuum diesel Product: Vacuum Diesel from collector tray is drawn and pumped by Vacuum Diesel Product + CR + IR Pump and is divided into 2 streams namely Vacuum Diesel IR, Vacuum Diesel CR + Product. Hot Diesel stream after heat recovery is routed to DHT/DHDS and cold stream after cooling to required rundown temperature is sent to the storage. c. LVGO Product LVGO from collector tray is pumped by LVGO Product + CR + IR Pump and is divided into 3 streams namely LVGO IR, LVGO CR and LVGO product. LVGO is combined with HVGO after heat recovery and the combined stream namely Vacuum Gas oil (VGO) is

144 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report routed to downstream unit. VGO is further cooled in cooler to required rundown temperature before routed to storage. d. HVGO Product HVGO product from Collector tray is pumped by HVGO Pump. Subsequently HVGO is combined with LVGO after heat recovery and the combined stream namely Vacuum Gas oil (VGO) is routed to downstream unit.VGO is further cooled in cooler to required undown temperature before routed to storage. e. Slop distillate product: Slop from collector tray flows by gravity to the Slop Drum. Slop from this drum is pumped by Slop Distillate Pump and is divided into 2 streams. One stream is returned under flow control back to Vacuum Column as over flash while the second stream as Slop Product is mixed with Vacuum residue. f. Vacuum residue product: (Vacuum Residue + Quench) from Vacuum Column bottom is pumped by VR + Quench Pump to crude preheat train for heat recovery in Crude/VR + Quench exchangers. The VR + Quench stream is then split into two streams. One stream as VR quench is returned back to the Vacuum Column and other stream VR product is routed to residue processing units such as SDA, BBU after heat recovery. VR product is further cooled to required rundown temperature before routed to storage. g. Tempered Water System

The cooling of the high pour point products like Vacuum residue & VGO is done by tempered water to prevent exchanger congealing and to reduce exchanger maintenance. Tempered water is pumped from Tempered Water Drum by Tempered Water Pumps to VR/TW cooler and VGO/TW cooler.

2.7.2.6 Steam Generation Section Make-up BFW is preheated by VR + Slop rundown stream in VR + Slop/BFW preheater. This make-up BFW then splits into two parts. One of the make-up BFW stream is fed to LP steams drum. The other Makeup BFW stream is fed to MP steam drum. a. Blowdown Blowdown from MP steam drum is flashed in a LP flash drum. The flashed condensates from this LP flash drum and blowdown from LP steam drum is sent to Steam Blowdown Drum where it is quenched with service water before draining it to storm sewer. b. Chemical Dosing Facility

145 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report This system caters to CDU/VDU units. c. Demulsifier Demulsifier chemical is unloaded into demulsifier drums. The drum is provided with a mixer which can be used for preparation of desired concentration levels of the chemical. Demulsifier injection is done at the inlet of First stage desalter. d. Filming Amine Filming amine is unloaded into Filming amine drum. The drum is provided with a mixer, which can be used for preparation of desired concentration levels of the chemical. It is injected in the column overhead circuit to prevent corrosion. e. Neutralising Amine Neutralising Amine chemical is unloaded into Neutralising Amine drum. The drum is provided with a mixer, which can be used for preparation of desired concentration levels of the chemical. It is injected in the column overhead circuit for pH adjustment and to prevent corrosion. f. Caustic Solution Caustic solution is required in the unit for caustic make-up to Vent Gas Caustic Scrubber. 10 wt% caustic solutions is obtained from OSBL, which shall be used for make-up in Vent Gas Caustic scrubber. 5 wt% Caustic solution might be required in the unit to be injected into crude line downstream of desalter.

2.7.2.7 VGO HDT VGO HDT unit shall treat the LVGO and HVGO from the CDU/VDU and gas oil from bottom processing unit. Fresh feed is preheated, pumped and mixed with the preheated recycle gas. The mixture is brought up to reaction temperature by the reaction furnace. In the reactors the reactions are highly exothermic; therefore, the temperature at the inlet of each bed is controlled by a quench gas injection. The reactor effluent is then fed into the hot HP separator drum. The vapor phase from hot HP separator is cooled and water is injected at the inlet of the air cooler. The air cooler effluent is collected in the cold HP separator drum where three phases are separated. The sour water is removed and routed to the sour water stripper system. The gas phase is sent to the recycle gas HP amine absorber where almost all H2S is removed. The recycle gas is separated in two parts, one towards quench and the other one with makeup gas to feed effluent exchanger. The hydrocarbon liquid phase from the cold HP separator drum is routed to the LP separator. At LP separator, the hydrocarbon liquid phase is combined with

146 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report hot HP separator liquid phase and routed to the inlet of the stripper where stripping is ensured by injection of medium pressure steam at the bottom of the column. The overhead vapors from the stripper is partially condensed by air and cooling water and collected in the reflux drum. The liquid hydrocarbon phase is used part as reflux to the stripper and part is sent for gas recovery. The stripper bottom is heated and feeds the main fractionator where hydrotreated VGO is stripped with superheated LP steam in the bottom section of the column. Fractionator overhead stream is cooled and party refluxed back to the column and partly recovered as unstabilized naphtha which is routed to Debutanizer. The diesel fraction is routed to side stripper where part is recycled back to the column and part is obtained as diesel product. Fractionator bottom product preheats the fresh feed, fractionator feed and reboils the debutanizer and the deethanizer and also generates low-pressure steam and is finally cooled in an air cooler before it is sent to storage. LP separator vapor phase and stripper reflux drum vapor and liquid streams are routed to Deethanizer via Deethanizer feed drum. Deethanizer bottom combines with Fractionator reflux drum liquid phase to feed Debutanizer. Debutanizer overhead vapour is totally condensed and part is routed back to column and net distillate is pumped as LPG. The purpose of Absorber is to maximize LPG recovery which is achieved by counter flow of cooled naphtha coming from Debutanizer bottom. Absorber overhead vapor go to LP amine absorber from where sweet gas is obtained. 2.7.2.8 INDMAX FCC with Propylene Recovery Unit INDMAX FCC is a fluidized catalytic process for selectively cracking a variety of feed stocks to light olefins. INMAX FCC is similar to conventional FCC in terms of basic process employed. But the cracking is higher in INDMAX unit. The objective of this process is maximization of LPG with higher selectivity towards propylene. LPG yield is typically 36-40 percent and propylene is typically 20 wt%. Dry gas produced from this unit is rich in ethylene. Hence, INDMAX unit provide opportunity for establishing downstream petrochemical units. Propylene is recovered from LPG in downstream PRU and sent to downstream Polypropylene unit. There is potential to use the dry gas rich in ethylene for the production of styrene monomer after reacting with benzene to form ethyl benzene. To achieve the higher conversions, unit operates at higher severity with high reactor temperature, higher quantity of dispersion steam in the reactor and higher catalyst to oil ratio. The catalyst employed is zeolitic in nature. High ZSM-5 to the extent of ~ 15% is added to

147 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report achieve the desired conversions and propylene make. Some licensors offer the catalyst impregnated with ZSM-5. The INDMAX unit reactor regenerator system utilizes a reactor/riser, catalyst stripper, 1st stage regeneration vessel, 2nd stage regeneration vessel, catalyst withdrawal well and catalyst transfer lines. Fresh feed, from upstream VGO HDT Unit, is finely atomized with dispersion steam and injected into the riser through feed injection nozzles over a dense catalyst phase. The small droplets of feed contact the freshly regenerated catalyst and instantly vaporize. The oil molecules mix intimately with the catalyst particles and crack into lighter and more valuable products. As the reaction mixture travels up the riser, the catalyst, steam and hydrocarbon product mixture passes through a riser termination device. This device quickly disengages the catalyst from steam and product vapors. Reactant vapors are then ducted to the top of the reactor near the reactor cyclone inlets, while catalyst is discharged into the stripper through a pair of catalyst dip legs. The vapors with entrained catalyst pass through single-stage high-efficiency cyclones. Reactor products, inerts, steam and a minute amount of catalyst flow into the base of the main fractionator and are separated into various product streams. Below the dense catalyst bed in reactor vessel, a steam ring strips off volatile hydrocarbon material from reacted catalyst particles. Stripped catalyst leaves the reactor vessel through catalyst withdrawal pipes and enters the 1st stage regenerator through a catalyst distributor that disperses the catalyst onto the bed surface. Catalyst and combustion air flows counter currently in the 1st stage regenerator vessel. Partially regenerated catalyst exits near the bottom of the vessel through a hollow stem plug valve. A lift line conveys the catalyst into the 2nd stage regenerator vessel utilizing lift air. CO-rich flue gas from the regenerator vessel exits through two-stage high efficiency cyclones. A mushroom grid evenly distributes the catalyst in 2nd stage regenerator vessel. Any carbon remaining in the catalyst is completely burned off with an excess amount of air in this regeneration stage. This results in high temperatures. Several design features like external cyclones and a catalyst cooler are incorporated to minimize any mechanical and/or physical temperature limitation. Hot regenerated catalyst flows into a withdrawal well, through regenerated catalyst slide valves and into the "wye" section at the base of riser. Here, it meets the hot feed. The INDMAX FCC gas recovery section employs a low pressure drop main fractionator design with warm reflux overhead condensers to condense the large amount of steam used in the convertor. A large wet gas compressor is required relative to FCC operation because of high amount of dry gas and LPG. The absorber and stripper columns, downstream

148 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report of the wet gas compressor are specifically designed for enhanced C3 recovery at relatively gasoline rates. In addition to the above three products, the product fractionator separates the catalytically cracked material into heavy naphtha, light and heavy cycle oils and catalyst slurry. The heavy cycle oil is recycled back to the reactor. The catalyst slurry contains some lighter hydrocarbon oil, clarified oil, which is subsequently separated and may be recycled back to either the reactor or to the internal fuel oil pool. The flue gas handling system downstream of the INDMAX regenerator requires considerations no different than those of as FCC system. It consists of a flue gas slide valve to control the differential pressure between the reactor and regenerator followed by an orifice chamber. Heat is recovered by flue gas cooler in the form of high-pressure superheated steam. Flue gas is de-sulphurized before sending out. a) Propylene Recovery Unit The Feed to the PRU consists of INDMAX Propylene from upstream INDMAX unit. The feed is first sent to a Depropanizer to recover a C3-rich cut from the propylene. The Depropanizer bottom is routed to the refinery LPG pool. The Depropanizer overhead is totally condensed against cooling water in the Depropanizer Condenser and the bubble point liquid enters Depropanizer Reflux Drum. The Depropanizer pressure is maintained by the overhead pressure controller which permits hot vapor to bypass the Depropanizer Condenser. The drum is pressurized by the hot vapor in order to maintain the reflux drum liquid at, or near, bubble point. If non condensable build up in the reflux drum, they can be purged to the High Pressure Separator on pressure control for LPG recovery. Water condensed in the tower overhead system is routed to the Sour Water Flash Drum. The hydrocarbon liquid out of the reflux drum is split into two streams; the Depropanizer Reflux & PP Mix .The reflux is pumped back to the tower while the P-P Mix pumps send the mixed C3‟s product stream to the Propylene Recovery Unit (PRU). PP Mix (Depropanizer overhead) sent for drying & for RSH/COS removal. The dry, sulfur- free PP Mix is then sent on to the C3 Splitter system. The PP Mix from the PP Mix RSH/COS Removal beds is fed to one of three feed trays in the C3 Stripper. The C3 Stripper overhead is sent to the C3 Rectifier. The C3 Stripper uses high- capacity MD Trays. The C3 Stripper has an intermediate, or side reboiler and bottom reboilers using hot water and LP steam as heating media. The bottom of the C3 Stripper, C3 LPG, is cooled by cooling water in the C3 LPG Cooler and sent on flow control to battery limits for storage.

149 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report The C3 Rectifier gets feed from the overhead of the C3 Stripper. The C3 Rectifier also uses high-capacity MD trays. The bottoms of the C3 Rectifier are pumped by the C3 Splitter Transfer Pumps, on flow control reset by level, back to the C3 Stripper. The overhead of the C3 Rectifier flows to the C3 Rectifier Condensers, condensed by cooling water, and then to the C3 Rectifier Reflux Drum. There is a vapor-liquid equilibrium in the reflux drum. The non-condensable vapor leaves the drum and is recycled back to the High Pressure Separator Condenser in the gas plant. The pressure in the reflux drum is controlled by a hot vapor bypass. It opens when the pressure is low. It resets the vent recycle flow when the pressure is high. It is expected to always have a small vent recycle flow. The vent recycle is on flow control and it is reset by pressure. The polymer-grade propylene (PGP) is withdrawn below the tray #134.

2.7.2.9 Diesel Hydro treater The Diesel Hydro treating Unit reduces the levels of sulphur and other contaminants in diesel fuel products to meet regulatory specifications. The diesel feedstocks, including straight-run diesel liquid streams from the Crude Distillation Unit and gas oil streams from the bottom processing units, are mixed with recycle hydrogen and heated to the reaction temperature in a fired heater. The feed mixture is passed over reactor beds (cobalt-molybdenum/ nickel- molybdenum catalyst) with inter-bed quench. Hydrogen sulfide and ammonia by-products are removed in the water wash section and an amine contactor downstream of the reactor. The aqueous wash fraction containing some hydrogen sulfide and ammonia is removed in a separator, and routed to the sour water collection system. The H2S-rich amine from the contactor is regenerated before being returned to the recycle gas scrubber as lean amine. The sweetened gas from the amine absorber is recycled back to the recycle gas compressor at the reaction section inlet. A stream of H2-rich gas through makeup gas compressor meets the feed stream. Liquid organic effluent from the reactor is routed to a stripper where distillates and unstabilized naphtha is separated. Unstabilized Naphtha is routed to a stabilizer to remove light end hydrocarbons, which are routed to the LPG treating plant for processing and stabilized naphtha is further processed. The stripper bottoms are separated into naphtha, kerosene, and diesel fractions in a fractionator column. Naphtha-cut boiling point material is removed as the overhead stream

150 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report and is sent for treatment. The hydro treated kerosene and diesel streams are sent to storage for blending. 2.7.2.10 Naphtha Hydrotreater Unit a. Naphtha Hydrotreater Section Naphtha feed to NHT passes through a surge drum and a charge pump. It is then combined with a H2-rich gas stream from the recycle gas compressor. The combined feed enters the reactor feed/effluent exchanger, where the feed is heated. The heated feed is brought up to the reaction temperature in a feed charge heater. The hot feed down-flows through a fixed-bed reactor where the catalyst reacts with the feed to remove sulphur as H2S, in presence of H2.The reactor effluent is cooled first in the reactor feed/effluent exchanger and then in the product air cooler. Wash water is injected into the reactor effluent upstream of the product air cooler so that any salt build up in the condenser may be washed out. Reactor effluent flows out of the condenser at a low temperature to ensure complete recovery of naphtha and enters the separator The separator is provided with a mesh coalescer to ensure complete separation of vapor, hydrocarbon liquid and sour water. Sour water is sent to SWSU, H2-rich vapor is recycled back to the reactor through recycle gas compressor. A H2-rich makeup stream is fed into the recycle stream through a makeup gas compressor. Liquid hydrocarbon from separator is heated by heat exchange with stripper bottoms in stripper feed/bottom exchanger and enters the stripper near its top. A steam reboiler provides stripper heat duty. Overhead vapor from the stripper pass onto the stripper trim cooler partly condenses and separates into three phases in the stripper receiver. Net overhead gas from the stripper receiver is passed onto the refinery fuel gas system after amine treatment to remove all H2S. Sour water from the receiver is sent to SWSU. Hydrocarbon liquid from the receiver is sent back to the stripper as total reflux. Hydrotreated sweet naphtha from stripper bottom is cooled in stripper feed/bottom exchanger and then sent to naphtha/gasoline pool. b. Naphtha Splitter Section The Hydro treated Naphtha from Naphtha Hydro treating unit passes through a surge drum and a charge pump. The feed enters the splitter column and is fractionated. The heat to the fractionator is provided by a Reboiler. The Overhead vapors are condensed in the overhead cooler into a Reflux drum. The overhead Light Naphtha is partially pumped as reflux to the column and partially taken as Light Naphtha Product. The Heavy Naphtha from the bottom of the splitter column is taken as Heavy naphtha Product.

151 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report The Light Naphtha becomes feed for Isomerization Unit while as Heavy naphtha becomes feed to CCR Unit. c. Continuous Catalytic Reformer Unit The Catalytic Reforming Unit processes the heavy naphtha stream to make it more suitable for the production of motor gasoline. The reforming process involves chemically rearranging the hydrocarbon molecules to produce higher-octane materials. The octane number is a key measure of motor gasoline performance. Hydrogen gas is produced as a by product of reforming, and is used as feed to the Naphtha Hydro treater Unit, Distillate Hydro treater Unit. The heavy naphtha feed streams are mixed with recycle hydrogen, preheated by exchange with reactor effluent, heated to reaction temperature in the charge heater and sent to the first of a series of three to four reactors. Each reactor is preceded by a gas fired feed heater to maintain a constant inlet temperature profile for the individual reactors (as reforming reactions that take place in the reactors are predominantly endothermic). Effluent from the last reactor is heat exchanged with the combined feed, Condensed in the product trim cooler and sent to the separator. The reformed naphtha product (reformate) is separated from the by-product hydrogen. A portion of the hydrogen is compressed and recycled to be mixed with heavy naphtha feed material. The remaining hydrogen is compressed for use in other refinery processing units. The reformate product is fractionated in the debutanizer for separation of light ends. The reformate liquid product is sent to storage, for use in motor gasoline blending. The Catalytic Reforming Unit reactor catalyst is continuously regenerated in the Catalytic Reforming Unit Catalyst Regenerator. The regeneration section of the reformer provides a continual stream of clean coke-free active catalyst that is returned back to the reactors. Continuous circulation of regenerated catalyst helps maintain optimum catalyst performance at high severity conditions for long on-stream periods of reforming operation. Catalyst regeneration takes place in dedicated equipment and uses nitrogen, air, and perchloroethylene as regenerating agents. The Catalyst Regenerator performs two principal functions - solid catalyst regeneration and circulation. Spent catalyst from the final Catalytic Reforming Unit reactor vessel is conveyed to the Catalyst Regenerator, where it is regenerated in four steps:  Coke burning with oxygen,  Oxychlorination with oxygen and chloride,  Catalyst drying with air/nitrogen, and

152 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report  Reduction of catalyst metals to "reduced" oxidation states. Exiting the Catalyst Regenerator, the regenerated catalyst is conveyed back into the first Catalytic Reforming Unit reactor. Small quantities of hydrochloric acid and chlorine are generated in the Catalyst Regenerator. The vent gas from the Catalyst Regenerator is scrubbed in two stages with caustic solution and water in the Vent Gas Wash Tower for removal of acid gases, in particular hydrochloric acid. From the Wash Tower, the cleaned. d. Isomerization Unit The fresh C5 /C6 feed is combined with make-up and re-cycle hydrogen which is directed to a charge heater, where the reactants are heated to reaction temperature. The heated combined feed is then sent to the reactor. Either one or two reactors can be used in series, depending on the specific application. The reactor effluent is cooled and sent to a product separator where the recycle hydrogen is separated from the other products Recovered recycle hydrogen is directed to the recycle compressor and back to the reactor section. Liquid product is sent to a stabilizer column where light ends and any dissolved hydrogen are removed. The stabilized Isomerate product can be sent directly to gasoline blending. 2.7.2.11 Resid Hydro processing Unit a) Ebullated Bed Hydrocracker Fresh hydrocarbon liquid feed is mixed with hydrogen and reacted within an expanded catalyst bed that is maintained in turbulence by liquid upflow so as to achieve efficient isothermal operation. Product quality is constantly maintained at a high level by intermittent catalyst addition and withdrawal. Reactor products flow to the high-pressure separator, low pressure separator, and then to product fractionation. Recycled hydrogen is separated and purified. Process features include on-stream catalyst addition and withdrawal, thereby eliminating the need to shut down for catalyst replacement. The expanded bed reactors operate at near isothermal conditions without the need for quenches within the reactor. The reaction section uses a commercially proven low pressure hydrogen recovery system. Separating the reactor effluent and purifying the recycled hydrogen at low pressure results in lower capital cost and allows design at lower gas rates. An available process option is the integration of Ebullated bed technology with distillate hydrotreating or hydrocracking to produce high quality middle distillate products. This can eliminate the need for additional downstream processing. Unconverted oil from an Ebullated

153 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report bed HCU can be sold as a stable, low sulfur IFO or sent to another heavy oil conversion unit for further upgrading. b) Slurry Hydrocracker Slurry Hydrocracker Unit converts vacuum residue and other heavy residue feed stocks into higher valued distillate products. The heart of this technology is its reactor that can operate at high temperatures required to maximize vacuum residue conversion. Reactor conditions also allow the majority of the products to vaporize and quickly leave the reactor, thereby maximizing the residence time of the feed‟s heavier component and minimizing any undesirable secondary cracking reactions which would produce lower valued products and increase hydrogen consumption. c) Catalyst Preparation Section Catalyst is supplied to the refinery in the bulk form and stored in the raw catalyst storage silo. The raw catalyst is then transferred from the storage silos to the hammer mills, then to a second dust collector, weigh hopper, and finally into the slurry Mixing Tank and then transferred to the Slurry Storage Tank. The slurry storage tank has a pump and internal mixers to prevent any catalyst settling. The catalyst slurry is transferred to the feed heater by the Slurry Injection Pumps. d) Reaction Section The reactor section configuration contains all of the equipment necessary to accomplish where they are immediately quenched to terminate any reactions. The overhead streams from the reactor are sent to the Hot Separator. e) Gas Liquid Separation Section Effluent from the reactor is cooled by direct quenching with cool recycle gas upstream of the Hot Separator. The Hot Separator prevents heavy, high boiling reactor effluent components from causing water separation problems in the downstream Cold Separator. The vapor from the Hot Separator is cooled by heat exchange with recycle gas and reactor feed. Vapor is further cooled and wash water is added to prevent the formation of salts. Final cooling of the vapor takes place in the air cooler. The effluent then passes to the Cold Separator, where the sour water, hydrocarbon liquid and hydrogen rich gas are separated into three phases. The liquid from the Hot Separator flow so that the Hot Flash Drum. The Hot Flash Drum vapor is cooled and sent to Cold Flash Drum. The hot flash liquid is sent directly to the Stripper in the Fractionation Section. The feed to the Cold Flash Drum is cold separator liquid, cooled hot flash drum vapor, and cold separator sour water. The Cold flash drum vapor can be sent to Hydrogen Recovery. The liquid is preheated and sent to Stripper in Fractionation Section.

154 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report The hydrogen rich gas from Cold Separator id recycled back to the Reaction Section by the recycle gas compressor. Make up hydrogen is added to make up the consumption of hydrogen in various reactions. f) Fractionation Section This section contains all of the equipment to recover the light gaseous products and separate the liquid hydrocarbons recovered in the flash drums into the desired boiling range fractions. This section typically includes a Stripper, a Debutanizer, an atmospheric Fractionator and a vacuum Fractionator. The purpose of the steam-stripped Stripper is to remove 99.99% of the hydrogen sulfide overhead with negligible loss of kerosene boiling range material in the overhead liquid. The Stripper overhead vapor is sent to the off gas treating section of the refinery. Liquid hydrocarbons recovered in the Stripper overhead receiver are directed to downstream Debutanizer. The Stripper bottoms product flows to the Atmospheric Fractionator via Fractionator Feed Heater. In Atmospheric Fractionator naphtha and diesel is recovered. In order to recover vacuum cuts, Atmospheric Fractionator bottom is routed to Vacuum Fractionator where vacuum diesel, light vacuum gasoil and heavy vacuum gasoil are produced. Unconverted pitch is obtained from Vacuum Fractionator bottom and sent to storage. g) Hydrogen Generation Unit In a refinery, the reaction chemistry of hydro-processing units used for upgrading the straight run products or for increasing middle distillate yields rely on continuous supply of high purity hydrogen. For this purpose, Hydrogen Generation Unit is employed. The working of unit is based on catalytic reforming and pressure swing adsorption (PSA) system to produce 99.9 mole% pure hydrogen gases. Hydrogen is produced by steam reforming of Regasified Natural Gas. LNG from surge drum is pumped to LNG vaporizer. Vaporized LNG after mixing with recycled hydrogen and superheated steam enters the pre-reformer. Superheated steam is added to adjust the steam- carbon ratio, and the mixture is heated. The superheated feed-steam mixture is distributed through multi-tubular reactor consisting of high alloy reformer tubes containing nickel-based catalyst. Reforming reactions produces CO, CO2 and H2, and heat for the endothermic reaction is supplied by a number of burners with PSA purge gas and refinery fuel gas/ naphtha as fuel. The reformed gas after being cooled undergoes shift conversion in shift converters. These are cylindrical fixed bed reactors containing iron/chromium oxide or copper/zinc oxide catalyst.

Shift conversion reaction converts most of CO into CO2 and H2 in presence of the catalyst.

155 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report The heat removed from the converted process gas is used to vaporize and further heat the feed, and preheat boiler feed water and demineralised water (make-up). Downstream of Shift convertor is Process Condensate Separator where condensate is separated and routed for BFW formation and steam generation.

Process gas is purified to remove inert gas impurities like CO2, CO, CH4, N2 and water vapor by high-pressure adsorption of these impurities on molecular sieves, active carbon and alumina gel in Pressure Swing Adsorption (PSA) system. All adsorbed gases are removed during desorption and regeneration of the beds, and used as reformer burners fuel. h) Sour Water Stripper Unit (Two stage) The rich amine stream from various units is received by a flash column in ARU battery limit. This flash column allows for the removal of any associated hydrocarbon along with some

H2S which might also be liberated. This H2S is removed from the liberated hydrocarbon vapors by means of a lean amine which is brought into contact with the vapors in a counter current fashion over packed bed. The rich amine from flash column free of any associated hydrocarbon is routed to amine regenerator column through lean amine/rich amine exchanger. This preheated rich amine stream contacts with reboiler vapors from bottom in a counter current fashion.

This ensures removal of H2S from rich amine stream. The vapors obtained from column top are condensed using a reflux condenser, the water thus obtained is sent back to the column as reflux thereby preventing the escape of ammonia to overhead system by contacting the vapors moving up in the column in a counter current fashion. The acid gases from column overhead circuit are routed to SRU in steam jacketed lines. In case of SRU shutdown or high pressure in column, the acid gases can also be routed to acid gas flare network.

2.7.2.12 Amine Regeneration Unit Rich amine from various absorber units is received in a flash column. Rich amine is allowed to flash in the column to drive off hydrocarbons. Some H2S also gets liberated.

The liberated H2S is again absorbed by a slip stream of lean amine solution making counter current contact with liberated gases over a packed bed. From the flash column, the rich amine is pumped by rich amine pumps under flow control to amine regenerator, after preheating in lean amine/rich amine exchanger. In lean amine/rich amine exchanger, the heat is supplied to rich amine by hot lean amine on shell side from the bottom of amine regenerator under level control. The lean amine from lean amine/rich amine exchanger is further cooled in lean amine cooler and routed to amine storage tank. Another

156 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report part of lean amine from lean amine cooler is used as slip stream to cartridge filter to remove solid particles picked up amine in the system. It is also used to remove foam causing hydrocarbon substances and thereafter routed to amine storage tank. In amine regeneration column, reflux water enters the column top and descends down.

This prevents amine losses into the overhead and ensures complete removal of H2S. The reboiler vapors from the bottom of the tower counter currently contacts the rich amine and strips off H2S. The overhead vapors from regenerator are routed to regenerator overhead condenser, where most of the water vapors condense and are pumped by amine regenerator reflux pumps as reflux to the column. The acid gases are routed to the SRU. In case the pressure goes high, acid gases are released to the acid flare. Reboiler heat by LP steam is supplied to the column through amine regenerator reboiler

2.7.2.13 Sulphur Recovery Unit Acid gas from ARU passes through acid gas knock out drum, to remove any liquid carryover, before feeding to main burner. Similarly, any liquid carryover in sour gas from SWSU is removed in sour gas knock out drum. The air to main burner is supplied by an air blower, which also supplies air to Super Claus stage and sulfur degassing. The air to the main burner is exactly sufficient to accomplish the complete oxidation of all hydrocarbons and ammonia present in the feed gas and to burn as much H2S as required to obtain desired concentration. The heat generated in the main burner is removed in the waste heat boiler by generating steam. Then the process gas is introduced into the first condenser in which it is cooled, sulphur vapor condensed and is separated from gas. Upstream of 1st Claus reactor, the process stream from waste heat boiler is heated in 1st steam reheater to obtain optimum temperature for the catalytic conversion. The effluent gases from 1st reactor passes onto 2nd sulfur condenser where sulphur vapor is condensed and uncondensed process gases pass to the 2nd steam reheater. Heated vapors are again subjected to conversion in the 2nd Claus reactor followed by cooling in the 3rd sulfur condenser. Then the process gas passes to the 3rd steam reheater and the 3rd Claus reactor. Following reactions takes place inside the Claus reactor.

H2S + 3/2 O2 SO2 + H2O + Heat

2H2S + SO2 2H2O+ 3/n Sn + Heat

2NH3 + 3/2 O2 3H2O + N2 The sulfur formed remains in vapor phase and goes in polymeric reaction, which forms polymericsulfur in vapor phase. The predominate reactions are:

157 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

3S2 S6 + Heat

4S2 S8 + Heat Some of these combustion reactions also take place in the burner section of the reaction furnace. The lists of reactions taken place in the reaction furnace are given below:

CH4 + 2O2 CO2 + 2 H2O

CO2 + H2S COS + H2O

COS + H2S CS2 + H2O

2H2S 2H2 + S2

COS + H2O H2S + CO2 The unconverted H2S from the clause reactor is sent to the TGTU unit. Sulfur condensed in condensers is routed via sulfur locks to sulfur cooler and drained into sulfur degasification vessel. Stripping air is supplied to the spargers located at the bottom side of the vessel. This strips off H2S from liquid sulfur and oxidizes the major part of H2S to sulfur. Air leaving the stripping columns, together with H2S released from sulfur degasification vessel, and is routed to TGT Unit. Liquid Sulphur from pit is pumped by sulphur pumps to Sulphur Yard.

2.7.2.14 Tail Gas Treating Unit

The Tail Gas Treating Section is required for the removal of sulphur compounds (H2S, SO2,

COS, CS2, elemental sulphur) from the tail gas from the Claus Section. This is achieved by catalytic reduction of sulphur compounds to hydrogen sulfide and the subsequent absorption of hydrogen sulfide in a regenerable absorption medium (Amine). Rich amine is subsequently treated in Amine Regeneration Section in order to release the absorbed hydrogen sulfide which is recycled back to the Claus section for further recovery of elemental sulphur. The H2S recycled allows an overall sulphur recovery efficiency of 99.9% to be achieved.

Tail gas enters the hydrogenation reactor preheated at 130°C. H2 reducing gas is mixed with

Claus tail gas in the preheat effluent stream via a controller which is reset by the SO2 concentration in the downstream of the hydrogen reactor. The effluent is preheated under temperature controller by an electrical heater. A pre-sulfiding line is provided to activate the TGU catalyst using acid gas from the acid gas KOD. Thus line is not used for normal operation. The hot preheated effluent passes through the catalyst bed of the hydrogenation reactor where SO2 and other sulfur compounds are converted to H2S. Due to exothermic reaction, the gas temperature increases. The reactor inlet temperature should be held reasonably steady to

158 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report provide stable conditions in the reactor. To avoid excessive outlet temperature, the inlet gas may be controlled at somewhat lower temperature to compensate for more SO2 and/or S in the tail gas feed. However, excessively low reactor inlet temperature will result in poor conversion. The SO2 monitor at the reactor effluent is observed to maintain an excess of ~3%

H2. In addition, if the circulating water in the quench loop shows the presence of finally divided sulfur this indicates incomplete reaction and the SO2 has reached the column to form sulfur via the Claus reaction:

2H2S + SO2 3S + 2H2O This behavior should be monitored as the presence of the sulfur not only means the reaction is incomplete but the column can be plugged. Monitoring the pH of the quench water provides a pre-warning to an impending problem. The pH should be maintained near 7.0. Hot reactor exit gas must be cooled before entering the absorber. A first stage gas cooling is accomplished by generating steam at the TGU waste Heat Boiler, decreasing the process gas temperature. BFW is fed to the shell side of the TGU-WHB on level control and low pressure steam is generated. When the steam flow and/or BFW flow rate changes, the water level in the steam generator varies. Rising level in the generator indicates that the BFW flow rate is exceeding the rate of steam generation. In this case, signal to the level control valve will decrease. If the steam generation exceeds the BFW rate, level will decrease. In this case, signal to the level control will increase. The process gas enters the quench column. The quench water recirculating loop consists of the quench water pump, filter and water cooler. The cooler removes the heat from the column, cooling the inlet gas. The water flow to the top of the column is controlled after being filtered by quench water filter. Decreasing the water flow rate will increase the bottom temperature. Increasing the water rate will increase the load in the quench water circulation pumps and flow through the quench water cooler and column. The quench column recirculation system has the provision to adjust the pH by addition of caustic to the column recirculation line. The pH of the quench water to the water pump is monitored and kept at a value between 7 and 9 in an effort to prevent corrosion and inhibit colloidal sulfur formation. The water system should be visually inspected for cloudiness. Low pH will indicate incomplete reduction of sulfur compounds. Sour water condensed from the inlet feed is removed from the quench water loop via a zevel controller from the quench column and is sent offsite to sour water storage. The rate depends on the water in the Claus tail gas, water produced in the hydrogenation reactor and the amount of water overhead in the quench column.

159 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Downstream of these reactors, additional recovery of reduced sulfur is accomplished in an amine absorber column that uses an aqueous methyl di-ethanolamine (MDEA) solvent to scrub H2S from the TGTU tail gas. The overhead stream from this contactor, containing very low sulfur levels, is sent to the tail gas thermal oxidizer for disposal. The rich MDEA solvent is regenerated in the TGTU amine stripper and H2S is returned to the inlet of the Claus SRU trains to be recovered. Regenerated MDEA solvent is recirculated back to the TGTU amine absorber column.

Tail gas from TGU is routed to the incinerator where residual sulfur is converted to SO2 and discharged into the atmosphere. The overhead line from the quench column flows to the absorber. The absorber is a packed column and is designed to absorb practically all the H2S in the recirculating Amine solvent. Amine absorber column that uses an aqueous methyl di-ethanolamine (MDEA) solvent to scrub H2S from the TGTU tail gas. The overhead stream from this contactor, containing very low sulfur levels, is sent to the tail gas thermal oxidizer for disposal. The rich MDEA solvent is regenerated in the TGTU amine stripper and H2S is returned to the inlet of the Claus SRU trains to be recovered. Regenerated MDEA solvent is recirculated back to the TGTU amine absorber column. The purpose of the incinerator system is to oxidize all the sulfur compounds in the tail gas to

SO2 and to vent the oxidized stream at high temperature and at a high elevation. The incinerator system included the two primary sections: In the incinerator burner, fuel gas is burnt with excess air to a temperature over 1650oC. The temperature is sufficient to heat the tail gas from TGU to ~768oC. This temperature is sufficient to oxidize the residual H2S and sulfur compound, while minimize NOx and SO3 formation. The effluent is discharged to the incinerator stack. The stack height of 60 meters is set to ensure dispersion of SO2 and to meet ground level concentration limits. Effluent tail gas from the TGU absorber is thermally oxidized with air to convert reaming sulfur compounds to SO2. Fuel gas and excess air are combusted at high temperature at the incinerator burner. Then it is mixed with the absorber overhead effluent tail gas in the primary oxidation chamber. The fuel gas and air rates are adjusted to control the temperature of the mixed and oxidized tail gas stream. The air is supplied by a dedicated incinerator air blower. Excess air is used to ensure sufficient oxygen is present to oxides the sulfur and other sulfur compound. Oxidation reactions are as follows:

H2S + 3/2 O2 SO2 + H2O

160 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

2COS + 3 O2 2 CO2 + 2SO2

CO + ½ O2 CO2

CS2 + 3 O2 2SO2 + CO2

Sn + nO2 n SO2 The incinerator effluent temperature is measured and used to adjust the flow rate of fuel gas to maintain the desired operating temperature of 768oC. The incinerator is refractory lined with an external thermal shroud to control the shell temperature. Skin thermocouples are provided to monitor the shell temperature. The shell temperature should be maintained between 149 – 350oC. The air blower is designed to provide supply of air and stack while providing a minimum of o 2% excess O2 at an operating temperature of 768 C. Ambient air is drawn through the inlet filter to remove solid debris and to protect against water during heavy rainfall. The combustion gas from the burner and combustion chamber flow into the incinerator where adequate residence time is provided for combustion. The incinerator stack vents the effluent to the atmosphere. A SO2/O2 analyzer is provided to determine the SO2 and O2 in the effluent stream. Further P-25 configuration is capable of producing additional ~95 KTPA of ethylene and it is proposed to recover and utilize this additional ethylene during PNCP phase-2 expansion. The proposed block flow diagram in quantitative manner is enclosed as Annexue 27 and Figure 2-11.

Table 2-10 Process Units with Proposed Capacity

S. Name of the Unit Units Proposed Capacity No 1 AVU MMTPA 10 2 State Run LPG treatment unit (SR-LPGT) MMTPA 0.152 3 VGO Hydrotreater unit MMTPA 3.6 4 Diesel hydrotreater unit MMTPA 5.0 5 Propylene Recovery unit MMTPA 1.15 6 Resid Hydrocracker unit- RHCU MMTPA 2.5 7 INDMAX MMTPA 2.5 8 NHT/ CCR/ ISOM MMTPA 0.95/0.625/0.205 9 HGU MMTPA 0.081 10 ALKYLATION MMTPA 0.67 11 SARU MTPD 185 12 CDW/LOBS MMTPA 0.56 13 SRU-I/II/ TGTU TPD 2*465 /930 14 SWS-I/II TPH 252+180 15 ARU TPH 1256

161 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Name of the Unit Units Proposed Capacity No 16 MUG Compressor MMTPA 0.17

Table 2-11 Proposed block flow diagram 2.7.3 Raw Material and Mode of Transportation

Products of the refinery are dispatched through all three means of transportation, i.e. pipelines, road and rail. The major portion is transported by pipeline. SMPL terminal is within the refinery battery area and in case of any emergency; all firefighting facilities and necessary assistance are being rendered by the refinery. Dispatch of products from the petrochemicals complex is done through both road and rail transportation.

At present crude is being received from Mundra-Panipat Pipeline (MPPL) of capacity 8.4MMTPA and Salaya Mathura Pipeline (SMPL) of Capacity 7.3 MMTPA (Chaksu to Panipat) Further a proposal to enhance Chaksu to Panipat section of SMPL pumping capacity from 7.3 to 19.1 MMTPA has been finalized by pipeline division. With this augmentation the total crude pumping capacity to Panipat refinery will be 27.5MMTPA.

162 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report The Storage details in the plant is given in Table 2-12 and the material balance is given in Table 2-13

Table 2-12 Proposed Raw Materials

Storage Mode of S. Raw Quant Mode of Unit Source Capacit Transport No. Material ity Storage y (KL) IOCL Crude basket for proposed plant MS storage Crude 10 MMTPA will be selected 1,58,000 Pipeline 1 Tanks at the time of processing of crude

Table 2-13 Material Balance

Feedstock Purchases KTPA Bonny Lt. 1670 Basrah Hy. 6670 Kuwait 5420 Maya 1250 Saturno 0.00 Mangla 1200 Dalia 470 Iran Mix 1670 Arab Mix 2080 Forcados 830 Escravos 830 Quaiboe 1250 Zaffiro 830 Bombay Hi 830 Crude Blend 25000.0 LNG 1447.6 C7-C8 from PNCP 228.0 C9+ Stream from PNCP 100.0 IFO from PNCP 112.0 C4 from PNCP 200.0 C5 from PNCP 170.0 Surplus H2 Available 6.8 Benzene 24.6 PTA 700.0 Total Naptha to PNCP 2735.8 Total Light Distillates 8631.2 Total Light Distillates (wt% on crude) 34.5

163 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Feedstock Purchases KTPA ATF 2000.0 BS-VI HSD 12756.6 Total Middle Distillates 14756.6 Total Middle Distillates (wt% on crude) 59.0 Bitumen 360.0 Coke 867.0 Product Sulphur 367.5 Total Heavy Distillates 1594.5 Total Heavy Distillates (wt% on crude) 6.4 Ref. Total Losses 2681.2 Total Loss 2681.2 Total Loss(wt% on crude) 10.72 Total Product 27663.5

2.7.4 Proposed Utilities

The following are the proposed utilities include new storage tanks, mounded bullets for LPG, propylene, control rooms, sub-stations, cooling water, nitrogen plant, DM plant, fire water facilities, instrument air dryers, flare system, ETP facilities, raw water facilities, etc., for the capacity expansion. New flare stack size & height 56” & 150m(Hydrocarbon) considered and with this height, the radiation level outside 90cm radius circle around flare stack shall be within allowable limits. New acid Gas flare 16” (Sour) with a dedicated burning tip is also considered. The incremental utilities required for additional facilities under P-25 expansion project are given in Table 2-14

Table 2-14 Proposed Utilities

S.No. Utility Units Capacity Remarks 1 Raw water m3/hr 2400 2 Cooling water from CT1 m3/hr 64000 and CT2 3 DM water m3/hr 850 4 Suspect condensate TPH 232.5 This condensate shall be generation treated in CPU 5 HP steam TPH 23.5 Case1, All units running at design capacity, except SRU operating to SRU balance 6 MP steam TPH 231.5 Case1 7 LP steam TPH 106.3 Case1 8 HP BFW TPH 122.3 Case1 9 MP BFW TPH 171 Case1 10 LP BFW TPH 14.4 Case1 11 Power KW 222513 Case1

164 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S.No. Utility Units Capacity Remarks 12 Nitrogen Nm3/hr 6500 13 RLNG Kg/hr 115116 14 Plant air Nm3/hr 9450 15 Instrumentation air Nm3/hr 11895 16 ETP m3/hr 450 17 Flare Kg/hr 2191374

Table 2-15 Proposed intermediate & final product storage details

S. No of Dia Class of Description Capacity (m3) HT (m) No Tanks (m) Material Intermediate Bullets 1 Propylene 3850 2 8 90 - 2 Alkylate Feed/LPG 3850 3 8 90 - Intermediate Tanks 3 NHT Feed 14000 2 34 20 A 4 Reformate 17454 1 35 20 A 5 Isomerate 7360 1 28 13 A 6 VGO Feed 30098 3 45 20 Excluded 7 INDMAX Feed 30098 2 45 20 Excluded 8 INDMAX Gasoline 17000 1 37 20 A 9 DHDT Feed 30000 4 49 20 B 10 RHCU Feed 30098 2 45 20 Excluded 11 Alkylate Product 20000 1 42 17.5 A 12 UCO 13630 1 32 18 Excluded Finished Product Bullets 13 LPG 3850 6 8 90 - Finished Product Tanks 14 Naphtha 14000 1 34 20 A 15 MS 15000 7 36 16.6 A 16 HSD 40000 4 55 18.8 B LOBS TANKS 17 API GRADE II LOBS 6315 2 24 15 Excluded (P 60) 18 API GRADE II LOBS 6315 2 24 15 Excluded (2 Cst) 19 API GRADE II LOBS 6315 2 24 15 Excluded (3 Cst) 20 API GRADE II LOBS 9515 2 24 15 Excluded (P 150) 21 API GRADE II LOBS 6315 2 24 15 Excluded (P 230) 22 API GRADE II LOBS 6315 2 24 15 Excluded (P 500) 23 API Grade III LOBS (4 6315 2 24 15 Excluded CST/ Light Lobs) 24 API Grade III LOBS (6 9515 2 24 15 Excluded

165 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. No of Dia Class of Description Capacity (m3) HT (m) No Tanks (m) Material CST/ Light Lobs) 25 API Grade III LOBS (8 6315 2 24 15 Excluded CST/ Light Lobs)

2.7.5 Sulphur Balance The Sulphur balance of the project is given in Table 2-16 Table 2-16 Sulphur Balance

S.No. Feed Stream Sulphur(ppmw) Feed (TPD) Sulphur(TPD) 1 Crude Blend 30000 75000 1650 2 RLNG 30 4343 0.1 3 C7-C8 from PNCP 0.2 684 0 4 C9+ Stream from PNCP 250 300 0.1 5 IFO from PNCP 400 336 0.1 6 C4 from PNCP 0 600 0 7 C5 from PNCP 0 510 0 8 Surplus H2 available 0 20 0 9 Mathura Ref. Naptha 500 450 0.2 Total feed Sulfur 1650.56 Product Stream Sulphur(ppmw) Product Sulphur(TPD) (TPD) 10 Mixed LPG‟s 0.85 2176 0 11 RFCC Propylene 0 332 0 12 Poly Propylene 0 1350 0 13 Polymer grade Propylene 0 0 0 14 Fuel gas from RFCC and 30 254 0.01 DCU 15 E-VI regular gasoline 8 10546 0.08 16 Premium gasoline 8 854 0.01 17 Benzene 0 74 0 18 PTA 0 2100 0 19 Total naptha to PNCP 500 8208 4.10 20 ATF 1067.1587 6000 6.40 21 BS VI Sulfur diesel 8 38270 0.31 22 Bitumen 46053.4492 1080 49.74 23 DCU Coke 138.84 Total Product sulfur 199.49 Total Sulfur as Refinery 13.09 Sox Total Sulphur in Feed, TPD 1650.56 Total Sulphur in Products, TPD 199.49

Total Sulphur in Refinery Sox, TPD 13.09 Sulfur Capacity in terms of Sulfur Product, TPD 1437.98

166 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S.No. Feed Stream Sulphur(ppmw) Feed (TPD) Sulphur(TPD) SRU PR 115 SRU PREP+PRAEP 450 SRU BS-VI 225 Total SRU Capacity available, TPD 790 New SRU Capacity required, TPD 648 No. of Trains Proposed 2 nos. Each train capacity(TPD) 465 Source : IOCL Panipat

2.8 Plot area

The proposed project is planned within the existing facility of IOCL located at Baholi village, Panipat District- 132140, Haryana. Out of total land area 1561.6 acres of Panipat Refinery, 491.6 acres will be utilized for the proposed expansion project.

In Latest EC- J-11011/177/2016-IA-II(I) dt.26.03.2018 was applied for BS-VI project, PX- PTA expansion and Naphtha cracker expansion project in a single application. But as per MoEF&CC application was bifurcated in one application was made for BS-VI PX-PTA expansion project and another application applied for Naphtha cracker expansion project. But area which is shown in EC- J-11011/177/2016-IA-II(I) dt.26.03.2018 was kept for all three project.

Area (1561.6 Acres.) which is provided is for Panipat Refinery only. In which 491.6 Acres land is available within the total area of Panipat Refinery. Plot plan is shown below as Figure 2-11 also attached as Annexure -15.

2.8.1 Site Photographs Site Photographs of Existing and proposed facility enclosed as Figure 2-10 to Figure 2-10

167 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

05.01.2021

ETP-1and 2 Peripheral Green belt

05.01.2021

Figure 2-7 Over view of admin green belt from top of the admin building

168 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

CDU Unit 05.01.2021 VDU Unit 05.01.2021 PTA Unit 05.01.2021

Figure 2-8 Photographs of Existing Unit

169 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

05.01.2021

Source:IOCL Panipat Figure 2-9 Treated Effluent Discharge Fall Out Point at Thirana Drain

170 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

05.01.2021

05.01.2021

Source:IOCL Panipat on 05-01-2021

Figure 2-10 Site Photographs of Proposed site

171 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.8.2 Land Area Breakup

Detailed Land breakup is summarized in Table 2-17. The Site layout is shown in Figure 2-11. Table 2-17 Land use planning of the Project Site

After Existing Proposed Percent S. No Description expansion (Acres) (Acres) (%) (Acres)

1. Built up area 943 491.6 1551.6 99.36 2. Roads 117

Green belt within 3 10 0 10 0.64 premises

Total 1070 491.6 1561.6 100

Note :  Due to space constraint 40% green belt cannot be planted inside the refinery. However, the plantation is taken up in and around the refinery and township areas. Additional Plantation activities are being done.  CISF Building which is already constructed in Proposed site will be demolished and relocated.

 Approximately ~300 trees will be removed from the proposed Project site for Proposed construction and Plantation will be compensated in different location.

172 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Source:IOCL Panipat

Figure 2-11 Existing and Proposed Refinery Layout

173 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.9 Water requirements a. Existing facility

Total water requirement of the existing facility is 3545 m3/hr of which fresh water requirement is 1720 m3/hr. along with this the Effluent generation is 1030 m3/hr and Sewage generation is 235m3/hr. b. Proposed

Total water requirement of the proposed facility is 3241 m3/hr of which fresh water requirement is 2400 m3/hr along with this the Effluent generation is 362 m3/hr and Sewage generation is 9m3/hr. c. After Expansion

Total water requirement of the proposed facility is 6786 m3/hr of which fresh water requirement is 4120 m3/hr along with this the Effluent generation is 1392m3/hr and Sewage generation is 244m3/hr.

Existing and proposed water consumption details given in Table 2-18 and water balance charts are given as Figure 2-11 and Figure 2-13 (Also attached in Annexure 10). d.Source of water Supply

The total water requirement will be met from Western Yamuna Canal. Approval for extraction of water enclosed as Annexure 10.

174 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 2-18 Existing and Proposed Water Requirements

EXISTING (m3/hr) PROPOSED (m3/hr) AFTER EXPANSION(m3/hr)

ter

used

used

Treated Treated Treated

Loss Loss Loss

Condensate

water used water used water used

Condensate

Outlet Outlet Outlet

FreshWa FreshWater FreshWater

Rejects Rejects Rejects

Condensate used

enerated

Description

Effluent Effluent Effluent

generated g generated

(a)+(b)+(c ) (a)+(b)+(c ) (a)+(b)+(c )

TotalWater TotalWater

TotalWater (c

Use of Use Outlets of Use Outlets of Use Outlets

Reuse of Reuse Rejects of Reuse Rejects of Reuse Rejects

Sewage generated Sewage generated S.No. (a) (b) (c ) Sewage generated (a) (b) ) (a) (b) (c ) Cooling 1 Tower 1200 590 460 150 0 0 90 0 0 0 1110 1847 1847 0 0 0 0 287 0 0 0 1560 3047 2437 460 150 0 0 377 0 0 0 2670 Service 2 Water 230 230 0 0 0 0 80 0 0 0 0 112 112 0 0 0 0 13 0 0 0 99 342 342 0 0 0 0 93 0 0 0 99 Domestic 3 Water 130 130 0 0 0 0 110 0 0 110 20 10 10 0 0 0 0 0 0 0 9 1 140 140 0 0 0 0 0 0 0 119 21 PNC Township Domestic 4 Water 125 125 0 0 0 0 125 0 0 125 0 0 0 0 0 0 0 0 0 0 0 0 125 125 0 0 0 0 125 0 0 125 0 PPMC 5 Consumption 60 60 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 60 60 0 0 0 0 0 0 0 0 0 Process Steam 6 Generation 0 0 0 0 0 0 0 0 0 0 0 850 18 832 0 0 0 0 0 362 0 488 850 18 832 0 0 0 0 0 362 0 488 Green Belt/ 7 Horticulture 0 0 0 0 0 0 0 125 0 0 0 10 1 9 0 0 0 0 0 0 0 0 10 1 9 0 0 0 0 0 0 0 0 Fire Water 8 Makeup 0 0 0 0 0 0 10 35 0 0 25 250 250 0 0 0 0 14 0 0 0 236 250 250 0 0 0 0 24 35 0 0 261 Refinery Units, PX/PTA, 9 CPP 1055 0 1055 0 0 0 100 1245 1030 0 115 0 0 0 0 0 0 0 0 0 0 0 1055 0 1055 0 0 0 0 190 1030 0 115

10 Storm Water 0 0 0 0 0 160 35 200 0 0 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 160 35 190 0 0 5

11 ETP-1/2 0 0 0 0 0 0 630 0 0 0 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 630 0 0 0 5

12 ETP-PTA 0 0 0 0 0 0 255 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 255 0 0 0 0

13 ETP- new 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 360 0 0 0 2 0 0 0 0 0 0 0 360 0 0 2 RO/DM 14 Plant 585 585 0 0 160 0 1055 630 0 0 0 162 162 0 0 48 0 0 674 0 0 0 747 747 0 0 208 0 1055 944 0 0 0

15 MEE 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 48 10 0 0 0 0 0 0 0 0 0 48 10 0 0 0 0

16 ATFD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10 0 0 0 0 0 0 0 0 0 0 10 0 0 0

TOTAL 3385 1720 1515 150 160 160 2490 2235 1030 235 1280 3241 2400 841 0 48 48 684 684 362 9 2386 6626 4120 2356 150 208 208 2604 1729 1392 244 3666 Total Water requirement= 3385 + Fresh water Total Water Fresh water Total Water requirement= 6626 + Fresh water 160(Rejects)=3545 m3/hr Requirement=1720m3/hr requirement=3241 m3/hr Requirement=2400m3/hr 160(Rejects)=6786 m3/hr Requirement=4120m3/hr Sewage Generated=235m3/hr(125m3/hr to Horticulture and 110m3/hr Sewage Generated=244m3/hr(9m3/hr to green belt, 125m3/hr to Sewage Generated=9m3/hr to Refinery unit) Horticulture and 110m3/hr to Refinery unit) Effluent generated=1030m3/hr (255m3/hr to Thirana Drain and Effluent RO/DM Plant inlet= 314m3/hr + Effluent generated=1392m3/hr (255m3/hr to Thirana Drain and 630m3/hr to RO Plant) generated=362m3/hr 360m3/hr(ETP treated water) 990m3/hr to RO Plant) Treated water Reused (ETP, RO and Sewage)= 832m3/hr + Treated water Reused (ETP, RO and Sewage)= 2356m3/hr(inclueds Treated water Reused (ETP and RO )= 1515m3/hr Note: 9m3/hr(Sewage treated water from ETP) 9m3/hr(Sewage treated water from ETP))

175 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-12 Water Balance of Existing Refinery (Source: IOCL Panipat)

176 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-13 Total Proposed Water Balance (Source: IOCL Panipat)

177 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

2.10 Air Pollution Control Measures a. Existing

APC measures for existing facilities are use of low NOX burner, Height of stack and temperature of flue gas (Example: 100 m tall chimney at CPP), Use of RLNG (Re-liquefied Natural Gas) as fuel, Double mechanical seal in Hydrocarbon service pumps, Incinerator

(Example: FCC incinerator converts CO into CO2 with recovery of heat), 5 nos. of Sulphur Recovery Units (SRU‟s), Major events in PRPC are made “Carbon Neutral”, OCEMS (On-line Continuous Emission Monitoring System) implementation with Dynamic Emission Limit Implementation in September 2018. b. Proposed

The gaseous emissions from the proposed project will be controlled to meet all the relevant standards stipulated by the regulatory authorities. Standards applicable to this project are classified into three categories:  Ambient Air Standards  Emission Standards  VOC control, Emission and Monitoring

2.11 Green Belt

Total 625 Acres (40% of total area of 1561.6acres) green belt is developed within the premises, outside and periphery of Panipat Refinery Complex. No. of trees planted from FY 2014-15 onwards is given in Table 2-19. The existing and proposed green belt layout is enclosed as Annexure 16.

2.11.1 Existing

S. No Location Acres 1 Polishing Pond+Eco park 92 2 Green Belt between PR and PNC 358 3 RWTP Old 10 4 Refinery Boundary 79 Total 539

Note: RWTP OLD Green belt is within PR Boundary and others are adjacent of PR.

178 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.11.2 Proposed

S. No Location Acres 1 Gwalara (Avenue plantation)* (~25.68km, S from the project boundary) 86 Total 86

2.11.3 After Expansion S.No Description Acres

1 Exising 539

2 Proposed 86

3 Total After expansion 625 (40% of 1561.6 acres)

Note:

Total Land area =1561.6 Acres (625 acres (40%)have been provided for green belt including avenue plantation)

2.11.4 Detail of Species Planted

S.No Description S.No Description

1 Kaijici 20 Alestonia 2 Legestovia 21 Nimboo 3 Jaerenda 22 Aeralvpornis 4 Legestonia 23 Amal Tas 5 Shisham 24 Amrud 6 Papri 25 Benjamin 7 Anaar 26 Kadavb 8 Neem 27 Cassia galuca 9 Chukresia 28 Cassia shamia 10 Budr 29 Kussum 11 Kaehvav 30 Safeda 12 Aovla 31 Toon 13 Pipal 32 Poplar

179 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S.No Description S.No Description

14 Jamun / Jamoa 33 Bail Patthar 15 Gulmohar 34 Guddal 16 Kauair 35 Casuarinas 17 Arjun 36 Chandni 18 Bottle bram 37 Siros 19 Bogan bail

2.11.5 Eco-Park in ETPs area

An eco-park has been developed in the south side of ETP-2 having landscaping. The park consists of a small water reservoir wherein fishes have also been kept. A scenic view has been created by providing artistic railing, gates made-up off iron & stones. 2.11.6 Maintenance of planted tree in township / refinery

 Watering of trees by using treated sewage from the proposed ETP.  Usage of manure (for the trees) generated from the township domestic waste treatment plant.  Routine watering, manuring, trimming is done in the township area.  Plant survival rate is around 75%.  In case of plants getting dried, the same are suitably replaced in the next coming appropriate weather. Table 2-19 No. of trees planted from FY 2014-15 onwards

Sr. no Year Nos of tree planted 1 2014-15 8145 2 2015-16 4642 3 2016-17 5016 4 2017-18 10000 5 2018-19 6250 6 2019-20 16890 7 2020-21 5000 (MoU Target)

180 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

05.01.2021 05.01.2021

05.01.2021

Source: IOCL Panipat Figure 2-14 A view of Eco-park located besides ETP-2

05.01.2021 05.01.2021

Source: IOCL Panipat Figure 2-15 Herbal park located in Township

181 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

05.01.2021 05.01.2021

Source: IOCL Panipat Figure 2-16 A view of Green Belt

05.01.2021

Source: IOCL Panipat Figure 2-17 Green Belt between PR &PNC

182 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

17.10.2020 17.10.2020

17.10.2020 17.10.2020

Source: IOCL Panipat Figure 2-18 Tree plantation – village Gwalara

183 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 2.12 Power and Fuel Requirements

Uttar Haryana Bijili Vitran Nigam Limites‟s provisionally acceptance of extension of load from 70000KW to 288000KW is attached as Annexure 11. The detailed Power and Fuel Requirement is given in Table 2-20

Table 2-20 Power and Fuel Requirement

Capacity Details Source Existing Proposed Total Power Requirement 175 222.513 397.513 Import of power from grid (MW/hr) Sourced from internally within IFO(MT/hr) 42.48 56.863 99.343 refinery Fuel Gas Sourced from internally within 18.32 84.284 102.604 (MT/hr) refinery RLNG 42.37 115.116 157.49 GAIL (MT/hr)

2.13 Manpower

The existing and proposed manpower details are given the Table 2-20.

Table 2-21 Manpower requirements Construction Phase S. No Description Proposed 1 Contract 10,000 (approximate) 2 Permanent 80 (approximate) 3 Total 10,080

184 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Operation Phase Manpower S. No Shift wise requirement Existing Proposed Total 1 Shift Working 245 230 475

2 General (48 hrs) 635 70 705 3 General (36 hrs) 127 0 127

4 Contract 720 480 1200

Total 1727 780 2507

2.14 Water Pollution Control Measures

Several measures are proposed to be incorporated at the designs stage towards minimizing the generation of wastewater and treatment of the generated effluent. Some of these measures are described below  Closed blow down system will be incorporated for hydrocarbon liquid discharges in all the process units, which will reduce the wastewater load to ETP both in terms of quantum load and quality. This is another of the in-plant control measures.  Appropriate segregation and collection philosophy (separate sewers for process waste, contaminated rainwater, spent caustic, cooling tower blow down, boiler blow down,etc.) will be incorporated for various effluents depending on individual stream characteristics.  A comprehensive wastewater management system to comply with treated effluent quality as specified by CPCB shall be established.  Process area will be paved to avoid contamination of soil/sub-soil/ground water in case of accidental spill/leakage of hydrocarbon liquids.

IOCL Panipat is having full-fledged effluent treatment plant system for maintaining CPCB discharge standards. The Effluent Treatment Plant is capable of handling (800 m3/hr.) to accommodate peak flows in during the wet season. The effluent treatment plant appropriate steps were taken to meet the most stringent norms. The Pollutants are treated and disposed in proper way as given in Table 2-20.

185 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 2-22 Water Pollution Treatment Methods S. No Pollutant Treatment Method Existing and Proposed Equipment 1 Free Oil Gravity Separation API, TPI 2 Emulsified oil Chemical Destabilization and Dissolved Air Flotation flotation (DAF) 3 Sulfides Chemical Oxidation Reaction Chamber 4 Organics Biological Oxidation & Bio Tower, Aeration (COD/BOD) Sedimentation Tank 5 Settleable Solids Sedimentation Final Clarifier 6 Microbes (bacteria, Disinfection by Chlorination Chlorine Treatment Algae, etc.) 7 Suspended Solids Sedimentation & Filtration Dual Media Filters (DMFs), Activated carbon gilters (ACFs)

For further removal of TDS and increased recycle of wastewater RO system with Ultra filtration has been installed. The RO plant takes ACF outlet as feed and produce low TDS RO permeate water as Product which is used as feed to DM plant in TPS. Totally 690 KLPH of RO permeate is produced.

The Existing and Proposed ETP and RO plants flow diagram is given in Figure 2-20 and Characteristics of Effluent Generated is given in Table 2-22.

186 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Source: IOCL Panipat Figure 2-19 Effluent Treatment plant 1 & 2 and PX/PTA

187 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Source: IOCL Panipat Figure 2-20 Flow Diagram of Proposed ETP plant

188 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 2-21 Proposed ETP plant Layout

189 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 2-23 Characteristics of Effluent Generated

S. No. Parameter units ETP-1 ETP-2 PTA-ETP 1 Oil % 0.1 0.1 NA 2 COD mg/L 1000 1000 6800 3 BOD mg/L 500 500 4700 4 TSS mg/L 150 150 1800 5 Phenol mg/L 30 30 -- 6 Sulfide mg/L 60 60 -- 7 Cyanide mg/L 5 5 --

Table 2-24 Characteristics of treated Effluent

S. No. Parameter units ETP-1 ETP-2 PTA-ETP 1 PH -- 6-8.5 6-8.5 6.5-8.5 2 Oil mg/L 5.0 5.0 NA 3 COD mg/L 125.0 125.0 250 4 BOD mg/L 15.0 15.0 30 5 TSS mg/L 20.0 20.0 100 6 Phenol mg/L 0.35 0.35 1.0 7 Sulfide mg/L 0.5 0.5 2.0 8 Cyanide mg/L 0.2 0.2 0.20

Source: IOCL Panipat Note: 1. Treated water from ETP- 1&2 is going to the DM-RO Plant which has tertiary facilities along with UF& RO 2. PTA-ETP outlet water is discharging in Thirana Drain which have a valid CTO- No.HSPCB/Consent/313105620PITCTO7559304 dated 04.05.2020 valid till 30.09.2021 for discharge quantity of 255m3/hr. The logbook of daily discharge into Thirana Drain and the treated effluent test report from NABL & MoEF accredited lab is attached as Annexure 28

2.15 Solid waste Management a) During Construction Phase During construction phase ~4.5 TPD of solid waste is envisaged. It will be the scope of the contractor to collect and dispose the solid waste generated during construction phase as per PCB norms. b) During Operation Phase During Operation Phase, total of 588.15 Kg/day of solid waste is generated of which 352.89 kg/Day of organic waste is composted and remaining Inorganic waste will be disposed through authorized vendors

190 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 2-25 Solid Waste Management

S. Quantity (Kg/day) Total List of Items Disposal Methods No Existing Proposed (kg/Day) Composting and used as 1 Organic waste 271.89 81 352.89 manure for Green Belt Disposed through authorised 2 Inorganic waste 181.26 54 235.26 vendors Total 453.15 135 588.15 As per CPCB 0.45 kg/ capita/ day 2.16 Hazardous Waste Management

The existing and proposed hazardous waste generation and disposal methods are given in Table 2-26. NABL accredited Lab Report on Hazardous waste material is enclosed in Annexure 30. Table 2-26 Hazardous Waste Management Quantity S. Mode of Waste (MTPA) Source of Waste No Plant Disposal/Facil category Existi Propos generation . ity ng ed Disposed to SPCB 1 DHDT Spent Catalyst 134 175 DHDT authorised dealer Catalyst Fines Disposed to CCR Spent Catalyst from Spent SPCB 2 Regenerati 0.85 1.58 Fines Catalyst Fines authorised on Section Collection Pot dealer CCR Disposed to Platforming Spent catalyst SPCB 3 Spent Catalyst 7.25 4.173 Process from Reactors authorised Unit dealer CCR Net GAS Chloride Platforming Spent 4 0.6 31.2 Treaters To TSDF Process Adsorbent Adsorbents Unit CCR Platforming Spent Fuel gas Chloride 5 4.25 1.8 To TSDF Process Adsorbent Adsorbent Unit CCR LPG Chloride Platforming Spent 6 0.05 1.26 Treatment To TSDF Process adsorbent Adsorbent Unit 7 CCR Spent 10.2 33.26 Debutanizer feed To TSDF

191 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Quantity S. Mode of Waste (MTPA) Source of Waste No Plant Disposal/Facil category Existi Propos generation . ity ng ed Platforming Adsorbent Chloride Treater Process Unit Indmax equilibrium INDMAX 8 Spent Catalyst 50 839.5 catalyst (E-cat) is To TSDF FCC withdrawn from Indmax FCC unit. Propylene Spent Adsorbents from 9 Recovery 10 20 To TSDF adsorbent Propylene Driers unit Propylene Spent Adsorbent from 10 Recovery 20 11 To TSDF adsorbent Arsine Guard Bed unit HCU/RHC Spent catalyst 11 U Reaction Spent Catalyst 136.5 5.256 withdrawn from To TSDF Section the reactors UOP Naphtha Spent Catalyst 12 Hydrotreati Spent Catalyst 1.4 4.5 To TSDF from Reactor ng Process Unit Disposed to Spent Catalyst SPCB 13 PENEX Spent Catalyst 1.4 2.96 From Reactor A authorised dealer Disposed to Spent Catalyst SPCB 14 PENEX Spent Catalyst 10.25 1.48 From Reactor B authorised dealer Disposed to Spent Catalyst SPCB 15 PENEX Spent Catalyst 5.125 0.987 From Reactor C authorised dealer Disposed to Spent Catalyst SPCB 16 PENEX Spent Catalyst 4 0.312 from Methanator authorised Reactor dealer Spent Makeup Gas 17 PENEX 4 0.45 To TSDF Adsorbent Chloride Treater Spent Makeup Gas 18 PENEX Molecular 7 3.25 To TSDF Driers Sieve Spent 19 PENEX 1.19 0.595 Penex Feed Driers To TSDF Molecular

192 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Quantity S. Mode of Waste (MTPA) Source of Waste No Plant Disposal/Facil category Existi Propos generation . ity ng ed Sieve VGO REACTOR/ REACTOR DIESEL 20 VGOHDT SPENT NA 500 To TSDF OPOLISHING CATALYST REACTOR Disposed to SPCB 21 CDWU Spent Catalyst NA 3.762 HCR Reactor authorised dealer Disposed to SPCB 22 CDWU Spent Catalyst NA 3.864 DW Reactor authorised dealer Disposed to SPCB 23 CDWU Spent Catalyst NA 3.621 HDF Reactor authorised dealer SR LPG Spent Catalyst 24 Spent Catalyst NA 3.250 To TSDF Treater from Reactor Spent Grading SR LPG Spent Grading 25 NA 0.15 Bed Catalyst from To TSDF Treater Bed Catalyst Reactor Spent Catalyst HGU from 26 Spent Catalyst 4.5 1.583 To TSDF (Note-1) Hydrogenation Reactor Spent Catalyst from HGU 27 Spent Catalyst 63 21 Predesuffurization To TSDF (Note-1) Reactor A/B (Dechlorination) Spent Catalyst from HGU Predesuffurization 28 Spent Catalyst 18.12 505.2 To TSDF (Note-1) Reactor A/B (Removal of Sulfur compound) Spent Catalyst from HGU Desuffurization 29 Spent Catalyst 19 6.387 To TSDF (Note-1) Reactor (Removal of Sulfur compound) HGU Spent Catalyst 30 Spent Catalyst 8 2.667 To TSDF (Note-1) from

193 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Quantity S. Mode of Waste (MTPA) Source of Waste No Plant Disposal/Facil category Existi Propos generation . ity ng ed Desuffurization Reactor (Deep Desuffurization) Spent Catalyst HGU 31 Spent Catalyst 25 9.4 from Prereformer To TSDF (Note-1) A/B HGU Spent Catalyst 32 Spent Catalyst 8 5.883 To TSDF (Note-1) from Reformer Spent Catalyst HGU 33 Spent Catalyst 30 10.107 from High Temp To TSDF (Note-1) Shift Reactor Spent Catalyst HGU 34 Spent Catalyst 24 16.883 from Low Temp To TSDF (Note-1) Shift Reactor Catalyst Spent Support Support Material from HGU 35 Material 16 5.6 Reactors,Prerefor To TSDF (Note-1) (Ceramic mer, Reformer & balls) Shift Reactors Catalyst Spent Support Support Material from HGU 36 Material 28 9.79 Reactors,Prerefor To TSDF (Note-1) (Aluminium mer, Reformer & balls) Shift Reactors HGU /PSA Spent Spent Adsorbent 37 250 51.938 To TSDF (Note-1) Adsorbent from PSA 38 SRU Spent Catalyst 36.8 53.5 Claus reactors To TSDF 39 TGTU Spent Catalyst 15 11.34 Reactor To TSDF Catalyst Support SRU/TGT Claus and TGTU 40 Material 8 11.4 To TSDF U reactors (Ceramic/alum ina balls)

Note-1: All data for HGU are preliminary for proposed case. Data given has been prorated from BS VI Panipat HGU data. Data shall be confirmed after getting data from the selected

194 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

CHAPTER 3 DESCRIPTION OF ENVIRONMENT

195 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3 DESCRIPTION OF ENVIRONMENT

3.1 Preamble

This chapter depicts the establishment of baseline for valued environmental components, as identified in and around the proposed project with an area of 491.6 acres located at M/s.Indian Oil Corporation Limited, Panipat Refinery & Petrochemical Complex, Panipat District, Panipat – 132140, Haryana. The primary baseline data monitored covered three (3) months i.e., from March to May 2019. The secondary data was collected from government and semi-government organizations published data. The primary baseline data has been generated by M/s. Hubert Enviro Care Systems (p) ltd, Chennai, a MoEF&CC approved environmental testing laboratory for the following terrestrial environmental components.  Meteorology: Temperature, Relative Humidity, Rainfall, Wind Speed & Direction- Refer Section -3.6

 Ambient Air Quality: Particulate matter <10 micron size (PM10),Particulate matter

<2.5 micron size (PM2.5), Sulphur Dioxide (SO2), Nitrogen Dioxide (NO2),Carbon

Monoxide (CO), Lead (Pb),Ozone (O3),Benzene (C6H6), Benzo (a) pyrene (C20H12),

Arsenic (As), Nickel (Ni),Ammonia (NH3), Vanadium,VOC, methane HC, Non methane HC- Refer Section - 3.7  Ambient Noise Levels: Day equivalent noise levels, Night equivalent noise levels - Refer Section - 3.8  Inland Water Quality: Groundwater Quality, Surface Water Quality - Refer Section - 3.10  Soil Quality - Refer Section -3.11  Biological Environment - Refer Section -3.12  Socio Economic Status - Refer Section - 3.13

3.2 Study area

A 10 Km radial distance with the proposed project site as the epicentre has been identified as the General study area for assessing the baseline environmental status. The core study area is the project area and its immediate surroundings to the tune of 1.0 Km radius from the boundary. Further the Project Impact/Influence Area (PIA) is 10Km from the boundary of the project site which covers parts of Panipat District of Haryana State.

196 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.3 Description of the Study Area

As Described in Chapter 1, M/s. IOCL Panipat is located at PR 42-128 Gram Panchayat Baholi, Refinery Road, Panipat, and Haryana. Aasandh Railway Station is located approximately at a distance of 6.68 Km towards SSW from the project boundary and NH 1 is located approximately at a distance of 7.63 Km towards East from the project boundary. An overall idea of the study area with reference to the physical conditions are presented for better understanding in the following sections before proceeding into the section on the prevailing environmental conditions of the study area. The map showing the satellite image and Topo Map of the study area is given in Figure 3-1 & Figure 3-2 respectively.

197 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 3-1 Map showing the Satellite Image of the study area

198 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 3-2 Topo Map of Study area

199 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.4 Environmentally/Ecologically Sensitive areas

This section details with the environmentally sensitive areas present within the project site and surrounding environments. It included national parks, state forest, essential habitats etc. The environmental sensitive areas covering an aerial distance of 15 Km from the project boundary is given in Table 3-1 and Figure 3-4.

Table 3-1Environmentally Sensitive Areas within 15 Km from Project Boundary S. Areas Aerial distance (within 15km) from Proposed project location boundary No 1 Areas protected under international No such protected area is present within 15km radius from the study area. conventions, national or local legislation for their ecological, landscape, cultural or other

related value

)

2 Areas which are important or sensitive for )

km ecological reasons - wetlands, watercourses or km other water bodies, coastal zone, biospheres, Description Description

mountains, forests. S. Direction

S. Direction N Distance (~ Distance No (~ Distance o

Inside Munak Drain - Mor Majra Drain 6.81 W the 1 site 30 New Delhi Branch 0.05 S Ganda Nala 7.11 E 2 (Western Yamuna Canal) 31 Main Drain No 2/Indri 0.05 E Jind Distributary 7.13 W 3 Drain 32 New Delhi Parallel Khukrana Branch Branch (Western 0.1 S 7.21 S Canal 4 Yamuna Canal) 33 5 Gohana Distributary 0.1 S 34 Bhalsi Minor 7.87 SSW Nahar Kuna Hansi/Hanal Lift Irrigation 0.19 N 9.7 N 6 Nadi 35 Channel 7 Madlauda Minor 0.22 S 36 Bhadaur Drain 9.91 S 8 Thirana Minor 0.23 S 37 Gagsina Subminor 10.12 N 9 Khandra Drain 0.67 S 38 Lohari Minor 10.13 S Left Branch Gohana Begampur Minor 0.8 N 10.13 S 10 39 Distributary 11 Joshi Drain 0.82 W 40 Jundla Drain 10.14 N 12 Untala Minor 1.78 S 41 Rasin Minor 10.38 NNE

Phurlak Drain 2.14 N Bansa Drain 10.86 13 42 NNW

Tributary Drain No 1 2.32 SS Pundri Drain 10.95 ESE 14 W 43 15 Gagsina East Drain 2.62 N 44 Augmentation Canal 11.06 N

200 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No

W Rer Kalan Minor 2.67 Branch No 1 Canal 11.26 W N 16 W 45 Kabir Branch/Bazida 2.7 E Bansa Subminor 11.7 17 Distributary 46 NNW 18 Munak Minor 2.76 N 47 Israna Distributary 12.05 SSE

Hansi Branch(Western 4.31 N Hulana Distributary 12.18 SSE Yamuna Canal) 19 W 48

Munak Canal 4.46 NN Narayana Distributary 12.32 SSE 20 W 49

Goli Distributary 4.88 NN Seori Minor 13.12 NW 21 W 50

Gudah Minor 5.34 E Bala Tributary Drain 13.26 WS 22 51 W 23 Binjhaul Minor 5.39 SE 52 Barauta Drain 13.55 NNE

W Jind Distributary No Pabana/Pawana Drain 5.47 13.68 WS N 2 W 24 W 53

Nohra/Nauhra Drain 5.68 SS Naultha Minor 13.72 S 25 E 54

Ganda Nala/Panipat 5.7 ES No 1R Israna Minor 13.91 S Main Drain 26 E 55 27 Joshi Distributary 5.82 W 56 Idyana Subminor 14.15 SSW

Kurian Minor 5.86 N Tributary Drain No 2 14.84 S 28 W 57 29 Untala Drain 6.6 S

3 Areas used by protected, important or sensitive No such protected area is present within 15km radius from the study area. species of flora or fauna for breeding, nesting,

foraging, resting, over wintering, migration

)

4 Inland, coastal, marine or underground water )

km km

Description Description

S. Direction

S. Direction N Distance (~ Distance No (~ Distance o 1 Munak Drain - 30 Mor Majra Drain 6.81 W

201 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Inside the site New Delhi Branch 0.05 S Ganda Nala 7.11 E 2 (Western Yamuna Canal) 31 Main Drain No 2/Indri 0.05 E Jind Distributary 7.13 W 3 Drain 32 New Delhi Parallel Khukrana Branch Branch (Western 0.1 S 7.21 S Canal 4 Yamuna Canal) 33 5 Gohana Distributary 0.1 S 34 Bhalsi Minor 7.87 SSW Nahar Kuna Hansi/Hanal Lift Irrigation 0.19 N 9.7 N 6 Nadi 35 Channel 7 Madlauda Minor 0.22 S 36 Bhadaur Drain 9.91 S 8 Thirana Minor 0.23 S 37 Gagsina Subminor 10.12 N 9 Khandra Drain 0.67 S 38 Lohari Minor 10.13 S Left Branch Gohana Begampur Minor 0.8 N 10.13 S 10 39 Distributary 11 Joshi Drain 0.82 W 40 Jundla Drain 10.14 N 12 Untala Minor 1.78 S 41 Rasin Minor 10.38 NNE

Phurlak Drain 2.14 N Bansa Drain 10.86 13 42 NNW

Tributary Drain No 1 2.32 SS Pundri Drain 10.95 ESE 14 W 43 15 Gagsina East Drain 2.62 N 44 Augmentation Canal 11.06 N

W Rer Kalan Minor 2.67 Branch No 1 Canal 11.26 W N 16 W 45 Kabir Branch/Bazida 2.7 E Bansa Subminor 11.7 17 Distributary 46 NNW 18 Munak Minor 2.76 N 47 Israna Distributary 12.05 SSE

Hansi Branch(Western 4.31 N Hulana Distributary 12.18 SSE Yamuna Canal) 19 W 48

Munak Canal 4.46 NN Narayana Distributary 12.32 SSE 20 W 49

Goli Distributary 4.88 NN Seori Minor 13.12 NW 21 W 50

Gudah Minor 5.34 E Bala Tributary Drain 13.26 22 51 WS

202 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No W

23 Binjhaul Minor 5.39 SE 52 Barauta Drain 13.55 NNE

W Jind Distributary No Pabana/Pawana Drain 5.47 13.68 WS N 2 W 24 W 53

Nohra/Nauhra Drain 5.68 SS Naultha Minor 13.72 S 25 E 54

Ganda Nala/Panipat 5.7 ES No 1R Israna Minor 13.91 S Main Drain 26 E 55 27 Joshi Distributary 5.82 W 56 Idyana Subminor 14.15 SSW

Kurian Minor 5.86 N Tributary Drain No 2 14.84 S 28 W 57 29 Untala Drain 6.6 S

5 State, National boundaries Nil

6 Routes or facilities used by the public for S.No Description Distance(~km) Direc access to recreation or other tourist, pilgrim tion areas 1 SH -14 (Panipat-Safidon-Jind) 7.07 S 2 NH -44 (Srinagar-Panipat-Kanyakumari) 7.39 E

3 Nearest Railway jn - Panipat Jn 10.12 SE

4 Nearest Railway Station (Asan) 6.68 S

7 Defense installations No defense installation found within 15km from the project area. 8 Densely populated or built-up area Description Population (Nos.) Distance (~Km) Direction Panipat 791634 ~5.18 SE

Areas occupied by sensitive man-made land uses

9

(hospitals, schools, places of worship, community S. S. facilities) Places Places

No No

(~km) (~km)

Distance Distance

Direction Direction

Civil Hospital 1 1.26 ENE Bishon Sarup 9.91 SE Govt Sr Sec School 23 Colony Dadlana Govt Middle School 2 2.31 SSW 24 Civil Hospital 9.92 NE BalJattan 25 10.33 SSW 3 Govt School 2.33 NE Raj Hospital

203 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Begumpur Madlauda Malhotra Mother & 10.52 SE 4 Govt School 2.86 W 26 Child Hospital Rairkalan Govt Middle School 5 3.04 ESE 27 Hyderabadi Hospital 11.12 SE Bholi Govt Hospital 11.37 E 6 3.18 SSE 28 Khotpura/PHC Govt School Jeetgarh Govt High School 7 3.31 NNW 29 Gourav Hospital 11.55 SE Munak Govt Hospital 11.79 NE 8 Govt Girls High 3.47 NNW 30 Hasnapur School Munak Govt School 9 3.93 WSW 31 Hospital Bhadar 11.89 S Dharamgarh 32 RP Hospital 12.04 SE 10 Delhi Public School 4.19 NE Govt Public School 11 5.47 SSW 33 PHC Didwara 12.82 W Karnal 34 RP Welter Hospital 13.21 NE 12 Govt School Nohra 5.03 SSE Govt Hosptal 13.67 W 13 5.47 SSW 35 Salwan Govt School Khandra Givt Hosptal 14.15 ENE 14 Govt Sr Sec School 5.48 SW 36 Lalupura Shera Govt Sr Sec School 15 5.62 SE 37 Hospital Kalkha 14.87 SSW Kabri Govt Sr Sec School 16 5.84 SSW Govt Buildings Assan Kalan Grama 17 5.86 SE Sachivalayam 0.99 NE Govt School Jawahar 1 Dadlana Nagar Munak Bijli Board NN 3.19 18 Small Wonders 6.15 ESE 2 Office W World School Post Office Refinery 4.02 NE 19 Govt Sr Sec School 6.21 ENE 3 Township Gudha NN 4.07 20 Govt School 6.67 NE 4 BDO Office Munak W Sheikhupura Munak Police NN 4.21 21 6.78 ESE 5 Station W MASD Public School Govt Public School 22 6.91 NNE 6 6.59 W Raipur Jattan Sub-Tehsil Ballah

204 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Office 7 Police Station Ballah 6.62 W 23 Govt School Gagsina 6.99 N Food Supply Office 6.71 W 24 7.03 S 8 Ballah Govt School District Towm 25 7.14 N Planner Office 8 ESE Govt Boys Sr Sec 9 HUDA School Gagsina District Fisheries 8.62 SE 26 Govt School Bada 7.16 NE 10 Office Basti District Commandant Home 8.91 SE 27 7.38 NW Guards Industrial Govt High School 11 Area Pabana Hasanpur Block Education 28 7.42 SSW 8.95 SSW Govt School 12 Office Madlauda Mohidinpur E-Disha Karnal 9.16 SE 29 7.5 WNW 13 HUDA Govt School Ballah Head Post Office 9.55 SE 30 Govt Sr Sec School 7.66 E 14 Industrial Area Kohand Gram Sachivalayam 9.76 W 31 Govt School Eldeco 7.92 E 15 Golli Estate PWD Office GRT 9.78 SE 32 Govt High School 7.96 NW 16 Rd Balrangran The Joint Director 33 8.08 SSW General of Foreign 9.83 SE Govt High School 17 Model Town Untla Public Health Engineering 9.85 NE 34 8.09 SSW Department 18 Gharaunda DAV Public School Ziledar Office Irrigation 9.85 NE 35 8.5 SSE Department Bal Vikas 19 Gharaunda Progressive School City Police Station 36 8.54 SW 20 9.96 SE Govt School Kavi Bishon Sarup

205 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Colony

Tehsil Gharaunda 10.19 NE 37 Govt Sr Sec School 8.82 NNE 21 Office Phurlak MC Municipal Govt School For 38 9.08 SE Corporation Palika 10.37 SE Blind Industrial Area 22 Bazar Panipat Uttar Haryana Bijlee 10.47 NE 39 Govt Girls Sr Sec 9.13 SSW 23 Nigam Gharaunda School Madlauda Sub-divisional 40 9.42 SE Office UHBVNL 10.92 SE Arya Group Of 24 Vikas Nagar Schools Post Office WS 10.96 41 Govt Sr Sec School 9.57 SE 25 Bushlana W Ramnagar Mayor Office Palika 11.5 ESE 42 Dr M K K Arya 9.63 SE 26 Bazar Model School Govt High School 43 9.64 W 27 Post Office Padha 12.17 NW Golli Government Senior 13.17 W 44 Secondary School 9.66 NE 28 Post Office Didwara Gharaunda Bhardwaj CSC 14.04 W 45 Govt School 9.7 SSE 29 center Salwan Sondhapur Govt Model Sanskriti 46 Sec School Bishop 9.85 SE Religious Places Sarup Colony Shiv Mandhir 1.26 ENE 47 Govt School 10 E 1 Dadlana Chandoli Sani Mandir 1.45 NE 48 10.01 SE 2 Dadlana Govt School Tehsil Govt Sr Sec Vishno Mandir 1.6 NNE 49 School(New) 10.04 NE 3 Dadlana Gharaunda Govt Sr Sec School 50 10.07 S 4 Shiv Mandir Sithana 1.66 SE Sutana Dada Khedaji NN Maharaj Temple 1.67 51 10.09 NNE W 5 Kutana Govt School Sataundi Goga Pir Temple 52 Govt High school 10.14 SSW 6 1.9 SSW Bhalsi Baba Dhanni Ram

206 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No samadhi Gurudwara Sahib 2.27 E 53 Govt Sr Sec School 10.22 SE 7 Rajapur Model Town Lord Shiva Temple 2.27 SSW 54 Govt Sr Sec School 10.24 S 8 Baljattan Jattal shiv Mandir 2.28 NE 55 SN Hindu Sr Sec 10.59 ENE 9 Begampur School Alipur Khalsa Kali Maa Mandir 2.28 SSW 56 Govt School 10.63 WSW 10 Baljattan Bhuslana Vamiki Mandir 2.8 W 57 Govt High School 10.79 E 11 Raikarlan Alipur Khalsa Gurdwara Sahib 3.08 ESE 58 Govt Primary School 10.93 SE 12 Bholi Kasturba Gurudwara Sahib NN 3.66 59 Govt Middle School 11.12 NNE 13 SabaMunak W Rasin Maharishi Balmiki NN 3.77 60 11.22 ENE 14 Mandir Munak W Govt School Majra Shiv Temple WS 4.01 61 Govt School Har 11.65 E 15 Dharmargh W Singh Pura Shiv Mandir Panipat 4.07 NE 62 11.95 W 16 Refinery Township Govt School Bulsan Shri Satti Mata 4.63 E 63 Govt Sr Sec School 11.98 NW 17 Mandir Mahamdpur Padha Guru Ravidass 5.21 NNE 64 Govt Sr Sec School 12.08 SE 18 Mandir Khora Kheri Model Town Guru Ravidas 5.58 SE 65 12.21 SSW 19 Mandir Kabri Govt School Lohari Jaharvir Goga Medi 5.65 SSW 66 12.36 N 20 Mandir Assan Kalan Govt School Picholla Govt Sr Sec School 67 12.43 S 21 Shiv Mandir Gudha 6.14 ENE Bhadar Shiv Mandir Shah 6.34 NNE 68 12.72 N 22 Jahanpur Govt School Bansa Devi Mandir 6.82 NE 69 Govt High School 12.8 NNE 23 Sheikpura Bijan

207 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Guru Ravidash 6.86 E 70 12.81 W 24 Mandir Kohand Govt School Didwara Baba Jotram Mandir 6.88 N 71 Govt School 12.9 ESE 25 Gagsina Rajakheri Govt High School 72 12.9 E 26 Shiv Mandir Raipur 7.1 NNE Punduri Govt Sr Sec School 73 13.12 SW 27 Shiv Mandir Kohand 7.13 ENE Nara Devi Maa Mandir WN 7.19 74 13.33 WSW 28 Ballah W Govt School Badodh Dada Kalapeer 7.48 N 75 Govt Middle School 13.38 ENE 29 Gagsina Kalheri Basanti Mata 76 13.71 WNW Mandir Pabana 7.7 NW Govt High School 30 Hasanpur Kurlan Durga Mandir 7.73 N 77 Govt Sr Sec School 13.73 N 31 Gagsina Jani Gurudwara Singh 7.78 NNE 78 Govt Girls Sec 13.91 W 32 Sabha School Salwan Govt School Nangal 79 14.2 SE 33 Shiv Mandir Untala 7.98 SSW Kheri Zion global worship 8.15 SSE 80 Govt Sr Sec School 14.28 SE 34 center Ugra Kheri Jahar Veer Guga Ji NN 8.21 81 Govt School Pucca 14.51 NNW 35 Temple Balrangam W Khera St Marys Catholic 8.22 SSE 82 Govt Hgh School 14.81 SSW 36 Chrch Kalkha Baba Balak Nath 8.42 SW 83 Govt Girls School 14.92 SSW 37 Mandir Kavi Kalkha Colleges 38 Shiv Mandir Phulrak 8.73 NNE Siddhi Vinayak Shivalay Mnadir 3.66 E 8.84 SE 1 College 39 Kacha Camp Arya Kanya Gurukul Jeetpuri Temple 6.03 W 9.29 NE 2 College Of Education 40 Gharaunda Prem Institute of Jain Sthanak 7.15 E 9.61 SSW 3 Medical Sciences 41 Madlauda

208 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Thakur Jugal 4 GDR College of 7.7 E Kishore Mandir 9.64 W Education 42 Golli Desh Bandhu Govt Shiv Mandir Garhi 8.2 ESE 9.81 ENE 5 Polytechnic College 43 Govt Polytechnic Guru Ravidas Ji 8.61 SSE 9.9 NNE 6 College Jattal 44 Mandir Satundi Govt College for Bhai Lalo Ji 8.65 SSW 9.94 SE 7 Women Madlauda 45 Gurudwara Arya Adarsh Girls Sanatan Dharma 8.71 SW 10.02 SE 8 College 46 Mandir Model Town PKG College of 9 Engineering and 8.89 SSW John Wisely 10.09 SE Technology 47 Methodist Church Sarswati College for Devi Mandir Tehsil 8.91 SW 10.14 SE 10 girls, Qawi 48 Camp Institute of Hotel 9.12 SE 10.2 NE 11 Management 49 Jesus church BRM College of Shree Geeta Mandir 9.14 NE 10.22 SE 12 Education 50 Geeta Colony Dada Kheda 9.48 SE 10.63 E 13 Arya (P. G.) Collage 51 Chandoli Govt Agriculture WS College Bishon Sarup 9.85 SE Dada Kheda 10.89 14 W Colony 52 Bhuslana Siddhi Vinayak 10.81 SE 10.92 NE 15 College 53 Mount olivet church Bhagwan Parshuram Shiv Temple Dinger 11.66 SW 11 ENE 16 College of Education 54 Majra Haryana College of Jagannath Mandir 11.99 SE 11.05 SE 17 Nursing College 55 Old HBC Maharshi Dayanand Jamma Masjid khali 12.13 NW 11.08 SE 18 Women College 56 Bazar Govt ITI College 12.82 SE 11.11 SE 19 Viaks Nagar 57 Masjid Imam Saheb

209 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Hazrat Bu Ali Shah 20 Govt College 12.97 NE Qalandar Dargah 11.17 SE Gainpura 58 Kaland Peer LCRT College Of Chhath Pooja 12.99 SSE 11.17 NE 21 Education 59 Mandir Gharaunda Govt College for 13.26 NE 11.35 SE 22 Women Gharaunda 60 Masjid Gumbadan R.P. Educational 23 Trust Group of 13.29 NE 11.4 SE Institutions 61 Matkek Wali Masjid Hazrat Bu Ali Shah 24 14.78 WSW Qalandar Dargah 11.64 SE Metis College 62 Ramnagar Jayawant prarthana Hospitals 11.66 SSE 63 bhawan church Govt Hospital Ganapathi Mandir 1.26 NE 11.8 SE 1 Dadlana 64 Sonali Rd Govt Hospital Dera Baba Jodh 2.69 W 11.82 SE 2 Rairkalan 65 Sachiyar Gurudwara Panipat Refinefy 3.71 NE 12.06 SSW 3 Township Hospital 66 Shiv Temple Lohari

4 Govt Hospital Munak 3.87 NNW 67 Shiv Mandir Padha 12.25 NW 5 PHC, Khandra 5.08 SSW 68 Shiv Mandir Badhar 12.53 S Ancient Shiv 5.73 ENE 12.64 SSW 6 PHC Gudha 69 Temple Wasir Sri Kali Devatha 5.87 SE 12.75 N 7 Kabdi Hospital 70 Temple Picholia Sant Kabir Das ji 6.58 W 12.85 NNE 8 Govt Hospital Ballah 71 Mandir Bijna Govt Hospital Gurdwara Sahib 7.15 N 12.96 N 9 Gagsina 72 Bansa Shri Vishavakarma 7.31 WNW 13.08 E 10 Civil Hospital Ballah 73 Mandir Pundri Cygnus Mata Mata Kali Mander 7.48 E 13.19 W 11 Kalawati Hospital 74 Didwara Golli

210 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Govt Hospital Kavi/ Basanti Mata 8.51 SW 13.24 W 12 PHC 75 Mandir Salwan WN 8.53 SSW 13.32 13 Jindhal Hospital 76 Shiv Temple Kurlan W Hari Temple Vikas 8.57 SSW 13.58 SE 14 PHC Madlauda 77 Nagr Shiv mandir 8.67 ESE 13.82 NNE 15 The Kidney Hospital 78 Jhinweheri Shri Veer 16 Shree Balaji Multi 9.15 SE Abhimanyu Tirth 13.88 NNE Speciality Hospital 79 Birachpur Brain Care Centre Dr 17 Gaurav Bhateja MD 9.18 SE Syosang Devta 13.99 NNE Neuro Psychiatry 80 Birchapur Galaxy Multi Shiv Mandir 9.2 SE 14.28 ENE 18 Speciality Hospital 81 Arianpur Dr Ved Guptha 9.32 ESE 14.33 N 19 Hospital 82 Shiv Mandir Jani Shiv Temple 9.51 NE 14.56 NNE 20 Life Line Hospital 83 Samalakha

21 Chhabra Hospital 9.54 SE LHDM & Prem 9.75 SE 22 Hospital Pvt Ltd

)

10 Areas containing important, high quality or scarce )

resources, (groundwater resources, surface km resources, forestry, agriculture, fisheries, tourism, km minerals) Description Description

S. Direction

S. Direction N Distance (~ Distance No (~ Distance o

Inside Munak Drain - Mor Majra Drain 6.81 W the 1 site 30 New Delhi Branch 0.05 S Ganda Nala 7.11 E 2 (Western Yamuna Canal) 31 Main Drain No 2/Indri 0.05 E Jind Distributary 7.13 W 3 Drain 32 4 New Delhi Parallel 0.1 S 33 Khukrana Branch 7.21 S

211 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No Branch (Western Canal Yamuna Canal) 5 Gohana Distributary 0.1 S 34 Bhalsi Minor 7.87 SSW Nahar Kuna Hansi/Hanal Lift Irrigation 0.19 N 9.7 N 6 Nadi 35 Channel 7 Madlauda Minor 0.22 S 36 Bhadaur Drain 9.91 S 8 Thirana Minor 0.23 S 37 Gagsina Subminor 10.12 N 9 Khandra Drain 0.67 S 38 Lohari Minor 10.13 S Left Branch Gohana Begampur Minor 0.8 N 10.13 S 10 39 Distributary 11 Joshi Drain 0.82 W 40 Jundla Drain 10.14 N 12 Untala Minor 1.78 S 41 Rasin Minor 10.38 NNE

Phurlak Drain 2.14 N Bansa Drain 10.86 13 42 NNW

Tributary Drain No 1 2.32 SS Pundri Drain 10.95 ESE 14 W 43 15 Gagsina East Drain 2.62 N 44 Augmentation Canal 11.06 N

W Rer Kalan Minor 2.67 Branch No 1 Canal 11.26 W N 16 W 45 Kabir Branch/Bazida 2.7 E Bansa Subminor 11.7 17 Distributary 46 NNW 18 Munak Minor 2.76 N 47 Israna Distributary 12.05 SSE

Hansi Branch(Western 4.31 N Hulana Distributary 12.18 SSE Yamuna Canal) 19 W 48

Munak Canal 4.46 NN Narayana Distributary 12.32 SSE 20 W 49

Goli Distributary 4.88 NN Seori Minor 13.12 NW 21 W 50

Gudah Minor 5.34 E Bala Tributary Drain 13.26 WS 22 51 W 23 Binjhaul Minor 5.39 SE 52 Barauta Drain 13.55 NNE

W Jind Distributary No Pabana/Pawana Drain 5.47 13.68 WS N 2 W 24 W 53

Nohra/Nauhra Drain 5.68 Naultha Minor 13.72 S 25 SS 54

212 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report S. Areas Aerial distance (within 15km) from Proposed project location boundary No E

Ganda Nala/Panipat 5.7 ES No 1R Israna Minor 13.91 S Main Drain 26 E 55 27 Joshi Distributary 5.82 W 56 Idyana Subminor 14.15 SSW

Kurian Minor 5.86 N Tributary Drain No 2 14.84 S 28 W 57 29 Untala Drain 6.6 S

11 Areas already subjected to pollution or Panipat, Haryana attracts CEPI score of 83.54 environmental damage. (those where existing legal environmental standards are exceeded) 12 Areas susceptible to natural hazard which could The area comes under seismic Zone-IV (High Damage Risk Zone). There is no susceptible to natural hazards like subsidence, landslides, erosion, cause the project to present environmental flooding or extreme or adverse climatic conditions. problems Note : (earthquakes, subsidence, landslides, erosion, Seismic Zone-II : Low risk flooding or extreme or adverse climatic Seismic Zone-III : Moderate Risk conditions) Seismic Zone-IV : High Risk Seismic Zone-V Very high Risk

213 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 3-3 Environmental sensitive areas covering within 15 Km from project boundary

214 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 3-4 Environmental sensitive areas covering within 15 Km from project boundary

215 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.5 Physical Conditions of PIA district

In this section, the physical conditions of PIA district are discussed in general and wherever possible references to the conditions prevailing in the study area in particular are also provided. The physical conditions are discussed as under:

 District profile  Drainage, land use, geology, Physiography  Natural resources  Climatic conditions, seismic zone characteristics and natural hazard

3.5.1 PIA District Profile

Panipat district, lying in the east central part of Haryana State and is located between 29°09‟15”: 29°27‟25” north latitudes and 76°38‟30”: 77°09‟15” east longitudes. The total geographical area of the district is 1268 sq. Km. administratively; the district is controlled by division. The district is sub-divided into five development blocks namely Panipat, Bapoli, , Madlauda and Israna. Source:http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

3.5.2 Climatic Conditions

The climate of the district can be classified as sub tropical and semi arid. The area receives normal annual rainfall is about 680 mm which is spread over 31 rainy days. 77% of rainfall occurs during south-west monsoon. The normal annual rainfall of district based on average of 5 years (2006-2010) has been computed as 591 mm. Source:http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

3.5.3 Natural Resources ofPIA District 3.5.3.1 Flora & Fauna Flora: The natural vegetation in the study area is sparse. Various kinds of trees and shrubs are found growing indigenously. On account of the pressure of population and extensive cultivation, very little land has been left under natural forest cover. Strip forests along the roads and canals and block forests of Babool (Kikar) are on the forest record. Most of the area is occupied by agriculture fields. Wherever the forests are present, they are of open evergreen scrub or thorn type comprising mainly of:

216 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report  ButeaMonosperma (Dhak)  Prosopis Cineraria (Jand)  CapparisDeciduas (Kaur)  CapparisSeparia (Hins) Among the fruit trees the important are MangiferaIndica (Mango) and SyzygiumCumini (Jamun). Some of the important medicinal plants in the study area are AchyranthesAspera, Argemone Mexicana, Croton Sparcifours, Euphorbia Hirta, SolanumXanthocarpum, TribulusTerristris, VitexNegundo, AbrusPrecatorius, Abutilon Indicum and AdhatodaVasica.

Fauna:The majority domestic animals are Cow, Buffalo, Horse, Donkey, Goat, Pigand Dog. The main Birds are Pintail, Coot, House Sparrow, Myna, Cattle Egret, Little Egret, Pond Heron, Indian Ring Dove, Blue Rock Pigeon, etc.,

Source:http://cpcb.nic.in/displaypdf.php?id=UGFuaXBhdC5wZGY=

3.5.3.2 Forest Resources The district is covered by Panipat forest range which comes under the Karnal Forest Division headed by the Deputy Conservator of Forests stationed at Karnal. The district falls in North Haryana Forests Circle with headquarters at . As regards, proportion of forest cover, Haryana State (1.4 percent forest cover of total area) is at bottom place among the State of the country. Panipat district has 3.2 percent area under forests. Forests and forest produce have a recognised place both in rural and urban economy of the district. Nurseries of different tree species like Timber, fuel, shady, ornamental, fruit trees, etc., are raised for afforestation and reafforestation.

The district is not rich in its forest wealth. Tropical dry deciduous forests are found here. Mostly the vegetation consists of Khair (Acacia catecha), Kikar (Acacia nilotica), Shisham (Dalbergiasissoo), Nim (Azadirachtaindica), Tut (Morisalba), Sirish (Albizialebbeck), VilayatiImli (Inga dulcis) etc., Peepal (Ficusreligiossa) and Badh (Ficusbenghalensis) are often seen planted near village settlements and the people look upon these trees with religious ferour. Ber (Ziziphusmauratiana), Aam (Mangiferaindica) and Jamun (SygiumJambolanum) are the main fruit trees.

Due to extension of cultivation, very little of nature forest is left over. Presently, forests form 3.24 percent of the total area of the district. Wherever these forests are present, are of open type,

217 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report dry deciduous scrub, consisting of following shrubs and trees: Dhak, Jal, Kaindu, Jand, Jhar, Babul, Neem, Tut, etc. Shisham (Ficusreligiosa), Badh (Ficusbengalensis), etc., are the important tree species grown in the plains. Safeda (Eucalyptus hybrid) has been introduced since 1963 in forest areas and along the road routes. The natural vegetation is mainly of forest growth and its degradation stages.

During the monsoon a number of herbaceous plants appear as underground in the jungles. Kikar and Khajur are very common in swampy or marshy localities and in low-lying areas. Farash is common in saline areas where hardly and other tree can grow. Shisham is extensively planted along canal banks and road sides. Peepal and Badh are often planted near village settlements. To awaken people regarding medicinal plants, Haryana Forest Dept has developed 32 Herbal gardens/ Parks (between 2005 and 2011) in all the districts of the state and named the parks in the name of important medicinal plants. In Panipat district such a Herbal garden is named as BilvaVatika which is located in Patti Kalyana village.

There was a time when dense jungles of the district harboured various kinds of wild animals and birds. But with the development of communications, clearance of jungles, increases in irrigational facilities and extension of cultivation due to pressure of population, rich stocks have considerably finished, some species are almost extinct. Hog deer, which was quite abundant in swampy areas, is now available in traces. Grey and black partridges are sufficiently available. Black buck, nilgai and chinkara are still available though not in plenty. Hare are commonly available. Pea fowl is abundantly found in cultivated fields, in groves and orchards. Blue rock pigeons are also commonly noticed. Common quail comes with the ripening of wheat. The common and Jack snipe are also found in rice fields. The jheels abound in ducks and geese. The pintail, mallard, pochard, shoveller teals, comb duck, spotbil and goose are the common species of ducks available. The grey leg goose is to be found on the large marshes and the black barred goose is to be seen on river side. The pelicans, cranes, herons, bitterns and many sort of waders cover jheels; sars and kunj are conspicuous. In 1986, a Deer Park-cum-Breeding centre was established in National Fertilizers Limited at Panipat. Nardak area, once a favourite habitat of the lions and tigers is now completely devoid of these carnivores. Jackals can be seen which make much damage to crops.

218 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Source: http://censusindia.gov.in/2011census/dchb/DCHB_A/06/0607_PART_A_DCHB_PANIPAT.pdf

3.5.3.3 Irrigation The Western Yamuna Canal (WJC) is the major source of canal irrigation. The WJC passes through the central part of the district covering part of Madlauda. Panipat and Samalkha blocks. Out of 96,000 ha net irrigated area, 28,000 ha is irrigated by canal and 68,000 ha is irrigated by ground water. About 70.83% of the irrigation is based on ground water resources. The gross irrigated area has been worked out as 1,90,000 ha, which is 3.49% to the State total. Percentage of Gross Area Irrigated to Total Cropped Area has been worked out as 99.5% with the irrigation intensity of 197.9.

Source:http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

3.5.3.4 Agricultural Resources

Net area sown in the district is 96,000 ha which constitutes about 76% of the total area. Area sown more than once is 95,000 ha bringing the total cropped area to 1,91,000 ha. Paddy constitutes main kharif whereas the wheat is the main . The details of area under cultivation, production and average yield of important crops of the district during the year 2011- 12 is given in Table 3-2.

Table 3-2Production details of the district (Panipat) during the year 2011-12 Area under cultivation Production Average yield S.No Crops (ha) (Tonnes) (Kgs/ha) 1 Rice 76,900 1,74,000 2,255 2 Bajra 500 2000 1792 3 Wheat 86,600 3,99,000 4,584 4 2000 15000 7689 Source: http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

3.5.3.5 Mineral Resources

The whole of Panipat district is formed of alluvium rocks of recent period. The underground water in the district is generally fresh and suitable for domestic and irrigation purposes. Underground water level is comparatively high. Due east of Grand Trunk Road (Delhi – ), sand is mined from all along the Yamuna river to be used as constructional materials. Brick earth or ordinary clay is available in plenty in all parts of the district which is used in the 219 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report manufacturing of bricks. Minor occurrence of saltpetre is also reported from north-western parts of the district which appears as thin white encrustation on the surface of the earth. It is primarily used in the production of nitrates and potash. Mineral map of Haryana is given in Figure 3-5

Source:http://censusindia.gov.in/2011census/dchb/DCHB_A/06/0607_PART_A_DCHB_PANIP AT.pdf

220 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Source: Maps of India Figure 3-5Mineral Map of Haryana

221 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.5.4 Land Use & Land Cover

Total geographical area of Panipat District is 1268.01sq Km. respectively. Details of land use/land cover statistics given in Table 3-3. Land Use pattern and land use map are given in Figure 3-6. Land use/Land cover pattern for Panipat District is given in Figure 3-7.

Table 3-3 Land use/Land cover statistics for Panipat district (2015-16) Area in Area in Area in Area S.No. Particulars (Sq.Km) (Acres) (Hectares) in (%) 1 Builtup, Urban 109.1 26959.16 10910 8.60 2 Builtup, Mining 36.01 8898.25 3601 2.84 3 Agriculture, plantation 5.81 1435.68 581 0.46 4 Forest, Deciduous 1049.6 259361.41 104960 82.78 Barren/Unculturable/Wastelands, 5 1.38 341.00 138 0.11 Salt Affected land Barren/Unculturable/Wastelands, 6 11.85 2928.19 1185 0.93 Sandy area Wetlands/Water Bodies, 7 4.56 1126.80 456 0.36 River/Stream/Canals 8 Builtup, Rural 0.59 145.79 59 0.05 9 Agriculture, Crop land 15.98 3948.74 1598 1.26 10 Agriculture, Fallow 6.76 1670.43 676 0.53 11 Grass/Grazing 0.49 121.08 49 0.04 Barren/uncultureable/Wastelands, 12 0.75 185.33 75 0.06 Scrub land Wetlands/Water Bodies, Inland 13 6.15 1519.70 615 0.49 Wetland Wetlands/Water Bodies, 14 18.96 4685.11 1896 1.50 Reservoir/Lakes/Ponds Total 1267.99 313326.7 126799 100

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Figure 3-6Land use/Land cover pattern for Panipat district

223 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 3-7 Land use/Land cover Map of Panipat district

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3.5.4.1 Land use land cover for the study area

Total geographical area of the study area is 445.62 sq.Km. The land use pattern of the study area is given in Table 3-4, Land use pattern and land use map of the study area is given in Figure 3-8 and Figure 3-9 respectively.

Table 3-4Land use pattern of the Study Area Area S.No. Description Area (Sq.km ) Area (Acres) Area (Hectares) (%) 1 Cropland 328.96 81287.66 32896 75.09 2 Urban 73.90 18261.06 7390 16.87 3 Rural 13.57 3353.21 1357 3.10 4 Scrub land 6.91 1707.50 691 1.58 Rivers/ Streams/ 5 5.84 1443.09 584 1.33 Canals Reservoirs/ Lakes/ 6 2.88 711.66 288 0.66 Ponds 7 Fallow land 2.32 573.28 232 0.53 8 Salt Affected land 1.24 306.41 124 0.28 9 Plantation 0.99 244.63395 99 0.23 10 Grass/Grazing 0.95 234.75 95 0.22 11 Mining 0.46 113.67 46 0.11 12 Inland Wetland 0.04 9.88 4 0.01 TOTAL 438.06 108246.82 43806 100

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Figure 3-8Land use pattern of the Study Area

226 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 3-9Land use map of the Study Area

227 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.5.5 Topography

Panipat district forms part of Indo gangetic plain and lies in Yamuna Sub basin of the basin. Physio-graphically, the district is characterized by two distinct features - vast upland plains and Yamuna flood plains. The district is mainly drained by River Yamuna and its tributaries. Topography of Panipat Town is almost flat with gentle slope in the northwest to southeast direction towards Yamuna River. Panipat Main Drain originating in the northwestern side passes through the town towards Yamuna in southeast direction. Source: http://dcmsme.gov.in/dips/har_panipat.pdf Physical map of Haryana State is given in Figure 3-10 and Contour map of the study area is given in Figure 3-11.

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Figure 3-10 Physical map of Haryana State

229 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report

Figure 3-11 Contour map of the Study Area

230 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.5.6 Geomorphology of PIA District

The district forms a part of Indo gangetic plain and lies in Yamuna Sub basin of main Ganga basin. Physiographically, the district is characterised by two distinct features i.e. vast upland plain and Yamuna flood plain. The width of the flood plain varies according to the amount of shift experienced by the river. It is narrow in the Northern part and widens downstream. The district is mainly drained by the river Yamuna and its tributaries. The river Yamuna is major Perennial River which flows all along the eastern margin of the district from northern to southern direction. The district is also drained by the artificial drain named as „Naurah Drain‟ which originate in southern eastern part of Madlauda block and flows through south western part of Panipat and all along eastern boundary of Israna block in southerly direction. The district has two types of soils viz-tropical arid brown and arid brown soils (solemnized). The arid brown soils are found in major parts of the district whereas tropical arid brown soils are found in north eastern part of the district especially in parts of Bapoli and Panipat blocks.

Source: http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

3.5.6.1 Geomorphology of the study area Total geographical area of the study area is 445.62 sq.Km . The Geomorphology pattern of the study area is given in Table 3-5, Geomorphology pattern of the study area is given in Figure 3-12. Geomorphology map of the study area is given in Figure 3-13.

Table 3-5Geomorphology pattern of the study area Sl. Area in Sq. Area in Area in Particulars Area in % No Km Acre Hectare Fluvial Origin – Older 1 436.11 107764.96 43611 99.55 Alluvial Plain 2 Water bodies 1.95 481.85 195 0.45 Total 438.06 108246.82 43806 100

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Figure 3-12 Geomorphology pattern of the study area

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Figure 3-13 Geomorphology Map of Study Area

233 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.5.7 Hydrogeology of PIA District

The district is occupied by geological formations of Quaternary age comprising of recent alluvial deposits belonging to the vast Gangetic alluvial plains. The Central Ground Water Board has drilled 08 exploratory boreholes in the depth range of 103 to 460 m and 35 piezometers in the depth range of 33 to 348 m and 01 Slim Hole to delineate and determine potential aquifer zones, evaluation of aquifer characteristics, behaviour of water levels etc.

The ground water exploration undertaken by CGWB has revealed the existence of 8 -23 granular zones down to a maximum depth of 460 m. These zones mainly comprise of various grades of sand and gravel. The first granular zone forms the water table aquifer and occurs down to 50 – 150 m below ground level. The second aquifer occurs between 130 and 250m depth, the third one exists between 286 and 366 m depth. Total thickness of the alluvium is not precisely known. However, the bedrock has not been encountered up to 460 m depth at village Dadlana (deepest exploration borehole) in the district. The discharge range from 605 to 3258 lpm for 6 - 20 m of draw down. The transmissivity of the aquifers lies between 350 and 1990 m2/day.

Source:http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

3.5.8 Drainage Pattern in PIA District

The district is mainly drained by the river Yamuna and its tributaries. The river Yamuna is major Perennial River which flows all along the eastern margin of the district from northern to southern direction. The district is also drained by the artificial drain named as „Naurah Drain‟ which originate in southern eastern part of Madlauda block and flows through south western part of Panipat and all along eastern boundary of Israna block in southern direction. Drainage map of the study area is given in Figure 3-14.

Source:http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

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Figure 3-14Drainage map of the study area

235 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 3.5.9 Soils in PIA District

The district has two types of soils viz-tropical arid brown and arid brown soils (solemnized). The arid brown soils are found in major parts of the district whereas tropical arid brown soils are found in north eastern part of the district especially in parts of Bapoli and Panipat blocks.

Source:http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

3.6 Seismicity

As per Vulnerability Atlas of India – 3rd Edition, the project location/study area falls in Zone IV, which is categorized as a High Damage Risk Zone. The seismicity map of India is shown in Figure 3-15

236 EIA Report

Figure 3-15Seismicity Map of India

237 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.7 Air Environment

Baseline ambient air quality assessment gives the status in the vicinity of site and is an indispensable part of environmental impact assessment studies. Significant changes, in predominant winds and weather conditions are observed in winter, summer and post- monsoon seasons apart from the local topographic influences. The baseline status of air environment in the study area is assessed through a systematic air quality surveillance programme.

3.7.1 Meteorological Conditions

The regional air quality is influenced by the meteorology of that region. The principal weather parameters that influence the concentration of the air pollutants in the surroundings are wind speed, wind direction and temperature. The meteorological data is useful for proper interpretation of the baseline data. It is used as input for air quality dispersion models for predicting the post project environmental scenario i.e. ground level concentrations due to proposed utilities like Boilers, etc.

3.7.2 Meteorological Data Collection

Available secondary data pertaining to the meteorological parameters was obtained from the IMD Climatological tables. In addition, baseline meteorological data was generated during the study period March 2019 to May 2019.The methodology adopted for monitoring surface observations is as per the standard norms laid down by Bureau of Indian Standards (BIS) i.e. IS:8829 and Indian Meteorological Department (IMD).

3.7.3 General Meteorological Scenario based on IMD Data The nearest Indian Meteorological Department (IMD) station located to project site is Karnal. The Climatological data for Karnal(2942‟ N and 77o 02‟ E), published by the IMD, based on daily observations at 08:30 and 17:30 hour IST for a period of 1971 to 1999 is presented in the following sections on the meteorological conditions of the region. The monthly variations of the relevant meteorological parameters are reproduced in Table 3-6.

238 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report Table 3-6Climatological Summary – karnal (1971-1999) Predominant Relative Vapour Wind Temp (oC) Rainfall Humidity Pressure Directions (%) hPa (From)* Mont No. h Dail Dail Monthly of 08:3 17:3 08:3 17:3 08:3 y y Total(mm Rain 17:30 0 0 0 0 0 Max. Min. ) y days Jan 19.7 7.4 15.4 1.3 78 58 10.4 11.9 NW NW Feb 22.2 9.3 15.9 1.6 72 53 11.5 12.8 NW NW Mar 27.4 13.4 23.9 1.8 66 48 14.5 15.7 NW SW Apr 34.9 19.2 7.1 0.8 50 33 17.0 16.1 NW NW May 38.7 23.6 15.0 1.5 49 32 19.9 18.7 NW NW Jun 38.1 25.5 48.2 2.7 61 44 25.6 24.5 SE SW Jul 33.8 25.2 165.3 7.2 78 66 30.7 30.7 SE SE Aug 32.6 24.7 146.2 7.3 81 73 31.3 32.0 SE SE Sep 32.6 22.9 64.3 2.8 76 64 28.0 28.7 SE SE Oct 31.7 17.7 5.0 0.4 69 51 20.4 21.0 NW NW Nov 27.4 12.6 1.2 0.4 70 52 14.4 15.8 NW NW Dec 22.1 8.2 12.5 1.1 75 55 11.0 12.6 NW NW Max. 38.7 25.5 165.3 7.3 81 73 31.3 32 Annual Wind Min. 19.7 7.4 1.2 0.4 49 32 10.4 11.9 Predominant direction is Avg. 30.0 17.3 519.9 29.1 69 52 19.5 20.0 NORTH /Total. WEST

As per the above IMD Climatological summary of Karnal(1971-1999) is given in Table 3-6, the observations drawn are the following.

 Daily maximum temperature is 38.7oC and the daily minimum temperature is 7.4oC were recorded in the months of May and January respectively.  Maximum and minimum relative humidity of 81% and 32% were recorded in the months of August and May respectively.  Maximum and minimum rainfall of 165.3mm and 1.2 mm was recorded in the months of July and November respectively. Annual total rainfall recorded in the region was 519.9 mm.  Annual Wind predominant pattern is from North West. 239 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.7.4 Meteorological data during Study Period The meteorological data of study period was used for interpretation of baseline status and to simulate the meteorological conditions for prediction of impacts in modelling studies. Meteorology Data for the Study Period (March 2019 to May 2019)is presented in Table 3-7 and Wind rose pattern shown in Figure 3-16.

Table 3-7Meteorology Data for the Study Period (March - May 2019). S. No Parameter Observation 1. Temperature Max Temperature: 450C Min Temperature: 100C Avg Temperature: 31.280C 2. Average Relative Humidity 43.91% 3. Average Wind Speed 2.8 m/s 4. Predominant Wind Direction North West

Figure 3-16Wind Rose during (March - May 2019).

240 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report 3.7.5 Atmospheric Inversion

Atmospheric inversion level at the project site was monitored; the results observed at the site during the study period are as follows

 Average atmospheric temperature: 31.280C  Average Relative humidity: 43.91 %  Average Wind speed: 2.8 m/s

The Peak inversion level calculated based on the temperature and wind speed at the project site and the maximum inversion height is derived by the graph plotted based on the temperature and wind speed. The Peak inversion level at the project site varies from 50 to 4000m during 6 AM to 5 PM, the maximum recorded at 5 PM, April 2019. This is shown in the following Figure 3-17.

Figure 3-17Atmospheric inversion level at the project site

3.8 Ambient Air Quality The selection criteria for monitoring locations are based on the following:

 Topography/Terrain  Meteorological conditions  Residential and sensitive areas within the study area  Representatives of regional background air quality/pollution levels and

241 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 EIA Report  Representation of likely impacted areas

3.8.1 Ambient Air Quality Monitoring Stations

To evaluate the baseline air quality of the study area, Eight (08) monitoring locations have been identified for the study period as per secondary sources (Indian Meteorological Data, Climatological Normals (1971-1999). The wind predominance was from North West. Map showing the AAQ monitoring locations is given in Figure 3-18 and the details of the locations are given in Table 3-8.

Table 3-8Details of Ambient Air Quality Monitoring Locations Distance Station Type of (~Km) from Azimuth Location Code Wind Project Directions boundary A1 Project Site - Within Site A2 Razapur c/w 2.66 E A3 Barauli c/w 6.57 E A4 New Bahauli d/w 2.95 ESE A5 Panipat d/w 9.23 SE A6 Madlauda c/w 8.7 SSW A7 Dharamgarh c/w 3.76 WSW A8 Munak u/w 3.55 NNW Note: c/w- cross wind direction, u/w- up wind direction, d/w- down wind direction

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Figure 3-18Map showing the Ambient Air Quality monitoring locations

243 3.8.2 Ambient Air Quality Monitoring Techniques and Frequency

Ambient air quality was monitored twice in a week for One (01) season (shall cover 12 weeks), i.e. during Pre-Monsoon season (from March to May 2019). PM10, PM2.5, SO2, NOx,

CO, Pb, O3, NH3, C6H6, C20H12, As & Ni were monitored. Sampling was carried out as per Central Pollution Control Board (CPCB) monitoring guidelines at each location. Analytical methods used for analysis of parameters are given in Table 3-9.

Table 3-9Analytical Methods for Analysis of Ambient Air Quality Parameters (NAAQ) S. NAAQ standards: Samplin N Parameters Analytical method 2009 g Time o Sulphur Dioxide IS 11255: (Part 2) / USEPA Method 50 80(24 1 24 Hours (SO2), 6 (Annual) Hours) μg/m3 Nitrogen Dioxide IS: 5182 (Part - 6): 2006 / CPCB 40 80 (24 2 24 Hours (NO2), guidelines Volume1 (Annual) Hours) μg/m3 Particulate In house method Matter 40 60 (24 3 (Gravimetric method) 24 Hours (PM ), (Annual) hours) 2.5 based on CPCB guidelines Volume1 μg/m3 Particulate Matter IS:5182 (Part– 23): 2006 60 100 (24 4 24 Hours (PM10), CPCB guidelines Volume1 (Annual) hours) μg/m3 IS:5182(Part–10):1999 (Reaff:2006) 4 5 CO, mg/m3 2 (8 hours) 8 Hours CPCB guidelines Volume1 (1hour) IS:5182(Part–22):2004 (Reaff:2006) 0.5(Annual 1(24 6 Pb, μg/m3 24 Hours CPCB guidelines Volume1 ) hours) In house method 100(8hours 180 7 O , μg/m3 (Spectrophotometric method) based 8 Hours 3 ) (1hour) on CPCB guidelines Volume1 In house method 100(Annual 400(24 8 NH , μg/m3 (Spectrophotometric method) based 8 Hours 3 ) hours) on CPCB guidelines Volume1 GC FID/ GC MS based on 5 Benzene, 9 IS 5182 (Part:12)/ CPCB guidelines 5 (Annual) (Annual 24 Hours μg/m3 Volume1 ) In House Validated method By Benzo (a) 1 HPCL , UV & GC MS Based on 10 pyrene, 1 (Annual) (Annual 24 Hours IS:5182(Part–12) CPCB guidelines ng/m3 ) Volume1 Arsenic, ng/ In house method (AAS method) 6 11 6 (Annual) 24 Hours m3 Based on CPCB guidelines Volume (Annual

244 EIA Report S. NAAQ standards: Samplin N Parameters Analytical method 2009 g Time o 1 ) In house method (AAS method) 20 Nickel, ng/ 12 Based on CPCB guidelines Volume 20(Annual) (Annual 24 Hours m3 1 ) HECS/AIR/AMBIENT/SOP/018:20 13 TVOC - - 8 Hours 13 Methane 14 Hydrocarbo IS 5182 (Part 17) - - 8 Hours n Non- Methane 15 IS 5182 (Part 17) - - 8 Hours Hydrocarbo n 16 Vanadium EPA method IO 3.1&3.5 - - 24 Hours

3.8.2.1 Results and Discussions

The variations of the pollutants PM10, PM2.5, SO2, NO2, CO, Pb, O3, NH3, C6H6, C20 H12, As, Ni, VOC,Vanadium, Methane & Non Methane are compared with National Ambient Air Quality Standards (NAAQS), MoEF&CC Notification, November 2009. Ambient Air Quality Monitoring Data ( March to May 2019) for the study area is given in Table 3-10 and trends of measured ambient concentration in the study area were graphically represented in Figure 3-18.

245 HECS/EIA/IOCL Panipat/Final/17.07.2021/1063 Table 3-10Summary of the average baseline concentrations of pollutants Locations NAAQ Project New Parameters Conc. Razapur Barauli Panipat Madlauda Dharamgarh Munak Standards Site Bahauli A1 A2 A3 A4 A5 A6 A7 A8 Min. 70.06 62.38 58.82 54.31 67.35 53.17 56.30 60.05 PM10 Conc. Max. 100 212.14 171.90 154.98 151.64 204.59 131.40 124.20 140.81 (µg/m³) Avg. (24 Hours) 128.00 106.90 97.83 93.89 123.31 84.82 83.59 92.63 98th „tile 211.48 171.36 154.49 151.17 203.94 130.99 123.80 140.37 Min. 35.90 32.05 30.27 28.02 34.54 27.44 29.01 30.89 PM2.5 Conc. Max. 60 107.24 87.12 78.66 77.00 103.46 66.88 63.27 69.76 3 (µg/m ) Avg. (24 Hours) 64.98 54.42 49.89 47.92 62.63 43.38 42.77 46.54 98th „tile 106.90 86.84 78.41 76.76 103.14 66.67 63.07 69.54 Min. 18.28 15.24 14.27 12.99 15.77 14.50 12.83 12.50 SO2 Conc. Max. 80 29.96 22.60 21.02 19.12 24.13 25.32 18.38 19.52 (µg/m3) Avg. (24 Hours) 22.83 18.04 16.83 15.32 18.98 18.75 14.92 15.20 98th „tile 29.87 22.53 20.96 19.06 24.05 25.24 18.32 19.45 Min. 32.27 26.18 24.23 21.69 27.24 22.98 21.36 20.69 NO2Conc. Max. 80 61.10 46.38 43.22 39.41 49.42 51.81 37.93 40.20 3 (µg/m ) Avg., (24 Hours) 43.71 34.13 31.72 28.69 36.01 34.58 27.89 28.46 98th „tile 60.91 46.23 43.08 39.28 49.27 51.64 37.81 40.07 BLQ BLQ BLQ BLQ 3 1 BLQ (LOQ BLQ (LOQ BLQ (LOQ BLQ (LOQ Pb (μg/m ) Avg. (LOQ (LOQ (LOQ (LOQ (24 hour) 0.05) 0.05) 0.05) 0.05) 0.05) 0.05) 0.05) 0.05) 4 CO (mg/m3) Avg. 0.72 0.69 0.61 0.75 0.78 0.63 0.73 0.65 (1hour) 3 O3 (μg/m ) Avg. 180 16.74 11.75 10.95 11.95 15.42 10.2 10.9 12.47

246

Locations NAAQ Project New Parameters Conc. Razapur Barauli Panipat Madlauda Dharamgarh Munak Standards Site Bahauli A1 A2 A3 A4 A5 A6 A7 A8 (1hour)

3 5 BLQ BLQ BLQ (LOQ BLQ (LOQ BLQ (LOQ BLQ BLQ (LOQ BLQ C H (μg/m ) Avg. 6 6 (Annual) (LOQ 1) (LOQ 1) 1) 1) 1) (LOQ 1) 1) (LOQ 1)

C20H12 (a) , 1 BLQ BLQ BLQ (LOQ BLQ (LOQ BLQ (LOQ BLQ BLQ (LOQ BLQ Avg. (ng/m3) (Annual) (LOQ 1) (LOQ 1) 1) 1) 1) (LOQ 1) 1) (LOQ 1) 6 BLQ BLQ BLQ (LOQ BLQ (LOQ BLQ (LOQ BLQ BLQ (LOQ BLQ As (ng/ m3) Avg. (Annual) (LOQ 2) (LOQ 2) 2) 2) 2) (LOQ 2) 2) (LOQ 2) BLQ BLQ 3 20 BLQ BLQ BLQ BLQ BLQ BLQ Ni (ng/m ) Avg. (LOQ (LOQ (Annual) (LOQ 10) (LOQ 10) (LOQ 10) (LOQ 10) (LOQ 10) (LOQ 10) 10) 10) BLQ BLQ 400 BLQ BLQ BLQ BLQ NH (μg/m3) Avg. 23.61 (LOQ 21.26 (LOQ 3 (24 hour) (LOQ 10) (LOQ 10) (LOQ 10) (LOQ 10) 10) 10) VOC BLQ(LOQ BLQ(LO BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LO Avg. - (μg/m3) 0.1) Q 0.1) 0.1) 0.1) 0.1) 0.1) 0.1) Q 0.1) Methane HC Avg. - 1.95 1.27 1.08 1.38 1.18 1.42 0.89 1.55 (μg/m3) Non Methane Avg. - 0.48 0.31 0.23 0.35 0.29 0.26 0.17 0.33 HC(μg/m3) Vanadium(n BLQ(LOQ BLQ(LO BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LO Avg - g/m3) 0.01) Q 0.01) 0.01) 0.01) 0.01) 0.01) 0.01) Q 0.01) Note: BDL (Below detection limit), DL (Detection limit), BLQ (Below Limit Of Quantification), LOQ (Limit of Quantification)

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Figure 3-18 Trends of Measured Ambient Concentrations in the Study Area

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3.8.2.2 Observations The ambient air quality has been monitored at 8 locations as per NAAQS, 2009 within the study area. It is observed that during study period PM10 and PM2.5 values are exceeding the prescribed NAAQS standards in the study area. The results obtained are summarised as below:

 The average baseline levels of PM10vary from 83.59 to 128 µg/m³, the maximum value of 212.14µg/m³ was observed in Project Site and minimum value of 53.17µg/m³ was observed in Madlauda.

 The average baseline levels of PM2.5vary from 42.77 to 64.98µg/m³.The maximum value of 107.24µg/m³ was observed in Project Site and minimum value of 27.44µg/m³ was observed in Madlauda.

 The average baseline levels of SO2 vary from 14.92 to 22.83µg/m³, the maximum value of 29.96µg/m³ was observed in Project Site and minimum value of 12.50µg/m³ was observed in Munak.

 The average baseline levels of NO2vary from 27.89 to 43.71µg/m³, the maximum value of 61.10 µg/m³ was observed in Project Site and the minimum value of 20.69µg/m³ was observed in Munak.  The average baseline levels of CO vary from 0.61 to 0.78 mg/m³, the maximum value of 0.78 mg/m³ was observed in Panipat and the minimum value of 0.61 mg/m³ was observed in Barauli.

 The nearest HSPCB AAQ monitoring station is Sector-18, Panipat in which the

maximum and minimum levels for the period March to May 2019 is PM10 (487.59

and 29.52µg/m³), PM2.5 (131.87 and 15.96 µg/m³), SO2 (148.33 and 5.82 µg/m³), NOx (120.5 and 11.87 ppb) and CO (77.44 and 0.14 mg/m³). The average values of same

station for the above period is PM10 (169.49µg/m³), PM2.5 (47.27µg/m³), SO2 (30.56

µg/m³), NO2 (48.86ppb) and CO (11.13 mg/m³).

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3.9 Noise Environment

The prevailing ambient noise level at a particular location is nothing but the resultant (total) of all kinds of noise sources existing at various distances around that location. The ambient noise level at a location varies continuously depending on the type of surrounding activities.

Ambient noise levels have been established by monitoring noise levels at Eight (08) locations in and around 10Km distance from project area during the study period using precision noise level meter. The noise monitoring locations in the study area were selected after giving due consideration to the various land use categories. The land use categories include commercial, residential, rural and sensitive areas. Noise levels were recorded on an hourly basis for one complete day at each location using pre- calibrated noise levels. Map showing noise monitoring locations is Figure 3-19.

3.9.1 Results and Discussions

Based on the recorded hourly noise levels at each monitoring location, the day equivalent (Ld) and night equivalent (Ln) were calculated;  Ld: Average noise levels between 6:00 hours to 22.00 hours.  Ln: Average noise levels between 22:00 hours to 6.00 hours.

The comparison of day equivalent noise levels (Ld) and night equivalent noise levels (Ln) with the respective CPCB stipulated noise standards for various land use categories are shown in the Table 3-11.

Table 3-11Day and Night Equivalent Noise Levels Distanc Noise level CPCB e (~Km) Azimu in dB(A) Standard S. Locatio from th Leq Environme Location No n Code Project Directi LNig ntal Setting Nig Lday bounda on Day ht ht (Ld) ry (Ln) 1 Project Site Within Site 69.4 60.5 75 70 Industrial 2 Razapur N2 2.66 E 47.5 42.5 55 45 Residential 3 Barauli N3 6.57 E 49 42.8 55 45 Residential 4 New Bahauli 2.95 ESE 51 41.5 55 45 Residential

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Distanc Noise level CPCB e (~Km) Azimu in dB(A) Standard S. Locatio from th Leq Environme Location No n Code Project Directi LNig ntal Setting Nig Lday bounda on Day ht ht (Ld) ry (Ln) 5 Panipat 9.23 SE 54.8 44.7 55 45 Residential 6 Madlauda N6 8.7 SSW 52 43.5 55 45 Residential 7 Dharamgarh N7 3.76 WSW 52.5 44.3 55 45 Residential 8 Munak N8 3.55 NNW 50 44 55 45 Residential

3.9.1.1 Observations It is observed that the day equivalent and night equivalent noise levels at all locations are within prescribed CPCB standards

 In industrial area (Project site), day time noise level was about 69.4dB(A) and 60.5 dB(A) during night time, which is within prescribed limit byCPCB for Industrial area (75 dB(A) Day time & 70 dB(A)Night time).  In residential area (Dharamgarh, Barauli, Razapur, New Bahauli, Madlauda, Panipat, Munak) day time noise levels varied from 47.5dB (A) to 54.8dB (A) and night time noise levels varied from 41.5dB (A) to 44.7dB(A) across the sampling stations. The field observations during the study period indicate that the ambient noise levelsin Residential area are within the limit prescribed by CPCB for Residential area (55 dB (A) Day time & 45 dB (A) Night time) .

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Figure 3-19 Map showing the noise monitoring locations

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3.10 Water Environment 3.10.1 Surface Water Resources

The district possesses a good network of canals emanating from Western Yamuna Canal (Delhi Branch) which passes through the centre of the district in north south direction. All the distributaries depend upon this canal for water requirement. The canal takes off from the Yamuna river at Tajewala and a strong masonary weir is built. There is a regulator at Indri and canal bifurcates into Branch and Main Branch. Again Main Branch bifurcates into Hansi Branch, Delhi Branch and Gohana distributary at Munak in . Near Munak after bifurcation, the Hansi Branch entering from the north western edge of the district passes into . But the Delhi Branch of the Western Yamuna Canal after entering the district takes a direction towards Panipat town and then goes in a southerly direction and enters district. Main distributaries that irrigate the Bhangar area of the district are Gohana Distributary, Bhutana Sub-Branch, Israna Distributary, Naraina Distributary, Bazidah Distributary, Hulana Distributary and Samalkha Distributary.

3.10.2 Surface Water Quality Assessment

Water quality monitoring and assessment can be used to determine ambient water quality, the extent and causes of a water quality problem, or to measure the effectiveness of best management practices being implemented in water system. Monitoring helps to determine the trends in the quality of the aquatic environment and the impact due to the release of contaminants, other anthropogenic activities, and/or by waste treatment operations (impact monitoring).To establish the baseline status of water environment, the representative sampling locations for surface water within a radial distance of 10Km from project site have been selected as per CPCB guidelines of Water Quality Monitoring through an adequate survey of the project area. Test methods used for the analysis of water quality parameters is given in Table 3-12. Water sampling and map of sampling location are given in Table 3-13 and Figure 3-20.

Table 3-12Test methods used for the analysis of water quality parameters

Sl. No Parameter Measured Test Method 1 Turbidity IS 3025(Part - 10):1984 2 pH IS:3025 (Part - 11): 1983 (Reaff: 2006) 3 Conductivity IS:3025 (Part - 14): 1983 (Reaff: 2006) 4 Total Dissolve Solids IS: 3025:1(Part - 16) 1984 (Reaff 2006) 5 Total Suspended Solids IS 3025 (Part - 17) 1984 (Reaff 1996)

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Sl. No Parameter Measured Test Method 6 Alkalinity as CaCO3 IS:3025,1 (Part - 23) 1986 (Reaff 2009) 7 Total Hardness as CaCo3 IS:3025 (Part - 21) 1983 (Reaff 2006) 8 Sodium IS:3025,5(Part - 45) 1993 (Reaff 2006) 9 Potassium IS:3025,5(Part - 45) 1993 (Reaff 2006) 10 Calcium as Ca IS 3025 (Part - 40):1991 11 Magnesium as Mg IS 3025 (Part - 46) 1994 12 Chloride IS 3025 (Part - 32):1988 13 Sulphate SO4 IS 3025(Part - 24):1986 14 Nitrate as NO3 ASTM (Part - 31)1978 15 Phosphate IS 3025 (Pt 45) 1993 (R 2006) 16 Fluorides as F IS 3025 (Part - 60):2008 17 Cyanide IS 3025 (Part-27):1986 18 Arsenic IS 3025:(Part-37):1988(Reaff 2009) 19 Boron IS:3025 (Part - 57):2003 20 Cadmium IS 3025 (Part - 41)1991 21 Chromium, Total IS:3025 (Part - 52) 2003 (Reaff 2009) 22 Copper IS:3025 (Part - 42)1992 (Reaff: 2009) 23 Lead IS:3025 (Part - 47) 1994 (Reaff 2009) 24 Manganese IS 3025:(Part - 59):2006 25 Mercury IS 3025 (Part48):1994 RA 1999 26 Nickel IS 3025:(Part-54):2003(Reaff 2009) 27 Selenium IS 3025 Part (56)2003 28 Zinc IS:3025 (Part - 49) 1994 (Reaff 2009) 29 Dissolved Oxygen IS:3025 (Part - 38)1989 (Reaff 2009) 30 BOD 5210B APHA22nd Edn 2012 31 COD IS:3025 (Part-58)-2006

Table 3-13Details of Surface water sampling locations Distance in SI.No Location Location Code Direction ~km Main drain no 2 u/s near project 1 SW1 0.09 NE site 2. Main drain no 2 d/s near Razapur SW2 2.31 E Western Yamuna canal d/s near 3 SW3 0.98 SE Sithana 4 Pond near Khukrana SW4 6.82 S 5 Pond near Assan kalan SW5 5.61 S 6 Western Yamuna canal u/s SW6 0.42 W

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Distance in SI.No Location Location Code Direction ~km 7 Pond near Paban Hasanpur SW7 7.66 NW 8 Pond near Gagsina SW8 7.25 N

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Figure 3-20 Map showing the surface water monitoring locations

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Table 3-14 Physicochemical Parameters of Surface water samples from the study area. Main Surface Main Western Wester Pond drain Pond Pond water drain Yamuna n near Pond No.2 u/s near near SL standar No.2 d/s canal d/s Yamun Paban near Parameter Unit near Khukra Assan NO ds (IS near near a canal Hasan Gagsina Project na Kalan 2296 Razapur Sithana u/s pur site Class-A) SW 1 SW 2 SW 3 SW 4 SW 5 SW 6 SW 7 SW 8 1 Turbidity NTU -- 12 15 20 115 51 18 128 55 2 pH (at 25°C) -- 6.5-8.5 7.05 7.18 7.55 7.36 7.73 7.28 7.3 7.23 µS/c 3 Electrical Conductivity - 968 1164 431 752 1896 326 1743 1096 m 4 Total Dissolved Solids mg/l 500 654 799 289 508 1279 203 1152 724 5 Total Suspended Solids mg/l - 21 34 46 264 117 37 294 126 6 Total Alkalinity as CaCO3 mg/l - 168.0 193.4 145.9 132.8 235.2 111.5 294.3 184.4 7 Total Hardness as CaCO3 mg/l 200 320.3 350.4 165.1 230.9 554.2 115.1 416.6 396.7 8 Sodium as Na mg/l - 60 84 9 52 153 3 143 70 9 Potassium as K mg/l - 5.6 7.8 3.2 8.1 9.2 1.5 8.3 7.6 10 Calcium as Ca mg/l - 60.12 68.14 39.15 46.17 116.64 28.06 87.48 72.9 11 Magnesium as Mg mg/l - 41.31 43.74 16.33 28.05 63.82 10.93 48.1 52.1 12 Chloride as Cl mg/l 250 148.91 182.53 23.32 117.64 384.28 9.9 295.84 168.12 13 Sulphate as SO4 mg/l 400 114.04 153.68 10.56 73.07 231.8 5.32 174.92 103.53 14 Nitrate as NO3 mg/l 20 3.1 4.8 1.4 8.3 5.7 1.3 9.5 7.8 15 Phosphate as PO4 mg/l - 5.6 5.34 0.09 1.25 8.1 1.04 6.17 3.42 16 Fluorides as F mg/l 1.5 0.17 0.29 0.14 0.25 0.34 0.27 0.31 0.25 BLQ( BLQ(L BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 17 Cyanide mg/l 0.05 LOQ OQ OQ Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) 0.01) 0.01) 0.01) BLQ BLQ BLQ BLQ 18 Arsenic mg/l 0.05 0.006 0.006 (LOQ 0.027 0.01 (LOQ (LOQ (LOQ 0.005) 0.005) 0.005) 0.005)

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Main Surface Main Western Wester Pond drain Pond Pond water drain Yamuna n near Pond No.2 u/s near near SL standar No.2 d/s canal d/s Yamun Paban near Parameter Unit near Khukra Assan NO ds (IS near near a canal Hasan Gagsina Project na Kalan 2296 Razapur Sithana u/s pur site Class-A) SW 1 SW 2 SW 3 SW 4 SW 5 SW 6 SW 7 SW 8 BLQ( BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(L BLQ(LO 19 Boron as B mg/l - LOQ OQ Q 0.1) Q 0.1) Q 0.1) Q 0.1) OQ 0.1) Q 0.1) 0.1) 0.1) BLQ( BLQ(L BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 20 Cadmium as Cd mg/l 0.01 LOQ OQ OQ Q 0.001) Q 0.001) Q 0.001) Q 0.001) Q 0.001) 0.001) 0.001) 0.001) BLQ( BLQ(L BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 21 Chromium, Total mg/l 0.05 LOQ OQ OQ Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) 0.01) 0.01) 0.01) BLQ( BLQ(L BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 22 Copper as Cu mg/l 1.5 LOQ OQ OQ Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) 0.01) 0.01) 0.01) BLQ( BLQ(L BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 23 Lead as Pb mg/l 0.1 LOQ OQ OQ Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) 0.005) 0.005) 0.005) 24 Manganese as Mn mg/l 0.5 0.033 0.049 0.034 0.026 0.021 0.029 0.114 0.147 BLQ( BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(L BLQ(LO LOQ OQ 25 Mercury mg/l 0.001 Q Q Q Q OQ Q 0.0005 0.0005 0.0005) 0.0005) 0.0005) 0.0005) 0.0005) 0.0005) ) ) BLQ( BLQ(L BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 26 Nickel as Ni mg/l - LOQ OQ OQ Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) 0.01) 0.01) 0.01) BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ( BLQ(L BLQ(L BLQ(LO 27 Selenium as Se mg/l 0.01 Q 0.005) Q 0.005) Q 0.005) Q 0.005) LOQ OQ OQ Q 0.005)

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Main Surface Main Western Wester Pond drain Pond Pond water drain Yamuna n near Pond No.2 u/s near near SL standar No.2 d/s canal d/s Yamun Paban near Parameter Unit near Khukra Assan NO ds (IS near near a canal Hasan Gagsina Project na Kalan 2296 Razapur Sithana u/s pur site Class-A) SW 1 SW 2 SW 3 SW 4 SW 5 SW 6 SW 7 SW 8 0.005) 0.005) 0.005) BLQ( BLQ(L BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(L BLQ(LO 28 Zinc mg/l 15 LOQ OQ Q 0.1) Q 0.1) Q 0.1) Q 0.1) OQ 0.1) Q 0.1) 0.1) 0.1) 29 Dissolved Oxygen mg/l 6 5.9 6.3 6.3 5.8 6.1 6.2 6 6.1 Chemical Oxygen Demand 30 mg/l - 41 47 14 12 56 4 52 9 as O2 31 BOD, 3 days @ 27°C as O2 mg/l 2 8 10 2 1.8 2 1.4 2 1.1 Note: BDL - Below Detection Limit; DL – Detection Limit; BLQ – Below Limit Of Quantification; LOQ – Limit Of Quantification

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3.10.2.1 Results and Discussions

Surface water sample results are discussed below:  Water sampling results are compared with Surface water standards IS 2296:1992.  pH in the collected surface water samples varies between 7.05 to 7.73 which is within the limit of IS 2296:1992.  The Total Dissolved Solids (TDS) value of collected surface water sample ranges from 203 mg/l to 1279 mg/l.  The Total hardness value of the collected surface water sample ranges between 115.1 mg/l – 554.2 mg/l.  BOD value of surface water sample ranges from 1.1 to 10 mg/l  COD value of surface water varies from 4 to 56 mg/l. Table 3-15 Surface water Standards (IS 2296:1992)

S.No Parameters Unit A B C D E 1 Colour Hazen 10 300 300 ------2 Turbidity NTU ------3 pH -- 8.5 8.5 8.5 8.5 8.5 4 Conductivity µS/cm ------1000 2250 Total Dissolved 5 mg/l 500 --- 1500 --- 2100 Solids Alkalinity as 6 mg/l ------CaCO3 Total Hardness as 7 mg/l 300 ------CaCo3 8 Calcium as Ca mg/l 80.10 ------Magnesium as 9 mg/l 24.28 ------Mg. 10 Sodium Na mg/l ------11 Potassium mg/l ------12 Chloride as Cl mg/l 250 --- 600 --- 600 13 Sulphate as SO4 mg/l 400 --- 400 --- 1000 14 Phosphate mg/l ------

15 Nitrate as NO3 mg/l 20 --- 50 ------16 Fluorides as F mg/l 1.5 1.5 1.5 ------17 Cyanide mg/l 0.05 0.05 0.05 ------18 Arsenic mg/l 0.05 0.2 0.2 ------19 Cadmium mg/l 0.01 --- 0.01 ------20 Chromium, Total mg/l 0.05 0.05 0.05 ------21 Copper mg/l 1.5 --- 1.5 ------

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S.No Parameters Unit A B C D E 22 Lead mg/l 0.1 --- 0.1 ------23 Zinc mg/l 15 --- 15 ------24 Manganese mg/l 0.5 ------25 Selenium mg/l 0.01 --- 0.05 ------26 Mercury mg/l 0.001 ------27 Dissolved Oxygen mg/l 6 5 4 4 --- 28 COD mg/l ------29 BOD mg/l 2 3 3 ------

Class A – Drinking water without conventional treatment but after disinfection.

Class B –Water for outdoor bathing.

Class C – Drinking water with conventional treatment followed by disinfection.

Class D – Water for fish culture and wild life propagation.

Class E – Water for irrigation, industrial cooling and controlled waste disposal

3.10.3 Groundwater resources

The ground water development in all the blocks has exceeded the available recharge, thus all the blocks have been categorized as over exploited. Stage of ground water development, ranges from 127% (block-Madlauda) to 210% (block-Samalkha). Net annual replenishable ground water availability in the district has been assessed as 308.65 MCM. The total ground water draft for all uses in the district is 514.56 MCM, thus leaving shot-fall (over draft) of 205.91 M C M. Stage of ground water development in the Panipat district has been assessed to be 167%.Depth to water level during Pre Monsoon & Post Monsoon for Panipat District, is given in Figure 3-21.

Source:http://cgwb.gov.in/District_Profile/Haryana/Panipat.pdf

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Figure 3-21Depth to water level during Pre-Monsoon& Post Monsoon in Panipat District 3.10.3.1 Groundwater Quality Block-wise ground water resource potential of the district has been assessed by CGWB as per GEC-97 as on 31st March 2009. Groundwater is the principal source for domestic and drinking purposes in almost all villages near the study area. The quality of the groundwater received is influenced by pollution of soil and air, industrial and domestic waste disposal, organic components, pathogenic microorganisms, application of fertilizers and pesticides in agriculture, etc. Total Eight (08) ground water monitoring locations were identified for assessment in different villages around the project site based on the usage of sub surface water by the settlements/ villages in the study area. The groundwater results are compared with the desirable and permissible water quality standards as per IS 10500 (2012) for drinking water. Groundwater quality monitoring locations and results are given in Table 3-16 and Table 3-17. Map showing the groundwater monitoring locations are given in Figure 3- 22.

Table 3-16 Details of Groundwater Quality Monitoring Locations Location Distance in SI.No Location Direction Code ~Km 1 Near Refinery complex GW1 0.05 E 2 Razapur GW2 2.66 E 3 Barauli GW3 6.57 E 4 New Bahauli GW4 2.95 ESE 5 Panipat GW5 9.23 SE 6 Madlauda GW6 8.7 SSW 7 Dharamgarh GW7 3.76 WSW 8 Munak GW8 3.55 NNW

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Figure 3-22Map showing the groundwater monitoring locations

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Table 3-17Physico chemical analysis of Ground water samples from study area

li

Drinking water

u

Standard (IS a

arh

New New

Munak

Bara

Bahauli Panipat

earRefiner

Razapur Madlaud

SL 10500: 2012) Dharamg y Complex Parameters Unit N NO Permi Accep ssible table GW1 GW4 GW3 GW5 GW7 GW6 GW2 GW8 Limit Limit BLQ BLQ BLQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 1. Colour Hazen 15 5 (LOQ 1) (LOQ 1) (LOQ 1) Q 1) Q 1) Q 1) Q 1) Q 1) BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 2. Turbidity NTU 5 1 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) 3. pH - NR 6.5-8.5 7.58 7.75 7.83 8.01 7.48 7.35 7.63 7.53 Electrical µS/c 4. - - 1263 681 948 895 736 1038 598 1158 Conductivity m Total Dissolve 5. mg/l 2000 500 820 436 607 580 476 693 386 755 Solids Total BLQ(LOQ BLQ BLQ BLQ BLQ BLQ BLQ BLQ 6. Suspended - - 1) (LOQ 1) (LOQ 1) (LOQ 1) (LOQ 1) (LOQ 1) (LOQ 1) (LOQ 1) Solids Total 7. Alkalinity as mg/l 600 200 293 199 269 316 258 368 147 339 CaCO3 Total 8. Hardness as mg/l 600 200 470 296 377 378 333 434 220 363 CaCO3 9. Sodium as Na mg/l - - 61 18 34 12.35 9 17 26 43 Potassium as 10. mg/l - - 9.4 2.7 4.1 1.9 1.5 2.7 5.8 3.7 K 11. Calcium as Ca mg/l 200 75 80.16 58.24 71.25 63.12 61.3 85.72 46.09 68.14 12. Magnesium as mg/l 100 30 65.61 36.45 48.21 53.46 43.74 53.46 25.52 46.81

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li

Drinking water

u

Standard (IS a

arh

New New

Munak

Bara

Bahauli Panipat

earRefiner

Razapur Madlaud

SL 10500: 2012) Dharamg y Complex Parameters Unit N NO Permi Accep ssible table GW1 GW4 GW3 GW5 GW7 GW6 GW2 GW8 Limit Limit Mg 13. Chloride mg/l 1000 250 132.62 41.28 72.39 27.32 19.21 37.47 59.36 97.42 14. Sulphate SO4 mg/l 400 200 89.51 23.64 28.52 15.34 10.64 23.69 33.41 56.28 15. Nitrate as NO3 mg/l NR 45 5.4 2.31 6.1 7.7 4.3 8.3 21.23 9.7 Phosphate as BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 16. mg/l - - 0.04 PO4 Q 0.02) Q 0.02) Q 0.02) Q 0.02) Q 0.02) Q 0.02) Q 0.02) 17. Fluorides as F mg/l 1.5 1 0.28 0.23 0.34 0.98 0.17 0.24 0.86 0.27 BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 18. Cyanide mg/l NR 0.05 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 19. Arsenic as As mg/l 0.05 0.01 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) BQL(LOQ BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO 20. Boron as B mg/l 1.0 0.5 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Cadmium as BQL(LOQ BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO 21. mg/l NR 0.003 Cd 0.001) Q 0.001) Q 0.001) Q 0.001) Q 0.001) Q 0.001) Q 0.001) Q 0.001) Chromium as BQL(LOQ BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO BQL(LO 22. mg/l NR 0.05 Cr 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 23. Copper as Cu mg/l 1.5 0.05 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) 24. Total Iron mg/l NR 0.3 1.8 2.3 2.7 2.4 1.9 1.4 1.1 1.3 BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 25. Lead as Pb mg/l NR 0.01 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Manganese as BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 26. mg/l 0.3 0.1 0.081 Mn Q 0.05) Q 0.05) Q 0.05) Q 0.05) Q 0.05) Q 0.05) Q 0.05) 27. Mercury mg/l NR 0.001 BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO

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li

Drinking water

u

Standard (IS a

arh

New New

Munak

Bara

Bahauli Panipat

earRefiner

Razapur Madlaud

SL 10500: 2012) Dharamg y Complex Parameters Unit N NO Permi Accep ssible table GW1 GW4 GW3 GW5 GW7 GW6 GW2 GW8 Limit Limit 0.0005) Q Q 0.0005) Q Q Q Q Q 0.0005) 0.0005) 0.0005) 0.0005) 0.0005) 0.0005) BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 28. Nickel as Ni mg/l NR 0.02 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Q 0.01) Selenium as BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 29. mg/l NR 0.01 Se 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) Q 0.005) BLQ(LOQ BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO BLQ(LO 30. Zinc as Zn mg/l 15 5 0.254 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1) Q 0.1)

Note:BDL - Below Detection Limit; DL – Detection Limit; BLQ – Below Limit of Quantification; LOQ – Limit Of Quantification; NR – No Relaxation

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3.10.3.2 Results and Discussions

A summary of analytical results are presented below:

 The pH of the collected ground water sample ranges from 7.35 to 8.01.  The concentrations of fluoride in the collected ground water sample ranges from 0.17 to 0.98 mg/l.  Total Dissolved Solids (TDS) value of the collected ground water sample varies from 386 mg/l to 820 mg/l.  Total hardness of the collected ground water sample ranges from 220 mg/l to 470mg/l,  The Total alkalinity as calcium carbonate, Magnesium and Chloride are well within the permissible limits of IS 10500:2012.  Most of the heavy metals concentrations in the collected ground water samples are below detection limits.

3.11 Soil Quality

Soil quality monitoring locations & results are given in Table 3-18 and Table 3-19. Map showing the soil monitoring locations are given in Figure 3-23.

Table 3-18Soil & Sediment Quality Monitoring Locations SI.No Location Location Code Distance in ~Km Direction 1 Project Site S1 - - 2 Razapur S2 2.66 E 3 Barauli S3 6.57 E 4 New Bahauli S4 2.95 ESE 5 Panipat S5 9.23 SE 6 Madlauda S6 8.7 SSW 7 Dharamgarh S7 3.76 WSW 8 Munak S8 3.55 NNW

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Figure 3-23Map showing the soil monitoring location

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Table 3-19Physico Chemical parameters of soil samples from the study area

Project New Dharamgh Sl. Razapur Barauli Panipat Madlauda Munak Parameters Units Site Bahauli ar No S1 S2 S3 S4 S5 S6 S7 S8 1 Soil Texture - Clay Clay Clay Clay Clay Clay Clay Clay 2 Sand % 19.55 16.93 15.60 15.5 9.76 18.86 16.8 20.6 3 Silt % 22.61 20.41 19.48 16.8 20.08 20.54 17.9 14.5 4 Clay % 57.84 62.66 64.92 67.7 70.16 60.60 65.3 64.9 5 pH 7.21 7.66 7.74 7.8 7.88 7.58 7.96 7.19

Electrical 6 μmho/cm 1447 683.0 4410 280 538 700 299 2380 conductivity 7 Infiltration Rate cm/hr 42.80 40.4 36.5 48.0 41.05 45.40 43.0 40.1 8 Bulk Density gm/cc 1.42 1.17 1.19 1.23 1.16 1.34 1.30 1.24 Cation Exchange meq/100 9 28.55 27.18 30.14 31.2 32.55 28.15 30.06 27.4 Capacity gm 10 Moisture content % 0.73 3.49 7.51 3.24 9.46 0.947 6.56 1.89 Water Holding 11 % 44.60 39.31 40.89 30.1 42.60 43.36 29.7 28.6 Capacity 12 Organic Carbon % 0.97 1.30 1.06 1.16 1.29 1.11 1.2 0.98 13 Organic matter % 1.67 2.24 1.82 2.0 2.22 1.91 2.06 1.69 14 Nitrogen as N mg/kg 890.3 783.7 805.3 860.5 733.4 785.8 953.0 890.8 15 Phosphorus mg/kg 13.61 3.51 15.7 7.8 7.70 3.83 2.2 3.5 16 Potassium mg/kg 49.60 79.91 97.60 9.96 89.58 21.90 19.89 9.92 17 Calcium mg/kg 1706.29 759.12 957.65 119.53 318.54 477.95 238.56 2937.44 18 Magnesium mg/kg 214.28 239.73 407.0 239.06 167.43 119.49 119.28 452.52 BDL(D BDL(DL BDL(DL BDL(DL BDL(DL BDL(DL BDL(DL 19 Boron mg/kg BDL(DL 0.1) L 0.1) 0.1) 0.1) 0.1) 0.1) 0.1) 0.1) BLQ(L BLQ(LO BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LOQ BLQ(LOQ 20 Cadmium mg/kg OQ 0.1) Q 0.1) 0.1) 0.1) 0.1) 0.1) 0.1) 0.1) 21 Copper mg/kg 5.99 21.12 28.51 11.24 30.25 9.44 16.47 19.53

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Project New Dharamgh Sl. Razapur Barauli Panipat Madlauda Munak Parameters Units Site Bahauli ar No S1 S2 S3 S4 S5 S6 S7 S8 22 Iron mg/kg 1985.4 1483.0 4983.4 3162.0 6554.8 1731.6 9685.5 7315.2 23 Manganese mg/kg 99.06 235.5 383.3 168.47 451.76 141.50 225.97 350.92 24 Zinc mg/kg 65.02 126.22 228.6 79.23 188.43 93.45 160.96 88.44 Note: BDL - Below Detection Limit; DL – Detection Limit; BLQ – Below Limit of Quantification; LOQ – Limit Of Quantification

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3.11.1 Results and Discussions

Summary of analytical results

 The pH of the soil samples ranged from 7.19 to 7.96, indicating the soils are neutral to moderately alkaline in nature.  Conductivity of the soil samples ranged from 280 to 4410µmho/cm.  Nitrogen content ranged from 733.4 mg/kg to 953 mg/kg.  Phosphorous ranged from 2.2 mg/kg to 15.7 mg/kg.  Potassium content ranges from 9.92 mg/kg to 97.60mg/kg.

3.12 Biological Environment Biological environment is a good bio-indicator of changing environmental quality. The secondary data source of 15 km radius area around the project site was considered for the study on biodiversity. Both terrestrial and aquatic ecological analysis was carried out through secondary data. Assessment of flora and fauna was undertaken in the study area through literature review /desk research was carried out to determine the existing conditions within the study area and to identify habitats and species of potential importance that may be affected by the Project. The following parameters were primarily considered in the study.  Collection of secondary data from literature about the flora and faunal diversity.  Identification of rare endangered plants and animal species (if any).

Flora A total of 173 flowering plants were recorded from the secondary source belonging to 58 families. Table 3-20List of Flora recorded from Secondary source

S.No Family and species Habit Common IUCN Name/Vernacular Name

1 ARACEAE 1 Lemna minor Herb Duckweed LC 2 Spirodela polyrrhiza Herb Duckweed LC 2 HYDROCHARITACEAE 3 Hydrilla verticillata Herb Water Thyme LC 3 COMMELINACEAE 4 Commelina benghalensis Herb Kankawa LC 5 Commelina forskaolli Herb Dayflower LC 6 Commelina paludosa Herb Swamp Dayflower NA 7 Murdania nudiflora Herb Naked-stem Dewflower NA

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4 PONTEDERIACEAE 8 Eichhornia crassipes Herb Water hyacinth LC 9 Monochoria hastata Herb Arrow Leaf Pondweed LC 5 CANNACEAE 10 Canna indica Herb Sarvajjaya LC 6 TYPHACEAE 11 Typha angustata Herb − LC 7 CYPERACEAE 12 Cyperus alopecuroides Herb Nut grass LC 13 Cyperus compactus Herb − LC 14 Cyperus difformis Herb − LC 15 Cyperus iria Herb Iria flatsedge LC 16 Cyperus rotundus Herb − LC 8 POACEAE 17 Apluda mutica Grass Bhongla LC 18 Arundo donax Grass Wild cane LC 19 Cenchrus ciliaris Grass − 20 Coix lacryma-jobi Grass Samkru LC 21 Cymbopogon martini Grass Gandhabel LC 22 Cynodon dactylon Grass Dobri LC 23 Dactyloctenium aegyptium Grass Makra LC 24 Dichanthium annulatum Grass Sheda Grass LC 25 Digitaria ciliaris Grass Wild Crabgrass LC 26 Eleusine indica Grass Malankuri LC 9 PAPAVERACEAE 27 Argemone mexicana Herb bharbhand LC 28 Argemone ochroleuca Herb − 29 Fumaria indica Herb Papara NA 10 MENISPERMACEAE 30 Cissampelos pareira Climber Akanadi LC 31 Cocculus hirsutus Climber farid buti LC 32 Tinospora cordifolia Climber chinnaruha LC 11 RANUNCULACEAE 33 Ranunculus sceleratus Herb Shim LC 12 NELUMBONACEAE 34 Nelumbo nucifera Herb Kamal LC 13 VITACEAE 35 Cayratia trifolia Climber amalbel LC 14 ZYGOPHYLLACEAE 36 Balanites aegyptiaca Tree hingot LC 37 Tribulus terrestris Herb − NA 15 FABACEAE 38 Abrus precatorius Climber chirmithi LC 39 Acacia nilotica Tree Babul LC

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40 Acacia farnesiana Tree durgandh khair LC 41 Acacia leucophloea Tree reonja LC 42 Aeschynomene indica Herb Didhen LC 43 Albizzia lebbeck Tree Saras LC 44 Albizzia procera Tree Safed siris LC 45 Alhagi pseudalhagi Shrub Javasa LC 46 Alysicarpus bupleurifolius Herb Chauli LC 47 Bauhinia purpurea Tree Kaniar LC 48 Butea monosperma Tree dhak LC 49 Caesalpinia bonduc Shrub gajga LC 50 Cassia occidentalis Herb Kasunda LC 51 Cassia tora Herb Panwar LC 52 Crotalaria medicaginea Herb 53 Dalbergia sissoo Tree Shisham LC 54 Desmodium gangeticum Herb − LC 55 Desmodium triflorum Herb − LC 56 Erythrina suberosa Tree Dhaul dhak LC 57 Indigofera linifolia Herb bhangra LC 58 Indigofera linnaei Ali Herb pandarphali LC 59 Lathyrus aphaca Herb − LC 60 leucocephala Tree − LC 61 Medicago lupulina Herb − LC 62 Medicago polymorpha Herb − LC 63 Melilotus alba Herb − LC 64 Melilotus indica Herb − LC 65 Millettia peguensis Tree − LC 66 Mimosa hamata Shrub − LC 67 Mimosa pudica Herb − LC 68 Parkinsonia aculeata Shrub − LC 69 Pithecellobium dulce Tree Jangal Jalebi LC 70 Pongamia pinnata Tree Dithouri, Karuaini LC 71 Prosopis cineraria Tree Jand LC 72 Prosopis juliflora Tree − LC 73 Rhynchosia minima Climber − LC 74 Rhynchosia rothii Benth Climber Silky Snoutbean LC 75 Sesbania bispinosa Shrub Dhaincha LC 76 Sesbania sesban Shrub − LC 77 Tamarindus indica Tree Imli LC 78 Tephrosia purpurea herb Sarphonk LC 79 Teramnus labialis Climber kalyan LC 80 Vicia hirsuta Herb Jhunjhuni ankari, LC 81 Vicia sativa Herb Akra, Akta, 16 ROSACEAE − 82 Potentilla supina Herb Spreading Cinquefoil LC

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83 RHAMNACEAE − 84 Zizyphus jujuba Tree Bada ber LC 85 Zizyphus nummularia Tree Jhar BerI LC 86 Zizyphu oenoplia Shrub Makkay, LC 17 ULMACEAE 87 Holoptelea integrifolia Tree chilbil LC 18 CANNABACEAE 88 Cannabis sativa Shrub bhang LC 19 PUTRANJIVACEAE 89 Putranjiva roxburghii Tree Putijia 20 MORACEAE 90 Ficus benghalensis Tree Barh LC 91 Ficus palmata Forssk Tree Anjiri, LC 92 Ficus racemosa Tree Goolar LC 93 Ficus religiosa Tree aswattha LC 94 Ficus virens Aiton Tree Pilkhan LC 95 Morus alba Tree Shahtoot LC 96 Morus macroura Tree Shahtoot LC 97 Streblus asper Tree Daheya LC 21 URTICACEAE 98 Pouzolzia pentandra Herb Narrow-Leaf Pouzolz's Bush LC 22 CASUARINACEAE 99 Casuarina equisetifolia Tree Junglisaru LC 23 CUCURBITACEAE 100 Coccinia indica Climber Kundru LC 101 Cucumis maderaspatanus Climber bilari LC 102 Trichosanthes cucumerina Climber Chachinda LC 24 CELASTRACEAE 103 Celastrus paniculatus Climber malkangani 25 OXALIDACEAE 104 Oxalis corniculata Herb Amrul LC 105 Oxalis debilis Kunth Herb Large-Flowered Pink Sorrel LC 106 Oxalis latifolia Kunth Herb Khatmitthi LC 26 EUPHORBIACEAE 107 Acalypha indica Herb − 108 Croton bonplandianum Herb Kala Bhangra NA 109 Euphorbia cyathophora Herb Titli phool LC 110 Euphorbia helioscopia Herb Hirruseeah LC 111 Euphorbia heterophylla Herb Wild Poinsettia LC 112 Euphorbia hirta Herb Bara dudhi LC 27 PHYLLANTHACEAE 113 Flueggea leucopyrus Shrub Shinar, Ainta LC 114 Phyllanthus amarus Herb Bhui aonla LC 115 Phyllanthus fraternus Herb bhuinanvalah LC

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116 Phyllanthus reticulatus Shrub Kale madhu ka per LC 28 PASSIFLORACEAE 117 Passiflora foetida Climber Jhumka lata LC 29 SALICACEAE 118 Casearia graveolens Tree Safed-Karai, Chilla LC 119 Flacourtia indica Tree bilangada LC 30 COMBRETACEAE 120 Terminalia arjuna Tree Arjun LC 121 Terminalia bellerica Tree bahuvirya LC 122 Terminalia chebula Tree Harra LC 31 LYTHRACEAE 123 Ammannia baccifera Herb Aginbuti LC 124 Lawsonia inermis Shrub Mehendi LC 32 ONAGRACEAE 125 Ludwigia perennis Herb Perennial Water Primrose LC 126 Ludwigia octovalvis Herb Ban long 33 MYRTACEAE 127 Eucalyptus camaldulensis Tree Coolabah LC 128 Syzygium cumini Tree Jamun 34 ANACARDIACEAE 129 Spondias pinnata Tree ambara LC 35 SAPINDACEAE 130 Dodonaea viscosa Shrub Sanatta LC 36 RUTACEAE 131 Aegle marmelos Tree Bel LC 132 Limonia acidissima Tree Kaith LC 133 Murraya koenigii Shrub Kari patta 37 SIMAROUBACEAE 134 Ailanthus excelsa Tree Mahanimb LC 38 MELIACEAE 135 Azadirachta indica Tree Neem LC 136 Melia azedarach Tree Bakain LC 137 Toona ciliata Tree Toon LC 39 MALVACEAE 138 Abelmoschus moschatus Herb Pink Swamp Mallow LC 139 Abutilon indicum Shrub Kanghi LC 140 Bombax ceiba Tree Shalmali LC 141 Corchorus aestuans Herb Chonch LC 142 Corchorus capsularis Herb patta shaak LC 143 Corchorus trilocularis Herb Horn-Fruited Jute LC 40 MORINGACEAE 144 Moringa oleifera Tree Senjana LC 41 SALVADORACEAE 145 Salvadora persica Tree jaal NA

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42 CAPPARACEAE 146 Capparis decidua Shrub kair LC 147 Capparis sepiaria Shrub kairiya LC 148 Capparis zeylanica Shrub Aradanda LC 149 Cleome gynandra Herb jakhiya LC 150 Cleome viscosa Herb Bagra LC 43 BRASSICACEAE 151 Cardamine flexuosa Herb Wood Bitter Cress LC 152 Coronopus didymus Herb Pitpapra LC 153 Lepidium sativum Herb chansur LC 154 Sisymbrium irio Herb khubkaln, asalio LC 155 Rorippa indica Herb Chamsuru LC 44 TAMARICACEAE 156 Tamarix aphylla Tree Farash LC 157 Tamarix dioica Roxb Tree Farash LC 45 POLYGONACEAE 158 Polygonum barbatum Herb Bearded Knotweed LC 159 Polygonum glabrum Willd Herb Denseflower Knotweed LC 160 Polygonum plebeium Herb chimati saag LC 161 Rumex dentatus Herb Ambavati, Amrule, LC 47 AMARANTHACEAE 162 Achyranthes aspera Herb aghara LC 163 Alternanthera ficoidea Herb Sanguinarea LC 164 Alternanthera paronychioides Herb Smooth Chaff Flower NA 165 Alternanthera pungens Herb Khaki Weed LC 166 Alternanthera sessilis Herb Stalkless Joyweed LC 55 PRIMULACEAE 167 Anagallis arvensis Herb Scarlet Pimpernel LC 56 RUBIACEAE 168 Oldenlandia corymbosa Herb red chickweed LC 57 GENTIANACEAE 169 Centaurium pulchellum Herb barik chirayata LC 58 APOCYANACEAE 170 Calotropis gigantea Shrub Safed aak LC 171 Calotropis procera Shrub Aak LC 172 Pentatropis spiralis Climber Aakari Bel LC 173 Telosma cordata Climber Fragrant Telosma LC

Note: LC- Least Concern, NT- near Threatened, EN- Endangered, NA-Not yet assessed, DD - Data Deficient, VU-Vulnerable, IUCN- International Union for Conservation of Nature.

Summary: 1. A total 173 species under 58 families observed based on secondary source. 2. No endangered species are found in the study area.

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Birds A total of 101 species of birds belonging to 82 genera, 44 families, and 15 orders were documented from the secondary data for the study area. Table 3-21List of bird species recorded from Secondary source S.No Order/family /common name Scientific name Red List status

Order: GALLIFORMES Family: Phasianidae 1 Indian Peafowl Pavo cristatus LC 2 Black Francolin Francolinus LC francolinus 3 Grey Francolin Francolinus LC pondicerianus Order: PHOENICOPTERIFOMES Family: Podicipedidae 4 Little Grebe Tachybaptus ruficollis LC Order: COLUMBIFORMES Family: Columbidae 5 Rock Pigeon Columba livia LC 6 Eurasion Collared Dove Streptopelia decaocto LC 7 Spotted Dove Spilopelia chinensis LC 8 Laughing Dove Streptopelia LC senegalensis 9 Yellow-legged Green Pigeon Treron phoenicopterus LC Order: CAPRIMULGIFORMES Family: Apodidae 10 Indian House Swift Apus affinis LC Order: CUCULIFORMES Family: Cuculidae 11 Greater Coucal Centropus sinensis LC 12 Pied Cuckoo Clamator jacobinus LC 13 Asian Koel Eudynamys LC scolopaceus 14 Drongo Cuckoo Surniculus lugubris LC 15 Common Hawk Cuckoo Hierococcyx varius LC Order: GRUIFORMES Family: Rallidae

16 White-breasted Waterhen Amaurornis LC phoenicurus 17 Purple Swamphen Porphyrio porphyrio LC Order: PELECANIFORMES Family: Ciconiidae

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18 Painted Stork Mycteria leucocephala NT 19 Asian Openbill Anastomus oscitans LC 20 Black-necked Stork Ephippiorhynchus NT asiaticus Family: Ardeidae 21 Black-crowned Night Heron Nycticorax nycticorax LC 22 Indian Pond Heron Ardeola grayii LC 23 Cattle Egret Bubulcus ibis LC 24 Grey Heron Ardea cinerea LC 25 Purple Heron Ardea purpurea LC 26 Great Egret Ardea alba LC 27 Intermediate Egret Ardea intermedia LC 28 Little Egret Egretta garzetta LC Family: Threskiornithidae 29 Black-headed Ibis Threskiornis NT melanocephalus 30 Indian Black Ibis Pseudibis papillosa LC 31 Glossy Ibis Plegadis falcinellus LC Family: Phalacrocoracidae 32 Little Cormorant Microcarbo niger LC Order: CHARADRIIFORMES Family: Recurvirostridae 33 Black-winged Stilt Himantopus LC himantopus Family: Charadriidae 34 Little Ringed Plover Charadrius dubius LC 35 Red-wattled Lapwing Vanellus indicus LC Family: Jacanidae 36 Pheasant-tailed Jacana Hydrophasianus LC chirurgus Family: Scolopacidae 37 Common Sandpiper Actitis hypoleucos LC 38 Common Redshank Tringa totanus LC Order: ACCIPITRIFORMES Family: Accipitridae 39 Black-winged Kite Elanus caeruleus LC 40 Shikra Accipiter badius LC 41 Brahminy Kite Haliastur Indus LC 42 Black Kite Milvus migrans LC Order: STRIGIFORMES Family: Strigidae 43 Spotted Owlet Athene brama LC Order: BUCEROTIFORMES Family: Bucerotidae

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44 Indian Grey Hornbill Ocyceros birostris LC Family: Upupidae 45 Common Hoopoe Upupa epops LC Order: PICIFORMES Family: Picidae 46 Lesser Golden-Backed Woodpecker Dinopium benghalense LC Family: Ramphastidae 47 Brown-headed Barbet Psilopogon zeylanicus LC 48 Coppersmith Barbet Psilopogon LC haemacephalus Order: CORACIIFORMES Family: Meropidae 49 Green Bee-eater Merops orientalis LC Family: Coraciidae 50 Indian Roller Coracias benghalensis LC Family: Alcedinidae 51 White-throated Kingfisher Halcyon smyrnensis LC Order: PSITTACIFORMES Family: Psittaculidae 52 Alexandrine Parakeet Psittacula eupatria NT 53 Rose-ringed Parakeet Psittacula krameri LC Order: PASSERIFORMES Family: Campephagidae 54 Long-tailed Minivet Pericrocotus ethologus LC Family: Oriolidae 55 Eurasian Golden Oriole Oriolus oriolus LC Family: Dicruridae 56 Black Drongo Dicrurus macrocercus LC Family: Laniidae 57 Bay-backed shrike Lanius vittatus LC 58 Long-tailed Shrike Lanius schach LC Family: Corvidae 59 RufousTreepie Dendrocitta LC vagabunda 60 House crow Corvus splendens LC 61 Large-billed Crow Corvus macrorhynchos LC Family: Nectariniidae 62 Purple Sunbird Cinnyris asiaticus LC Family: Ploceidae 63 Black-breasted Weaver Ploceus benghalensis LC 64 Streaked Weaver Ploceus manyar LC 65 Baya Weaver Ploceus philippinus LC Family: Estrildidae

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66 Indian Silverbill Euodice malabarica LC 67 Scaly-breasted Munia Lonchura punctulata LC Family: Passeridae 68 House Sparrow Passer domesticus LC Family: Motacillidae 69 Paddyfield Pipit Anthus rufulus LC 70 Western Yellow Wagtail Motacilla flava LC 71 Grey Wagtail Motacilla cinerea LC 72 Citrine Wagtail Motacilla citreola LC 73 White-browed Wagtail Motacilla LC maderaspatensis 74 White Wagtail Motacilla alba LC Family: Alaudidae 75 Crested Lark Galerida cristata LC Family: Cisticolidae 76 ZittingCisticola Cisticola juncidis LC 77 Ashy Prinia Prinia socialis LC 78 Plain Prinia Prinia inornata LC 79 Common Tailorbird Orthotomus sutorius LC Family: Acrocephalidae 80 Paddyfield Warbler Acrocephalus agricola LC Family: Hirundinidae 81 Red-rumped Swallow Cecropis daurica LC 82 Wire-tailed Swallow Hirundo smithii LC 83 Barn Swallow Hirundo rustica LC 84 Plain Martin Riparia paludicola LC Family: Pycnonotidae 85 Red-vented Bulbul Pycnonotus cafer LC Family: Sylviidae 86 Lesser Whitethroat Sylvia curruca LC Family: Zosteropidae 87 Oriental White-eye Zosterops palpebrosus LC Family: Leiothrichidae 88 Large Grey Babbler Argya malcolmi LC 89 Common Babbler Argya caudata LC 90 Jungle Babbler Turdoides striata LC Family: Sturnidae 91 Asian Pied Starling Gracupica contra LC 92 Brahminy Starling Sturnia pagodarum LC 93 Common Myna Acridotheres tristis LC 94 Bank Myna Acridotheres LC ginginianus

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Family: Muscicapidae 95 Indian Robin Saxicoloides fulicatus LC 96 Oriental Magpie Robin Copsychus saularis LC 97 Verditer Flycatcher Eumyias thalassinus LC 98 Bluethroat Cyanecula svecica LC 99 Black Redstart Phoenicurus ochruros LC 100 Pied Bushchat Saxicola caprata LC 101 Brown Rock Chat Oenanthe fusca LC

Note:LC- Least Concern, NT- near Threatened, EN- Endangered, NA-Not yet assessed, DD - Data Deficient, VU-Vulnerable, IUCN- International Union for Conservation of Nature.

Summary: 1. A total of 101 species of birds belonging to 82 genera, 44 families, and 15 orders were documented from the secondary data for the study area. 2. No Eco-Sensitive Areas or Wildlife Sanctuaries exists inside the 15km radial distance. 3. No endangered species are found in the study area. 4. Birds such as Painted Stork (Mycteria leucocephala) , Black-necked Stork(Ephippiorhynchus asiaticus), Black-headed Ibis (Threskiornis melanocephalu)s and Alexandrine Parakeet (Psittacula eupatria) comes under near threatened species.

REFERENCES:  Kumar, P. & S. Sahu (2020). Composition, diversity and foraging guilds of avifauna in agricultural landscapes In Panipat, Haryana, India. Journal of Threat- ened Taxa 12(1): 15140–15153. https://doi.org/10.11609/jott.5267.12.1.15140-15153  Dhadse S. , J. P. Kotangale P. R. Chaudhari S. R. Wate, Diversity of birds at Panipat refinery, Haryana (India) Environ Monit Assess (2009) 158:1–8.  Gupta, R.C., Kaushik, T. K. and Kumar, S. (2010a). Evaluation of the extent of wetland birds in district , Haryana, India. Journal of Applied and Natural Science, 2(1):77-84.  Gupta, R.C., Kaushik, T. K. and Kumar, S. (2010b). An account concerning arrival and departure time of few selected winter migratory birds in Haryana rural ponds. Environment Conservation Journal, 11(1&2):1-9, 2010.  Kalsi, R.S. (1998). Birds of Kalesar Wild Life Sanctuary, Haryana, India. Forktail, 13: 29-32.  Kumar, A., Sati, J.P. and Tak, P.C. (2003). Checklist of Indian Water Birds. Buceros, 8(1):1-30.

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Table 3-22 Systematic list of butterfly species

S\N Family Scientific Name Common Name IUCN Status 1 Danaus chrysippus Plain Tiger LC 2 Danaus genutia Common Tiger LC

3 Euploea core Common Crow LC 4 Nymphalidae Phalanta phalantha Common Leopard LC 5 Neptis hylas Common Sailer LC 6 Vanessa cynthia Painted Lady LC 7 Acraea violae Tawny Coster LC 8 Hypolimnas misippus Danaid Egg fly LC 9 Tirumala limniace Blue Tiger LC 10 Eurema hecabe Common Grass Yellow LC 11 Eurema andersoni One Spot Grass Yellow LC Pieridae 12 Catopsilia pomona Common Emigrant LC 13 Anaphaeis aurota Pioneer LC 14 Delias eucharis Common Jezebel LC 15 Appias albino Common Albatross LC 16 Graphium doson Common Blue Jay LC 17 Papilionidae Papilio polytes Common Mormon LC 18 Papilio demoleus Lime Butterfly LC 19 Chilades Plains Cupid LC 20 Lycaenidae Zizeeria karsandra Dark Grass Blue LC 21 Pseudozizeeria maha Pale Grass Blue LC Note:LC- Least Concern, NT- near Threatened, EN- Endangered, NA-Not yet assessed, DD - Data Deficient, VU-Vulnerable, IUCN- International Union for Conservation of Nature.

Summary No endangered species are found in the study area. REFERENCE  Nasim Ahmad Ansari, Jeet Ram, Asghar Nawab., Structure and composition of Butterfly (Lepidoptera: Rhopalocera) fauna in Surajpur wetland, National Capital Region, India Asian Journal of Conservation Biology, July 2015. Vol. 4 No. 1, pp. 43-53

MAMMALS The following are the list of mammals found:

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Table 3-21 List of Mammals recorded from Secondary source S.No Species name Common Name IUCN Status 1 Hemiecbinus boritus Long-eared Hedgehog LC 2 Suncus murinus House Shrew LC 3 Hesperoptenos tickelli Tickell's Bat LC 4 Scotophilus heathi Greater Yellow Bat LC 5 Macaca mulatta Bandar LC 6 Herpestes edwardsi Indian Grey Mongoose LC 7 Felis chaus Jungle cat LC 8 Lepus nigricollis Indian Hare LC 9 Funambulus pennanti Northern Palm Squirrel LC 10 Hystrix indica Indian Crested LC Porcupine 11 Rattus rattas House Rat LC 12 Mus musculus House Mouse LC 13 Bandicota bengalensis Lesser Bandicoot Rat LC 14 Tatera indica Indian Gerbi LC 15 Meriones hurrianae Indian Desert Gerbil LC 16 Varanus varius Monitor lizards LC Note:LC- Least Concern, NT- near Threatened, EN- Endangered, NA-Not yet assessed, DD - Data Deficient, VU-Vulnerable, IUCN- International Union for Conservation of Nature.

Summary A total of 16 species observed based on secondary source. No endangered species are found in the study area. REFERENCES Mammals  Blanford, W. T. 1880. The Fauna of British India including Ceylon and Burma, Mammalia, pp: 1-617. Taylor & Francis, London.  Ohir, V. P., Kumar, S. and Bajaj, B. R. (Eds) 1976. Gazetteer of India, Haryana District Gazetteers-Karnal. Cbandigarb: 1-688.  Ellerman, J. R. and Morrison-Scott, T. C. S. 1951. Checklist of Palaeartic and Indian Mammals 1758 to 1946: 1-810. British Museum (Natural-History), London.  Prero, K., Kumar, Sand Bajaj, B. R. (Eds) 1970. Gazetteer of India, Haryana District Gazetteers-lind. : 1-312.  N. K. SINHA MAMMALS OF HARYANA (1992) Rec.zoo Surv. India, 91 (3-4) : 399-416. 3.13 Socio Economic profile

Panipat district having a population of 1,205,437 consists of 646,857 male populations and 558,580 female populations.

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Source: http://censusindia.gov.in/2011census/dchb/DCHB_A/06/0607_PART_A_DCHB_PANIPAT.p df

3.13.1 Socio Economic Aspects A socio-economic study was undertaken in assessing aspects which are dealing with social and cultural conditions, and economic status in the study area. The study provides information such as demographic structure, population dynamics, infrastructure resources, and the status of human health and economic attributes like employment, per-capita income, agriculture, trade, and industrial development in the study area. The study of these characteristic helps in identification, prediction and evaluation of impacts on socio-economic and parameters of human interest due to proposed project developments. The parameters are:  Demographic structure  Infrastructure Facility  Economic Status  Health status  Cultural attributes  Awareness and opinion of people about the project and Industries in the area. The following Table 3-22 provides the certain important social indicators of Panipat district. Table 3-22Social Indicators S.No Social Indicators Panipat District 1 Decadal growth rate % 24.6 2 Urban population % 46.0 3 Sex ratio 864 4 0-6 age group % 14.07 5 Population density (Persons per square ) 951 6 Scheduled caste population % 17.1 7 Scheduled tribe population % 0 8 Literacy rate % 75.9 9 Work Participation rate % 34.2 10 Main Workers % 28.12 11 Marginal Workers % 6.08 12 Cultivators % 17.5 13 Agricultural labourers % 15.1 14 Workers in household industries % 3.8 15 Other workers % 63.5

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Source:http://censusindia.gov.in/2011census/dchb/DCHB_A/06/0607_PART_A_DCHB_PAN IPAT.pdf

3.13.1.1 Population and Household Size Panipatdistrict having a population of 1,205,437 consists of 646,857 male populations and 558,580 female populations.

Source: http://censusindia.gov.in/2011census/dchb/DCHB_A/06/0607_PART_A_DCHB_PANIPAT.p df

3.13.1.2 Sex Ratio As per 2011 Census there are 864 females for every 1,000 males in Panipat district. The sex ratio of 0-6 age group is837 for district. Source: http://censusindia.gov.in/2011census/dchb/DCHB_A/06/0607_PART_A_DCHB_PANIPAT.p df

3.13.1.3 Scheduled Caste (SC) Population of the Scheduled Castes has been reported as 206,213 persons in the district out of which 130,212 are in rural and 76,001 in urban. Source: http://censusindia.gov.in/2011census/dchb/DCHB_A/06/0607_PART_A_DCHB_PANIPAT.p df

3.13.1.4 Education & Literacy The study of the education and literacy profile in the region is relevant in order to have an understanding whether the proposed project can utilize skilled human resources available within the area. According to 2011 census data, the literacy rate in the Panipat district is 75.9%. The literacy rate has been the major determinant of the rise or fall of the other indicators. The accessibility of Primary and Upper Primary education has increased the literacy rate as well as reducing the dropout rate Table 3-23. Show the details of education infrastructures in Panipat District. Table 3-23Education Infrastructures in Panipat district Total schools Rural Schools Type of school Government Private Government Private Primary 244 37 216 19

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Primary + Upper Primary 0 106 0 45 P + UP+ Secondary + Higher Secondary 1 115 0 82 UP only 59 0 57 0 UP + Secondary + Higher Secondary 89 6 83 0 P + UP + Secondary 0 76 0 55 UP + Secondary 31 1 29 1 (Source: District Information Systems on Education (DISE report card 2016-17))

3.13.1.5 Health Facilities Primary Health Centers (PHCs) and Sub-centers (SCs) are providing the preventive, curative and rehabilitative health care services to the rural people. The district has good number of public health systems accessible and affordable apart from the private health facilities. The Health Facilities given in Panipat district is given in Table 3-24. Table 3-24Socio Economic analysis: Health care Name Type Facilities As on 26thDec 2019 of the of Total Facility Active Facilities Distri Facili Total Publ Priva Urb Rur Total Publ Priva Urb Rur ct ty [(A+ ic te [B] an al [(A+ ic te [B] an al B) or [A] [C] [D] B) or [A] [C] [D] (C+D (C+D )] )] Panipa SC 104 104 0 13 91 90 90 0 0 90 t PHC 33 33 0 11 22 23 23 0 7 16 CHC 7 6 1 3 4 7 6 1 3 4 SDH 0 0 0 0 0 0 0 0 0 0 DH 1 1 0 0 1 1 1 0 0 1 Total 145 144 1 27 118 121 120 1 10 111 (Note: SC – Sub Center; PHC – Primary Health Center; CHC – Community Health Center; SDH – Sub District Hospital; DH – District Hospital) (Source: National Health Mission, as on December26, 2019)

3.13.1.6 Economic Activity & Livelihood Pattern In Panipat district, as per the Census 2011, there were a total of 412,318workers, comprising 72,120cultivators, 62,358agricultural labourers, 15,824house hold Industry workers and2,62,016 other workers. Source: http://censusindia.gov.in/2011census/dchb/0607_PART_B_DCHB_PANIPAT.pdf

3.13.2 Social Economic Profile of the study area The villages and towns covering 10Km radius from the boundary of the project site are taken for the study. Table 3-25 shows the list of locations which comes under the study area. Table 3-26 shows the socio-economic indicators within the study area

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Table 3-25List of villages in the study area

Sl. Town/Vill Sl. Town/Vill Name Name No age Code No age Code Panipat District - Madlauda CD Block 36 800385 Panipat (M Cl + OG) 1 059447 Baholi (12) 37 059497 Kabri (18) (CT) 2 059445 Bal Jattan (11) 38 059496 Kachrauli (1) (CT) 3 059431 Bhalsi (45) PanipatTarafAnsar 39 059500 4 059421 Dharamgarh (1) (CT) 5 059444 Khandra (10) Sikanderpur (19) 40 059498 6 059439 Khukhrana (24) (CT) 7 059430 Madlauda (7) Karnal District - Assandh CD Block MahayudinpurThiran 41 059339 Balla (30) 8 059443 a (9) 42 059341 Goli (32) 9 059441 Nauhra (20) 43 059340 MorMajra (31) 10 059424 Qawi (3) Karnal District - Ghraunda CD Block 11 059420 RairKalan (29) 44 059415 AlipurKhalsa (36) 12 059423 Shadipur (8) 45 059361 Anchla (56) 13 059422 Sherah (2) 46 059370 Badshahpur (20) 14 059440 Shohdapur (25) 47 059360 Balran Gran (70) 15 059446 Sithana (14) 48 059375 Begampur (24) 16 059438 Sutana (23) 49 059367 Gagsina (16) 17 059442 Untiliya (44) 50 059378 Garhi Multan (26) 18 059432 Waisari (43) 51 059376 Gudha (23) 19 059499 AsanKhurd (CT) 52 059416 Har Singh Pura (37) Panipat District - Panipat CD Block 53 059414 Kaimla (25) 20 059450 Ali Asgharpur (32) 54 059365 Kapron (27) 21 059470 AsanKalan (21) 55 059362 KheriMunak (71) 22 059454 Babarpur (34) 56 059372 KhoraKheri(18) 23 059452 Badauli (33) 57 059377 Kohand (30) 24 059448 Dadlana (25) 58 059364 Kutana (26) 25 059469 Faridpur (17) 59 059373 Malakpur (28) 26 059451 Ganjbar (31) 60 059363 Munak (28) 27 059472 Jatol (27) PabanaHassanpur 61 059359 28 059455 Mahmadpur (15) (72) 29 059457 Nizampur (3) 62 059369 Phurlak (21) 30 059456 Ratipur (16) 63 059371 Raipur Jattan (19) 31 059453 Razapur (13) 64 059366 Shah Jahanpur (17) 32 059468 Sarai Bachhra (4) 65 059374 Sheikhopura (22) 33 059449 Sarai Kohand (29) 66 800384 Gharaunda (MC) 34 059458 SimlaMolana (2) 35 059471 Sondhapur (26)

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Table 3-26Summary of Socio-economic indicators within the study area S.No Particulars Study area Unit 1 Number of villages in the Study Area 59 Nos. 2 Number of Towns in the Study Area 7 Nos. 3 Total Households 124375 Nos. 4 Total Population 624417 Nos. 5 Children Population (<6 Years Old) 47188 Nos. 6 SC Population 108599 Nos. 7 ST Population 0 Nos. 8 Total Working Population 210197 Nos. 9 Main Workers 180839 Nos. 10 Marginal Workers 29358 Nos. 11 Cultivators 22601 Nos. 12 Agricultural labours 25826 Nos. 13 Household Industries 9144 Nos. 14 Other Workers 152626 Nos. 15 Literates 425334 Nos. (Source: Census 2011)

3.13.2.1 Employment and Livelihood within study area Majority of population in the study area comes under other working categories.As agriculture cannot be a main sustenance for most of farmers, they have dual professions. Farming is mostly seasonal, they involve in other livelihood activities like business, non-agriculture labour, agriculture labour and other service sectors. Fragmentation of landholding leads to adopt to have additional occupation. The Summary of Employment and Livelihood within the study area is given in Table 3-27

Table 3-27 Summary of Employment and Livelihood within the study area

Sl.NO Type of workers Study Area (Nos.) 1 Cultivators 22601 2 Agri. Labourers 25826 3 Household Industries 9144 4 Others 152626 (Source: Census 2011)

3.13.2.2 Educational Infrastructure within study area The district has good primary and secondary education infrastructure in urban and rural areas. The people around the study area have well connected to educational infrastructures. The educational facilities in the study area are summarized in

Table 3-28.

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Table 3-28Details of Education facilities within study area

S. No Type of School Numbers 1 Government Pre-Primary school 0 2 Private Pre-Primary school 52 3 Government Primary school 121 4 Private Primary school 116 5 Government Middle school 74 6 Private Middle school 106 7 Government Secondary school 55 8 Private Secondary school 90 9 Government Senior Secondary school 32 10 Private Senior Secondary school 69 (Source: Census 2011)

The following Table 3-29 shows the literates population and the percentage within the study area Table 3-29 Literates population and the percentage within the study area Populatio Literates % Sl. No Name n Population Literates Panipat District - Madlauda CD Block 1 Baholi (12) 1553 1171 75.40 2 Bal Jattan (11) 3045 1989 65.32 3 Bhalsi (45) 1663 1106 66.51 4 Dharamgarh (1) 3248 2105 64.81 5 Khandra (10) 2153 1341 62.29 6 Khukhrana (24) 1889 1227 64.96 7 Madlauda (7) 14356 9395 65.44 8 MahayudinpurThirana (9) 1905 1189 62.41 9 Nauhra (20) 3114 1936 62.17 10 Qawi (3) 6917 4382 63.35 11 RairKalan (29) 5399 3304 61.20 12 Shadipur (8) 21 8 38.10 13 Sherah (2) 4062 2627 64.67 14 Shohdapur (25) 6423 3911 60.89 15 Sithana (14) 5722 3378 59.04 16 Sutana (23) 6268 3902 62.25 17 Untiliya (44) 2781 1727 62.10 18 Waisari (43) 816 540 66.18 19 AsanKhurd (CT) 6873 5633 81.96 Panipat District - Panipat CD Block

20 Ali Asgharpur (32) 122 43 35.25

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Populatio Literates % Sl. No Name n Population Literates 21 AsanKalan (21) 4960 2958 59.64 22 Babarpur (34) 1908 1219 63.89 23 Badauli (33) 3822 2411 63.08 24 Dadlana (25) 11413 8042 70.46 25 Faridpur (17) 2237 1308 58.47 26 Ganjbar (31) 2876 1927 67.00 27 Jatol (27) 3645 2443 67.02 28 Mahmadpur (15) 2085 1083 51.94 29 Nizampur (3) 1649 1067 64.71 30 Ratipur (16) 0 0

31 Razapur (13) 3327 1446 43.46 32 Sarai Bachhra (4) 263 48 18.25 33 Sarai Kohand (29) 74 39 52.70 34 SimlaMolana (2) 1735 1052 60.63 35 Sondhapur (26) 7634 4415 57.83 36 Panipat (M Cl + OG) 295970 213996 72.30 37 Kabri (18) (CT) 7049 4057 57.55 38 Kachrauli (1) (CT) 5400 3252 60.22 39 PanipatTarafAnsar (CT) 42877 29693 69.25 40 Sikanderpur (19) (CT) 8894 5264 59.19 Karnal District - Assandh CD Block

41 Balla (30) 15187 9441 62.17 42 Goli (32) 4438 2730 61.51 43 MorMajra (31) 2105 1387 65.89 Karnal District - Ghraunda CD Block

44 AlipurKhalsa (36) 3330 2155 64.71 45 Anchla (56) 1383 802 57.99 46 Badshahpur (20) 29 26 89.66 47 Balran Gran (70) 7007 4133 58.98 48 Begampur (24) 1303 832 63.85 49 Gagsina (16) 7698 5163 67.07 50 Garhi Multan (26) 998 656 65.73 51 Gudha (23) 4180 2674 63.97 52 Har Singh Pura (37) 2029 1354 66.73 53 Kaimla (25) 7677 4855 63.24 54 Kapron (27) 255 143 56.08 55 KheriMunak (71) 923 557 60.35 56 KhoraKheri(18) 2244 1350 60.16 57 Kohand (30) 10193 5927 58.15 58 Kutana (26) 2307 1293 56.05 59 Malakpur (28) 1351 695 51.44 60 Munak (28) 11507 6800 59.09 61 PabanaHassanpur (72) 3723 2275 61.11

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Populatio Literates % Sl. No Name n Population Literates 62 Phurlak (21) 3757 2497 66.46 63 Raipur Jattan (19) 2793 1731 61.98 64 Shah Jahanpur (17) 839 542 64.60 65 Sheikhopura (22) 3197 2074 64.87 66 Gharaunda (MC) 37816 26608 70.36 Total 624417 425334 68.12

(Source: Census 2011)

3.13.2.3 Health facility within the study area The majority of people visit nearby Hospitals/health services provided by the Government. The area has got good public health facilities at easily reachable distances. There was no major health issues reported in our survey. Even for any minor ailments they contact medical facilities immediately as it is very accessible to them. The local transport facilities and the communication facilities are the main reasons to get immediate medical attention. The incidents of institutional delivery are high due to awareness, education, economic development, proximity to health delivery system. The Infant mortality rate and the maternal mortality rate have significantly reduced. The health facilities within the study area are given in Table 3-30.

Table 3-30 Health facility within the study area

Sl.No Type Numbers 1 Community health centre 1 2 Primary health centre 4 3 Primary health sub-centre 24 4 Maternity and Child Welfare Centre 5 5 TB hospital/Clinic 1 6 Hospital Allopathic 3 7 Hospital Alternative Medicine 4 8 Dispensary 17 9 Veterinary hospital 36 10 Mobile health clinic 1 11 Family Welfare Centre 1 12 Non-Government Medical facilities Out Patient 439 (Source: Census 2011)

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3.13.2.4 Drinking water facilities within the study area We found that in all the villages, the drinking water connectivity is well established. The bore wells and piped water are main sources of drinking water. Table 3-31 shows the drinking water sources of villages in the study area.

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Table 3-31 Drinking water sources of Villages in the study area Tap Tap Tube Tank/P Water Covered Uncover Hand River/C Water- Wells/B Spring ond/Lak Others Untreat Well ed Well Pump anal Treated orehole (Status e (Status Sl. No Name ed (Status (Status (Status (Status (Status (Status A(1)/NA (Status A(1)/NA (Status A(1)/NA A(1)/NA A(1)/NA A(1)/NA A(1)/NA A(1)/NA (2)) A(1)/NA (2)) A(1)/NA (2)) (2)) (2)) (2)) (2)) (2)) (2)) (2)) Panipat District - Madlauda CD Block 1 Baholi (12) 1 1 2 2 1 1 2 2 2 2 2 Bal Jattan (11) 1 1 2 2 1 1 2 2 2 2 3 Bhalsi (45) 1 1 2 2 1 1 2 2 2 2 4 Dharamgarh (1) 1 2 2 2 1 1 2 2 2 2 5 Khandra (10) 1 1 2 2 1 1 2 2 1 2 6 Khukhrana (24) 1 1 2 2 1 1 2 2 2 2 7 Madlauda (7) 1 1 2 2 1 1 2 2 2 2 MahayudinpurThirana 8 1 1 2 2 1 1 2 2 2 2 (9) 9 Nauhra (20) 1 1 2 2 1 1 2 2 2 2 10 Qawi (3) 1 1 2 2 1 1 2 2 2 2 11 RairKalan (29) 1 1 2 2 1 1 2 2 2 2 12 Shadipur (8) 1 1 2 2 1 1 2 2 2 2 13 Sherah (2) 1 1 2 2 1 1 2 2 2 2 14 Shohdapur (25) 1 1 2 2 1 1 2 2 2 2 15 Sithana (14) 1 1 2 2 1 1 2 2 2 2 16 Sutana (23) 1 1 2 2 1 1 2 2 2 2 17 Untiliya (44) 1 1 2 2 1 1 2 1 2 2 18 Waisari (43) 1 1 2 2 1 1 2 1 2 2 Panipat District - Panipat CD Block 19 Ali Asgharpur (32) 1 2 2 2 1 1 2 1 1 2 20 AsanKalan (21) 1 2 2 2 1 1 2 2 2 2

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Tap Tap Tube Tank/P Water Covered Uncover Hand River/C Water- Wells/B Spring ond/Lak Others Untreat Well ed Well Pump anal Treated orehole (Status e (Status Sl. No Name ed (Status (Status (Status (Status (Status (Status A(1)/NA (Status A(1)/NA (Status A(1)/NA A(1)/NA A(1)/NA A(1)/NA A(1)/NA A(1)/NA (2)) A(1)/NA (2)) A(1)/NA (2)) (2)) (2)) (2)) (2)) (2)) (2)) (2)) 21 Babarpur (34) 1 2 2 1 1 1 2 2 2 2 22 Badauli (33) 1 2 2 2 1 1 2 2 1 2 23 Dadlana (25) 1 2 2 2 2 1 2 2 1 2 24 Faridpur (17) 1 2 2 2 1 1 2 1 1 2 25 Ganjbar (31) 1 2 2 2 2 1 2 2 2 2 26 Jatol (27) 1 1 2 2 1 1 2 1 1 2 27 Mahmadpur (15)

28 Nizampur (3) 1 2 2 2 2 1 2 1 1 2 29 Ratipur (16) 1 2 2 2 2 1 2 2 1 2 30 Razapur (13) 1 2 2 2 1 2 2 2 2 2 31 Sarai Bachhra (4) 1 1 2 2 1 1 2 1 1 2 32 Sarai Kohand (29) 1 1 2 2 1 1 2 1 1 2 33 SimlaMolana (2) 1 2 2 2 1 1 2 2 1 2 34 Sondhapur (26) 1 1 2 2 1 1 2 1 1 2 Karnal District - Assandh CD Block 35 Balla (30) 1 2 2 2 1 1 2 1 2 2 36 Goli (32) 1 2 2 2 1 1 2 1 1 2 37 MorMajra (31) 1 2 2 2 1 1 2 1 2 2 Karnal District - Ghraunda CD Block 38 AlipurKhalsa (36) 1 2 2 2 1 1 2 1 2 2 39 Anchla (56) 1 2 2 2 1 1 2 2 1 2 40 Badshahpur (20) 1 2 2 2 1 1 2 1 2 2 41 Balran Gran (70) 1 2 2 2 1 2 2 1 2 2 42 Begampur (24) 1 2 2 2 1 1 2 1 2 2

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Tap Tap Tube Tank/P Water Covered Uncover Hand River/C Water- Wells/B Spring ond/Lak Others Untreat Well ed Well Pump anal Treated orehole (Status e (Status Sl. No Name ed (Status (Status (Status (Status (Status (Status A(1)/NA (Status A(1)/NA (Status A(1)/NA A(1)/NA A(1)/NA A(1)/NA A(1)/NA A(1)/NA (2)) A(1)/NA (2)) A(1)/NA (2)) (2)) (2)) (2)) (2)) (2)) (2)) (2)) 43 Gagsina (16) 1 2 2 2 1 1 2 1 2 2 44 Garhi Multan (26) 1 2 2 2 1 1 2 2 2 2 45 Gudha (23) 1 2 2 2 1 1 2 2 2 2 46 Har Singh Pura (37) 1 2 2 2 1 1 2 2 2 2 47 Kaimla (25) 1 2 2 2 1 1 2 2 2 2 48 Kapron (27) 1 2 2 2 1 1 2 2 2 2 49 KheriMunak (71) 1 2 2 2 1 1 2 2 2 2 50 KhoraKheri(18) 1 2 2 2 1 1 2 2 2 2 51 Kohand (30) 1 2 2 2 1 1 2 2 2 2 52 Kutana (26) 1 2 2 2 1 1 2 2 2 2 53 Malakpur (28) 1 2 2 2 1 1 2 2 2 2 54 Munak (28) 1 2 2 2 2 1 2 2 2 2 55 PabanaHassanpur (72) 1 1 2 2 2 2 2 2 2 2 56 Phurlak (21) 1 2 2 2 1 1 2 2 2 2 57 Raipur Jattan (19) 1 2 2 2 1 1 2 2 2 2 58 Shah Jahanpur (17) 1 1 2 2 1 2 2 2 2 2 59 Sheikhopura (22) 1 2 2 2 1 1 2 2 1 2 Note: A – Available; NA – Not Available (Source: Census 2011)

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3.13.3 Summary

The Socioeconomic profile of the study area shows that the majority of people in the study area work in non-agricultural sector, however in rural area majority of the people in the rural area depends on agricultural sector. The average literacy rate of the study area is 68.12% which is less than the district literacy rate of 75.9%.

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CHAPTER 4 ANTICIPATED ENVIRONMENTAL IMPACTS AND MITIGATION MEASURES

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4 ANTICIPATED ENVIRONMENTAL IMPACTS & MITIGATION MEASURES 4.1 Introduction

One of the important components in the process of environmental impact assessment is identification of significant impacts as it leads to other elements such as quantification and evaluation of impacts. Any change in environment whether adverse or beneficial, wholly or partially, resulting from impacting activity is called Environmental Impact. Each individual activity with respect to each environmental parameter will have its own impact potential. Proposed project activities will be carried out in such a way so that potential adverse/negative impacts are avoided, wherever possible. While for remaining impacts which are inevitable, practicable mitigation measures will be recommended to minimize the adverse impacts.

The prediction of impacts helps to develop and implement mitigation measures/environment management plan in such a way that the developmental activity will minimize the deterioration of environmental quality.

4.2 Proposed Project Activities

The proposed project will have impacts on environment during the tenure of two phases; i.e. construction phase and operation phase.

4.3 Construction Phase

Construction phase of the proposed project is temporary and will mainly involve the following generic construction activities

 Excavation  Formwork & concreting  Material handling and Transportation  Use of Tools and Potable power tools  Scaffolding  Crane and Rigging Equipment  Mechanical Equipment‟s  Working in confined space

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4.3.1 Impacts During Construction Phase

As the main impacts of the construction phase are envisaged in terms of air pollution only, this natural mitigation would be significantly helpful in elimination of predicted impacts of the phase. However, the following principal major impacts to the environment are considered for further planning of mitigation measures:  The use of automobiles and machinery during construction can deteriorate the air quality and generate temporary emission.  The use of automobiles and machinery generates noise pollution from construction activities.  The irregular working hours, & traffic, night-working, flood-lighting and transportation damage the socioeconomic balance of surrounding region.  Effects may occur due to the accumulation of the contaminant in water resources & soil due to uptake of construction material.  Short term heavy construction might cause increase in noise level  Effects on work place condition & human health due to the accidents during the construction works.  Effects on the socio-economic activity due to direct impacts or indirect impacts on socio-economic activities.

4.3.2 Mitigation Measures for Construction Phase

 The entire construction activities will be confined with the designated area inside the existing premises.  The small amount of unused construction material shall be stored in proper area to utilise further in construction activities and surplus excavated material shall be disposed of in suitable pre-identified areas.  Construction material shall be stored at adequate distance from the water storage in order to prevent any chances of accidental leakage or spillage which could pollute the water storage  Wherever required impervious lining shall be provided to the storage premises to avoid accidental mixing or mixing due to fugitive losses.  To reduce the dust generation on site wherever & whenever required water shall be sprinkled on ground or stock pile of excavated soil.

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 Equipment‟s / machineries shall be used efficiently and shall be kept shut in order to reduce air emission, noise pollution and consumption of energy resource  Emission from the equipment‟s/machineries shall be monitored on regular basis and possible implementation shall be provided on site  Transport vehicles shall be monitored & maintained regularly to control the emission quality and fuel consumption  Provision of necessary PPEs like face mask & eye-glasses to employees /labours engaged in construction activities.  The machineries/equipment used on site shall be of highly maintained so they do work with optimum efficiency generating less noise pollution  Operation of machineries/equipment causing high noise level shall be stopped during the night time and all such operations shall be planned for day time only.  Transportation activities shall not be conducted during the night (other than in case of emergency) to avoid high noise level in nearby villages/locality.

4.3.3 Land environment a. Impacts

Since it is an expansion project, it will be implemented within the M/s IOCL, PR, premises; there is no additional land to be acquired for the proposed project. The expansion project will be done in land area, which is identified as appropriate location based on environmental and engineering requirements. The activities carried out during the construction phase will involve a change in the land use from vacant industrial land to a built up industrial land, which will pose the following impacts on the land environment. 1. Compaction of soil and a change in the soil structure due to the use of heavy construction vehicles and machineries. 2. Removal of soil from the site. 3. Mixing of the topsoil and subsoil. 4. Dispersion of dust.

b. Mitigation Measures

1. Employing techniques such as restricting access during wet conditions, using protective boarding and low ground pressure machineries to minimize compaction of soil. 2. The removed soil will be properly stored for subsequent reinstatement.

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3. Reuse of excess excavated material for road development, green belt development and landscaping. 4. A well designed closed depository for storage of construction materials to prevent land/soil pollution. 5. Effective stabilization of altered landforms to minimize soil erosion and the potential for water pollution (e.g. Vegetation). 6. Reuse of construction wastes such as sand, brick, gravel, cement for developing internal road and project structures. 7. Trucks with construction material susceptible for fugitive emission will be covered with tarpaulin covers during transport of construction materials 8. Transportation management will be adopted for movement of vehicles transporting construction materials and traffic will be regulated. 9. Vehicles deployed will confirm to emission norms (air/noise) of CPCB and have validPollution Under Control(PUC) certificates 10. Very old vehicles (more than 20 years) will not be allowed at site 11. Trucks will comply with standards for exhaust emissions and noise levels.

4.3.4 Air environment In order to predict the impact of constructional and operational activities on the ambient air quality, the data on emission, micrometeorology and from Indian meteorological department (IMD)were collected. All these data will be used to predict ground level concentration of

(GLCs) of SO2, NOX and PM10 for different temporal variations. In the construction phase, activities like site clearance, site leveling, movements of workers and material, construction of road, transportation activities will generate dust, gaseous pollutants and particulate matter and affect the air quality. Other impacts include - 1. Site Preparation-fencing, boundary and clearing of site will cause disturbance to the surroundings. 2. Excavation, backfilling and leveling. 3. Hauling and dumping of earth materials and construction spoils. 4. Foundation works can cause dust generation which will decrease the air quality and it can impact the labors working. 5. Fabrication, erection of steel structures such as tanks, pipelines and sheds. 6. Construction of internal roads drains and water supply. 7. Cleaning and landscaping.

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8. Emission from Construction DG & Construction Equipment‟s. a. Mitigation Measures

1. Barricading the construction area and minimizing exposed areas to reduce dust generation. 2. Areas generating dust during dry weather will be sprayed with water. 3. Appropriate enclosed areas for storage of construction materials. 4. Facilitating the workers with the required personal protective equipment‟s. 5. Efficient usage and maintenance of equipment‟s/machineries to lower air emissions, noise pollution and consumption of energy resource. 6. Exhaust vent of DG set will be provided with adequate stack height to ensure quick dispersal of gaseous emissions. 7. Periodic monitoring and maintenance of transport vehicles to check on the quality of emission to be within permissible limits and consumption of fuel. 8. Regular inspection of construction site to ensure timely removal and disposal of construction debris to the dumping sites or for recycle/reuse. 4.3.5 Water environment

a. Impacts

1. Contamination of watercourses by leakage from fuel and materials storage areas. 2. Oil and suspended solids in run-off from vehicles and access roads. 3. Use of heavy machineries and vehicles causes compaction of topsoil due to which a change in the surface water drainage pattern may occur. 4. Generation of sewage / process effluent and blow down. b. Mitigation measures

1. The water demand during the construction phase will be met from Western Yamuna Canal. 2. Impenetrable lining will be provided to storage premises to avoid accidental mixing or fugitive losses. 3. Storehouse will be located at a distance away from the water storage area to prevent accidental release or spillage. 4. Proper management of rain water run-off during monsoon and creating bunds to utilize the rain water for construction purpose. 5. An appropriate water management system will be implemented.

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4.3.6 Noise environment

a. Impacts

During construction phase, the noise will mostly be produced because of building activities and machineries used for carrying out construction. Construction activities mainly involve diesel generators, laying of foundation, erection of superstructure, clearing of obstruction and trees if any from the proposed area. Activities such as construction of labor camps, onsite office, pneumatic hammers, compressors, concrete mixers, construction material plants however, do not cause significant noise pollution. But if the work continuous for longer duration, it can affect the health of local people and workers involved in the project work. b. Mitigation Measures

1. Barricading the construction site. 2. The green belt will help in reducing the noise nuisance. 3. Selection of equipment‟s of high quality. 4. Proper planning and organizing of construction activities which will help in avoiding loud verbal exchanges between the intervening parties. 5. Transportation activities will be carried out only during the day and only in case of emergency, the transportation activities will be permitted in night time. 6. The vehicles used for construction activities and transportation of materials will be provided with the horn of low noise level as recommended by RTO/ concerned authorities. 7. Minimization of operation time of noisy equipment and operation of machineries/equipment that generate high levels of noise only during day time. 8. Inadequate use of plant and equipment, namely, running on full power when the work does not necessitate it will be avoided. 9. Personal protective equipment‟s, education and public awareness and exposure control through rotation of work will be provided to the workers engaged in construction activities in the area generating high levels of noise. 4.3.7 Waste generation

The source of waste are metal pieces, cardboards, wooden scrap, sand gravels etc., generation of chemical waste by general site practices (e.g. vehicle and plant maintenance/servicing), municipal waste generated by site workers.

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a. Mitigation measures

1. Recycling/reusing/recovering materials where possible and thereby neglecting or reducing the disposal requirements. 2. Separation of construction material for reuses either to be used on onsite filling or can be used as public fill. 3. Training the staff in waste minimizing practices. 4. Chemical waste should be stored in a locked area so as to avoid leaching of harmful chemicals in the soil or nearby water bodies (If any). 4.3.8 Ecology

Except for the removal of weeds, the ecological status of the site will be well maintained by conserving/ developing the greenbelt at the site.

4.3.9 Social environment

A socio-economic study was undertaken with the help of secondary sources in assessing aspects which are dealing with social and cultural conditions, and economic status in the study area. The study provides information such as demographic structure, population dynamics, infrastructure resources, and the status of human health and economic attributes like employment, per-capita income, agriculture, trade, and industrial development in the study area. There will be temporary employment for manpower required during construction phase available from local communities. Overall socioeconomic effect of construction phase will be positive due to direct and indirect employment opportunities for the local population Summary: Due to the running refinery nearby so adequate precautions must be taken, in areas of 1. Work permit system must be followed for carrying out any job inside the Refinery, Flare System, Effluent Treatment Plant(ETP), and New Tank Farm(NTF).Presently permit system available are Hot Permit, Cold Permit, Height Permit, Excavation Permit, Confined space Permit, Radiography Permit, Electrical energizing/ deenergizing Permit & Vehicle Entry Permit. The work permit system should be followed as per OISD-105 2. Jay Walking of Construction workers in the refinery area 3. Labour camps to be totally eliminated. Even small labour camp should not be allowed.

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4. No hot work including Civil jobs like chipping, excavation etc. which produces open flame/sparks ignition should be carried out in the plant area unless such work is authorized by fire & safety permit issued by IOCL/ authorized representative. 5. All contractor workers must have to undergo safety briefings before they are issued gate passes

4.4 Operation Phase From an Environmental perspective, this phase is of paramount significance due to its potential to invoke long term impacts. The adverse effects that are likely to occur during this operational phase of the project are Air pollution (gaseous Emissions), Effluent generation, Noise Generation, Solid waste Generation etc.

4.4.1 Impacts During Operational Phase

Because of its potential to create long-term impacts, this phase is very important from the environmental impact point of view. The basic impacts like gaseous emissions, water consumption/ pollution and solid waste will have the potential to adversely affect air, water and land / soil in the vicinity of the project site.

This phase will broadly include the following direct and indirect activities / actions:

 Storage and transportation of raw materials and finished products.  Gaseous emissions  Effluent Generation, treatment and disposal  Noise Generation  Solid waste generation 4.5 Air Environment Baseline data reveals that the ambient air quality has been monitored at 8 locations for 14 parameters as per NAAQS/CPCB guidelines within the study area. The maximum and

minimum baseline levels taken is PM10 (212.14 and 53.17µg/m³), PM2.5 (107.24 and

27.44µg/m³), SO2 (29.96 and 12.50µg/m³), NO2 (61.10 and 20.69µg/m³). The average of

baseline levels taken for 8 location ranges is PM10 (83.59 to 128 µg/m³), PM2.5 (42.77 to

64.98µg/m³), SO2 (14.92 to 22.83µg/m³), NO2 (27.89 to 43.71µg/m³) and CO (610 – 780µg/m³).

The nearest HSPCB AAQ monitoring station is Sector-18, Panipat in which the maximum

and minimum levels for the period March to May 2019 is PM10 (487.59 and 29.52µg/m³),

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PM2.5 (131.87 and 15.96 µg/m³), SO2 (148.33 and 5.82 µg/m³), NOx (120.5 and 11.87 ppb) and CO (77.44 and 0.14 mg/m³). The average values of same station for the above period is

PM10 (169.49µg/m³), PM2.5 (47.27µg/m³), SO2 (30.56 µg/m³), NO2 (48.86ppb) and CO (11.13 mg/m³).

Source: https://app.cpcbccr.com/ccr/#/caaqm-dashboard-all/caaqm-landing/data Some of the parameters are exceeding the National Ambient Air Quality Standards the study period from March to May 2019 . Stack emission of PM, SOx & NOx are due to process units. Adequate measures will be taken to control Air Pollution.

4.5.1 Meteorological data

The meteorological data for a month, i.e. from March to May 2019 was considered for the study. Data included for AERMET were daily wind speed, wind direction, temperature, relative humidity, air pressure, precipitation, and solar radiation recorded during the period. AERMET reformats meteorological data so that it can be used as input for AERMOD model.

The wind rose for the study period is given as Figure 4-1

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Figure 4-1 Wind rose diagram of Meteorological data considered for Modelling (March to May 2019) 4.5.2 AERMET Process For the 3 phase AERMET processing of the meteorological data, specifications of the land use in the area are required to determine the terrain roughness for modelling. The land use was characterized for in and around the site. The surface characteristics for the site and surroundings were selected and used to calculate the Albedo, Bowen ratio and surface roughness parameters.

4.5.3 AERMOD Process

AERMOD Software Version 8.0.5 was used for air dispersion modelling and is applicable to a wide range of buoyant or neutrally buoyant emissions up to a range of 50. In addition to more straight forward cases, AERMOD is also suitable for complex terrain and urban dispersion scenarios.

AERMOD is a steady-state plume model. In the stable boundary layer (SBL), it assumes the concentration distribution to be Gaussian in both the vertical and horizontal. In the convective

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boundary layer (CBL), the horizontal distribution is also assumed to be Gaussian, but the vertical distribution is described with a bi-Gaussian probability density function (pdf). This behavior of the concentration distributions in the CBL was demonstrated by Willis and Deardorff (1981) and Briggs (1993). Additionally, in the CBL, AERMOD treats “plume lofting,” whereby a portion of plume mass, released from a buoyant source, rises to and remains near the top of the boundary layer before becoming mixed into the CBL. AERMOD also tracks any plume mass that penetrates into the elevated stable layer, and then allows it to re-enter the boundary layer when and if appropriate. For sources in both the CBL and the SBL AERMOD treats the enhancement of lateral dispersion resulting from plume meander. The emissions from proposed stacks are estimated and used for the air dispersion modeling as shown in Table 4-1. Maximum incremental values for PM, SO2, NOx and CO have been represented as pictorial concentration contours and as tabular concentration values in following section

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4.5.4 Emissions-Point Source Table 4-1 Proposed Stack Emission details

S.No Stack details Stack Coordinates Stack Details Emission per stack (g/s)

N E Height (m) Temp Dia. (m) Exit Velocity Flue gas Flow PM SO2 NOx CO (°C) (m/s) Rate (Nm3/hr) 1. AVU (CDU/VDU) 29°29'6.07"N 76°52'11.49"E 90 165 5.3 4.76 257400 0.751 50.8 13.829 8.297 2. VGO- HDT 29°28'52.97"N 76°52'12.69"E 65 154 3.55 3.61 89750 0.125 0.306 4.778 1.972 3. Diesel Hydrotreater Unit 29°29'0.89"N 76°52'10.39"E 48 165 2.1 5.12 41430 0.058 0.142 2.208 0.908 4. MS Block_Charge Heater 29°28'55.06"N 76°52'25.87"E 70 161 2.8 6 92520 0.129 0.319 4.931 2.031 5. NHT Charge Heater 29°28'55.44"N 76°52'19.27"E 55 204 1.55 5.98 25380 0.035 0.086 1.353 0.556 6. Naphtha Stripper reboiler Heater 29°28'57.22"N 76°52'19.86"E 50 264 1.35 6 17260 0.024 0.058 0.919 0.378 7. CDWU_HCR Reactor Feed Heater 29°28'52.39"N 76°52'48.73"E 40 370 0.85 6 5700 0.008 0.019 0.297 0.131 8. CDWU_DW Reactor feed Heater 29°28'49.21"N 76°52'48.75"E 40 385 0.73 6 4150 0.006 0.014 0.217 0.094 9. CDWU_Vaccum Column Feed 29°28'51.32"N 76°52'51.05"E 50 220 1.35 6 18300 0.025 0.064 0.975 0.403 Furnace 10. Resid Hydrocracking Unit (RHCU) 29°28'52.57"N 76°52'35.96"E 70 182 2.25 5.67 53160 0.074 0.183 2.833 1.167 11. Resid Hydrocracking Unit 29°28'47.64"N 76°52'33.42"E 65 206 0.964 5.28 8630 0.012 0.031 0.469 0.206 (RHCU)_Vaccum Heater 12. Indmax FCC_Fresh Feed Furnace 29°29'0.65"N 76°51'45.77"E 60 155 1.8 6 38500 0.053 0.133 2.050 0.844 13. Indmax FCC_Flue Gas cooler 29°28'58.47"N 76°51'50.63"E 60 200 3.5 12 260750 3.622 3.711 6.084 7.189 14. Sulpur recovery unit (SRU) 29°29'8.51"N 76°51'45.77"E 65 290 2.6 21.38 216570 0.037 17.889 5.464 4.925 15. Spent Acid Recovery unit 29°29'7.13"N 76°51'49.23"E 60 200 0.8 3.5 3850 0.005 0.047 0.233 0.094 (SARU)_APH System & Stack 16. Spent Acid Recovery unit 29°29'5.73"N 76°51'52.10"E (SARU)_Decomposition furnace 60 80 1 8 18790 0.159 2.000 0.778 0.467 burner 17. Hydrogen Generation Unit 29°29'1.13"N 76°52'25.54"E 60 188 3.4 7.64 155111.13 0.732 2.256 5.186 1.036 18. CPP Stack 29°28'56.27"N 76°52'2.03"E 90 160 3.25 17.5 871660 11.555 101.795 78.190 22.303 Total (g/s) 17.41 179.853 130.794 53.001 Total (kg/hr) 62.676 647.4708 470.8584 190.8036

Source: M/s. IOCL Panipat Refinery

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Figure 4-2 Predicted 24-Hrs GLC‟s of Particulate matter within 10 km Radius of the Study Area Table 4-2 Estimated Top 10 Highest Concentrations of Particulate Matter obtained through Modeling

S. No UTM coordinates (m) Conc. Distance from Direction 3 E N (µg/m ) Centre of Project from Centre Site (~km) of Project Site 1. 679990 3263090 2.8897 2.24 WNW 2. 681990 3262090 2.84822 - - 3. 681990 3263090 2.61555 1 N 4. 679990 3262090 2.24488 2 W 5. 682990 3263090 1.8188 1.41 NE 6. 682990 3262090 1.76509 1 E 7. 680990 3264090 1.64169 2.24 NNE 8. 683990 3263090 1.55999 2.24 ENE 9. 679990 3264090 1.39182 2.83 NW 10. 682990 3261090 1.38934 1.41 SE

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Figure 4-3 Predicted 24-Hrs‟ GLC‟s of SO2 within 10 km Radius of the Study Area Table 4-3 Estimated Top 10 Highest Concentrations of Sulphur Dioxide Obtained Through Modeling

S. No UTM coordinates (m) Conc. Distance from Direction (µg/m3) Centre of from Centre E N Project Site of Project Site (~km) 1. 681990 3263090 30.51969 1 N 2. 681990 3262090 25.79022 - - 3. 679990 3263090 21.48982 2.24 WNW 4. 679990 3262090 20.33266 2 W 5. 682990 3262090 19.08763 1 E 6. 680990 3264090 18.89029 2.24 NNE 7. 682990 3263090 18.56007 1.41 NE 8. 679990 3264090 16.12646 2.83 NW 9. 683990 3263090 15.7179 2.24 ENE 10. 684990 3263090 13.58015 3.16 ENE

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Figure 4-4 Predicted 24-Hrs‟ GLC‟s of NOx within 10 km Radius of the Study Area Table 4-4 Estimated Top 10 Highest Concentrations of oxide of Nitrogen Obtained through Modeling

S. No UTM coordinates (m) Conc. Distance from Direction (µg/m3) Centre of from Centre E N Project Site of Project Site (~km) 1. 681990 3262090 22.28898 - - 2. 681990 3263090 21.7846 1 N 3. 679990 3263090 19.13681 2.24 WNW 4. 682990 3262090 16.68015 1 E 5. 682990 3263090 16.40949 2.24 NNE 6. 679990 3262090 15.4453 2 W 7. 683990 3263090 13.82858 2.24 ENE 8. 680990 3264090 13.46019 2.24 NNE 9. 682990 3261090 13.00614 1.41 SE 10. 679990 3264090 12.22661 2.83 NW

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Figure 4-5 Predicted 1-Hr‟ GLC‟s of CO within 10 km Radius of the Study Area Table 4-5 Estimated Top 10 Highest Concentrations of Carbon Monoxide Obtained through Modeling

S. No UTM coordinates (m) Conc. Distance from Direction (µg/m3) Centre of from Centre E N Project SIte of Project Site (~km) 1. 679990 3263090 30.66712 2.24 WNW 2. 681990 3263090 27.87902 1 N 3. 679990 3264090 25.14039 2.82 NW 4. 679990 3265090 25.06886 3.60 NNW 5. 682990 3263090 24.36052 1.41 NE 6. 681990 3262090 24.27332 Project site Project site 7. 682990 3262090 23.96826 1 E 8. 678990 3266090 22.83053 4.99 NNW 9. 679990 3261090 21.15259 2.24 WSW 10. 678990 3264090 20.94578 3.60 WNW

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Conclusion Maximum pollutant concentrations of PM, SO2 and NOx observed due to proposed expansion for a 24hr-average period have been studied and CO observed due to proposed expansion for a 1hr-average period have been studied. The total increase in concentrations above baseline status to estimate the percentage increase and summarized in Table 4-6.

Table 4-6 Total Maximum GLCs from the Stack Emissions (Point Source)

Pollutant Max. Base Estimated Total Conc. NAAQ % line Conc. Incremental Conc. (µg/m3) standard increase (µg/m3) (µg/m3) (µg/m3) PM 128 2.89 130.89 100 2.26 SO2 22.83 30.52 53.35 80 133.68 NOx 43.71 22.29 66 80 51.00 CO 780 30.66 810.66 4000 3.93

The incremental concentrations of PM, SO2, NOx and CO are observed to be 2.26%,

133.68%, 51% and 3.93% respectively. The total pollutant concentrations of PM, SO2, NOx 3 3 3 3 and CO are 130.89 µg/m , 53.35 µg/m , 66 µg/m and 810.66 µg/m .

4.5.5 Emissions-Line Source

Table 4-7 Transportation Emission details

S.n Type of No.of.Vehicle(Based on maximum PM NOx CO o Vehicle operation capacity) 1 4W 40 0.00125 0.0347 0.206

2 Truck 20 0.00139 0.0639 0.556

Total(g/s) 0.00264 0.0986 0.761

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Figure 4-6 Predicted 24-Hrs GLC‟s of Particulate matter within 10 km Radius of the Study Area Table 4-8 Estimated Top 10 Highest Concentrations of Particulate Matter obtained through Modeling UTM coordinates (m) Distance from Direction Conc. Centre of Project from Centre S. No E N (µg/m3) SIte (~km) of Project Site 1. 682990 3262090 0.12348 1 E 2. 682990 3263090 0.09791 1.41 NE 3. 682990 3264090 0.06307 2.24 NNE 4. 681990 3263090 0.05266 1 N 5. 681990 3262090 0.04627 Project Site Project Site 6. 680990 3264090 0.04153 2.24 NNW 7. 680990 3263090 0.03762 1.41 NW 8. 680990 3262090 0.03086 1 W 9. 683990 3263090 0.02979 2.24 ENE 10. 681990 3261090 0.02546 1 S

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Figure 4-7 Predicted 24-Hrs‟ GLC‟s of NOx within 10 km Radius of the Study Area Table 4-9 Estimated Top 10 Highest Concentrations of oxide of Nitrogen Obtained through Modeling Distance from UTM coordinates (m) Direction Conc. Centre of S. No from Centre (µg/m3) Project Site E N of Project Site (~km) 1. 682990 3262090 4.88628 1 E 2. 682990 3263090 3.80278 1.41 NE 3. 682990 3264090 2.48844 2.24 NNE 4. 681990 3263090 1.99801 1 N 5. 681990 3262090 1.76543 Project Site Project Site 6. 680990 3264090 1.5806 2.24 NNW 7. 680990 3263090 1.46244 1.41 NW 8. 680990 3262090 1.15887 1 W 9. 683990 3263090 1.11564 2.24 ENE 10. 682990 3261090 0.98826 1.41 SE

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Figure 4-8 Predicted 1-Hrs‟ GLC‟s of CO within 10 km Radius of the Study Area Table 4-10 Estimated Top 10 Highest Concentrations of Carbon Monoxide Obtained through Modeling UTM coordinates (m) Distance from Direction Conc. Centre of from Centre S. No E N (µg/m3) Project SIte of Project (~km) Site 1. 682990 3262090 500.6819 1 E 2. 682990 3263090 378.8535 1.41 NE 3. 681990 3262090 247.8971 Project Site Project Site 4. 682990 3264090 196.002 2.24 NNE 5. 681990 3263090 194.7381 1 N 6. 682990 3261090 140.8452 1.41 SE 7. 680990 3264090 139.6697 2.24 NNW 8. 681990 3261090 136.6366 1 S 9. 680990 3262090 136.2806 1 W 10. 680990 3263090 121.7243 1.41 NW

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Conclusion Maximum pollutant concentrations of PM, and NOx observed due to proposed expansion for a 24hr-average period have been studied and CO observed due to proposed expansion for a 1hr-average period have been studied.. The total increase in concentrations above baseline status to estimate the percentage increase and summarized in Table 4-6.

Table 4-11 Total Maximum GLCs from the VehicularEmissions (Line Source)

Pollutant Max. Base Estimated Total Conc. NAAQ % line Conc. Incremental Conc. (µg/m3) standard increase (µg/m3) (µg/m3) (µg/m3) PM 128 0.12 128.12 100 0.09

NOx 43.71 4.88 48.59 80 11.16 CO 780 500.68 1280.68 4000 64.19

The incremental concentrations of PM, NOx and CO are observed to be 0.09%, 11.16%, and

64.19% respectively. The total pollutant concentrations of PM, NOx and CO are 128.12 3 3 3 µg/m , 48.59 µg/m and 1280.68 µg/m .

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4.5.6 Emissions-Cumulative Source Table 4-12 Cummulating emission details

Stack Details Emission per stack (g/s) S.N Flue gas Flow Stack details Height Temp Dia. Exit Velocity o Rate PM SO2 NOx CO (m) (°C) (m) (m/s) (Nm3/hr) 1. AVU (CDU/VDU) 90 165 5.3 4.76 257400 0.751 50.8 13.829 8.297 2. VGO- HDT 65 154 3.55 3.61 89750 0.125 0.306 4.778 1.972 3. Diesel Hydrotreater Unit 48 165 2.1 5.12 41430 0.058 0.142 2.208 0.908 4. MS Block_Charge Heater 70 161 2.8 6 92520 0.129 0.319 4.931 2.031 5. NHT Charge Heater 55 204 1.55 5.98 25380 0.035 0.086 1.353 0.556 6. Naphtha Stripper reboiler Heater 50 264 1.35 6 17260 0.024 0.058 0.919 0.378 7. CDWU_HCR Reactor Feed Heater 40 370 0.85 6 5700 0.008 0.019 0.297 0.131 8. CDWU_DW Reactor feed Heater 40 385 0.73 6 4150 0.006 0.014 0.217 0.094 9. CDWU_Vaccum Column Feed Furnace 50 220 1.35 6 18300 0.025 0.064 0.975 0.403 10. Resid Hydrocracking Unit (RHCU) 70 182 2.25 5.67 53160 0.074 0.183 2.833 1.167 11. Resid Hydrocracking Unit (RHCU)_Vaccum Heater 65 206 0.964 5.28 8630 0.012 0.031 0.469 0.206 12. Indmax FCC_Fresh Feed Furnace 60 155 1.8 6 38500 0.053 0.133 2.050 0.844 13. Indmax FCC_Flue Gas cooler 60 200 3.5 12 260750 3.622 3.711 6.084 7.189 14. Sulpur recovery unit (SRU) 65 290 2.6 21.38 216570 0.037 17.889 5.464 4.925 Spent Acid Recovery unit (SARU)_APH System & 15. 60 200 0.8 3.5 3850 0.005 0.047 0.233 0.094 Stack Spent Acid Recovery unit (SARU)_Decomposition 16. 60 80 1 8 18790 0.159 2.000 0.778 0.467 furnace burner 17. Hydrogen Generation Unit 60 188 3.4 7.64 155111.13 0.732 2.256 5.186 1.036 101.79 18. CPP Stack 90 160 3.25 17.5 871660 11.555 78.190 22.303 5 S.n Type of Vehicle No.of.Vehicle(Based on maximum operation capacity) PM SO2 NOx CO o 1 4W 40 0.00125 0 0.0347 0.206 2 Truck 20 0.00139 0 0.0639 0.556 179.85 130.89 Total(g/s) 17.413 53.762 3 3 647.47 471.21 Total (kg/hr) 62.687 193.543 1 5

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Figure 4-9 Predicted 24-Hrs GLC‟s of Particulate matter within 10 km Radius of the Study Area Table 4-13 Estimated Top 10 Highest Concentrations of Particulate Matter obtained through Modeling Direction from UTM coordinates (m) Conc. Distance from Centre S. No Centre of Project (µg/m3) of Project Site (~Km) E N Site 1. 679990 3263090 2.90125 2.24 WNW 2. 681990 3262090 2.84822 Project site Project site 3. 681990 3263090 2.61555 1 N 4. 679990 3262090 2.25067 2 W 5. 682990 3263090 1.8188 1.41 NE 6. 682990 3262090 1.76509 1 E 7. 680990 3264090 1.64169 2.24 NNE 8. 683990 3263090 1.57804 2.24 ENE 9. 679990 3264090 1.39213 2.83 NW 10. 682990 3261090 1.38934 1.41 SE

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Figure 4-10 Predicted 24-Hrs‟ GLC‟s of SO2 within 10 km Radius of the Study Area Table 4-14 Estimated Top 10 Highest Concentrations of Sulphur Dioxide Obtained Through Modeling Distance from Direction from UTM coordinates (m) Conc. S. No Centre of Project Centre of Project (µg/m3) E N SIte (~Km) Site 1. 681990 3263090 30.51969 1 N 2. 681990 3262090 25.79022 - - 3. 679990 3263090 21.48982 2.24 WNW 4. 679990 3262090 20.33266 2 W 5. 682990 3262090 19.08763 1 E 6. 680990 3264090 18.89029 2.24 NNE 7. 682990 3263090 18.56007 1.41 NE 8. 679990 3264090 16.12646 2.83 NW 9. 683990 3263090 15.7179 2.24 ENE 10. 684990 3263090 13.58015 3.16 ENE

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Figure 4-11 Predicted 24-Hrs‟ GLC‟s of NOx within 10 km Radius of the Study Area Table 4-15 Estimated Top 10 Highest Concentrations of oxide of Nitrogen Obtained through Modeling Distance from Direction from UTM coordinates (m) Conc. S. No Centre of Project Centre of Project (µg/m3) E N SIte (~Km) Site 1. 681990 3262090 22.28867 Project site Project site 2. 681990 3263090 21.78424 1 N 3. 679990 3263090 19.5606 2.24 WNW 4. 682990 3262090 16.67996 1 E 5. 682990 3263090 16.40915 1.41 NE 6. 679990 3262090 15.66587 2 W 7. 683990 3263090 14.51588 2.24 ENE 8. 680990 3264090 13.46087 2.24 NNW 9. 682990 3261090 13.00591 1.41 SE 10. 680990 3263090 12.53905 1.41 NW

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Figure 4-12 Predicted 1-Hrs‟ GLC‟s of CO within 10 km Radius of the Study Area Table 4-16 Estimated Top 10 Highest Concentrations of Carbon Monoxide Obtained through Modeling Distance from Direction from UTM coordinates (m) Conc. S. No Centre of Project Centre of Project (µg/m3) E N SIte (~Km) Site 1. 682990 3262090 501.683 2.24 WNW 2. 682990 3263090 382.7534 1.41 NE 3. 681990 3262090 248.4416 2.82 NW 4. 682990 3264090 197.0063 2.24 NNE 5. 681990 3263090 195.8339 1 N 6. 682990 3261090 140.9032 1.41 SE 7. 680990 3264090 140.2272 2.24 NNW 8. 681990 3261090 137.0213 1 S 9. 680990 3262090 136.3246 1 W 10. 680990 3263090 122.1224 1.41 NW

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Conclusion Maximum pollutant concentrations of PM, SO2 and NOx observed due to proposed expansion for a 24hr-average period have been studied and CO observed due to proposed expansion for a 1hr-average period have been studied.. The total increase in concentrations above baseline status to estimate the percentage increase and summarized in Table 4-17.

Table 4-17 Total Maximum GLCs from the Cummulative Emissions (Point & Line Source)

Pollutant Max. Base Estimated Total Conc. NAAQ % line Conc. Incremental Conc. (µg/m3) standard increase (µg/m3) (µg/m3) (µg/m3) PM 128 2.90 130.9 100 2.27 SO2 22.83 30.52 53.35 80 133.68 NOx 43.71 22.29 66 80 51.00 CO 780 501.68 1281.68 4000 64.32

The incremental concentrations of PM, SO2, NOx and CO are observed to be 2.26%, 133.68%, 51.00% and 64.32% respectively. The total pollutant concentrations of PM, SO2, 3 3 3 3 NOx and CO are 130.89 µg/m , 53.55 µg/m , 66 µg/m and 1281.68 µg/m

4.5.7 Impacts due to Traffic and Transportation

The vehicular movement near project site has been assessed and given in Table 4-18.

Table 4-18 Existing & Proposed Vehicular movement per Peak hour Total Total Existin Propos vehicles PCU Propos PCU after S. Type of g Existin ed after Factors ed project No Vehicle vehicle g PCU vehicle project IRC PCU implemen s s impleme (SP 41) tation ntation 1 2 wheeler 97 72.75 0 0 97 0.75 72.75 2 3 wheelers 11 13.2 0 0 11 1.2 13.2 4 3 wheelers/c 82 82 40 40 122 1 122 ars 4 truck/Lorry 21 77.7 20 74 41 3.7 151.7 agricultural 5 46 230 0 0 46 5 230 tractor light 6 10 14 0 0 10 1.4 14 emission

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Total Total Existin Propos vehicles PCU Propos PCU after S. Type of g Existin ed after Factors ed project No Vehicle vehicle g PCU vehicle project IRC PCU implemen s s impleme (SP 41) tation ntation vehicle

267 489.65 60 114 327 603.65

Based on the traffic for the proposed project, the expected LOS due to the project is given in Table 4-19 Table 4-19 Traffic Volume after Implementation of the Project

Road Volume of Volume V/C LOS Traffic For the Road Capacity Traffic (V) Ratio Category* Classification (C) Free Flow Existing 267 489.65 3600 0.14 “A” Traffic After Free Flow 357 603.65 3600 0.17 “A” implementation Traffic

*LOS categories are A-Free Flow, B- Reasonably Free Flow, C-Stable Flow, D-Approaching unstable flow, E- Unstable flow, F- Forced or breakdown flow

Due to propose project there will be slight increment in the vehicle movement but the level of service (LOS) anticipated will be Free Flow. 4.6 Noise Environment a. Impact

The noise generated during the operational phase can be divided into two categories

A) Stationary source due to heavy duty machineries at the project site such as compressors, DG sets, pumps etc. B) Mobile source corresponding to mainly vehicular traffic for staff mobilization, materials, material transportation, liquid fuel transportation to project site, etc. Vibrations are expected to be generated by various activities associated with the proposed project during operational phase. The impact of vibrations beyond the site would be negligible during normal operation phase. However, the impacts on workers engaged in the plant area would be considerable due to occupational exposure. The proposed fixed major equipment/units such as compressors, pumps, DG sets etc., also generate vibrations during operational phase and may cause exposures to the workers/operators engaged at these units.

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All equipment‟s in the plant produce 40 to 55 dB(A) after control measures and equipment‟s are designed/operated to have a noise level not exceeding 85 to 90 dB(A) as per the requirement of Occupational Health and Safety Administration Standard (OHSAS). In addition, since most of the noise generating equipment would be in closed structures, the noise transmitted outside would be still lower and for any other case of higher noise sufficient safety ear plugs and ear muffs will be provided to the employees. b. Mitigation Measure

 The major noise generating equipment like Compressors, DG sets, pumps etc. will be enclosed in an acoustic enclosure designed for an insertion loss of 25 dB (A) and silencers to other equipment etc.  Major noise generating equipment will be designed with 85 dB (A) ensuring cumulative noise at 1.0 m remains at 85 dB (A).  The occupational noise exposure to the workers in the form of eight hourly time weighted average will be maintained well within the prescribed Occupational Safety and Health Administration (OSHA) standard limits.  Adequate PPE will be provided to the staff exposing to noise risks.  Acoustic silencers will be provided in equipment wherever necessary.  Acoustic design with sound proof glass paneling will be provided for critical operator cabins / control rooms of individual modules as well as central control facilities.  Use of personal protective equipment‟s/devices such as ear-muffs, ear plugs etc. will be strictly enforced for the workers engaged in high noise areas.  Periodic maintenance of the equipment to be used in the developmental works will be carried out. Worn out parts will be replaced and rotating parts will be lubricated to minimize noise emissions.  Implementation of greenbelt for noise attenuation will be undertaken: shrub plantation; landscaping with horticulture; and Tree plantation at vehicle parking areas and along approach roads.  Ambient noise levels will be monitored at regular intervals during operational phase of the project.  Low vibration generating machines/equipment will be selected to meet international standards and foundations will be so designed to minimize vibrations and secured properly.

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 Vibration generating sources and their platforms should be maintained properly to minimize vibrations and related impacts.  Various standards pertaining to vibrations are formulated by statutory bodies like Bureau of Indian Standards (BIS) and Director General of Mines Safety (DGMS), which is being practiced would be continued to mitigate the workers‟ health effects due to vibrations.  Vibration dampers will be provided around the source of generation.  Transportation Management Plan will be prepared and the transportation of construction materials will be planned in line with the same. 4.7 Water Environment

No water will be extracted from ground water sources. The source of water will be from Western Yamuna Canal. The total raw water requirement for existing facility is 3545 m3/hr and for proposed operation phase total requirement will be 3241 m3/hr. On total after expansion 6786m3/hr of water of which the fresh water of 4120 m3/hr will be taken from existing water source (Western Yamuna Canal). Hence there will be no separate permission is required for the proposed projects.

Existing effluent is being treated in existing ETP-1 of capacity 400m3/hr, Combined ETP-2 of capacity 400m3/hr and Combined PX/PTA ETP of capacity 275m3/hr and treated effluent is being used for cooling water and balance effluent of quantity 255m3/hr from PX/PTA ETP is being discharged in Thirana drain with valid approval from HSPCB (No.HSPCB/Consent/:313105620PITCTO7559304 dated 04-05-2020). As vide NGT Order non compliance of the consent order has been observed and actions taken by the refinery has given as below:

S. Recommendations of the Status of Compliance as on 31/12/2020, as No. Joint Committee and verified on 06/01/2021 Members of the Joint Committee 1. To stop illegal discharge into Complied with. the thirana drain. IOCL, Panipat has obtained the permission from the irrigation department for discharge of treated effluenet into the thirana drain, compliance of the condition of the revised Consent to Operate granted by HSPCB, for the discharge of 255 m3/hr of treated effluent from PTA plant in to Thirana drain vide CTO No.

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HSPCB/Consent/313105619/ PITCT O6796558 dtd. 25/7/2019

Further, during inspection of the thirana drain on 14.01.2020, the joint Committee observed that effluent is also being discharged by IOCL Panipat Naphtha Cracker Unit (Another unit of IOCL) through a 36” diameter pipe line. It was observed by the Joint Committee that now this pipe line has been disconnected.

Further, HSPCB has imposed environmental compensation of Rs. 74,10,000/- on the Panipat Naptha Cracker unit for not complying with the condition of consent to operate w.r.t “reuse and recycle” of treated effluent and the prosecution action against the erring officers of the IOCL for the violation of the provisions of Water Act, 1974, has also been initiated. 2. The unit needs to make Under Progress arrangement to cover all open potential sources of It was observed that work on installation of VOC VOCs emissions in effluent recovery has been started in ETP-I and II and is treatment plant and recovery expected to complete by May, as per details shared of VOCs after carrying out by IOCL to the Joint Committee. The status of the study regarding VOC completion as on date is as follows: emitting potential/study of different components of • Civil job: 80% completed. effluent treatment plant. • Mechanical job: Pre-fabrication completed. Site execution in progress. • Major jobs completed: Foundations, Structural Pre- fabrication, Covering of OWS sump, Grit chamber, Flash mixing. • Blower and Vessel delivery: March’21.

Expected date of Commissioning: May, 2021. 3. State Government may Complied with. further get the study done w.r.t to plan for restoration In this regard another Joint Committee of ground water quality based comprising of CPCB, HSPCB and district on the usage schedule of the Magistrate, Panipat has prepared restoration plan ground water in Panipat area, for the restoration of environment and public in consultation with district health and filed the same before the Hon’ble administration, State pollution Tribunal on 07.01.2021 (Annexure 3) control board and other concerned departments, to The Nodal agency (HSPCB) has forwarded the ensure ill effects of Restoration plan prepared by the Joint Committee contaminated ground water to various implementing agencies, for execution of

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on the health of local people. the same The cost of restoration would be finalized after appropriate study for restoration of ground water quality based on the usage schedule of the ground water in Panipat area by State Govt. As proposed in report of CGWB Engineering feasibility of dewatering and refilling of aquifers, as proposed in the report of CGWB, shall be relooked for its environmental implications 4. IOCL may be directed Complied with. to provide safe drinking water D istrict Administration, Panipat to nearby villages affected was approached by IOCL, Panipat to provide the by Drinking Water quality details of the borewells required to supply safe issues till the restoration of drinking water, to nearby villages. Public Health & the ground water quality. Engineering Department (PHED) provided estimate for 4 villages as per details given below :

• Village Singhpura and Village Sithana: Rs. 50.10 lacs disbursed to PHED on 22.09.2020 for work on depositary basis.

Further, Restoration plan w.r.t. provision of safe drinking water to nearby villages, as finalized by the Joint Committee has also been forwarded by Nodal Agency (HSPCB), to District Administration, for execution. 5. Extensive rainwater Complied with. harvesting may be more sustainable solution • to 50 Nos.rain water harvesting pits has been restore the quality of ground provided by IOCL within the premises. water. Panipat on an average receives • Further, additional 34 Nos. rain water harvesting 600mm of rain pits have been constructed and will be made annually. If the same can be operation in the next rainy season. harvested in an efficient way, the same can prove to restore the quality of groundwater in lesser time and cost with no further environment implication.

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6. Green Belt Complied with. Development is another sustainable solution to the The Joint Committee has observed plantation Environmental Issues over the done by IOCL at various locations. decades. Yearly targets and monitoring of them can give IOCL has completed plantation of 15000 Nos. of long term sustainable trees. solutions. The action to be taken by the IOCL should be IOCL has also deposited Rs.7.18 Crores with monitored quarterly, forest quantitatively and department for the plantation qualitatively by the of 2,00,000 Nos of trees on 500 District Administration and acres of land at Village Gwalra, State Pollution Control Distirct Panipat, out of which 35000/- no of Board. trees have been planted.

Restoration plan prepared by the Joint Committee in this regard, has also been forwarded to the Forest Department by the Nodal Agency (HSPCB), for execution. 7. Water stored in Partially complied with and the multiple lagoons/ponds remaining work is under progress. inside the plant should be treated and recycled before ▪ Storm Water Pond C has been emptied out. lining the lagoons to make Finishing work is under progress. Finishing work these lagoons impervious as was going during visit of the Joint Committee and mandated i n C O T d a t e d expected to be finished by the end of February, 2 5 - 0 7 2 0 1 9 . 2021. Thereafter, the work for Storm Water Pond B and Pond A shall be started and will be finished before rainy season as indicated by the representative of the industry. 8. No untreated water will be Complied with. stored in the lagoons/ponds except in the tanks, which are Polishing Pond A and B have been emptied out components of effluent and no untreated waste water is routed to these treatment plant. " polishing ponds. Concrete Lining of polishing Pond has been done and finishing work was going on during the Visit of Joint Committee.

Provision of a Covered Tank (No.53) having storage capacity of 20000 KL has been made, for storage of PTA untreated effluent during Caustic wash, which will be processed during normal operation. 9. The State PCB has given The IOCL has placed order for ZLD pilot plant revised consent,subject to on returnable basis vide No. 26790156 dated certain conditions, but even 28/1/2021, to establish technical feasibility and

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in the latest report the deciding design parameters for the full scale ZLD State PCB has suggested Plant. further remedial issues.

Wastewater will be segregated into sewage and effluent. Sewage and effluent will be treated in existing combined ETP.

For proposed, a new ETP will be constructed with ZLD for complete reuse of the water.

4.7.1 Impacts On Surface Water Bodies

PTA-ETP outlet water is discharging in Thirana Drain which have a valid CTO- No.HSPCB/Consent/313105620PITCTO7559304 dated 04.05.2020 valid till 30.09.2021 for discharge quantity of 255m3/hr. The logbook of daily discharge into Thirana Drain and the treated effluent test report from NABL & MoEF accredited lab- M/s. Nitya Laboratories is attached as Annexure 28.

4.7.2 Mitigation measures on Ground Water

Though the proposed development will not draw Groundwater, the following measures proposed as a part of development to improve the ground water scenario and also to ensure that ground water is not contaminated.

Strategic plans such as implementing the following structures for rain water harvesting and groundwater recharging purposes in project site will be adhered.

 Recharge pits  Only roof-top rain water harvesting  Monitoring of water quality and groundwater level variations in the project site. Due to discharge in Thirana drain, there is higher values of BOD, COD and SAR (NEERI Report 2020) and therefore secondary effects are possible in nearby villages water resources.

4.7.3 Impacts Due to Wastewater Generation The source of wastewater generation from the project is as follows:  Industrial wastewater/effluent  Cooling water blow down  Domestic Sewage  Equipment cleaning and floor washings, etc.

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The untreated wastewater if discharged into nearby surface water may affect the surface water and/or if disposed off on land without treatment may pollute the ground and surface water.

4.7.4 Mitigation Measures to Wastewater Generation Various mitigation measures are proposed to be adopted to minimize the impact if any on the water environment due to the wastewater/runoff generation during the operation phase of the project.  Institutional arrangement for monitoring of water pollution.  Corrective and preventive measures if any contamination happens.  Monitoring should ensure early determination of any threats to water resources in terms of contamination.  If contaminated, proper expertise will be brought to schematize the various recharge mechanism to reduce or nullify the impact effects. 4.8 Effluent Water Quality, Quantity and Treatment Method a. Existing

Approx. 1030 m3/hr of effluent and 235 m3/hr of sewage is generated in the existing facility which is reused back in RO plant and Cooling tower. The quantity of 775 m3/hr is treated in ETP-1 and 2 and being completely reused in RO plant and Cooling tower. Remaining 255m3/hr is treated in the PTA-ETP and Treated effluent from PTA ETP is discharged in Thirana drain (vide permission- No.HSPCB/Consent/:313105620PITCTO7559304 dated 04- 05-2020). The 235 m3/hr of sewage is generated in which 125 m3/hr is sent to horticulture and balance is sent to ETP for treatment.

b. Proposed

Due to the proposed expansion Approx. 362 m3/hr of effluent and 9 m3/hr of sewage are generated in the existing facility. The Effluent of 360m3/hr is reused back for process steam generation, 2m3/hr of sludge is generated which will be disposed off in scientific manner and sewage of 9 m3/hr is reused back for Green Belt. Rejects of 48 m3/hr effluents from RO/DM is directed to MEE and to ATFD, finally remaining 4 m3/hr of effluent as salt from ATFD is discharged to Disposal Facilities.

Zero liquid discharge is practiced for existing and proposed effluent generated. Hence, the impacts of effluent discharge on water bodies are avoided.

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Panipat Refinery has developed a Modernised effluent treatment plant (ETP) for treatment of process wastewater, generated from various units of the refinery as well as Township.

The treatment scheme is broadly divided into five sections as follows:

a) Physico-Chemical treatment, for removal of Hydrocarbons, Sulphides and Total suspended solids. b) Biological treatment system incorporating activated sludge system for oxidizing the organic matters. c) Tertiary treatment system comprising of pressure sand filters and activated carbon filters for removal of TSS, Odour, Colour and Organics. d) Sludge processing section comprising of Oily & Chemical Sludge Processing and disposal as a solid waste biodegradable material. e) Chemical dosing system comprising of storage facilities of various chemicals and preparations of chemical solutions of standard concentration for injection at various stages during effluent treatment. The Block Flow Diagram of Effluent Treatment Plant is shown in Figure 4-13.

ETP is envisaged in the Project to treat the liquid effluents generated from the Process and other units of P-25 project. Treated effluent from the ETP shall be routed to a RO-DM Plant for generating DM quality Water. The new ETP shall consist of treatment facilities/chains/systems along with associated facilities for treatment of effluent streams: The capacity of ETP shall be 450 m3/hr.

4.8.1 Process Description

The principal contaminants present in these effluent streams are mainly oil (free and emulsified), suspended solids, phenols, sulphides, ammonia and organic matter contributing to BOD &COD. The OWS feed effluent received by pumping at the Effluent Treatment Plant battery limit shall be stored and equalized in OWS Tank and then treated in API oil separators for Free oil removal. The Stripped Sour Water shall be stored in Stripped Sour Water Tanks and then mixed with OWS Stream at the inlet of TPI and treated in TPI oil separators for free oil & Suspended solids removal. The effluent after free oil removal in API and Tilted Plate Interceptor (TPI) separator shall be fed to of Dissolved Air Floatation unit for removal of emulsified oil.

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The effluents after oil removal shall be stored in Sequential Batch Reactor (SBR) Feed Tank. The effluent from SBR feed tank is routed to Walnut shell filter for further Oil & TSS removal and then biologically treated in 3 basin SBR system. The treated water from SBR unit shall be processed in the polishing section consisting of High Rate Solid Contact Clarifier (HRSCC), Dual Media Filters (DMF) and Activated Carbon Filters (ACFs). The l treated effluent from ACF shall meet MINAS standards and further routed to RODM recycle plant for DM production. No Effluent is disposed outside the refinery. The contaminated rain water stream shall be treated in a CRWS treatment chain of consisting of TPI oil separator for oil removal, DMF and ACF for final polishing before disposal/routing to storm water drain/horticulture/RO-DMP feed. Spent Caustic received in the ETP from the process units shall be equalised in the holdup tanks and then processed at a control rate. The spent caustic effluent shall be treated at controlled rate in a chemical oxidation section with H2O2 / Ozone in presence of FeSO4 as catalyst for removal of contaminants such as Sulphides, Phenols, COD, BOD, etc. The treated caustic shall be sent to the ZLD Plant with a provision of final treatment with the OWS effluent in the ETP.

4.8.2 Sanitary Sewage Treatment A Membrane Bio-Reactor (MBR) based package sanitary sewage treatment plant has been envisaged to treat Sanitary Effluent to remove mainly total suspended solids, COD and BOD.

4.8.3 VOC Control System Handling of Volatile Organic Compounds (VOC) in terms of their collection from oil handling units, routing to a Centralized VOC handling facilities and treatment in package unit (consisting of activated carbon based adsorption) to meet the VOC emission norms proposed by CPCB.

4.8.4 Slop & Sludge Handling

Slop oil shall be generated mainly form OWS tank, API, TPI. This slop oil shall be collected in wet slop oil sump and then pumped to wet slop oil tan. After draining of water from slop oil tank bottom, the dry slop oil is transferred to refinery heavy slop oil tanks.

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Separate Sludge handling facilities are provided for each Oily, Chemical and Bio sludge produced from ETP. Supernatant from each sludge handling section shall be rerouted to OWS Tank for recycle.

The Oily and Chemical Sludge after dewatering shall be disposed to the Secured Landfill.

The dewatered bio sludge from the ETP shall be utilized as manure in the green belt of the complex.

Unloading and handling of H2O2 and Methanol and handling of various other chemicals required to be dosed at various stages are included in ETP with all required safety provisions. The existing characteristics of the treated effluent are presented in the Table 4-20. The ETP block diagram in given in Figure 4-13

Table 4-20 Characteristics of the treated effluent

S. No. Parameter units ETP-1 ETP-2 PTA-ETP 1 PH -- 6-8.5 6-8.5 6.5-8.5 2 Oil mg/L 5.0 5.0 NA 3 COD mg/L 125.0 125.0 250 4 BOD mg/L 15.0 15.0 30 5 TSS mg/L 20.0 20.0 100 6 Phenol mg/L 0.35 0.35 1.0 7 Sulfide mg/L 0.5 0.5 2.0 8 Cyanide mg/L 0.2 0.2 0.20

Figure 4-13 Existing & Proposed ETP block diagram

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4.9 Land Environment

4.9.1 Potential Impact Due to Location The proposed expansion from existing 15MMTPA to 25MMTPA is proposed within the IOCL existing facility, there will be no additional land acquisition and resettlement or Rehabilitation required. Therefore, there will not be any direct impacts.

4.9.2 Impacts Due to Changes in Land Use Pattern

One of the factor that is usually considered as a major impact from any project is the land use change. But since the proposed expansion will be established within the existing IOCL site, no land use change is foreseen, as the current land use is that of industrial.

4.9.3 Mitigation Measures

The following mitigation measures may be explored:

 Periodic maintenance and check of wastewater conveyance pipelines  Attempt to restore by replacing a part or putting together the torn or broken parts of the conveyance pipeline in case of any leakage is detected.  Necessary preventive measures for spillage from pipelines, such as surface RCC channels along the pipelines shall be adopted.  Treated wastewater quality shall be ensured as per standards before using internal use. 4.10 Solid Waste Management

4.10.1 Impact Due to Solid Waste Generation During operation phase, various types of solid waste are likely to be generated which can be broadly categorized as Hazardous Waste and Non-hazardous Waste. Further, the generated solid waste generation may include Biodegradable, Recyclable and Inert compounds. The details of solid waste generation and its management proposed are discussed in Chapter 2, Section 2.15. If the solid waste generated is not properly managed and disposed in unauthorized manner, it will impact on soil quality, groundwater and air quality. 4.10.2 RO Rejects Treatment Facility The reject stream from the RO system in the RODM plant shall be routed to the ZLD feed storage tank. The ZLD Feed tank, with storage capacity equivalent to ~ 24 hours of design feed flow shall homogenize the feed and then the same shall be pumped at a controlled rate

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for further Processing. Pre-treatment of the feed stream as required prior to the evaporator Unit. Treatment Facilities for Hardness and Silica reduction from the feed water and making it acceptable for processing in the Evaporator and Dryer units of the ZLDP shall be provided. The feed to the evaporator unit from the ZLD feed tank shall be through the ZLD feed pumps.

4.10.3 Evaporation Section Feed at controlled rate (controlled by a flow control valve) shall pass through pre-heaters, calandrias and vapour separators of various effects. The evaporation takes place under vacuum, which shall be maintained mainly by vacuum system. Steam shall be supplied as a heating medium through thermal vapour recompression (TVR) to the 1st effect jacket. The concentrated product at the desired concentration shall continuously be taken out from the system.Multiple effects (minimum FOUR EFFECTS for good steam economy and maximum condensate recovery) falling film cum forced circulation evaporators with thermal vapour recompression (TVR) system are envisaged The unit shall be designed for operation under vacuum. The necessary flash vessels, as require, shall be provided so as to recover maximum heat from the feed purge and condensates and at the same time meet the temperature requirements of these streams at the battery limit of the plant. The vapours shall be condensed in a surface condenser or any other suitable system.

4.10.4 Dryer Section The concentrated feed shall then be passed through a Dryer Unit with forced circulation type or falling film type (ATFD) so as to recover maximum quantity of distillate / condensate from the feed and salts as a dry product shall be provided. The condensate/ Distillate shall be recycled back as treated Water and the solids/salts shall be disposed of as solids or crystals (having moisture content less than 6%) from the plant. The solids shall be discharged to a dumpster for removal to landfill. At least two Dumpster units of adequate size/volume shall be provided. Solid Waste generated from ETP. -Approximately 15.3 m3/day of solids are produced and shall be disposed to secured landfill. Solid Waste generated from RO-Recycle plant- Approximately 69 tons/day (This includes salts from ZLD) of solids are produced and shall be disposed to secured landfill. Strict guidelines will be put in place in order to manage the solid waste generation during the operational phase of the development. The main goals of the guidelines will be to ensure

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adopting recycling techniques and encouraging sorting of solid waste at source into organic and inorganic wastes..

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CHAPTER 5 ANALYSIS OF ALTERNATIVES

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5 ANALYSIS OF ALTERNATIVES 5.1 Introduction

Indian Oil Corporation Limited (IOCL), Panipat Refinery proposes Capacity Expansion from existing 15 MMTPA to 25 MMTPA.

The range of alternatives selected for the purpose of analysis includes:

 Site alternative  Water supply alternative  Technology alternative 5.2 Site Alternative

Panipat Refinery Indian Oils Major Refinery has a design crude processing capacity of 15MMTPA. Panipat refinery owned a land of 491.6 Acres. Since the proposed project is expansion within the existing facility there is no new site/ alternative sites considered.

5.3 Water Supply Alternative

After expansion, the total fresh water requirement of 4120 m3/hr for the refinery is met from water from Western Yamuna Canal. Since the proposed project uses the existing water source there is no alternative water supply considered

5.4 Technology Alternative

There are several technology for proposes expansion project. Technology is selected on the basis of specified guide line.

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Existing Technology

S. No. Unit Process Licensor 1 Atmospheric and vacuum distillation unit (AVU-I) EIL 2 Continuous Catalytic Reforming Unit (CCRU) Axens 3 Resid Fluidised Catalytic Cracking Unit (RFCCU) SWEC 4 Hydrogen Generation Unit (HGU) HTAS 5 Once Through Hydro Cracking Unit (OHCU) UOP 6 Diesel Desulphurisation Unit (DHDS) IFP 7 Visbreaker Unit (VBU) EIL 8 Merox UOP 9 Atmospheric and vacuum distillation unit (AVU-II) EIL 10 Delayed Cocker Unit (DCU) ABB, LUMMUS 11 Hydrogen Generation Unit (HGU) HTAS 12 Diesel Hydro treating Unit (DHDT) AXEN 13 Hydro Cracking Unit(HCU) UOP 14 Sulphur Recovery Unit Black & Veatch, USA

Proposed Technology

Sl.No. UNIT Licensors 1 AVU EIL 2 SR LPG Treater IOCL R&D 3 VGO HYDROTREATER UOP 4 DIESEL HYDROTREATER SHELL 5 PRU EIL 6 SRU Worly Parsons 7 RHCU with 75% Conversion AXENS 8 INDMAX IOCL+ABB LUMMUS 9 LPG Splitter EIL 10 NHT UOP 11 CCR UOP 12 ISOM UOP 13 SARU MEC (DuPont) 14 SWS EIL 15 ARU EIL 16 CDW Chevron

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CHAPTER 6 ENVIRONMENTAL MONITORING PROGRAM

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6 ENVIRONMENTAL MONITORING PROGRAM 6.1 Introduction

Environmental monitoring is an essential tool for sustainable development & ensuring effective implementation of environmental management plan & mitigation measures adopted. Environmental monitoring will undertake primarily to determine the environmental effects of human activities and secondarily to increase understanding of cause – effect relationships between human activity and environmental change. Environment monitoring is a repetitive & systematic measurement of the characteristics of environmental components to test specific hypotheses of the effect of human activities on the environment. Environmental monitoring program enables the proponent to identify the deviation of environmental quality due to the proposed project activities.

6.2 Environmental Effects Monitoring in EIA

Environmental effects monitoring programs provide the necessary information to:  Verify the accuracy of EIA predictions;  Determine the effectiveness of measures to mitigate adverse effects of projects on the environment. Environmental monitoring program is a vital process of any management plan of the development project. This helps in signalling the potential problems resulting from the proposed project and will allow for prompt implementation of effective corrective measures. The environmental monitoring will be required for the construction and operational phases. The main objectives of environmental monitoring area:

i. To assess the changes in environmental conditions, ii. To monitor the effective implementation of mitigation measures, iii. Warn significant deteriorations in environmental quality for further prevention action. iv. In order to meet the above objectives, the following parameters need to be monitored:  Afforestation,  Water Quality and Public Health,  Air and Noise quality,  Soil Conservation, and  Sanitation and Waste Disposal

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6.2.1 Post Project Environment Monitoring Program

The summarized form of post monitoring details is presented in the following Table 6-1. Table 6-1 Post Project Environmental Monitoring Plan S. Particulars Frequency of Parameters for Monitoring No monitoring 1. Air pollution monitoring Ambient air quality within Continuous PM, SOX, NOX, CO, HC, VOC the premises (CAAQMS) Ambient air quality within Twice in week All 12 parameters as given in the premises NAAQS Ambient air quality at 1 Twice in week All 12 parameters as given in location in Prevalent Down NAAQS Wind Direction Ambient air quality at 1 Twice in week All 12 parameters as given in location in Up Wind NAAQS Direction Stack monitoring Once in two PM, SOX, NOX, CO months for all the stacks and monthly for SRU as per CPCB norms 2. Noise monitoring At four locations within the Once in a month Noise Levels in dB(A) premises

3. Ground water quality monitoring Three locations at site and Quarterly Physicochemical properties, two location outside site Heavy metals 4. Soil Quality monitoring Two locations at site and two Half yearly Physicochemical properties, location outside site Nutrients, Heavy metals 5. Effluent Quality Monitoring Inlet and outlet of ETP Once a month As per MINAS Standard Inlet and out let of STP No STP Sewage is Biologically treated as a part of the CETP and standards are met. 6. Work place Monitoring Quarterly Noise, VOC, Lux levels

6.2.2 Monitoring Methodologies

Monitoring of environmental samples shall be done as per the guidelines provide by MoEF&CC/CPCB/SPCB-Haryana. The methods conducted or applied shall be approved or sanctioned by the any recognized body or authority i.e. MoEF&CC/CPCB/SPCB-Haryana.

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6.3 Reporting & Documentation

All the necessary reports and documents shall be prepared complying with the statutory rules & regulations. Proper and due care shall be taken to adhere to the laid down rules and regulation by the government. Regular and periodic record shall be kept in order to ensure easier, comparable and brisk review and projection of past, present and future performances. Also, the management shall ensure to prepare separate records for water, wastewater, solid waste, air, emission, regularly and periodically in order to provide better and smooth vigilance.

The management shall look into the fact that as soon as the preparation of reports gets over it shall be forwarded to the concerned authority with due care for the purpose of reviewing. Adhering to the rules and regulations the management shall ensure that the outcome of the reports and the conclusions been drawn shall be prepared as per the laid down regulations and procedures. No breach of any convention shall be availed.

These reports/documents shall be regularly and periodically reviewed and any changes/discrepancies found in mitigation measures/operation/management/technology shall be brought into notice instantaneously and all possible corrective actions shall be taken to match the discrepancies been witnessed.

6.4 Budget for Environmental Monitoring Plan

Particulars and frequency of environmental Monitoring is given in Table 6-2.

Table 6-2Budgetary allocation for Environmental Monitoring S. No Particulars Frequency of monitoring Cost in Lakhs 1. Air pollution monitoring Stack monitoring Monthly. Online analyzers have also been installed in 5 stacks. Ambient Monitoring Monthly. within as well as 2 outside 2. Noise monitoring At four locations Monthly within the premises 4 3. Ground water quality monitoring 3 locations inside, 2 Quarterly

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S. No Particulars Frequency of monitoring Cost in Lakhs outside Refinery 4. Soil Quality monitoring 4 locations Half yearly 5. Effluent Quality Monitoring Inlet and outlet of Daily 2 ETP/ OSW 6. VOC monitoring Monthly 2 Total 15

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CHAPTER 7 ADDITIONAL STUDIES

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7 ADDITIONAL STUDIES 7.1 Public Consultation

The project is falling under „A‟ category as per EIA Notification 2006 and Public Hearing is mandatory as per ToR obtained. Hence draft EIA report has been prepared as per the No: J- 11011/177/2016-IA II(I) dated 24th August 2018 and submitted for Public Hearing. Public Hearing advertisement was published in The Triban and newspapers on 3.03.2021.

Public hearing was conducted by HSPCB on 06-04-2021 at 12.30pm at at near the project site Baholi village, Post office Panipat-132140 and Sh. Dharmendrer Singh, I.A.S, Deputy Commisioner, Panipat presided over the meeting along with Sri Kamaljit Singh, Regional officer, HSPCB Panipat. Newspaper Publication details and Public Hearing minutes are enclosed as Annexure 24. The newspaper advertisement details are shown in Figure 7-1 & Figure 7-2. Public Hearing photographs are shown in Figure 7-3. The total fund allotted for the commitment made on the requirement of public during public hearing is INR 45.51Cr

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Figure 7-1 Public Hearing Advertisements (Hindi)

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Figure 7-2 Public Hearing Advertisements (English)

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Figure 7-3 Public Hearing photographs.

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7.1.1 Reply to the issues raised by the public during Public Hearing on 06.04.2021 Commitment on S.No Issue Raised by Issue Reply by IOCL Panipat fund allocation

1 Sh. Satpal Singh He suggested for the development Project proponent replied that developmental job is - R/o Villager- of the nearby village through CSR being done and will be continued in future also. The Sithana activities. allocation of CSR fund depends upon the profit margin of the company and varies every year. Hence, the activities are done as per availability of funds after discussion with the punchayats. 2 Sh. Satpal Singh He suggested that employment Project proponent replied that PRPC is committed to - R/o Villager- should be given to the people by appreciation of merit. Accordingly the PRPC Sithana the PRPC. provides prizes to the meritorious students of the nearby villages so as to promote their aspirations and facilitate development of skill locally. The recruitment process is governed as per guidelines of the corporation and the same to followed meticulously. 3 Sh. Satpal Singh He raised his concerned that crops Project proponent replied that whole green belt area An amount of Rs. 9.3 R/o Villager- are being damaged by neel gaye will be enclosed by brick wall soon.- Cr, is allocated for Sithana due to the green belt area of the brick wall PRPC is not enclosed from the crop construction and field side. implemented within the year March 2023 4 Sh. Satpal Singh He questioned that why Pir dargah Project proponent replied that the holy place is in the An amount of Rs.5 R/o Villager- has not been opened public or re- restricted area. Keeping in view the holy sentiments Lakhs is allocated for Sithana located. of the nearby peoples appropriate action for creating gallery type relocation shall be taken on discussion with District way and

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Commitment on S.No Issue Raised by Issue Reply by IOCL Panipat fund allocation

Administration implemented within the FY-2022-23 Deputy Commissioner Panipat directed that any gallery type way should be given to the public to reach to the Holy Palace because public sentiments cannot be controlled or bounded due to security reasons. Proper security arrangements as per requirements should be ensured. 5 Sh. BalwanSingh He questioned that labor living on Project proponent replied that labor is staying in An amount of Rs.36 Surpanch rent in nearby villages spread rented house in villages and therefore must be using Cr. is allocated for Villager- Kutana garbage and other kind of waste in the facilities whatever is available in respective labour quarters with the residential area of the villages villages. More over in the proposed project the necessary More over previously a company company will make labor quarters and will make the arrangements for the name Simplex has run after money necessary arrangements for the labor waste. However waste generated from of the local contractors from the simplex company has not taken any money from the residendial area refinery. the refinery and the information given to you is false. of labours and implemented within the year December 2022. 6 Sh. Balwan Singh He questioned that scholarship has Project proponent replied that Due to the - Surpanch not been given to the students of unprecedented COVID-19 Pandemic the operations Villager- Kutana the Kutana village in the FY 20-21. and finances of all the industries have been adversely impacted. At CSR activities are linked with profit of the corporation. Hence the CSR fund varies accordingly

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Commitment on S.No Issue Raised by Issue Reply by IOCL Panipat fund allocation

7 Sh. Balwan Singh He questioned that 5 rooms of Project proponent replied that PRPC is a committed An amount of Rs.16 Surpanch school building has not been to wellbeing and education of the villagers in the Lakhs is allocated for Villager- Kutana constructed as promise make by periphery. One school is being make in panipat for school building IOCL in my village. disabled children, which is unique in its type. It will construction for be done, for public school also. PRPC is constructing GovtSen Sec school, many facilities and therefore additional classroom , if Kutana and required. PRPC will extend necessary helps. implemented within the year August 2022. 8 Sh. Vikram He suggested that Gurudware Project proponent replied that the Holy place will - Singh R/O village situated near to the refinery come in the restricted area after expansion. Baholi premises should be to other place. Respecting the holy sentiments of the public. Appropriate action for relocation of Gurudwara shall be taken on discussion with District administration. 9 Sh. Vikram He suggested that crop yield of the Deputy commissioner Panipat replied that study shall This work will be Singh R/O village area has been decreased and the be conducted with the help of Agriculture carried out by the Baholi study of the same should be Department and KrishiVigyan Kendra. Moreover we Govt. administration conducted by the district have also prepared a restoration plan for the by using their own administration. Environment and Public health for the area around resources. refinery. There is a provision for the supply of the After completion of safe drinking water to the villages situated around the study, IOCL will the refinery and to improve the health facility in the take up the matter as area. All the suggestions given in the public hearing the administration will be considered and taken care. will dictate.

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Commitment on S.No Issue Raised by Issue Reply by IOCL Panipat fund allocation

10 Sh. Santosh Singh He questioned that why all houses Project proponent replied that the Limited number of - R/O village of the village baholi had not been vehicles is required in the PRPC. Hence all vehicles Baholi included for providing vehicle on cannot be hired presently total 83 vehicles have been service in the PRPC. hired based on the proposal of the gram panchayats after obtaining consensus of the villagers. 11 Sh. Jasbir Singh He questioned that agreement made Project proponent replied that PRPC has honored all - Panchayatsamiti in 1982 &1994 should be read it the agreements with all the stakeholders as per the Member village out again and conditions to be feasibility. Baholi complied accordingly. 12 Sh. NainpalRana He suggested that Refinery and Deputy Commissioner Panipat ensured that all the - Ex Sarpanch, District Administration along with suggestions and complaints have been considered village Dadlana Environment Department should and required action will be taken by all the take care of the issues of public concerned departments as per Law. residing near to the vicinity of the Refinery like quality of Environment around the Refinery safe guard of the trees planted proper arrangement of the rainy water, health facilities availability in the area relocation of the basti‟s situated near to the refinery wall.

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7.2 Risk Assessment Risk Assessment is performed for the instrument leaks and failure for different scenarios is incorporated as Annexure 13.

Material Safety Data Sheet is enclosed in Annexure 20.and the Disaster Management Plan is enclosed in Annexure 19. The certified post EC compliance is provided in Annexure 4.

7.3 Applicability of Environmental Clearance

List of latest Existing Environmental Clearance obtained by MoEF & CC:

Date of Status of S. No MoEF&CC File No Units issue Project J-11011/27/91-IA- Setting up Grassroot 1 16-07-1992 Commissioned II(I) refinery Expansion of Refinery J-11011/60/2000-IA- 2 from 6 MMTPA to 12 09-04-2001 Commissioned II MMTPA J-11011/52/2000-IA- Integrated PX & PTA 3 30-04-2001 Commissioned II project J-11011/9/2001-IA- 4 MS quality upgradation 06-12-2001 Commissioned II(I) J-11011/52/2000-IA- Modification in Plant 5 20-01-2003 Commissioned II(I) Layout Expansion of Refinery J-11011/7/2004-IA- 6 from 12 MMTPA to 15 09-08-2004 Commissioned II(I) MMTPA BS-VI upgradation and J-11011/177/2016-IA- PX/PTA Plant, 7 26-03-2018 Commissioned II(I) Petrochemical Complex expansion EC for Panipat Refinery J-11011/177/2016-IA 8 Capacity Expansion from - Applied Now II(I) 15 MMTPA to 25 MMTPA

EC compliance was submitted to Regional Office, MoEF&CC. The compliance of EC recommendations was certified. Certified copy is enclosed in Annexure 4.

7.4 Consent for Existing Operation

The facility is under operation with PCB consent obtained vide:No.HSPCB/Consent/: 313105620PITCTO7559304, valid up to 30th September 2021.

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7.5 ToR Issued by MoEF&CC

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7.6 Copy of Standard ToR

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CHAPTER 8 PROJECT BENEFITS

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8 PROJECT BENEFITS 8.1 Project Benefits

 Meeting the demand for distillate products & Petrochemicals needs nationwide and particularly in the Northern Capital Region (NCR).  It will also give the Opportunity to increase and improve refining margin.  Conversion of low value, low octane naphtha streams into high value high octane reformate.  The plant will require approx. 300 permanent manpower for operation and maintenance of the proposed plant. Besides, a contractual worker also will be required for regular maintenance works in the plant.  Since the project is big in nature it will affect the socio-economic status of the region due to capital investment. There will be cascading effects on economic status and avenues in the area as well as in the buffer zone where in, there will be a growth in employment scenario.

 People at large in the nearby villages will get advantage by getting more employment opportunities and getting better living standards.

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CHAPTER 9 ENVIRONMENTAL COST BENEFIT ANALYSIS

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9 ENVIRONMENTAL COST BENEFIT ANALYSIS

This Chapter is not in Scoping Stage

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CHAPTER 10 ENVIRONMENTAL MANAGEMENT PLAN

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10 ENVIRONMENTAL MANAGEMENT PLAN

10.1 Introduction

This Environmental Management Plan (EMP) for Indian Oil Corporation Limited identifies the principles, procedures and methods that will be used to control and minimize the environmental impacts of the proposed construction and operational activities associated with the revamp project. It is intended to ensure that commitments made by IOCL to minimize project related environmental and social impacts are upheld throughout all project phases.

As part of our ongoing commitment to excellence in environmental and social performance we will ensure the following:

 Fulfill all environmental conditions associated with project approvals.  Develop, promote and foster a shared sense of responsibility for environmental and performance of the project.  Promote environmental awareness and understanding among employees and contractors through training, identification of roles and responsibilities towards environmental management and linking project performance to overall environmental performance.  Monitor environmental performance throughout the project and implement an adaptive management approach to continuous improvement and to meet the future regulations.

10.2 Objectives of EMP

 To suggest the formation of a core group (Environment Management Cell) responsible for implementation of environmental control & protective measures as well as monitoring of such implementation.  To ensure project components are compliant with all laws and approval conditions  Continue baseline monitoring  Facilitate a continual review of post construction and operation activities.  To suggest preventive and mitigation measures to minimize adverse impact and to maximize beneficial impacts like  Preparation of afforestation or Greenbelt Development scheme.  Preparation of rain water harvesting scheme and energy conservation actions

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 To prepare a capital cost estimate and annual recurring cost for Environmental Management Plan.  To prepare a detailed action plan for implementation of mitigation measures.  Measure the effectiveness and success of proposed mitigation measures

10.3 EMP Structure and Organization

This EMP is designed as an overriding document in a hierarchy of control plans, and sets out the overarching framework of environmental management principles that will be applied to the project during preconstruction, construction and operation phase of the project.

The EMP contains guiding environmental principles and procedures for communication, reporting, training, monitoring and plan review to which all staff, contractors and subcontractors are required to comply with throughout the preconstruction, construction and operation phases of the proposed projects. Prism policy of EHS in Panipat Refinery is given in Figure 10-4.

Figure 10-1 Typical HSE Department Organogram The EMP should also be considered as an overall framework document that establishes the terms of reference for all project environmental and social sub-plans including the following:

 Environmental Supervision Plan (construction);  Environmental Monitoring Plan (construction and operation); and

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 Social and Health Management Plan (construction and operation).

10.4 EMP/EHS Roles and Responsibilities

This section describes the organizational structure and responsibilities for implementation of the EMP as shown in Table 10-1.

Table 10-1 Responsibility for EMP/EHS Implementation

S.No Organization Responsibility 1 Head, HSE  Overall responsibility for environmental performance M/s IOCL  Decision-maker on applicable policies.  Overall supervisory role during the construction phase  Overall responsibility for EMP implementation during the operating phase  Responsible for changes to the EMP as part of an adaptive approach to environmental and social management 2 HOD, HSE  Develop an environmental unit, headed by the Project M/s IOCL Environmental Officer to implement EMP responsibilities.  Oversight, implementation, monitoring and compliance of the EMP and any approval conditions, including construction supervision and performance of all staff, contractors and all subcontractors  Review of EMP performance and implementation of correction action, or stop work procedures, in the event of breaches of EMP conditions, that may lead to serious impacts on local communities, or affect the reputation of the project.  Ensuring effective communication and dissemination of the content and requirements of the EMP to contractors and subcontractors  Assisting the contractor with implementation of EMP sub-plans  Ensuring compliance to all project social commitments, including implementation of corporate social responsibility.  Report environmental performance of the project directly to MoEF&CC  Report on environmental performance also to other government regulators as required. 3 Manager/AM/S  Implementation of the Environmental Monitoring Plan during O, HSE construction and operation. Supervising  Supervision of contractor performance of implementation of Engineer the Construction.  Reporting any incidents or non-compliance with the EMP to the PCB.

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S.No Organization Responsibility  Ensuring adequate training and education of all staff involved in environmental supervision.  Making recommendations to the MoEF&CC regarding EMP performance as part of an overall commitment to continuous improvement. 4 Construction  Preparation and implementation of the Construction Contractor Management Plan  Prepare and maintain records and all required reporting data as stipulated by the EMP, for submission to the Supervising Engineer.  Ensure that all construction personnel and subcontractors are informed of the intent of the EMP and are made aware of the required measures for environmental and social compliance and performance  During construction, maintain traffic safety along access roads, with special emphasis on high trafficked areas 5 Independent  Report to MoEF&CC on project compliance with Environmental environmental and social commitments in the EMP, EIA and Monitoring other applicable standards. Consultant

10.5 Environmental Management Plan for Construction Phase

Environmental monitoring will be done during construction. The focus of monitoring during the construction phase will be to implement systematic observations to periodically measure the success of proposed mitigation measures and continue baseline data collection. The majority of construction monitoring shall be done visually and verified by the Construction Supervisor. Specific aspects to be addressed during construction include:

 Air quality  Noise  Water quality and water resources  Solid waste  Land environment

10.5.1 Air Quality

There will be major construction activities for the project, civil work like foundation for new vessels and supporting infrastructure for the new machineries will be carried out. During construction activities, dust emission and emissions from the movement of vehicles and

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construction activity is expected. However, following measures will be taken to reduce / contain such emissions.

 Water will be sprinkled on inner roads to prevent re-suspension of dust into ambient air due to movement of heavy vehicles etc.  Roads shall be kept free from mud, debris and other obstacles.  Separate civil construction material storage yard will be created within the site and it will be enclosed.  Cement bags will be separately stored under cover in bales. Sand will be stacked under tarpaulin cover.  Transport vehicles and construction equipment‟s/ machineries will be properly maintained to reduce air emissions.  All construction workers will be provided appropriate PPEs like dust mask, ear plug, helmet, safety belt etc. and it will be mandatory for them to wear while entering the site itself.  Increase signage and speed limit postings

10.5.2 Noise Environment

Following measures are proposed during construction period to mitigate adverse impacts of noise:

 Construction activities will be done on round the clock basis.  All machineries to be used for construction purpose will be of highest standard of reputed make and compliance of noise pollution control norms by this equipment‟s will be emphasized.  All construction workers working in high noise areas will be provided appropriate PPEs like ear muffs and made to wear them during working hours.

10.5.3 Water Quality and Water Resources

 Since the construction workers are hired from nearby villages there will be no housing facility at the site for construction workers and hence lesser water requirement  Proper and sufficient sanitary facility will be created at the site in the form of Toilets & existing ETP will be used for treatment of sewage generated.

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10.5.4 Solid Waste

 Main solid waste generation during construction phase will be construction debris like rubble, brick bats, debris, steel scrap, wooden scrap, sand, gravel etc. However, these materials are inert in nature and will not result into leaching of any substance or its constituent.  These materials will be carefully sorted and will be used within premises for filling of low lying areas.  Wooden scrap, steel scrap will be given to authorized scrap dealers.  On completion of civil work, all debris etc. will be completely removed from site to avoid any incompatibility with future use.  All the wastes will be stored at a designated site within the premises to prevent scattered discharge on land.

10.5.5 Land Environment

 Top soil layers shall be stored for reclamation and re-vegetation and reforestation at approved locations.  Existing storm water drainage facility will be used for disposal of storm water.

10.5.6 Material Handling Storage and Transportation

 Hazardous chemicals are stored in closed tanks and drums with appropriate blanketing systems.  All transfers from drums / tanks are being done through pumps in closed pipelines.  The loading of finished products to trucks and drums is done through automated filling systems with overflow protections.  All key raw materials are charged to the reactors through closed pipeline systems including pneumatic systems for solid handling.  Raw materials/ intermediates/ products are stored in closed tanks/drums provided with breather arrangements to avoid fugitive emissions.

10.5.7 Ecology

Project site is an existing unit so there will be no clearance of land envisaged for proposed projects and adequate measures will be taken to maintain the existing 539 Acres and Total 625 Acres green belt is developed outside and periphery of Panipat Refinery Complex. For

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compliance of EC condition green belt area augmentation, if any will be done through avenue plantation.

10.5.8 Socio Economic

There will be temporary employment for manpower required during construction phase available from local communities. Overall socioeconomic effect of construction phase will be positive due to direct and indirect employment opportunity for the local population.

10.6 Environmental Management Plan for Operation Phase

Monitoring during the operation phase shall reflect those environmental and socio-economic issues that may persist upon completion of construction activities. Monitoring shall focus on evaluating the effectiveness of project mitigation measures and continue baseline monitoring and sampling. The mitigation measures to prevent adverse impact during the operation phase of the project shall focus on the following:

 Air quality  Noise environment  Solid and hazardous waste  Land environment

10.6.1 Air Quality Management

The gaseous emissions from the proposed project will be controlled to meet all the relevant standards stipulated by the regulatory authorities. Standards applicable to this project are classified into three categories:  Ambient Air Standards  Emission Standards  VOC control, Emission and Monitoring

Following measures are proposed to mitigate negative impact during the operation phase of the project on the surrounding air environment.

10.6.1.1 Ambient Air Standards The ambient air quality around the premises will be limited to those limits as per National Ambient Air Quality Standards, National Ambient Air Quality Standards (Gazette No. 217 dated 18 November 2009)

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10.6.1.2 Emission Standards The emission from the new facilities envisaged in this configuration study will be conforming to the standards stipulated by Ministry of Environment and Forests (MoEF&CC) vide their notification GSR 186€ dated 18th March 2008. *As per MoEF&CC notification dated March 18, 2008 vide circular no G.S.R 186(E) for Industry. 1. The refinery complex is designed to meet all statutory requirements. Some of the major features of these environmental measures are as follows: 2. In case of mixed fuel (gas and liquid) use, the limit shall be computed based on heat supplied by gas and liquid fuels. 3. All the furnaces/ boilers with heat input of 10 MMKcal/hr. or more shall have continuous systems for monitoring of SO2, NOx, CO and PM. OCEMS connectivity to CPCB and SPCB will be ensured. Manual monitoring for all the emission parameters in such furnaces/ boilers shall be carried out once in two months. 4. All the emission parameters in furnaces/ boilers having heat input less than 10 MM KCal/hr. will be monitored once in a quarter. 5. In case of continuous monitoring, one hourly average concentration values shall be met 98% of the time in a month. Any concentration value obtained through manual monitoring, if exceeds the limiting concentration value, shall be considered as noncompliance. 6. Data on Ni + V content in the liquid fuel (in ppm) shall be reported. Ni + V content in the liquid fuel shall be monitored once in six months, if liquid fuel source & quality are not changed. Incase of changes, measurement is necessary after a change. In addition to the above, the particulate matter in emissions from stacks should not exceed the maximum permissible limit is 10 mg/Nm3 for gaseous fuel and 100 mg/Nm3 for liquid fuel. The refinery complex is designed to meet all the statutory requirements. Some of the major features of these environmental measures are as follows:  Low sulphur fuels will be used for internal fuel purpose.  Heaters/furnaces will be provided with well proven Low NOx burners to reduce the emissions of Nitrogen Oxides (NOx).  Under normal circumstances, there will be no continuous/intermittent point releases of volatile hydrocarbon streams. However, if during startup/shut down or an emergency situation any hydrocarbon streams are released, they will be directed to an elevated flare for complete combustion. This will eliminate the possibility of forming

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an explosive mixture due to sudden release of unburned hydrocarbons to the atmosphere.  The flares elevation will be such that there will be no impact of thermal radiation on the operating personnel in the refinery. To ensure complete combustion of released hydrocarbons through flares, a pilot burner shall always be burning with the aid of fuel gas. Further, to ensure smokeless and non-luminous flaring, the steam provision at the flare tip is also envisaged.  The heights of various stacks will be determined taking into consideration the "Guidelines for Minimum Stack Height" as per notification by MoEF dated 19th May 1993, which fixes the minimum stack height based on emission of Sulphur Dioxide. This is as given below: H=14(Q) 0.3 Where H = Stack Height in m, Q = Sulphur Dioxide emission in kg/hr. If, the Pollution Control Board specifies any minimum stack height, the higher of the two will be selected.  The refinery complex is designed in such a way that the total emissions from the refinery complex will meet all the applicable standards/stipulations.

10.6.1.3 VOC Control, Emission and Monitoring Fugitive emissions are primarily due to intermittent/continuous leakage or evaporation of Volatile Organic carbons (VOCs) from processing/storage area of the refinery. The major sources of such fugitive emissions of VOCs in the refinery are the main processing area, the storage tank farm area for crude oil & products and the loading/unloading gantry area. These fugitive emissions originate from the compressor joints and seals used in flanges, pumps, valve packings and connection joints to the atmosphere like sampling, relief valves, etc. In order to minimize the fugitive emissions, the following measures will be taken during engineering:  Minimum number of flanges, valves, etc.  High grade gasket material for packing.  Usage of state-of-the-art low leakage valves preferably with bellow seals.  Usage of pumps with Double Mechanical seals for light hydrocarbon services.  Provisions of floating roof storage tanks.

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 Provisions of double seal in some of storage tanks.  Provision of covering the oil-water separation units in ETP.  Provision of seals in the drains and manholes. IOCL Panipat Refinery has VOC Monitoring system in Existing Refinery and VOC facility in proposed Effluent Treatment Plant will be installed in Proposed expansion.

10.6.2 Noise Monitoring

Impacts of noise on workers are minimized through adoption of adequate protective measures in the form of a) Use of personal protective equipment (earplugs, earmuffs, noise helmets etc.), b) Education and public awareness, and c) Exposure control through the rotation of work assignments in the intense noise areas.

10.6.3 Water and waste water management Oil Spill Management

Hay filters are installed along both the open channels running through Panipat Refinery to prevent spilled oil from escaping out of the Refinery premises with the open channel water. Also oil traps have been installed at strategic locations to arrest oil spillage.

Rainwater Harvesting There are 21nos. of rainwater harvesting pits available within the IOCL Panipat Refinery township and 8nos of rainwater harvesting pit available in refinery complex. Additionally 34 nos of rainwater harvesting pits completed in IOCL Panipat refinery complex. The total catchement area on roof top is 78087 m2.

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Figure 10-2 Rain Water Harvesting Pits

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Waste water management Existing Approx. 1265 m3/hr of effluent/sewage is generated in the existing facility of which 255m3/hr of treated effluent discharged to Thirana Drain (No.HSPCB/Consent/:313105620PITCTO7559304 dated 04-05-2020). Remaining is treated and used for cooling tower.

Proposed Due to the proposed expansion Approx.371m3/hr of effluent/sewage is generated in the existing facility of which 4m3/hr salt is discharged to TSDF and remaining treated and used for Process steam generation and to greenbelt.

Table 10-2 Water Management

No Requirement Existing Proposed after expansion

1 Fresh water (m3/hr) 1720 2400 4120

2 Reuse of treated 1515 841 2356 effluent/Sewage/RO(m3/hr)

Table 10-3 Waste Water Management.

Liquid waste (m3/hr)

Unit Disposal Method Facility Details (m3/hr)

Existing

expansion

Additional Total After After Total

Existing: 255m3/hr of Existing: Combined ETP-1 of treated effluent capacity 400m3/hr, Combined 3 Effluent 1030 362 1392 discharged to Thirana ETP-2 of capacity 400m /hr Drain and remaining and Combined PX/PTA ETP reused in the plant of capacity 275m3/hr Proposed: 4 m3/hr of Proposed: ETP of capacity salt is discharged to 450m3/hr. Sewage will be Sewage 235 9 244 TSDF and remaining combined into the proposed reused in the plant ETP for treatment

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10.6.4 Land Environment During the design stage itself due care will be taken to select the process technologies generating minimum solid wastes so that their handling, treatment and disposal do not cause any serious impact on the existing land environment. Also, efforts will be made to recycle some of the spent catalysts by way of returning to the original supplier for reprocessing. The solid wastes management plan proposed is briefly described below. The provisions of Hazardous Waste (Management & Handling) Rules, 2008, amended up to 2009, will be complied with. There are primarily four types of solid wastes generated in a refinery: 1. Spent Catalyst /Chemicals 2. ETP Sludge‟s 3. General Solid Wastes 4. Tank Bottoms Sludge

10.6.4.1 Spent Catalyst/Chemicals Patented catalysts are used in various refinery process units. Some of the spent catalyst will be sent back to the original supplier for reprocessing. The other catalysts are normally sent to a secured landfill. The chemicals used in various process units will be procured, stored inside the closed vessel inside the refinery and used as per the rules of “Manufacture Storage and import of hazardous chemicals Rules 1989, amended 2000”.

10.6.4.2 ETP Sludge The oily & chemical sludge separated in different units of ETP shall be dewatered, handled and disposed so as to produce zero effluent discharge. The bio sludge from bio-treatment section will be separately dewatered and utilized inside the refinery as manure

10.6.4.3 General Solid Wastes Small quantities of non-hazardous, non-recyclable solid waste consisting of waste refractory, spent insulation, decoking solid waste used filter cartridges, spent charcoal, spent clay and sand will be generated will be sent to nearby authorized landfill agency for further disposal. 10.6.4.4 Tank Bottom Sludge This sludge is generated periodically during the tank cleaning operations approx 1000 T/ tank at the periodicity of 5 years. Tank bottom sludge shall be handled and disposed as per existing practice.

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10.7 Cumulative EMP

10.7.1 Construction Phase The overall impact of the pollution on the environment during construction phase is localised in nature, reversible and is for a short period. Air The suspended particulate pollution generated during transportation will be mitigated by covering the vehicles so as to ensure no spillage. Hosing down the wheels of the vehicles with water and providing washing troughs for them would further mitigate the amount of dust generated. In addition, emission of other pollutants from construction machinery using diesel driven prime movers, will be controlled by proper maintenance. Noise Noise emissions from construction equipment will be kept to a minimum by regular maintenance. Heavy and noisy construction work will be avoided during night time. Water The existing drinking and sanitation facilities at the refinery will be extended to the construction workforce. This is necessary to reduce pollution of any receiving water body and also to prevent hazards due to water borne vectors. Potable water shall be provided to the workers. Socio Economic Being the proposed project, small in terms of construction, there will be no permanent impact on the existing socio-economic system around the refinery.

10.7.2 Operation and Maintenance Phase It is envisaged that with strict adherence to the pollution prevention and control measures during the design stage, the environmental impacts could be moderated to the minimum possible level during the operation phase. Air  In-plant Control Measures Some of the important operational measures, which can reduce the impact on air environment, are as follows:  Ensuring the operations of various process units as per specified operating guidelines/operating manuals.  Strict adherence to maintenance schedule for various machinery/equipment.  Good housekeeping practices

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 Stack and Ambient Air Monitoring In order to keep a check on the emissions of SO2, NOx, SPM and CO from reactor/regenerator, boiler and furnace stacks shall be monitored as per statutory regulations. Continuous monitors for emissions shall be installed on all major stacks. Ambient Air Monitoring Stations shall continuously monitor quality of the air in the vicinity of the refinery premises. Sophisticated instruments for measuring Sulfur Dioxide, NOx, Hydrocarbon, and Carbon Monoxide shall be used in these Monitoring Stations. Noise As the plant is going to be operational on a 24-hour basis, noise considerations are very important. All equipments will be specified to meet 85 dB (A) at 1 m distance. The exposure of employees working in the noisy area shall be monitored regularly to ensure compliance with the OSHA requirements. A green belt of appropriate width exists around the refinery. Treated effluent from the wastewater treatment plant will be used for irrigating this belt. This green belt will help to reduce the noise and visual impact upon the surrounding population as much as possible. Water  In-plant Control Measures Some of the measures, which can be taken up during operational phase of the complex are: o Reducing the actual process water consumption by way of improvement in operation of processing units. o Looking into more options of reusing the treated effluent besides fire water make up or for horticulture development. o Ensuring proper monitoring and maintenance schedule for the effluent treatment plant. o Providing reuse and recycle of the treated effluent and water.  Water Quality Monitoring The monitoring of raw influent, the intermediate stages of Effluent Treatment Plant, the treated effluent, the receiving water body and the ground water quality in the surrounding areas will be carried out regularly. For regular monitoring of the operation of various pollution control facilities, a laboratory with sophisticated instruments and well-trained manpower shall be established. A separate Pollution Control Cell with qualified Chemical Engineers/Scientists also form part of the facility, which will ensure that all pollution control

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measures are effectively operating and to carry out day-to-day checks, trouble shooting and further improvements wherever necessary Land To improve the environmental quality following measures are recommended.  The solid waste generated in the form of packaging material etc. shall be sold off for making it suitable for reuse by reprocessing.  The solids wastes identified to be disposed off in the landfill shall be done as per scientifically established procedure for land filling.  In order to improve the aesthetics in the plant surrounding, further plantation shall be carried out the around the plant boundary. Socio-Economic Being the proposed project, small in terms investment, there will be no permanent impact on the existing socio-economic system around the refinery. However, IOCL shall take part actively in the overall development of the area.

10.8 Occupational Health and Safety

The workers are provided with proper health and safety measures. Personal protection equipment‟s are given to the employers and made sure they wear it during the work. Regular health camps are conducted for all the workers alike. The Health & Safety department makes sure all the workers are not exposed to any kind of toxicity and is within the prescribed limit. Copy of EHS policy enclosed as Figure 10-4; Organogram for OHC is given in Figure 10-3. The main objectives are:

1. Maintenance and promotion of workers‟ health and working capacity. 2. Improvement of working environment by following well-being program for its employees. 3. Monitor the workplace to maintain industrial hygiene practices. 4. Development of work culture in a direction which will support health and safety at work and thereby promoting positive social climate for smooth operation that will enhance productivity. 5. Area monitoring. 6. Employees to undergo annual health check-up. 7. All personnel will be provided with personal protective equipment‟s individually as required.

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10.8.1 Construction Phase During the construction phase the following measures will be employed; 1. Occupational Health Centre will be facilitated to address the emergencies that may arise. 2. Regular monitoring of occupational health of employees. 3. Personnel will be trained about firefighting systems and first aid practices. 4. Personal Protective equipment‟s will be provided to the workers.

10.8.2 Operational phase

General functions of the safety committee will be;

1. Conduct routine workplace inspections. 2. Provide Personal Protective Equipment. 3. Develop and implement safe work procedures and rules. 4. Provide on-going safety training & Enforce safety rules and appropriate discipline. 5. Promote safety awareness and reduce the potential for injury/loss. 6. Identify workplace hazards. 7. Enforce of safety rules, measure safety performance & reduce frequency/severity of injuries.

10.8.3 First aid Boxes

A first aid kit is a collection of supplies and equipment for use in giving first aid. First Aid boxes will be kept available in Security Room, Admin Block and at OHC. First Aid items will be issued to injure only by authorized persons.

Following are the contents of First Aid Box,

a. Dettol – Antiseptic solution b. Ciplox – Eye Drops c. Soframycin – Skin ointment d. Silverex – Burn ointment e. Betadine – Microbicidal solution f. Iodex – Pain reliever g. Sterilized Wool h. Surgical Paper Tape i. Small Sterilized Dressings j. Medium Sterilized Dressings

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k. Roller Bandage – 5 cm wide l. Roller Bandage – 10cm wide m. Band Aid n. Crocin / Paracetamol Tablet

Along with the above safety systems, company also ensured the below safety features to ensure Zero Accident.

1. No ignitable zones are declared and marked so. 2. Work permit system with strict compliance. 3. Dedicated chemical storage area with good ventilation and exhaust system and all chemical are stored as per compatibility. 4. Dyke walls provided for the day storage chemical tanks. 5. All reactors provided with safety valves followed by rupture discs and relief valve outlets are extended. 6. Calibration is ensured for the gauges of pressure, temperature and vacuum. 7. All reactors will be hydro tested and certified by the competent person as per standard prescribed. 8. Body earthing provided to all equipment‟s involved in the process, electrical earthing, static earthing and instrument earthing provided wherever required. 9. Ventilation air units (VAUs) and Exhaust air units (EAUs) and are provided to ensure good ventilation in the work environment. The tentative Emergency Organization Chart will be prepared and followed.

Figure 10-3 Organogram for OHC

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10.8.4 Eye Wash Fountain and Safety Shower

The facility will be provided with sufficient no‟s of Eye wash fountain / Safety showers at appropriate locations.

10.8.5 Existing Safety System Table 10-4 Existing Safety Equipment‟s

S. No Equipment Quantity 1 Self-Contained Breathing Apparatus 30 2 Airline Breathing Apparatus 3 3 Fire Proximity Suit 2 4 PVC Suit 20 5 PVC Apron 5 6 Safety Harness 50 7 Face Shield 10 8 Water Jel Blanket 35 9 Safety Net 40 10 Multigas Meter 10 11 High Beam Torch 4 12 Lifting Air Bags 4 13 Vertical Rescue Tripod & Stretcher 1 14 Leak Sealing Pad 2 15 Leak Sealing Kit 1 16 Vacuum Sealing Pad 1 17 Rescue Set – Hydraulic Cutter, Spreader and Drill 2 18 Hydraulic Platform 32 Meter Height –Bronto Make 1

10.8.6 Fire Extinguisher Suitability of fire extinguisher depending on the combustible material, fires has been classified into four types. Suitability of extinguishing media for different fires is provided in the following Table 10-5.

Table 10-5 Suitability of Extinguishing Media for Different Fires

Suitable Fire S. No Class of fire Extinguisher Class A: Organic Material i.e. wood, papers, rubber & DCP, Mechanical 1. plastics. Foam Class B: Flammable Liquid and Flammable Gases i.e., Mechanical Foam, 2. Petroleum Products, Paints, Chemicals etc. CO2 and DCP

3. Class C: Electrical DCP and CO2 Class D: Flammable Metals I.e. Lithium, Sodium, and 4. Special DCP, Sand Potassium etc.

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The company will have trained personnel for firefighting and intends to improve the firefighting skills of employee by conducting frequent training on Firefighting.

10.8.7 Emergency Equipment‟s and PPEs

The unit will have total 2 numbers of Emergency cupboards, in that one at Production Block and another at Utility Area.

Each Emergency Cupboard will have the following items;

 Breathing Apparatus  Air suits / Air Line Respirators  Nose Mask  PVC / Acid Suit  Helmet- Provided to individuals  Ear Plug  Safety Glass- 10 & Face Shield- to individuals  Gum boot- to individuals  Safety Belt- in safety dept.  Manila Rope / Life Safety Rope  Fire Axe  Fire Proximity Suit  Fire Gel Blankets / Water Gel Blanket  Resuscitator  Spill Kit  Safety Ladder  Emergency Flameproof Torches  Hand gloves 10.8.8 Occupational Health Monitoring

Medical Surveillance Program: Medical surveillance program is essential to assess and monitor employees' health and fitness both prior to employment and during the course of work; to determine fitness for duty and to provide emergency and other treatment as needed. Effectiveness of a medical program depends on active involvement of employees. M/s IOCL medical surveillance program will include the following major elements;

1. Developing an OH-IH Medical Surveillance Program.

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2. Pre-Employment Examination and Periodic Medical Examinations 3. Determination of Fitness for Duty. 4. Communications. 5. Emergency Medical Treatment. 6. Medical Records. Pre-Employment Screening / Examinations - All employees will be subjected to pre- placement medical examinations to determine their fitness for the jobs on site. Potential exposures to the work environment will be considered before placing an employee on the job.

Periodic Medical Examinations - Periodic medical examination is the same as the pre- employment screening and may be modified according to current conditions, such as changes in the employee's symptoms, site hazards or exposures. Comparison of sequential medical reports with baseline data is essential to determine biologic trends that may mark early signs of adverse health effects, and thereby facilitate appropriate protective measures. The frequency and content of examinations are normally one year. Apart from this for workers working in Hazardous area, medical examination is conducted by Doctor Authorized by Factory Inspectorate.

10.9 Environmental Management Cell

A separate environment management cell, HSE department consisting of qualified engineers is in place which monitors all aspects of environmental impacts being caused due to process units at IOCL, Panipat Refinery.

10.10 Corporate Environmental Policy

The safety policy of PR is given in Figure 10-4.

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Figure 10-4 EHS Policy

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10.11 Budgetary Provision for Environmental Management Plan

The detailed breakup of Budget allotted for Environmental Management Plan is given in Table 10-6

Table 10-6 Budget allotted for Environmental Management Plan

Capital Recurring S. No. Activity Cost(Lakhs) Cost(Lakhs) 1 Air Pollution i.Stack 400 126.76 ii.APC equipment 50 2 Water Pollution i.ETP 26925 2269.15 ii.STP 500 3 Noise Pollution i.Acoustic Enclosure 10 4 Solid waste management 80 331.14 5 Storm Water management/ Rain water 100 2 harvesting 6 Greenbelt Development 96.32 13.69 Total 28161.32 2742.74

10.12 Corporate Social Responsibility

CSR activities shall be carried out as per corporation‟s CSR policy. Existing activities and spending for the Period 2018 -2020 enclosed as Annexure 25.

10.13 Corporate Environmental Responsibility (CER)

The company is aware of the obligations towards the Environment and to fulfill the social obligations. As per OM F. No: 22-65/2017-IA.III dated 1st May 2018 M/s IOCL will Allocate 0.125% of the project cost (32946 Crores) towards CER i.e. 0.125% of 32946 Crores = 41.18 Crores

CEPI value of Panipat is 83.54

As per CEPI compliance for CPA 2 times of slab to be allotted(2 * 41.18)=82.36 Crores. CER details will be provided later.

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CHAPTER 11 SUMMARY & CONCLUSION

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11 SUMMARY & CONCLUSION

An Environmental Impact Assessment Study has been carried out and assessed for the proposed project based on the ToR and baseline quality data collected for the study area. Identification and anticipation of the potential environmental impacts due to the proposed project with a delineation of appropriate impact mitigation measures in an Environmental Management plan during both construction and operation phases is provided in the EIA report prepared.

Based on the above evaluation the significance, value addition, impact on various components of environment during construction and operation phases is summarized below;

 IOCL Panipat, Haryana attracts CEPI score of 83.54.IOCL Panipat Refinery will comply the CEPI guidelines by MoEF&CC.  The Project Proponent will follow all the statutory norms and guidelines as per CPCB/MoEF&CC to safeguard environment.  No land acquisition is carried out since the existing land area is used for proposed expansion.  The incremental concentrations of PM, SO2, NOx and CO are observed to be 2.26%, 133.68%, 51.00% and 64.32% respectively. The total pollutant concentrations of PM, 3 3 3 3 SO2, NOx and CO are 130.89 µg/m , 53.55 µg/m , 66 µg/m and 1281.68 µg/m .

 On total after expansion 6786 m3/hr of raw water of which the fresh water of 4120 m3/hr will be taken from existing water source (i.e. , Western Yamuna canal). No water will be drawn from ground water sources.  The wastewater generated in the Refinery complex will be treated in ETP, treated effluent will be reused in the process.  Hazardous waste generated in IOCL Panipat refinery are disposed by TSDF and disposed to SPCB authorized recyclers as per CPCB/MoEF&CC guidelines.  No endangered species are found in the study area. Birds such as Painted Stork (Mycteria leucocephala) , Black-necked Stork(Ephippiorhynchus asiaticus), Black- headed Ibis (Threskiornis melanocephalu)s and Alexandrine Parakeet (Psittacula eupatria) comes under near threatened species

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 The project will induce indirect employment generation for local communities as well as state & region as a whole and preference will be given to the local communities as per IOCL Panipat refinery Policy.

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CHAPTER 12 DISCLOSURE OF CONSULTANTS

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12 DISCLOSURE OF CONSULTANTS

In order to assess the potential environmental impacts due to the proposed Panipat Refinery Capacity Expansion from existing 15 MMTPA to 25 MMTPA within existing refinery complex, M/s IOCL, PR has engaged Hubert Enviro Care Systems (P) Limited, Chennai to undertake EIA study. The nature of consultancy service rendered covers terrestrial environmental assessment.

12.1 Brief Profile of Hubert Enviro Care Systems (P) Limited (HECS)

Enviro Care Systems was started in the year of 1997 by Dr. J.R.Moses with the vision to serve the world in all environmental related problems by completing the latest technological advancements available.

In the year 2004, Enviro Care Systems became Hubert Enviro Care Systems (P) Ltd after having collaboration with Hubert Stavoren B.V. for higher Technology.

The company provides total pollution control solutions to several industries like Thermal Power Plant, Pharma, R&D Facilities, Electroplating and Manufacturing, IT Parks, Residential Complexes, Dairies, Food Processing, Textile mills, Breweries, etc.

The company is specialized in executing projects right from concept development, supply, erection, commissioning and operation on turnkey basis. HECS has successfully executed more than 200 environmental engineering projects for various industrial sectors both in India and overseas. HECS has state-of-art facilities to provide quality environmental consultancy and engineering solutions.

Strengths of HECS Number of Employees as on May 2021

Total No of Employees 1096 Consultancy 43 Laboratory 125 Projects 34 Operation & Maintenance 894

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Declaration of Experts contributing to the EIA I hereby certify that I was involved in the preparation of EIA/EMP for the “Panipat Refinery Capacity Expansion from existing 15 MMTPA to 25 MMTPA within the existing refinery complex” at Baholi village, Panipat District, Haryana state by M/s. Indian Oil Corporation Limited as EIA Coordinator with the support of the following Functional Area Experts.

EIA Co-ordinator

Name: Dr. J R Moses

Signature: Date:14-07-2021

Contact Information: Hubert Enviro Care Systems Pvt. Ltd., # A-21, Phase III, Behind Lions Club School, Thiru-vi-ka Industrial Area, Guindy, Chennai –600032. Tamil Nadu, India. Email: [email protected] Website: www.hecs.in

Functional Area Experts (FAEs): S. Functional Duration of Name of the Expert Signature No. Areas Involvement Jan 2019 till Dr. J R Moses date 13. AP FAE Jan 2019 till Mr. Vamsee Krishna Navooru date Jan 2019 till 14. AQ FAE Dr. J R Moses date Jan 2019 till Dr. J R Moses date FAE Jan 2019 till 15. WP Mr. Vamsee Krishna Navooru date Jan 2019 till FAA Mr. Chengalvarayan date Jan 2019 till Mr. A. Manoharan March 2021 16. SHW FAE Jan 2019 till Mr. Vamsee Krishna Navooru date

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S. Functional Duration of Name of the Expert Signature No. Areas Involvement Jan 2019 till 17. SE FAE Mr. V. Dhivakar date Jan 2019 till Dr.. Sundararajan date 18. EB FAE Jan 2019 till Dr. Rajkumar Samuel date Jan 2019 till 19. HG FAE Mr. MallikarjunaRao date Jan 2019 till 20. Geo FAE Mr. MallikarjunaRao date Jan 2019 till Mr. Vivek P. Navare date 21. NV FAE Jan 2019 till Mr. Vamsee Krishna Navooru date Jan 2019 till 22. LU FAE Mr. VenkateswarluRachala date Jan 2019 till 23. RH FAE Dr. J R Moses date Jan 2019 till Mr. A. Manoharan March 2021 24. SC FAE Feb 2020 till Dr.B.C.Nagaraja date AP - Air pollution monitoring, prevention and control AQ - Meteorology, air quality modeling and prediction EB - Ecology and biodiversity HG - Hydrology, ground water and water conservation LU - Land use N&V - Noise & Vibration RH - Risk assessment and hazards management SC - Soil conservation SE - Socio-economics SHW - Solid and hazardous waste management WP - Water pollution monitoring, prevention and control Geo -Geology

12.2 QCI-NABET - EIA Accreditation

Consultancy Hubert Enviro Care Systems Pvt. Ltd., Chennai NABET Certificate No & NABET/EIA/1922/RA 0172 Valid up to 13/10/2022 Date of validity MoEF Reg. Lab F.No. Q-15018/21/2017-CPW

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12.3 Copy of QCI NABET Accreditation

Further details may be seen on the following URL: www.hecs.in

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HUBERT ENVIRO CARE SYSTEMS (P) LIMITED A-21, III-Phase, Behind Lions Club School, Thiru vi ka Industrial Estate, Guindy, Chennai – 600 032 Ph: +91-44-43635555; Fax: +91-44-43635500

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