EQMS India Pvt. Ltd. - Welcome to...
Transcript of EQMS India Pvt. Ltd. - Welcome to...
NOVEMBER,2017
EQMS India Pvt. Ltd.
304-305, Rishabh Corporate Tower, Plot No. 16,
Community Center, Karkardooma, Delhi – 110092,
Phone: 011-30003200; E-mail : [email protected];
Website : www.eqmsindia.com
ENVIRONMENTAL IMPACT ASSESSMENT
REPORT
For
Expansion of Existing Pesticide Plant for
Manufacturing of Technical Grade Pesticides
at
Village – Biratiya Kalan, Tehsil – Raipur, Distt –
Pali, Rajasthan
By
INTECH ORGANICS LIMITED (Formerely known as Intech Pharma Pvt Ltd)
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
Pali, Rajasthan
EQMS India Pvt. Ltd. 2
Table of Contents
Chapter 1. Introduction ........................................................................................................ 12
1.1. Project & Project Proponent .......................................................................................... 12
1.2. Nature ofthe Project ....................................................................................................... 13
1.3. Importance & Benefits of Project ................................................................................... 13
1.4. Purpose of the EIA Study .............................................................................................. 13
1.5. Project Site Location ...................................................................................................... 14
1.6. Regulatory Framework .................................................................................................. 17
1.7. Public Hearing ............................................................................................................... 18
1.8. Approved Terms of Reference for EIA Study byMoEF&CC ........................................... 20
1.9. Structure of the EIA Report ............................................................................................ 30
Chapter 2. : Project Description ........................................................................................... 33
2.1. Project Site Details ........................................................................................................ 33
2.2. Land Requirement ......................................................................................................... 35
2.3. Products with Capacityforproposed projects .................................................................. 35
2.4. Manufacturing Process .................................................................................................. 38
2.5. Environmental Aspects: ................................................................................................. 58
2.5.1. Liquid Effluent Management .......................................................................................... 58
2.5.2. Emission Control System: - ........................................................................................... 60
2.5.3. Solid and Hazardous waste ........................................................................................... 63
2.5.4. Noise Environment ........................................................................................................ 64
2.5.5. Green Belt Development ............................................................................................... 65
2.5.6. Project Cost: .................................................................................................................. 65
2.5.7. Proposed CSR activities and budget ............................................................................. 65
Chapter 3. : DESCRIPTION OF THE ENVIRONMENT ....................................................... 66
3.1. Background and Salient Environmental Features of the Study Area .............................. 66
3.1.1. Environmental Setting and Salient Environmental Features of the Project Area ............ 66
3.1.2. Primary Data Collection: Monitoring Plan and Quality Assurance Procedures ............... 72
3.2. Physical Enviroment ...................................................................................................... 76
3.2.1. Topography ................................................................................................................... 76
3.2.2. Drainage ........................................................................................................................ 76
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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3.2.3. Geology ......................................................................................................................... 76
3.3. Hydrogeology ................................................................................................................ 77
3.3.1. Stage of Ground Water Development ............................................................................ 78
3.3.2. Depth to Ground Water Table ........................................................................................ 78
3.3.3. Seismicity of the Study Area .......................................................................................... 78
3.4. Land use ....................................................................................................................... 79
3.5. Meteorology................................................................................................................... 82
3.5.2. Met Data Generated at Site ........................................................................................... 83
3.6. Ambient Air Quality ........................................................................................................ 86
3.6.2. Observations on Ambient Air Quality (May 2017): ......................................................... 92
3.7. Noise Environment ........................................................................................................ 93
3.7.2. Observation on Ambient Noise Quality: ......................................................................... 95
3.8. Water Quality ................................................................................................................. 95
3.8.1. Ground Water Quality .................................................................................................... 95
3.9. Soil Quality .................................................................................................................. 104
3.9.1. General Characteristics of the Soil in the District ......................................................... 105
3.9.2. Methodology ................................................................................................................ 106
3.9.3. Analysis of Soil Samples ............................................................................................. 107
3.9.4. Observation on Soil Quality (Post Monsoon season 2016) .......................................... 108
3.9.5. Observation on Soil Quality (May 2017) ...................................................................... 112
3.9.6. Cropping Pattern ......................................................................................................... 112
3.10. Traffic Study ................................................................................................................ 115
3.11. Ecological Environment ............................................................................................... 117
3.11.1. Flora .................................................................................................................... 117
3.11.2. Fauna .................................................................................................................. 123
3.12. Socio-Economic Environment ...................................................................................... 127
3.12.2. Economic Structure ............................................................................................. 134
3.12.3. Workers Scenario ................................................................................................ 134
3.12.4. Basic Infrastructure Facilities Availability (as per the Census records of 2011) .... 139
Chapter 4. Impacts Assessment and Prediction ................................................................ 146
4.1. General ....................................................................................................................... 146
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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4.2. Construction Phase ..................................................................................................... 147
4.3. Operation Phase ......................................................................................................... 149
4.3.1. Air Environment ........................................................................................................... 149
4.3.2. Model Details ............................................................................................................... 149
4.3.3. Predicted GLC due to INTECH Expansion Project ...................................................... 150
4.3.4. Meteorological Data ..................................................................................................... 151
4.3.5. Receptor Locations...................................................................................................... 151
4.3.6. Summary of Predicted GLC’s ...................................................................................... 151
4.3.7. Discussion of the Cumulative Impacts at monitoring locations: .................................... 155
4.4. Noise Environment ...................................................................................................... 161
4.4.1. Impacts due to Transportation ..................................................................................... 161
4.4.2. Impact of noise on community ..................................................................................... 161
4.5. Water Environment ...................................................................................................... 162
4.5.1. Water Demand ............................................................................................................ 162
4.5.2. Effluent Generation and Discharge .............................................................................. 163
4.6. Land/Soil Environment ................................................................................................ 164
4.6.1. Land Diversion ............................................................................................................ 164
4.6.2. Land Deterioration ....................................................................................................... 164
4.6.3. SOLID/HAZARDOUS WASTE ..................................................................................... 164
4.7. Biological Environment ................................................................................................ 164
Operation stage Impacts .......................................................................................... 166
4.8. Socio – Economic Environment ................................................................................... 168
4.9. INFRASTRUCTURE .................................................................................................... 169
Chapter 5. ENVIRONMENTAL MANAGEMENT PLAN ...................................................... 170
5.1. Environment Management Plan (Construction and Operation Phase) ......................... 170
5.2. Fly ash Management plan ........................................................................................... 173
5.3. Rain Water Harvesting Plan ........................................................................................ 174
5.4. Environment Management Cell (EMC) ........................................................................ 174
5.5. Institutional Arrangement ............................................................................................. 175
5.6. Resource Conservation/ Waste Minimization .............................................................. 177
5.9. EMP for Biological Environment Quality ...................................................................... 179
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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5.10. Budget for EMP ........................................................................................................... 183
5.11. Conclusion .................................................................................................................. 184
Chapter 6. Risk Assessment& DISASTER MANAGEMENT PLAN .................................... 185
6.1. Introduction ................................................................................................................. 185
6.2. Risk Assessment ......................................................................................................... 185
6.3. Risk Screening Approach ............................................................................................ 187
6.4. Hazardous Materials Storage ...................................................................................... 195
6.5. QRA Approach ............................................................................................................ 195
6.6. Thermal Hazards ......................................................................................................... 196
6.7. Damage due to Explosion............................................................................................ 198
6.8. Toxic Release .............................................................................................................. 198
6.9. Data Limitations ........................................................................................................... 199
6.10. Likely Failure Scenarios .............................................................................................. 199
6.11. Weather Effect ............................................................................................................. 199
6.12. Incidents Impacts ........................................................................................................ 199
6.13. Consequential Impacts ................................................................................................ 200
6.14. Thermal and Explosion Hazards .................................................................................. 200
6.15. Toxic Hazards ............................................................................................................. 201
6.16. General Control Measures ........................................................................................... 201
6.17. Flammable Gas Fires .................................................................................................. 201
6.18. Process Safety System ............................................................................................... 201
6.19. Safety Recommendations............................................................................................ 204
6.20. Commonly Recommended Control Measures ............................................................. 204
6.21. Occupational Health and Safety .................................................................................. 205
6.22. Emergency Management Plan .................................................................................... 206
6.23. Many of the hazards are as result of working environment .......................................... 207
6.24. Key Process Safety Measures ..................................................................................... 207
6.25. Transportation: ............................................................................................................ 208
6.26. Emergency facilities ..................................................................................................... 217
6.27. Objectives ................................................................................................................... 217
6.28. Emergency Management Plan [EMP] .......................................................................... 217
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6.29. Responsibilities & Role of Key Personnel .................................................................... 219
6.30. Over all In-charge –Incharge Production / Manager Production).................................. 219
6.31. Chief Site Coordinator- Manager (Prod.) ..................................................................... 219
6.32. Chief Maintenance Coordinator- Manager (Maintenance)............................................ 220
6.33. Chief Service Coordinator - Manager (HR) .................................................................. 220
6.34. Chief Material Coordinator- Manager (Materials) ......................................................... 220
6.35. Incident Controller Concerned Plant -Manager Concerned Plant ................................. 221
6.36. Shift In-charge (Concerned Plant): .............................................................................. 221
6.37. Security Officer Vehicle Control and Security Personnel Deployment at the Locations 221
6.38. Fire & Safety Controller- Incharge (F&S) ..................................................................... 222
6.39. Fire Control Room In-Charge ...................................................................................... 222
6.40. Fire Supervisor should also ensure the following: ........................................................ 223
6.41. Post Emergency Recovery .......................................................................................... 223
6.42. Accident Investigation .................................................................................................. 223
6.43. Damage Assessment .................................................................................................. 224
6.44. Clean-up and Restoration ............................................................................................ 224
6.45. Conclusion &Recommendations .................................................................................. 224
Chapter 7. Summary and Conclusion ................................................................................ 226
7.1. Prelude ........................................................................................................................ 226
7.2. Regulatory Compliance ............................................................................................... 226
7.3. Baseline Conditions ..................................................................................................... 226
7.4. Environmental Impacts and Mitigation Measures ......................................................... 226
7.5. Project Benefits ........................................................................................................... 227
7.6. Conclusion and Recommendations ............................................................................. 227
Chapter 8. Disclosure of Consultant .................................................................................. 229
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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List of Tables
Table 1.1 : Details of permits and clearance applicable .............................................................17
Table 1.2 TOR Compliance Status ............................................................................................20
Table 2.1 : Salient Features of the Project ................................................................................33
Table 2.2 Land Distribution at Site (As per Approved ToR) .......................................................35
Table 2.3 Land Distribution at Site (As per Applied for Amendment of ToR) .............................35
Table 2.4 (A): Existing &Proposed products (as per approved TOR) .........................................35
Table 2.5 Material Balance for Methyl Bromide .........................................................................39
Table 2.6 Details of Raw Material with Quantity ........................................................................52
Table 2.7 Bulk Storage ..............................................................................................................56
Table 2.8 Water consumption & Waste water generation in Existing Plant ................................56
Cumulative Water Requirement and Water Balance Approved ToR and Applied for amendment
of ToR (received TOR on 11th September 2017 (Letter No. J-11011/327/2016-IA.II (I))} ...56
Table 2.9 Total water Consumption and Waste Water Generation ............................................57
Table 2.10 Effluent Standards for Pesticide Industry .................................................................60
Table 2.11 Stacks for Proposed Projects ..................................................................................61
Table 2.12 National Emission Standards for Pesticide Manufacturing and Formulation Industry
..........................................................................................................................................62
Table 2.13 Pollution Load .........................................................................................................63
Table 2.14 Hazardous Waste Generation Quantity ...................................................................64
Table 3.1 : Salient Environmental Features of Proposed Site ....................................................68
Table 3.2 : Summary of Methodology for Primary/Secondary Baseline Data Collection ............72
Table 3.3 Geological Sequence ................................................................................................77
Table 3.4 : Land use of the Study Area .....................................................................................79
Table 3.5 Long Term Meteorological Data of Ajmer (30 years’ average) ...................................82
Table 3.6 No. of days with zero oktas of cloud cover (Ajmer) ....................................................83
Table 3.7 Monthly Percentages of Calm Periods (IMD Ajmer) ...................................................83
Table 3.8 Site Specific Meteorological Data (Oct 2016 to Dec2016) .........................................84
Table 3.9 Site Specific Meteorological Data (May 2017) ...........................................................84
Table 3.10 Ambient Air Quality Monitoring Locations ................................................................87
Table 3.11 Ambient Air Quality Monitoring Results (24-hour average) ......................................87
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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Table 3.11 continued ........ ........................................................................................................88
Table 3.11 continued ........ ........................................................................................................89
Table 3.12 Ambient Air Quality Monitoring Results (24-hour average) ......................................90
Table 3.13 Ambient Noise Quality Monitoring Locations ...........................................................93
Table 3.14 Ambient Noise Quality in the Study Area (Post Monsoon Season) ..........................93
Table 3.15 Ambient Noise Quality in the Study Area (May 2017) ..............................................94
Table 3.16 Ground Water Sampling Locations ..........................................................................95
Table 3.17 Surface Water Sampling Locations..........................................................................96
Table 3.18 Ground Water Quality in the Study Area (May-2017) ...............................................98
Table 3.18 continued, .......Ground Water Quality in the Study Area (May-2017) ..................... 100
Table 3.19 Surface Water Quality in the Study Area (May-2017) ............................................ 103
Table 3.20 Soil Sampling Locations ........................................................................................ 106
Table 3.21 Physicochemical Characteristics of Soil Oct-Dec 2016) ......................................... 107
Table 3.22 Physicochemical Characteristics of Soil (May 2017) .............................................. 110
Table 3.23 Area under Major Field Crops&Horticulture, 2010-11 ............................................ 113
Table 3.24 Production and Productivity of Major Crops, 2010-11 ............................................ 114
Table 3.25 Traffic survey near the plant site ............................................................................ 115
Table 3.26 : PCU Factors Applied for Different Class of Vehicles ........................................... 116
Table 3.27 Total PCU on single Lane Road near Plant Site .................................................... 116
Table 3.28 List of Flora within Core zone ................................................................................ 118
Table 3.29 List of Common Plant Species Present in Study Area ........................................... 120
Table 3.30 List of Medicinal Plants and their Medicinal Value ................................................. 123
Table 3.31 Mammalian Fauna reported in study area ............................................................. 125
Table 3.32 : Reptiles and Amphibian observed in Study Area ................................................. 125
Table 3.33 Avifauna Sighted during the primary survey .......................................................... 126
Table 3.34 : Caste-wise Population Distribution of 2.0-km Radial Zone................................... 128
Table 3.35 Caste-wise Population Distribution of 10-km radial Study Area ............................. 129
Table 3.36 Male-female wise Literates & Illiterates ................................................................. 133
Table 3.37 Village wise Occupational Pattern in the Study Area ............................................. 135
Table 3.38 Distribution of Work Participation Rate .................................................................. 136
Table 3.39 Composition of Non-Workers................................................................................. 139
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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Table 3.40 Village wise Basic Amenities Availability in the Study Area ................................... 142
Table 4.1 Stack Parameters and Emission Details from Proposed Expansion Project (Process)
........................................................................................................................................ 150
Table 4.2 Emission Load Proposed Expansion Project (Process) ........................................... 150
Table 4.3 Summary of Maximum 24-hour Incremental GLC due to the Proposed Expansion
Project Stacks .................................................................................................................. 151
Table 4.4 : Summary of Maximum GLC at Monitoring Locations due to the Proposed
ProjectAmbient Air Quality Monitoring Results (24-hour average) .................................... 152
Table 4.5 CREP Guidelines Compliance ................................................................................. 167
Table 5.1 Environment Management Plan .............................................................................. 170
Table 5.2 : Ash utilization plan ................................................................................................ 173
Table 5.3 Table: Ecological criteria & Observations ............................................................... 179
Table 5.4 Species suggested for plantation under Greenbelt Development Programmed ....... 181
Table 5.5 Greenbelt Budget for 5 Year .................................................................................... 182
Table 5.6 Proposed Environmental Monitoring Program ......................................................... 182
Table 5.7 : EMP Budget .......................................................................................................... 183
Table 6.1 Liquid/Gaseous Bulk Storages ................................................................................ 187
Table 6.2 : Hazardous Analysis of Products ............................................................................ 189
Table 6.3 : Hazardous Analysis Raw materials stored in Bulk ................................................. 192
Table 6.4 Risk Classification ................................................................................................... 196
Table 6.5 Effects due to Incident Radiation Intensity ............................................................... 197
Table 6.6 Thermal Radiation Impact to Human ....................................................................... 197
Table 6.7 Tolerable Intensities for Various Objects ................................................................. 197
Table 6.8 Damage due to Overpressure ................................................................................. 198
Table 6.9 Different Failure Scenarios ...................................................................................... 199
Table 6.10 : Hazards Scenario Impact .................................................................................... 199
Table 6.11 Transportation, Unloading and Handling Safety Measures .................................... 208
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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List of Figures
Figure 1.1 : Location Map of Project Site Google Map ..............................................................15
Figure 1.2 : Location Map .........................................................................................................16
Figure 2.1 Plant Layout Plan .....................................................................................................34
Figure 2.2 Process Flow Diagram .............................................................................................43
Figure 2.3 Combined Water Balance for proposed expansion project (With TOR approved and
applied for Amendment) .....................................................................................................57
Figure 2.4 ETP Flow Diagram ...................................................................................................59
Figure 3.1 Road Connectivity Map ............................................................................................67
Figure 3.2 Location Map of 10-km Radius Study Area ..............................................................70
Figure 3.3 Google Map of 10-km Radius Study Area ................................................................71
Figure 3.4 Close view Map with Project Site coordinates ..........................................................74
Figure 3.5 Environment Sampling Location Map .......................................................................75
Figure 3.6 Drainage Map of Study Area ....................................................................................76
Figure 3.7 Seismic Zones Map ..................................................................................................79
Figure 3.8 : Graph Showing Land Use of the Study Area (10 km Radius) .................................80
Source: Interpretation of Satellite image....................................................................................81
Figure 3.9 Land use/Land Cover Map of 10 Km Radial Study Zone .........................................81
Figure 3.10 Wind Frequency Distribution (Post monsoon Season 2016) ...................................85
Figure 3.11 Wind Frequency Distribution (May 2017) ................................................................85
Figure 3.12 Wind Frequency distribution (May 2017) ................................................................86
Figure 3.13 : Soil Map of Rajasthan (Pali) District ................................................................... 106
Figure 3.14 Male-Female Wise Population Distribution ........................................................... 131
Figure 3.15 : Scheduled Caste Population in Study Area ........................................................ 131
Figure 3.16 Scheduled Tribes Population in Study Area ......................................................... 132
Figure 3.17 : Male-Female Wise Distribution of Literates &Illiterates ....................................... 132
Figure 3.18 : Workers Scenario ............................................................................................... 137
Figure 3.19 : Composition of Main Workers Population ........................................................... 138
Figure 3.20 : Composition of Marginal Workers....................................................................... 138
Figure 3.21 Composition of Non-Workers ............................................................................... 139
Figure 5.1 Structure of Environmental Management Department ............................................ 175
Figure 5.2 : Corporate Occupational Health, Safety and Environmental Policy ....................... 179
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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List of Annexure
Annexure I : Nabet Acrediation Certificate of consultant
Annexure II : Approved ToR Letter issued by MOEF&CC
Annexure III : Consent to Establish copy issued by RPCB for existing unit of company
Annexure IV : Consent to Operate copy issued by RPCB for existing unit of company.
Annexure V : Consent to Operate copy for Hazardous waste issued by RPCB for existing
unit of company.
Annexure VI : Consent to Operate Compliance submitted to RPCB
Annexure VII : NOC from District Forest Officer and Application submitted to Chief
Wildlife warden
Annexure VIII : Raw data of all AAQ measurement for 12 weeks of all stations carried
by Enkay Enviro Service Pvt Ltd for the period of Oct-2016 to Dec-2016
and One Month AAQ measurement data carried by EQMS and
monitoring team during 1st May-2017 to 31st May-2017 .
Annexure IX : Schedule I Species Conservation plan approved by DFO
Annexure X : Material Safety Data Sheet for all the Chemicals (Product and Raw
Materials)
Annexure XI : Baseline Environment Monitoring Report of Enkay Enviro Services Pvt
Ltd.
Annexure XII : Existing Site Photograph with green belt.
Annexure XIII : Acknowledgement Copy of application submitted for amendment of
ToR to MoEF&CC
Annexure XIV : Membership Certificate for disposal of Hazardous waste with Udaipur
Chamber of Commerce, Udaipur.
Annexure XV : Public Hearing advertisement in newspaper, minutes of meeting with
signature
Annexure XVI : Amended TOR Letter received on 11th September 2017
Annexure XVII : Letter for Change in Name
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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CHAPTER 1. INTRODUCTION
1.1. Project & Project Proponent
The agrochemicals industry is a significant industry for the Indian economy. The Indian
pesticides and insecticide industry is fourth largest in the world and the second in the
Asia-Pacific region only after China.
INTECH ORGANICS LIMITED (Formerly known as Intech Pharma Pvt Ltd) was
established in the year 1999. The Company has been ever since the beginning been
involved with manufacturing of chemicals which have been distributed across India &
overseas as well.
The Company began Commercial production of specialty chemicals in the end of 2004 &
since then has been regularly meeting the demands of its reputed customers. The
Company's technical wing is deep rooted with a very strong team having a vast
experience of handling this product for more than 3 decades. Company’s team is
constantly working towards improving its systems, product to cater to the changing
requirements of its customers.
INTECH ORGANICS LIMITED (Formerely known as Intech Pharma Pvt Ltd)
(henceforth INTECH) applied in MOEF&CC and received TOR on 15th June 2017 (Letter
No. J-11011/327/2016-IA.II (I)) for proposes expansion of existing products and
manufacturing technical grade pesticides as well as formulations of pesticides, capacity of
4000 MTPA to 59914 MTPA at Khasra no 143, 143/1, 118, 118/1, 118/2, 119, 120, 121,
122, 124, 126 at village – Biratiya Kalan, Tehsil – Raipur,Distt – Pali (Rajasthan).Further
as per market requirement & management strategy for increase in production from 4000
MTPA to 63414 MTPA at Khasra no 143, 143/1, 118, 118/1, 118/2, 119, 120, 121, 122 at
village – Biratiya Kalan, Tehsil – Raipur,Distt – Pali (Rajasthan).INTECH has (received
TOR on 11th September 2017 (Letter No. J-11011/327/2016-IA.II (I))}. Henceforth
cumulative/ final survey no. and production capacity are being presented in EIA report.
As per approved TOR the existing plant is set up in an area of 6900 SQM. The expansion
is planned in 35900 SQM land, which is already under process of possession with
INTECH. The total land area after expansion will be 42907 SQM. Around 14247 SQM (~
33 %) of total plot area is being/will be developed as greenbelt. Total cost of the project
will be approx. INR 27.0 Crores.As per amendment of ToR Application (Applied to
MoEF&CC on 25th July 2017 which received on 11th September 2017 (Letter No. J-
11011/327/2016-IA.II (I). The total land area after expansion will be 107165.81 SQM.
Around 35365 SQM (~ 33 %) of total plot area being/will be developed as greenbelt.
Henceforth cumulative/ final land area is being presented in EIA report
This chapter provides background information of the project, need of the project, need
of the EIA study, scope and EIA methodology adopted and structure of the report.
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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1.2. Nature of the Project
INTECH propose to enhance the production capacity of existing product and
manufacturing technical grade as well as formulations of pesticide Agrochemicals
ingredients. The proposed expansion is planned in the future earmarked land including
existing land. As per EIA Notification dated 14.09.2006 and as amended on 01.12.2009,
the project falls in Category ‘A’, S. No. – 5 (b) appraised in MOEF&CC.
1.3. Importance & Benefits of Project
The role of the pesticides in the wellbeing of human race needs no emphasis. Insecticides
are used to ward off or kill insects. Pesticide usage has become essential in order to
maximize agriculture production and reduce public health pestilence. The rapid changes
in cropping patterns, increased fertilization and adoption of programs for high yielding
varieties have all contributed to increased use of pesticides. Further, pest problems keep
on changing with the changing environment. New physiological kinds evolve as a result of
mutations to withstand new conditions in nature. Many pest species develop resistant
strains when the same pesticide is used far too often. The problems of pest resurgence
and secondary pest out-breaks crop up with the indiscriminate use of pesticides. These
associated problems offer a great scope for revolutionizing the use of pesticides.
However, in India though the overcall pesticide growth figures may appear impressive, the
rate of consumption in comparison per hectare of cultivated land is very low in
comparison to other countries. India used 180 g of pesticides/ha. as against 10,790g,
1870 g and 1490 g/ha used in Japan, Europe and U.S.A. respectively. India spent just Rs.
2.15/ha. on pesticides while Japan and U.S.A spent Rs.110/ha and Rs.35/ha respectively
during the same period. India consumed 12 gm. of pesticides per kg. of fertilizer used
against 146 gm. in Japan and 19 gm in U.S.A. This is one of the major factors that can be
attributed to low per hectare yields in our country since the crops and especially the high
yielding varieties cannot manifest their production potential in absence of proper pest
protection. That the production potential remains suppressed for want of protection can be
exemplified by considering how in wheat, a crop comparatively resistant to insect
pestilence, we have had a “revolution” where as in paddy which is one of the most heavily
infested crops, we have had no break-through. In case of wheat, the per hectare yield in
India rose from 827 kg.to 1338 kg. Corresponding yields of paddy in India on the other
hand was 1826 kg. as against 6185 kg., 5326 kg., 5105 kg. and 4000 kg., in Japan,
Egypt, USA and USSR respectively.
Within the country, itself, there is a great imbalance between different regions with regard
to the use of pesticides. Of the total of approximately Rs.5000 million spent on pesticides
in at the farm level, south contributed for about 45 per cent of the total consumption in the
rest of the country.
1.4. Purpose of the EIA Study
The objectives of the present EIA are to:
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt –
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EQMS India Pvt. Ltd. 14
• To identify and describe the elements of the community and environment likely to be
affected by the expansion, and/or likely to cause impacts upon both the natural and
man-made environment
• To describe the proposed expansion project and associated works together along with
the requirements.
• To identify and quantify any environmental impacts associated with the proposed
expansion and recommend appropriate mitigation measures.
• To identify existing landscape and visual quality in the study area so as to evaluate
the landscape and visual impacts of the proposed expansion.
• To propose mitigation measures to minimize pollution, environmental disturbance and
nuisance during construction and operation of the proposed expansion.
• To identify, assess and specify methods, measures and standards, to be included in
the detailed design, construction and operation of the proposed expansion which are
necessary to mitigate these impacts and reduce them to allowable levels within
established standards/guidelines.
• To identify and justify the need for environmental monitoring to define the scope of the
requirements necessary. To ensure the implementation and the effectiveness of the
environmental protection and pollution control measures adopted.
• To identify constraints associated with the mitigation measures recommended in this
EIA.
• To identify any additional studies necessary to fulfil the objectives required for the EIA
Study
1.5. Project Site Location
INTECHproposedexpansionof manufacturing of technical grade pesticides fromm 4000
MTPA to 63414 MTPA. Project site is located at khasra no 143, 143/1, 118, 118/1, 118/2,
119, 120, 121, 122 at village – Biratiya Kalan, Tehsil – Raipur,Distt – Pali (Rajasthan).
The site is well connected to NH112(earlier known as NH-65A) (Degana - Raipur), NH-14
(Beawar-Sirohi-Radhanpur) at an aerial distance ~1.16 Km (SW) ~4.85 Km, (S) direction.
Nearest railwaystationisBar &Pali railway station located at an aerial distance of ~ 6.44
km in (ESE), 86 km, WSW, direction respectively from the project site.
Nearest airport from project site is Dabok Airport (UDR) in Udaipur located at an aerial
distance of ~ 167 km (SSW) direction. Jodhpur Air port is around 125 km.
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Figure 1.1 : Location Map of Project Site Google Map
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Figure 1.2 : Location Map
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1.6. Regulatory Framework
Prior Environmental Clearance is required from concerned authorities for all projects
and activities mentioned in “Schedule” as per Environmental Impact Assessment
notification dated September 14, 2006. The project comes under “project and activity-5
(b) of schedule.” Considering the products portfolio, the proposed project falls in
“Category A” of Schedule of the EIA notification which requires Environmental
Clearance (EC) from MoEF&CC, New Delhi.
INTECH has commenced the process of obtaining required statutory permission from
concerned authorities. Details of permits and clearance applicable to this project along
with status is given in Table 1.1.
Table 1.1 : Details of permits and clearance applicable
S. No Permit / Clearance/Standards Proposed Project Existing Plant
1
No Objection Certificate /Consent to Establish from Rajasthan State Pradesh Pollution Control Board (RSPCB)
Mandatory, shall be applied after obtained Environmental Clearance
Valid NOC from RSPCB for existing plant is available with INTECH
2 Factory License To be applied for factory license after obtained environment clearance.
Valid Factory License is avialble with INTECH
3 Water Permission
Have permission for using surface water from Irrigation department, Govt of Rajasthan and ground water permission also to be opt (water source will be ground water and surface water)
Water is being purchase through tankers from local suppliers.
5
Consent to Operated under Air (Prevention and Control of Pollution) Act, 1981, Water (Prevention and Control of Pollution) Act,1974 and Hazardous Waste (Management, Handling and Trans boundary Movement) Rules 2016.
Mandatory, shall be applied after getting Environmental Clearance
Valid NOC from RSPCB for existing plant available with INTECH.
(Source: INTECH)
In addition to environmental regulatory compliance, other applicable statutory rules
and regulations including (but not limited to) are the following:
Permission for storage of hazardous/ Explosive Chemicals form Chief Controller of
Explosive (CCOE), Labour laws and Safety guide lines as per Labour
Commissioner, Government of Rajasthan
Boiler Regulations as per Chief Inspector of Boilers, Government of Rajasthan
ESIC.
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1.7. Public Hearing
As per Ministry of Environment and Forest, GOI, New Delhi vide its Notification No. S.O.1533 dated September 14, 2006 and subsequent amendment thereof. An advertisement was published in Dainik Bhaskar and local news Rajasthan Patrika dated 13 September 2017. In the presence of ADM - Pali, SDM- Raipur and Regional officer RSPCB, Rajathan and nearby area public, Public Hearing was conducted on 17thOctober 2017 at Tehsil Office, Raipur for Expansion of Existing pesticide plant for manufacturing of technical grade pesticides at village – Biratiya Kalan, Tehsil – Raipur, Distt Pali, Rajasthan by M/s Intech Organics Limited (Formerly known asIntech Pharma Private Limited) which is coverd under Category-A. Most of the issue raised during public hearing were related to employment, CSR and clarity related to environmental aspects all were addressed satisfactorily (referTable 1.1.as under) The issues raised during the public hearing with reply and public hearing minutes with signatures in hindi language duly signed by RO of RSPPB and ADM Pali are enclosed as Annexure XV.
Table 1.1: Query raise and its response
S.
No.
Name of the person with address
Query/ Suggestion Response
1. Shri Shaitan Singh Village Bhiratia Kalan, Tehsil Raipur, District Pali
Issue raised related to Ambient air emission and its management plan
Authorized Person from the EQMS India Pvt Ltd on behalf of PP have replied that in this proposed project to control air pollution adequate air pollution controlling equipment will be installed such as cyclone separator attached with boiler, Adequate stack height, Alkali scrubbing system to control the fugitive emission.
2. Shri Dilip Nayak Village Bhiratia Kalan, Tehsil Raipur, District Pali
Issue raise related to no. of people to be employed.
Project Proponent responded that proposed expansion project will generate employment for 430 persons (directly or indirectly) and unit will prefer local people for employment as per their qualification.
3. Shri Murlidhar Vaishnav Village Bhiratia Kalan, Tehsil Raipur, District Pali
Query related to Corporate social responsibility from last 2-3 years.
Client representative responded that for corporate Social Responsibility following activities has been proposed.
Medical Camps(for eye and general checkups), cleanliness, sanitation facilities will increase, Renovation of aanganwadi Kendra will be done, will conduct various skill development programs, approach will be to increase
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S.
No.
Name of the person with address
Query/ Suggestion Response
the interest in the field of sports, development of greenbelt will be done for which around 4000 plant samplings will be planted.
4. Shri Jabbar Singh Raipur District Pali
He asked whether waste water will be generated by the company or not.
Project Proponent responded that at present no waste water is generated from the existing unit and for the Proposed expansion safety tank, soak Pit, ETP will be installed and waste water generated will be treated in proposed ETP, maximum water shall be recycled and reused hence Proposed expansion project also based on Zero Liquid Discharge concept.
5. Shri s Lal Bhati, Village Dhulkhedi, Tehsil Raipur District Pali
Issue raise related to Local people employment and number of person employed in existing unit
Project propend responded that currently out of total employed persons 52% of the workers are from local area only and for the proposed expansion 430 person will be employed. Employment shall be provided to the local people on the basis of their capability and educational qualification.
6. Shri Pankaj Chauhan, Village Dhulkhedi, Tehsil Raipur District Pali
soil analysis shall be done for nearby area and assure us there is no harm on our land
Authorized member from Project proponent responded that the product manufactured in the company is Insecticide. The proposed project will not have any effect on the soil quality of the nearby lands.
Environmental monitoring and testing of the samples from the nearby areas has been done and the results shows that the product manufactured in the company will not have any effect on the soil quality and monitoring reports are shown.
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1.8. Approved Terms of Reference for EIA Study by MoEF&CC
Based on the documents submitted and presented before 14thExpert Appraisal
Committee (Industry-2) meeting held during 26th – 27th Oct-2016 and 21stExpert
Appraisal Committee (Industry-2) meeting held on 27th –29th March, 2017. Terms of
Reference (TOR) was issued by MoEF&CC vide their File No: J-.11011/327/2016 IA_II
(I) dated 15th June 2017 for production capacity of 4000 MTPA to 59914 MTPA.
INTECH has also proposes amendment in approved ToR by adding new products,
R&D product and by products as per company stragey and market requirement. Due
to proposes of amendment of ToR, minor changes in Raw materials, water, land, co-
ordinates, layout plant, proposed environment protection etc is also considered in this
EIA report as per standard TOR. Amendment of ToR application has already been
applied on 25th July-2017 in MoEF&CC which received on 11th September 2017
(Letter No. J-11011/327/2016-IA. II (I).
EIA/EMP report is based on approved TOR dated 15th June 2017 & Standard ToR for
Industry-2 and applied for amendment of ToR (which received on 11th September
2017 (Letter No. J-11011/327/2016-IA.II (I))}.
The compliance status of proposed TOR is given in Table 1.2.
Table 1.2 TOR Compliance Status
S. No. Tor Points Compliance
7. Executive Summary Attached with EIA report in English and Hindi
8. Introduction I. Details of the EIA Consultant including
NABET accreditation
NABET accreditation certificate attached as Annexure I
II. Information about the project proponent Project Proponent information given in Chapter1 section no. 1.1of EIA report
III. Importance and benefits of the project. Importance and benefits of the project is given in Section No. 1.3
9. Project Description i. Cost of project and time of completion.
Total cost of the project is Rs 27 Crores, Project implementation initiated after EC recommendations and tentatively scheduled for completion of project is five years.
ii. Products with capacities for the proposed project.
Product with capacities for the Proposed project is given in Chapter 2, Section No. 2.4
iii. If expansion project, details of existing products with capacities and whether adequate land is available for expansion, reference of earlier EC if any.
Existing unit formulating Methyl Bromide (98%)Thus EC not applicable. INTECH proposed expansion to
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manufacture technical grade pesticide chemicals and formulations, details given in chapter 2 Section 2.4
iv. List of raw materials required and their source along with mode of transportation.
Details of Raw Material with Quantity and storage details given in Table No. 2.6. transportation of Raw material to be done by road.
v. Other chemicals and materials required with quantities and storage capacities
Details of raw material is given on Chapter 2 Table No 2.6
vi. Details of Emission, effluents, hazardous waste generation and their management.
Emission, effluents, hazardous waste generation and their management given in chapter 2 Section no 2.5.3.
vii. Requirement of water, power, with source of supply, status of approval, water balance diagram, man-power requirement (regular and contract)
Proposed project utilities given in Chapter 2 Section 2.6
viii. Process description along with major equipment’s and machineries, process flow sheet (quantitate) from raw material to products to be provided
Process description along with Material balance with major equipment’s and machineries given in Chapter 2 Section No. 2.4
ix. Hazard identification and details of proposed safety systems.
Hazard identification and safety measures proposed in Chapter 6
x. Expansion/modernization proposals:
a. Copy of all the Environmental Clearance(s) including Amendments thereto obtained for the project from MOEF/SEIAA shall be attached as an Annexure. A certified copy of the latest Monitoring Report of the Regional Office of the Ministry of Environment and Forests as per circular dated 30th May, 2012 on the status of compliance of conditions stipulated in all the existing environmental clearances including Amendments shall be provided. In addition, status of compliance of Consent to Operate for the ongoing I existing operation of the project from SPCB shall be attached with the EIA-EMP report.
b. In case the existing project has not obtained environmental clearance, reasons for not taking EC under the provisions of the EIA Notification 1994 and/or EIA Notification 2006 shall be provided. Copies of Consent to Establish/No Objection Certificate and Consent to Operate (in case of units
Existing unit formulating Methyl Bromide (98%). Thus EC was not applicable, Expansion is proposing to manufacture some technical grade pesticide chemicals and formulations; Hence EC is applicable. Consent to Establishment and Consent to Operate granted by RPCB is attached as Annexure III, IV & V respectively Compliance report of Consent to operate of existing unit is attached as Annexure V
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operating prior to EIA Notification 2006, CTE and CTO of FY 2005-2006) obtained from the SPCB shall be submitted. Further, compliance report to the conditions of consents from the SPCB shall be submitted
10. Site Details i. Location of the project site covering village,
Taluka/Tehsil, District and State, Justification for selecting the site, whether other sites were considered.
Location of the project site covering village, taluka, district and state is mentioned in Chapter 1 of Section 1.5 As proposed expansion is on adjacent to existing premises thus no other sites were considered.
ii. A topo sheet of the study area of radius of 10 km and site location on 1:50,000/1: 25,000 scale on an A3/A2 sheet. (including all eco-sensitive areas and environmentally sensitive places)
Topo sheet of the study area of radius of 10 km and site location given in Figure 1.2.
iii. Details w.r.t. option analysis for selection of site
As proposed expansion is on adjacent to existing premises thus alternative site selection is not applicable.
iv. Co-ordinates (lat-long) of all four corners of the site.
Co-ordinates (lat-long) of all four corners of site is given in Figure No. 3.4 of EIA report
v. Google map-Earth downloaded of the project site.
Google map of the project site given in Figure No 1.2 of EIA report
vi. Layout maps indicating existing unit as well as proposed unit indicating storage area, plant area, greenbelt area, utilities etc. If located within an Industrial area/Estate/Complex, layout of Industrial Area indicating location of unit within the Industrial area/Estate.
Plant Layout indicating existing unit, proposed expansion unit, storage area, plant area, greenbelt area, utilities etc given in Figure 2.1 of EIA report
vii. Photographs of the proposed and existing (if applicable) plant site. If existing, show photographs of plantation/greenbelt.
Photographs of the proposed and existing site and Green belt are attached as Annexure XII
viii. Land use break-up of total land of the project site (identified and acquired), government/ private - agricultural, forest, wasteland, water bodies, settlements, etc shall be included. (not required for industrial area)
Land use breakup of the total land of the project site is given in Chapter 2 Table No 2.4
ix. A list of major industries with name and type within study area (10km radius) shall be incorporated. Land use details of the study area
No major industries within 10 Km radius. Land use of study area is given in Chapter 3 Section
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3.4 of EIA report.
x. Geological features and Geo-hydrological status of the study area shall be included
Geological features and Geo-hydrological status of the study area given in Chapter 3 Section No. 3.2.3 and 3.3
xi. Details of Drainage of the project up to 5km radius of study area. If the site is within 1 km radius of any major river, peak and lean season river discharge as well as flood occurrence frequency based on peak rainfall data of the past 30 years. Details of Flood Level of the project site and maximum Flood Level of the river shall also be provided. (mega green field projects)
Details of drainage of the proposed project is given in Section No 3.2.2 Figure No 3.6. of EIA report.
xii. Status of acquisition of land. If acquisition is not complete, stage of the acquisition process and expected time of complete possession of the land.
For the proposed expansion project land procurement is under process. Maximum land is already purchased and remaining land is under negotiation with farmers. Land will be in possession of company before EC obtained.
xiii. R&R details in respect of land in line with state Government policy
Not Applicable
11. Forest and wildlife related issues (if applicable): i. Permission and approval for the use of forest
land (forestry clearance), if any, and recommendations of the State Forest Department. (if applicable).
No forest land involve thus not applicable
ii. Land use map based on High resolution satellite imagery (GPS) of the proposed site delineating the forestland (in case of projects involving forest land more than 40 ha)
Land use map of the study area is given in Section 3.4 and Figure 3.9. of Chapter 3 of EIA report
iii. Status of Application submitted for obtaining the stage I forestry clearance along with latest status shall be submitted.
Not Applicable
iv. The projects to be located within 10 km of the National Parks, Sanctuaries, Biosphere Reserves, Migratory Corridors of Wild Animals, the project proponent shall submit the map duly authenticated by Chief Wildlife Warden showing these features vis-à-vis the project location and the recommendations or comments of the Chief Wildlife Warden-thereon.
No national parks Sanctuaries, Bio-sphere reserves, migratory corridor of wild animal found within 10 km of radius of project thus not applicable.
v. Wildlife Conservation Plan duly authenticated by the Chief Wildlife Warden of the State Government for conservation of Schedule I fauna, if any exists in the study area
There is no endangered or Schedule-I faunal species in the study area except Peafowl (Pavo Cristatus)
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which is schedule –I species but is of least concern category. Though a conservation plan for Pavo cristatus,is approved by DFO and Application submitted for approval to Chief Wildlife warden Copy Attached as Annexure VII
vi. Copy of application submitted for clearance under the Wildlife (Protection) Act, 1972, to the Standing Committee of the National Board for Wildlife
Not Applicable
12. Environmental Status i. Determination of atmospheric inversion level
at the project site and site-specific micro-meteorological data using temperature, relative humidity, hourly wind speed and direction and rainfall.
Site-specific micro-meteorological data using temperature, relative humidity, hourly wind speed and direction and rainfall given in Section No.3.5 and 3.5 of Chapter3 of EIA report
ii. AAQ data (except monsoon) at 8 locations for PM10, PM2.5, SO2, NOX, CO and other parameters relevant to the project shall be collected. The monitoring stations shall be based CPCB guidelines and consider the pre-dominant wind direction, population zone and sensitive receptors including reserved forests.
AAQ data (except monsoon) at 8 locations for PM10, PM2.5, SO2, NOX, CO given in Section No 3.6 of Chapter 3 of EIA report
iii. Raw data of all AAQ measurement for 12 weeks of all stations as per frequency given in the NAQQM Notification of Nov. 2009 along with - min., max., average and 98% values for each of the AAQ parameters from data of all AAQ stations should be provided as an annexure to the EIA Report.
Raw data of all AAQ measurement for 12 weeks of all stations attached as Annexure VIII
iv. Surface water quality of nearby River (100m upstream and downstream of discharge point) and other surface drains at eight locations as per CPCB/MoEF&CC guidelines.
Three location taken for Surface water quality, its analysis and observation given in Section No. 3.8 of Chapter No of EIA report.
v. Whether the site falls near to polluted stretch of river identified by the CPCB/MoEF&CC, if yes give details.
Not Applicable
vi. Ground water monitoring at minimum at 8 locations shall be included.
Ground water monitoring at 8 locations given in Section No. 3.8.2 of chapter No. 3 of EIA report
vii. Noise levels monitoring at 8 locations within the study area.
Noise levels monitoring at 8 locations is given in Section No 3.7 of Chapter No 3 of EIA report
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viii. Soil Characteristic as per CPCB guidelines. Soil Characteristic as per CPCB guideline is Given in Section no.3.9 of Chapter No 3. Of EIA report
ix. Traffic study of the area, type of vehicles, frequency of vehicles for transportation of materials, additional traffic due to proposed project, parking arrangement etc.
Site is well connected with NH-112, Traffic study of the area, type of vehicles, frequency of vehicles for transportation of materials, additional traffic due to proposed project, details given in Section No. 3.10 of Chapter No. 3of EIA report
x. Detailed description of flora and fauna (terrestrial and aquatic) existing in the study area shall be given with special reference to rare, endemic and endangered species. If Schedule-I fauna are found within the study area, a Wildlife Conservation Plan shall be prepared and furnished.
Biological environment of the study area given in Section No. 3.11 of Chapter No. 3 of EIA report. The conservation plan for Schedule I species is attached as Annexure VIII.
xi. Socio-economic status of the study area. Socio Economic status of study area is given in Section No.3.12 of Chapter 4 of EIA report
13. Impact and Environment Management Plan i. Assessment of ground level concentration of
pollutants from the stack emission based on site-specific meteorological features. In case the project is located on a hilly terrain, the AQIP Modelling shall be done using inputs of the specific terrain characteristics for determining the potential impacts of the project on the AAQ. Cumulative impact of all sources of emissions (including transportation) on the AAQ of the area shall be assessed. Details of the model used and the input data used for modelling shall also be provided. The air quality contours shall be plotted on a location map showing the location of project site, habitation nearby, sensitive receptors, if any.
Cumulative impact due to proposed project the ground level concentration of pollutants from the stack emission based on site-specific meteorological features given in Section No. 4.3 of Chapter No.4 of EIA report
ii. Water Quality modelling - in case of discharge in water body
Plant based on Zero effluent discharge concepts thus water quality modelling not applicable
iii. Impact of the transport of the raw materials and end products on the surrounding environment shall be assessed and provided. In this regard, options for transport of raw materials and finished products and wastes (large quantities) by rail or rail-cum road
Traffic assessment study carried out, due to proposed expansion project, there will be negligible impact due to additional traffic and road is sufficient to cater the
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transport or conveyor-cum-rail transport shall be examined.
additional load.
iv. A note on treatment of wastewater from different plant operations, extent recycled and reused for different purposes shall be included. Complete scheme of effluent treatment. Characteristics of untreated and treated effluent to meet the prescribed standards of discharge under E(P) Rules.
Generation of high TDS/High COD effluent and Low TDS /Low COD treated in ETP. Detail treatment plan given in Section No. 2.5.1. of chapter no 2 of EIA report
v. Details of stack emission and action plan for control of emissions to meet standards.
Stacks emission with control measures given in Section No. 2.5.2 of Chapter No 2 of EIA report.
vi. Measures for fugitive emission control Fugitive emission control given in Section No 2.5.2 of Chapter No 2 of EIA report
vii. Details of hazardous waste generation and their storage, utilization and management. Copies of MOU regarding utilization of solid and hazardous waste in cement plant shall also be included. EMP shall include the concept of waste-minimization, recycle/reuse/recover techniques, Energy conservation, and natural resource conservation.
Plan for hazardous waste generation and their storage, utilization and management given in Section No 2.5.3. of Chapter no 2 of EIA report Copies of MOU regarding utilization of solid and hazardous waste shall be submitted with Final EIA report.
viii. Proper utilization of fly ash shall be ensured as per Fly Ash Notification, 2009. A detailed plan of action shall be provided.
Fly ash management plan is given in Section No. 5.2 of Chapter No 5 of EIA report
ix. Action plan for the green belt development plan in 33 % area is.e. Land with not less than 1,500 trees per ha. Giving details of species,
width of plantation, planning schedule etc.
shall be included. The green belt shall be around the project boundary and a scheme for greening of the roads used for the project shall also be incorporated.
Action plan for the green belt development plan in 33 % area is given in Section No 5.8 of Chapter No 5 of EIA report
x. Action plan for rainwater harvesting measures at plant site shall be submitted to harvest rainwater from the roof tops and storm water drains to recharge the ground water and to use for the various activities at the project site to conserve fresh water and reduce the water requirement from other sources.
INTECH realizes the importance of rainwater harvesting however it will be prudent that rain water harvesting is not taken up in INTECH plant area. This is because if some hazardous dust (in spite of all possible precautions) gets mixed with rainwater and enter the ground water and the ground water will get
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contaminated. If required INTECH may do rain water harvesting at alternate place with due approval from authorities.
xi. Total capital cost and recurring cost/annum for environmental pollution control measures shall be included.
The overall investment in the project is 2700 lacs About Rs. 382.0 Lac is proposed for the environment protection program.
xii. Action plan for post-project environmental monitoring shall be submitted.
Action plan for post-project environmental monitoring given in Chapter No 5 of EIA report
xiii. Onsite and Offsite Disaster (natural and Man-made) Preparedness and Emergency Management Plan including Risk Assessment and damage control. Disaster management plan should be linked with District Disaster Management Plan
Given as Chapter 6
14. Occupational health i. Plan and fund allocation to ensure the
occupational health & safety of all contract and casual workers
Plan and fund for occupational health and safety for all contract and casual workers shall be complied as per applicable Norms
ii. Details of exposure specific health status evaluation of worker. If the workers' health is being evaluated by pre-designed format, chest x rays, Audiometry, Spirometry, Vision testing (Far & Near vision, color vision and any other ocular defect) ECG, during pre-placement and periodical examinations give the details of the same. Details regarding last month analyzed data of above mentioned parameters as per age, sex, duration of exposure and department wise.
Occupational Health Safety details given in Section 6.21 in Chapter 6 of EIA report
iii. Details of existing Occupational & Safety Hazards. What are the exposure levels of hazards and whether they are within Permissible Exposure level (PEL)?If these are not within PEL, what measures the company has adopted to keep them within PEL so that health of the workers can be preserved,
iv. Annual report of health status of workers with special reference to Occupational Health and Safety.
15. Corporate Environment Policy Corporate HSE Policy is in
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i. Does the company have a well laid down Environment Policy approved by its Board of Directors? If so, it may be detailed in the EIA report.
place and will be followed during the project
execution. Site specific
policy will be developed after commissioning of the
plant.
Details of Corporate HSE policy and compliance mechanism given in Chapter
5.
Hierarchical system of HSE cell is given in Section No 5.3. of Chapter No 5 of EIA report
ii. Does the Environment Policy prescribe for standard operating process / procedures to bring into focus any infringement / deviation / violation of the environmental or forest norms / conditions? If so, it may be detailed in the EIA.
iii. What is the hierarchical system or Administrative order of the company to deal with the environmental issues and for ensuring compliance with the environmental clearance conditions? Details of this system may be given.
iv. Does the company have system of reporting of non-compliances / violations of environmental norms to the Board of Directors of the company and / or shareholders or stakeholders at large? This reporting mechanism shall be detailed in the EIA report
16. Details regarding infrastructure facilities such as sanitation, fuel, restroom etc. to be provided to the labor force during construction as well as to the casual workers including truck drivers during operation phase.
Infrastructure facilities such as sanitation, fuel, restroom etc. to be provided to construction workers including truck drivers during operation phase..
17. Enterprise Social Commitment (ESC) I. Adequate funds (at least 2.5 % of the project
cost) shall be earmarked towards the Enterprise Social Commitment based on Public Hearing issues and item-wise details along with time bound action plan shall be included. Socio-economic development activities need to be elaborated upon.
CSR budget shall be earmarked toward the enterprises social commitment. Item wise details along with time bound action plan will be submitted after public consultation.
CSR given in Section No 2.5.7. Chapter No 2 of EIA report
18. Any litigation pending against the project and/or any direction/order passed by any Court of Law against the project, if so, details thereof shall also be included. Has the unit received any notice under the Section 5 of Environment (Protection) Act, 1986 or relevant Sections of Air and Water Acts? If so, details thereof and compliance/ATR to the notice(s) and present status of the case.
None
19. A tabular chart with index for point wise compliance of above TOR.
Complied
Specific ToR
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20. Commitment that no banned pesticides will be manufactured.
No banned pesticides will be manufactured.
21. Details on solvents to be used, measures for solvent recovery and for emissions control.
There is provision of stripper for recovery of solvent (VOC) from HTDS effluent before MEE shown in Figure No. 2.5 of Chapter No 2 of EIA report
22. Details of process emissions from the proposed unit and its arrangement to control
Stacks emission with control measures given in Section No 2.5.2.of Chapter No 2 of EIA report
23. Ambient air quality data should include VOC, other process-specific pollutants* like NH3*, chlorine*, HCl*, HBr*, H2S*, HF*, CS2etc., (* - as applicable)
Ambient air quality data is given in Chapter 3 Section No. 3.6 of EIA report
24. Work zone monitoring arrangements for hazardous chemicals.
Given in Chapter 6
25. Detailed effluent treatment scheme including segregation for units adopting ‘Zero’ liquid discharge.
Waste water treatment scheme given in Section No 2.5.1.of Chapter No 2. of EIA report Plant based on Zero Liquid Discharge concepts
26. Action plan for odor control to be submitted. To control the odor suction hood will be provided which will be connected to the scrubber. Details is mentioned in Section No.2.5.2 of Chapter No.2. if EIA report
27. A copy of the Memorandum of Understanding signed with cement manufacturers indicating clearly that they co-process organic solid/hazardous waste generated.
Copy of the Memorandum of Understanding Submitted with Final EIA report
28. Authorization/Membership for the disposal of liquid effluent in CETP and solid/hazardous waste in TSDF, if any.
Authorization/Membership for the disposal of solid/hazardous waste in TSDF and other will be Submitted with Final EIA report
29. Material Safety Data Sheet for all the Chemicals are being used/will be used
Attached as Annexure IX
30. Authorization/Membership for the disposal of solid/hazardous waste in TSDF
Authorization/Membership for the disposal solid/hazardous waste in TSDF and other will be Submitted with Final EIA report Existing plant has obtained membership for disposal of hazardous waste from
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt
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EQMS India Pvt. Ltd. 30
S. No. Tor Points Compliance
UCCI, Udaipur, attached as Annexure XI
31. Details of incinerator if to be installed Not applicable
32. Risk assessment for storage and handling of hazardous chemicals/solvents. Action plan for handling & safety system to be incorporated
Refer Chapter 6 mentioned risk assessment.
33. Arrangements for ensuring health and safety of workers engaged in handling of toxic materials.
Refer Chapter 6 mentioned risk assessment.
Additional TOR
34. Public hearing to be conducted and issues raised and commitments made by the project proponent on the same should be included in EIA/EMP Report in the form of tabular chart with financial budget for complying with the commitments made.
Public hearing were conducted on 17th Oct 2017, issues raised and commitment made by project proponent marked in Table 1.1 and PH MOM attached as Annexure XV
35. Adequate plan for Green belt to be drawn and should start from TOR stage in existing plant and shown in EIA report.
Adequate plan for Green belt given in Section No 5.8 of chapter No 5. of EIA report
36. Itemized product capacities to be firmed up and be given in EIA-report.
Product detail with capacities in given in Chapter 2 Section 2.4.
37. Source segregation of process effluent (high TDS/COD and low TDS/COD) to be exercised and Plant shall be based on Zero Liquid Discharge.
Waste water treatment scheme given in Section No 2.5.2. of Chapter No.2. of EIA report Plant shall be based on Zero Liquid Discharge concepts
38. Plan for odor control. Given in Section No 2.5.2.of Chapter No.2.of EIA report
1.9. Structure of the EIA Report
This EIA report has been prepared on the basis of available on-site primary data
(survey/ monitoring) and secondary/literature data. The EIA report contains project
features, baseline environmental setup, assessment of environmental impacts, and
formulation of mitigation measures, environmental management and monitoring plan
with risk & disaster management plan. The report would include 8 Chapters excluding
Executive Summary, which is included at the beginning of the report. The structure of
the EIA Report with necessary tables, drawings and annexure is as follows:
Chapter 1: Introduction
This chapter provides background information on need of project, need of EIA study
and brief of the project. The scope and EIA methodology adopted in preparation of EIA
report have also been described in this Chapter. It also covers the identification of
project & project proponent, brief description of nature, size, location of the project and
its importance to the country and the region. Scope of the study details about the
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EQMS India Pvt. Ltd. 31
regulatory scoping carried out as per the generic structure given in the EIA
Notification, 2006.
Chapter 2: Project Description
This chapter deals with the project details of the proposed Chemicals Manufacturing
Plant, with type of project, need for the project, location, size & magnitude of operation
including associated activities required by and for the project, proposed schedule for
approval and implementation, including technical details of raw material, quality and
quantity etc.
Chapter 3: Description of the Environment
This chapter presents the existing environmental status of the study area around the
proposed project including topography, drainage pattern, water environment,
geological, climate, transport system, land use, flora & fauna, socio-economic
aspects, basic amenities etc. Environmental assessment of the proposed project site
in regard to its capability to receive the proposed new development is also discussed
in this Chapter.
Chapter 4: Anticipated Environmental Impacts and Mitigation Measures
This chapter describes the overall impacts of the proposed project activities and
underscores the areas of concern, which need mitigation measures. It predicts the
overall impact of the proposed project on different components of the environment viz.
air, water, land, noise, biological, and socio-economic.
Chapter 5: Environmental Management Plan & Environmental Monitoring Program
This chapter details the inferences drawn from the environmental impact assessment
exercise. It describes the overall impacts of the proposed activities during construction
and operation phases and underscores the areas of concern, which need mitigation
measures. It also provides mitigation and control measures for environmental
management plan (EMP) for minimizing the negative environmental impacts and to
strengthening the positive environmental impacts of the proposed project. Technical
aspects of monitoring the effectiveness of mitigation measures have been given in this
Chapter also.
Chapter 6: Risk Assessment & Disaster Management Plan
This chapter deals with the risk assessment carried out for the proposed pesticide
manufacturing plant and disaster management plan.
Chapter 7: Summary & Conclusion
This chapter provides the summary and conclusions of the EIA study of the proposed
project with overall justification for implementation of the project and also explanation
of how, adverse effects will be mitigated. This chapter also includes the conclusions
of the Public Hearing.
Chapter 8: Disclosure of Consultants Engaged
This chapter provides the disclosure of consultants engaged to carry out the EIA
study along with other additional studies.
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Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt
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EQMS India Pvt. Ltd. 33
CHAPTER 2. : PROJECT DESCRIPTION
2.1. Project Site Details
M/s Intech Pharma Private Limited has proposed an expansion of existing pesticide
plant to manufacturing of technical grade pesticides located at khasra no 143, 143/1,
118, 118/1, 118/2, 119, 120, 121, 122 at village – Biratiya Kalan, Tehsil – Raipur, Distt
– Pali (Rajasthan).
Table 2.1 : Salient Features of the Project
S. No. Feature Approved TOR dated 15th June-2017
Amendment of ToR (received on 11th September 2017 (Letter No.
J-11011/327/2016-IA.II (I))}
1 Products Technical grade pesticides and Formulations - Major steps of Process: Reaction, Extraction, Distillation Crystallization, Filtration, Drying and Packing etc..
2 Production capacity From 4000 MTPA to 59914 MTPA
From 4000 MTPA to 63414 MTPA
3 Total Plot Area 42907 m2 107165.81m2
4 Water Requirement (KLD) 194 (one time); Daily- 89.5 KLD
221.46 (one time); Daily- 102.14 KLD
5 Power Requirement 3800 KVA, Source Rajasthan Rajya Vidhut Vitran Nigam.
6 Manpower Requirement 430 Nos
7 Green belt 14124 m2 (Approx. 33% of total area)
35365 m2 (Approx. 33% of total area)
8 Project cost including Environmental controlling equipment
Rs.27 crores
9 Environmental Systems Cost (Scrubbers, RO, MEE, ATFD, Stripper, ETP & STP)
Rs. 3.82 crores (capital cost)
10 Recurring cost/ annum for environmental pollution control measures
Rs.35.50 lacs
11 Neighboring Features Bar– 4.71 Kms. SSE [Scattered Habitation Village Biratiya Kalan 1.20 km SW; Hajiwas 2.30 km NNE]
12 Connectivity Nearest railway station: Bar Railway station (6.44km SE); Nearest highway: NH-112 – 1.16 km NH-14----4.85 km S Nearest Airport: Jodhpur Airport 125 km Dabok Airport – 167 km (SSW)
(Source: Site Visit/PFR)
This chapter deals with the project details of the proposed manufacturing of technical
grade pesticide plant with existing pesticide plant and R&D products, location, size &
magnitude of operation including associated activities required by and for the project,
proposed schedule for approval and implementation, including technical details of raw
material, quality and quantity, process, etc.
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EQMS India Pvt. Ltd. 34
Figure 2.1 Plant Layout Plan
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2.2. Land Requirement
The project land is adjacent to existing formulation unit land. Existing land is already
converted for industrial use. Proposed land is mainly single crop agriculture land and is
depend agriculture is depending on rain. The proposed project land distribution is as given
below:
Table 2.2 Land Distribution at Site (As per Approved ToR)
Particulars Land area of Existing
Plant
Land Area after
proposed
expansion
Area(SQM) (%) Area (SQM) (%)
Plant Area, Office Area, 2623 38 20116 47
Paved Area (Road, Corridor,
Parking and drainage) 950 14 4280 10
Green Belt Area 2277 33 14124 33
Open Area 1050 15 4280 10
Total Plot Area 6900 100 42800 100
Table 2.3 Land Distribution at Site (As per Applied for Amendment of ToR)
Particulars Land area of Existing
Plant
Land Area after proposed
expansion
Area(SQM) (%) Area (SQM) (%)
Plant Area, Office Area, 1970.27 38 39513.42 47
Paved Area (Road, Corridor,
Parking and drainage) 725.89 14 22089.60 22
Green Belt Area 1711.03 33 35364.7 33
Open Area 777.74 15 10198.08 10
Total Plot Area 5184.93 100 107165.81 100
Site layout plan is shown in Figure 2.1.
2.3. Products with Capacityforproposed projects
INTECH presently producing a Methyl Bromide (98%) formulation. INTECH proposed
and expansion of existing pesticide plant for manufacture technical grade pesticide
and formulations. Details of the proposed products in expansion projects are as given
below:
Table 2.4 (A): Existing &Proposed products (as per approved TOR)
Name of
Product
Existing
MT/Year
Proposed
MT/Year
Total
MT/Year
Remarks
Methyl Bromide
4000 (98% MB-
Formulation)
10,200 14,200 10,000 (Technical)+4200
(98% formulation)
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Chloropicrin 0 10000 10000 -
Aluminum
Phosphide
0 17,857 17,857 10,000 (Technical)+7857
(56% formulation)
Zinc Phosphide 0 17,857 17,857 10,000 (Technical)+7857
(56% formulation)
BY PRODUCT
H3PO4 (55-60%) 0 1656 1656 -
Sulphuric Acid
(50%-55 % )
0 6660 6660 -
Sodium Bromide
(15%-20%)
0 1500 1500 -
Caustic Solution
10%
0 7296 7296 -
(B) Additional Products (Applied for amendment of TOR)
Name of Product Existing MT/Year
Proposed MT/Year
Total MT/Year
Remarks
N-Propyl Bromide 0 500 500
ISO Propyl Bromide 0 500 500
Vinyl Bromide 0 500 500
2-Cyno-4-Bromo methyl Bi-phenyl
0 500 500
Trimethyl Sulfoxonium Bromide
0 500 500
Ethyl Bromide 0 500 500
R& D Product 0 500 500
BY PRODUCT
Sulphuric Acid / Spent Acid 0 500 500
Hydro Bromic Acid 0 617 617
(C) Commulative Products {Approved ToR and Applied for amendment of TOR
(received TOR on 11th September 2017 (Letter No. J-11011/327/2016-IA. II (I))}
Name of Product CAS No
LD 50 LC50 Existing MT/Year
Proposed
MT/Year
Total MT/Ye
ar
Remarks
Methyl Bromide
74.83.9
Oral LD 214
mg/kg Rat
1-hour inhalation
LC50 in rats is 4.5 mg/L,
4000 (98% MB-Formulatio
n)
10,200 14,200 10,000 (Technical)+42
00 (98% formulation)
Chloropicrin 76-06-2
Oral LD 50 37.7 mg/kg
Rat
4-hour inhalation LC50 for chloropicrin vapor in rats is 11.9 ppm
0 10000 10000 -
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt
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Aluminum Phosphide
20859-73-8.
11.5 mg/kg
The rodent 4-hour
inhalation LC50 for
phosphine gas is 10.7
ppm
0 17,857 17,857
10,000 (Technical)+7
857 (56% formulation)
Zinc Phosphide 1314-84-7.
In rats, the LD50
for the technical product
is 40 mg/kg,
In bluegill sunfish
(LC50 = 0.8 mg/l) and
rainbow trout (0.5 mg/l)
0 17,857 17,857
10,000 (Technical)+7
857 (56% formulation)
N-Propyl Bromide 106-94-5
3600 mg/kg
Rat
Inhaation253 g/m3 Rat 30
min 0 500 500
ISO Propyl Bromide
75-26-3
LD50:4837 mg/kg
Inhalation 31171 ppm , Mouse 4 hrs
0 500 500
Vinyl Bromide
593-60-2.
LD50: 500
mg/kg (Oral, Rat)
inhalation (2h) LC50 for rat, 390 mg/l, 0 500 500
2-Cyno-4-Bromo methyl Bi-phenyl
114772 – 54
– 2
-- -- 0 500 500
TrimethylSulfoxonium Bromide
25596-24-1
-- --- 0 500 500
Ethyl Bromide
74-96-4
ORAL (LD50): Acute: 1350 mg/kg [Rat]
VAPOR (LC50):
Acute: 13490 ppm 4 hour(s)
0 500 500
R & D Product
BY PRODUCT
H3PO4 (55-60%) 7664-38-2
ORAL (LD50): Acute: 1530 mg/kg [Rat]
DUST (LC50):
Acute: >850 mg/m 1
hours [Rat].
0 1656 1656 -
Sulphuric Acid (50%-55 % )
7664-93-9
ORAL (LD50): Acute: 2140 mg/kg [Rat.].
VAPOR (LC50):
Acute: 510 mg/m 2
hours [Rat].
0 7160 7160 -
Sodiuim Bromide (15%-20%)
7647-15-6
ORAL (LD50): Acute: 3500 mg/kg [Rat
Fish: Bluegill/Sunfish: LC50 > 1000 mg/L;
96h;
0 1500 1500 -
Caustic Solution 10%
1310-73-2
Dermal Inhalation, 0 7296 7296 -
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt
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EQMS India Pvt. Ltd. 38
LD50 Rabbit: 1350 mg/kg
rat: LC50 = 2300 mg/m3/2H;
Hydro Bromic Acid
10035-10-6
Oral, rat: LD50 =
>90 mL/kg;.
Inhalation, rat: LC50 =
2858 ppm/1H;.
0 617 617
2.4. Manufacturing Process
Manufacturing process steps of pesticides with their mass/ material balance are
described in this section: -
A. METHYL BROMIDE
1) The Raw material are charged into reaction vessel as per stoichiometry
2) The reaction takes place in standard temperature & pressure converting the
raw material into product Methyl Bromide
3) The Methyl Bromide is then purified to remove the inorganic bromides with
the caustic soda solution and soda ash solution
4) The Methyl Bromide is scrubbed in Sulphuric acid to remove moisture in the
Methyl Bromide
5) The methyl bromide is liquefied and stored in the storage tank
6) The Additive warning agent chloropicrin is added in formulating tank.
7) The formulated Methyl Bromide is packed in assorted packing in cans and
cylinders
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Table 2.5 Material Balance for Methyl Bromide
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Product
Remarks
1 Bromine 0.84 Methyl Bromide 0.924
2
Sulphur
0.05 Sulphuric Acid 0.26 Combined is Spent
Acid which is a By
Product
3 Methanol
0.34 Sodium Bromide 0.116 Sodium Bromide is By
Product
4 Water 0.03
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5 Caustic 0.02
6 Soda Ash 0.02
Total 1.3 Total 1.3
Note – These are the theoretical values calculated on stoichiometric reaction
B. CHLOROPICRIN
The Raw materials i.e. Sodium hypo chloride is charged into reaction vessel and
Nitromethane will be added slowly in reaction vessel.
The reaction is taken place in standard temperature & pressure converting the raw
material into product CP
Thereafter agitation will be done for 1 hour and settling of the same will be carried
out.
After settling caustic will be separated from the product.
Product will be filtered and collect
MATERIAL BALANCE FOR CHLOROPICRIN
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Product
Remarks
1 Hypo –NaOCl 1.359 CP 1.000
2 Nitromethane-
CH3NO2 0.371 Caustic 0.729
Total 1.729 Total 1.729
Note – These are the theoretical values calculated on stoichiometric reaction
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C. ALUMINUM PHOSPHIDE
Process Description
Aluminium Phosphide is manufactured by reacting Al and Phosphorous in a closed
reactor. Al Phosphide is formed, instantaneously liberating heat of reaction which
externally control to circulating water in jacket of reactor.
After complete the reaction, Technical Al Phosphide generated, which is finally
blended with other ingredients as per the market demand.
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During the course of reaction, P2O5 (as H3PO4 mist) generated, which are pass
through scrubber, followed with mist eliminator so as to control the emission of
pollutant. Dilute Phosphoric Acid is generated as by-product.
Material Balances for Aluminum Phosphide
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Product
Remarks
1 Al –Powder 0.47 Al Phosphide 1
2
Phosphorous
0.636 Phosphoric Acid
( 50 %)
0.212 Phosphoric Acid is
scrubbed
3 Water 0.106
Total 1.212 Total 1.212
Note – These are the theoretical values calculated on stoichiometric reaction
D. ZINK PHOSPHIDE
Process Description
Zinc Phosphide is manufactured by reacting Zinc and Phosphorous in a closed
reactor. Zinc Phosphide is formed, instantaneously liberating heat of reaction which
externally control to circulating water in jacket of reactor.
After complete the reaction, Technical Zinc Phosphide generated, which is finally
blended with other ingredients as per the market demand.
During the course of reaction, P2O5 (as H3PO4 mist) generated, which are pass
through scrubber, followed with mist eliminator so as to control the emission of
pollutant.
Dilute Phosphoric Acid is generated as by-product.
MATERIAL BALANCE ZINC PHOSPHIDE
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Product
Remarks
1 Zinc -Powder 0.76 Zinc Phosphide 1
2
Phosphorous
0.276 Phosphoric Acid
( 50 %)
0.082 Phosphoric Acid is
scrubbed
3 Water 0.046
Total 1.082 Total 1.082
Note – These are the theoretical values calculated on stoichiometric reaction
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Figure 2.2 Process Flow Diagram
Additional Products (Applied for Amendment of ToR)
1. N-PROPYL BROMIDE: -
The Raw materials i.e. water; sulphur and NPA are charged into reaction vessel along
with the brominating as per stoichiometry.
The reaction is taken place in standard temperature & pressure converting the raw
material into product Nab
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The NPBr is going through with agitation, settling and separator. Spent acid separated
from the main product.
Product will be washed and distilled and collect final product.
Material Balance for N-Propyl Bromide
Sr No
Raw Material Input/MT of Product (MT)
Product / By Product
Output MT/ MT of
Product
Remarks
1 N-PROPHYL ALCHOHAL (NPA) 0.488 NPBr 1.000
2 SULPHUR (S) 0.043 Spent Acid 0.230
3 BROMINE (Br) 0.650 WASTE WATER 2.006
4 SODA ASH (Na2CO3) 0.005
5 SALT (NaCl) 0.001
6 WATER 0.049
7 WASHING WATER 2.000
Total 3.236 3.236
Note – These are the theoretical values calculated on stoichiometric reaction
GLASS LINE REACTOR
WATER
SULPH
UR
NPA
OTBNAGITATION /
SETTLING / SEPERATOR
BROMINATI
ON
DISTILLATION
NPBr
SPENT
ACID
RESIDUE
WASHING WASTE
WATER
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2. ISO-PROPYL BROMIDE: -
The Raw materials i.e. water; sulphur and IPA are charged into reaction
vessel along with brominating as per stoichiometry.
The reaction is taken place in standard temperature & pressure converting
the raw material into product IPBr
The IPBr is going through with agitation, settling and thereafter separator.
Spent acid separated from the main product.
Product will be washed and distilled and collected final product.
Material Balance for ISO-Propyl Bromide
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Product
Remarks
1 N-PROPHYL
ALCHOHAL
(NPA) 0.488 NaBr 1.000
2 SULPHUR (S) 0.043 Spent Acid 0.230
3 BROMINE (Br) 0.650 WASTE WATER 2.006
4 SODA ASH
(Na2CO3) 0.005
5 SALT (NaCl) 0.001
GLASS LINE REACTOR
TER SULPHUR
IPA
AGITATION / SETTLING /
SEPERATOR
BROMINATION
DISTILLATION
IPBr
SPENT ACID
RESIDUE
WASHING WASTE WATER
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6 WATER 0.049
7 WASHING
WATER 2.000
Total 3.236 3.236
Note – These are the theoretical values calculated on stoichiometric reaction
3. VINYL BROMIDE: -
The raw material i.e. MEG, Sulphur charged into glass line reactor along with brominating as per stoichiometry.
The reaction is taken place in standard temperature & pressure converting into product intermediate.
Agitation, settling and separation to be carried out of product and spent acid separated from product.
In glass line reactor agitation, settling and separation carried out and HBr will be separated from final product i.e. vinyl bromide.
GLASS LINE REACTOR
RAW MATERIAL CHARGING MEG
SULPHUR
WATER
NAGITATION / SETTLING
SEPERATOR
BROMINATION
DISTILLATION
INTERMEDIATE
SPENT ACID
RESIDUE
GLASS LINE REACTOR
AGITATION / SETTLING
SEPERATOR
VINYL BROMIDE
HBr
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Material Balance of Vinyl Bromide
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Productr
Remarks
1 MEG (MONO-
ETHELENE
GLYCOL) 0.579 NPBr 1.000
2 BROMINE 1.495 Spent Acid 0.230
3 SULPHUR 0.100 WASTE WATER 2.006
4 WATER 2.000
5 CAUSTIC 0.005
6 SODA ASH 0.005
Total 4.184 4.184
Note – These are the theoretical values calculated on stoichiometric reaction
4. BROMO-OTBN[2-CYNO 4-BROMOMETHYLBI-PHENYL]:-
The Raw materials i.e. water, MDC, OTBN, are charged into reaction vessel along
with bromination as per stoichiometry. A reactive agent AIBN also added in the
reaction vessel.
The reaction is taken place in standard temperature & pressure converting the raw
material into crude product (Bromo – OTBN)
HBr is separated from the product. Product will be washed by sodium bi-carbonate
and water.
Product will be distilled and solvent to be recovered. Further product will be washed
through methanol.
Further product will centrifuge and methanol solvent will recover.
Received product in powder form and it will be dried and collect finish product.
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Material Balance of Bromo OTBN
Sr No
Raw Material Input/MT of Product (MT)
Product / By Product
Output MT/ MT of
Product
Remarks
1 OTBN 0.710 BROMO OTBN 1.000
2 BROMINE (Br) 0.588 HBr 0.364
3 MDC (METHYL DI-CHLORIDE) 3.548 MDC 3.193
4 METHANOL 1.500 METHANOL 1.275
5 WATER 0.066 WASTE WATER 2.051
6 SODIUM BI-CARBONATE 0.050 RESIDUE 0.580
7 AIBN 0.001
8 WASHING WATER 2.000
Total 8.463 8.463
Note – These are the theoretical values calculated on stoichiometric reaction
GLASS LINE REACTOR
WATER MDC
OTBN
AIBN
AGITATION / SETTLING /
SEPERATOR
BROMINATIO
DISTILLATION
MDC
HBr
CRUDE PRODUCT
WASHING WASTE WATER
CENTRIFUSE
BROMO-
METHANOL
MENTHANO
L WASHING
MOTHER
LIQUOR
METHANOL
RECOVERY
MDC
RECOVERY
RESIDUEWA
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EQMS India Pvt. Ltd. 49
5. TRIMETHYL SUIFOXONIUM BROMIDE (TMSOBr):-
The Raw material are charged into reaction vessel along with solvent and catalyst as per stoichiometry
The reaction is taken place in standard temperature & pressure converting the raw material into product TMSOBr
Solvent to be recovered from process and finished product will be collected.
Material Balance of TMSOBr
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Product
Remarks
1 MBr 0.549 TMSOBr 1.000
2 DMSO 0.451 IPA 0.851
3 CATALYSY -
TMOF 0.001 RESIDUE 0.150
4 IPA (ISO-
PROPYL
ALCHOHAL) 1.000
Total 2.001 2.001
Note – These are the theoretical values calculated on stoichiometric reaction
GLASS LINE REACTOR
DMSO
TMOF
IPA
AGITATION / SETTLING
SEPARATOR
MBr
IPA
IPA
RECOVERY
TMSOBr
RESIDUE
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EQMS India Pvt. Ltd. 50
6. ETHYL BROMIDE (EBr): -
The Raw material are charged into reaction vessel along with bromination as per stoichiometry
The reaction is taken place in standard temperature & pressure converting the raw material into product EBr
Spent acid to be separated from the product by separator.
Product to be distilled and final product will collect.
Material Balance of EBr
Sr
No
Raw Material Input/MT of
Product (MT)
Product / By
Product
Output MT/
MT of
Productr
Remarks
1 ETHANOL 0.422 Ebr 1.000
2 BROMINE (Br) 0.734 SPENT ACID 0.232
3 WATER 0.028 WASTE WATER 1.005
4 SULPHUR 0.049
5 SODA ASH
(Na2CO3) 0.005
6 WASHING
WATER 1.000
Total 2.237 2.237
Note – These are the theoretical values calculated on stoichiometric reaction
GLASS LINE REACTOR
ETHANOL
WATER
SULPHUR
AGITATION / SETTLING
SEPARATOR
BROMINATION
DISTILLATION
EBr
SPENT ACID
RESIDUE
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EQMS India Pvt. Ltd. 51
2.4.2 Equipment List
Some of the key equipment for the proposed expansion project are given below as
these are in engineering stage: -
A. Methyl Bromide& their derivatives products:
Sr. No Particulars
1 Glass lined reactor
2 S.S. 316 storage tank
3 Moisture absorption traps
4 Supporting condensers in MSGL- 12 sqmtrs with necessary lagging
covered with glass wool.
5 30 TR X 2 capacity chilling plant , with 100 HP motor along with
circulation pumps Chilling lines to all the receiving vessels and
delivery lines at -15 C
6 Steam pack boiler 4 TPH capacity 3 nos
7 Transformer 1000 kVA / 2000 kVA./ 800 kVA
8 semi-automatic can filling machine
9 semi-automatic can sealing machine
10 Air Compressors
11 Cooling Towers
12 25 MT MS storage tank for Methanol &
13 25 KL tank for Sulfuric acid
14 SS 316 Glass Lined Tanks
15 Fractional Distillation Units Glass Columns with fittings
16 SS-316 Storage tanks
17 HDPE Storage tanks 15KL
18 DG set 1000 kva / 2X 500 kVA
B. Aluminum/Zinc Phosphide:
Sr.
No.
Particulars
1 Reaction Pot
2 Mixing Unit
3 Phosphorous melter
4 P2O5 Scrubbing system
5 Burning Chamber
6 Cooling Chamber
7 Jaw Crusher
8 Rod Mill
9 Vibro Screen
10 Ribbon Blander
11 Knife Grinder
12 Tableting Machine
13 N2 Plant
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EQMS India Pvt. Ltd. 52
C. Chloropicrin
Sr. No Particulars
1 Glass lined reactor
2 30 TR X 2 capacity chilling plant with 100 HP motor along with
circulation pumps
3 Storage for Product
There will no major equipment added due to increase the production capacity for which
amendment of ToR application has been applied to MoEF&CC.
2.5 Raw Materials required along with estimated quantity,
Raw material shall be sourced from registered supplier within India and Imported (if
required) based on the need and availability. Details of raw material along with the
Quantity and Means of storage is given in Table 2.4
Table 2.6 Details of Raw Material with Quantity
S. No Material Storage Quanity at site
Mode of Transportation
Storage Facility
A TOR APPROVED (dated 15th June 2017, F.No J-11011/327/2016-IA.II(I)
1 Methanol 50 T Through Tankers Underground storage tank (25 T X 2 )
2 Sulphuric acid 50 T Through Tankers Above ground storage tank (50 T X 1 )
3 Bromine NIL Through ISO tankers
In ISO Tanker Storage (No storage at Site)
4 Phosphorus 100 T Through Trucks In packed drums Above ground
5 Caustic Soda 20 T Through Trucks Above ground under shed
6 Nitro-methane 50 T Through ISO Tankers / trucks
In drums, above ground, under shed
7 Sodium Hypo Chloride
100 T Through Tankers Storage Above ground in drums / tanks
8 Soda Ash 5 T Through Trucks In Bags, Above ground under shed
9 Sulphur 10 T Through Trucks In Bags, Above ground under shed
10 Al-powder 50 T Through Trucks Above ground under shed
11 Zinc Powder 50 T Through Trucks Above ground under shed
B. Applied for amedement in TOR Additional Raw Materials (Received TOR on 11th September 2017 (Letter No. J-11011/327/2016-IA.II (I))}
1 N-Propyl Alchohal (NPA)
5 T Through Tankers / trucks
Storage in Drum / Storage tank
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EQMS India Pvt. Ltd. 53
2 Salt (NaCl) 2 T Through Trucks In Bags, Above ground under shed
3 ISO-Propyl Alcohol 5 T Through Tankers / trucks
Storage in Drum / Storage tank
4 MEG (Mono-Ethylene Glycol)
5 T Through Tankers / trucks
Storage in Drum / Storage tank
5 OTBN 5 T Through Trucks Storage in Drum
6 MDC (Methylene Di-Chloride)
10 T Through Tankers / Truck
Storage in Drum / Storage tank
7 Sodium Bi-Carbonate 2 T Through Trucks In Bags, Above ground under shed
8 DMSO 5 T Through Tankers / Truck
Storage in Drum / Storage tank
9 Ethanol 5 T Through Tankers / Truck
Storage in Drum / Storage tank
C (A+B)
Cumulative Raw Material List (As per Approved ToR and Applied for amendment of ToR which received on 11th September 2017 (Letter No. J-11011/327/2016-IA.II (I))
S. No Material Storage Quantity
at site
Mode of Transportatio
n Storage Facility
CAS NO
LD50 LC 50
1 Methanol 50 T Through Tankers
Underground storage tank (25 T X 2 )
67-56-1.
5825 MG/KG rat
83.2mg/L RAT (4 H)
2 Sulphuric acid
50 T Through Tankers
Above ground storage tank (50 T X 1 )
7664-93-9
2140 mg/kg Rat
510 mg/m3 (Rat) 2 Hrs
3 Bromine NIL Through ISO tankers
In ISO Tanker Storage
7726-95-6
Acute oral toxicity (LD50): 2600 mg/kg [Rat]
Acute toxicity of the vapor (LC50): 750 1 hours [Mouse].
4 Phosphorus (white)
100 T Through Trucks
In packed drums Above ground
12185-103
LD50 Rat (Charles-River, female) oral 3.03 mg/kg
Highly toxic. LC50< 2 mg/l
5 Caustic Soda 20 T Through Trucks
Above ground under shed
1310-73-2
Dermal LD50 Rabbit: 1350 mg/kg
Inhalation, rat: LC50 = 2300 mg/m3/2H;
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– Pali, Rajasthan
EQMS India Pvt. Ltd. 54
6 Nitro-methane
50 T Through ISO Tankers / trucks
In drums, above ground, under shed
75-52-5
ORAL (LD50): Acute: 940 mg/kg [Rat.].
LC50 > 12.75 mg/L ( Rat ) 1 h
7 Sodium Hypo Chloride
100 T Through Tankers
Storage Above ground in drums / tanks
7681-52-9
LD50 = 8200 mg/kg ( Rat )
> 10500 mg/l (Rat) 1h
8 Soda Ash 5 T Through Trucks
In Bags, Above ground under shed
497-19-8.
4090 mg/kg ( Rat )
Inhalation Rat 2.30 mg/LRat 2 Hrs
9 Sulphur 10 T Through Trucks
In Bags, Above ground under shed
7704-34-9
Rat oral LD50 of greater than 5,000 mg/kg
The acute inhalation LC50 sulfur in rats is greater than 2.56 mg/l;
10 Al-powder 50 T Through Trucks
Above ground under shed
7429-90-5.
> 2000 mg/kg
> 888 mg/l/4 Hr Rat
11 Zinc Powder 50 T Through Trucks
Above ground under shed
7440-66-6
>2000 mg/Kg
> 5.41 mg/L Inhalation
12 N-Propyl Alcohol (NPA)
5 T Through Tankers / trucks
Storage in Drum / Storage tank
71-23-8
ORAL (LD50): Acute: 1870 mg/kg [Rat.].
VAPOR (LC50): Acute: 67882.3 ppm 4 hour(s) [Mouse].
13 Salt (NaCl) 2 T Through Trucks
In Bags, Above ground under shed
7647-14-5
3000 mg/kg Rat Oral
7650 mg/l Fishes
14 ISO-Propyl Alcohol
5 T Through Tankers / trucks
Storage in Drum / Storage tank
67-63-0.
ORAL (LD50): Acute: 5045 mg/kg [Rat]
73 mg/l/4h (Rat) Inhalation
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt
– Pali, Rajasthan
EQMS India Pvt. Ltd. 55
15 MEG (Mono-Ethylene Glycol)
5 T Through Tankers / trucks
Storage in Drum / Storage tank
107-21-1
ORAL (LD50): Acute: 4700 mg/kg [Rat].
VAPOR (LC50): Acute: >200 mg/m 4 hours [Rat].
16 OTBN 5 T Through Trucks
Storage in Drum
114772-53-1.
OralLD 50 1421 mg/Kg (Rat)
--
17 MDC (Methylene Di-Chloride)
10 T Through Tankers / Truck
Storage in Drum / Storage tank
75-09-2
ORAL (LD50): Acute: 1600 mg/kg [Rat].
Acute toxicity of the vapor (LC50): 52000 1 hours [Rat].
18 Sodium Bi-Carbonate
2 T Through Trucks
In Bags, Above ground under shed
144-55-8
Acute oral toxicity (LD50): 3360 mg/kg [Mouse].
Inhalation Rat LC50: >4.74 mg/l for 4.5 hrs
19 DMSO 5 T Through Tankers / Truck
Storage in Drum / Storage tank
67-68-5.
ORAL (LD50): Acute: 14500 mg/kg [Rat
Inhalation - rat - 4 h - 40250 ppm
20 Ethanol 5 T Through Tankers / Truck
Storage in Drum / Storage tank
64-17-5.
Oral, rat: LD50 = 9000 mg/kg;
Inhalation, rat: LC50 = 20000 ppm/10H;
Note – Henceforth cumulative List of products and raw material details will be
presented in EIA report.
2.5.2 Bulk Storages
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– Pali, Rajasthan
EQMS India Pvt. Ltd. 56
The following raw materials will be stored in bulk with required safety measures.
Table 2.7 Bulk Storage
S. No Material Capacity Remarks
RAW MATERIAL
1 Methanol 2X 25 MT Underground tanks
2 Sulphuric acid 50 MT Over ground Tank
2.6 Infrastructure& Utilities required for INTECH Proposed Expansion Project: -
2.6.1 Water requirement and water balance
As per approved ToR
One-time water demand after expansion will be 194.5 KLD. Daily fresh water demand
will be 89.5 KLD which will be sourced from tanker water supply. By implementing
various recycle/reuse schemes water will be reused/recycled. Water consumption &
Waste water generation breakup is given in Table 2.8
Table 2.8 Water consumption & Waste water generation in Existing Plant
Sr. No Description Water Consumption
KLD
Waste Water
Generation
(KLD)
Effluent Treatment &
Disposal Facility
1 Domestic 5 4 To Soak pit
2 Process 0 - -
3 Cooling tower 3 0.3 After treatment for
Greenbelt
4 Boiler 3 0.5
5 Floor washing
and equipment
washing
1 1
Fresh Water
consumption
12
Cumulative Water Requirement and Water Balance Approved ToR and Applied for
amendment of ToR (received TOR on 11th September 2017 (Letter No. J-11011/327/2016-
IA.II (I))}
One time consumption= Recycle water +Fresh water requirement ( Loss +By products)
221.47 KL = (119.33+102.14) KL
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– Pali, Rajasthan
EQMS India Pvt. Ltd. 57
Table 2.9 Total water Consumption and Waste Water Generation
1 One Time Consumption (First Day)
1.1 Process water 22.27 KL
1.2 Cooling Water 61 KL
1.3 DM Plant 113.2 KL
1.4 Plant washing 5 KL
1.5 Domestic consumption 20 KL
Total 221.47 KL
2 Recycle water
2.1 ETP Recycle 22.33 KL
2.2 Boiler 97 KL
Total 119.33 KL
3 Fresh water requirement(Loss+ By product)
3.1 By Product 8.77 KL
3.2 ETP Loss 8.57 KL
3.3 Cooling tower Loss 54 KL
3.4 Boiler steam Loss 10.8 KL
3.5 Domestic loss ( Gardening fallowed by STP) 20 KL
Total 102.14 KL
Figure 2.3 Combined Water Balance for proposed expansion project (With TOR
approved and applied for Amendment)
Note – Henceforth cumulative/Final Water Consumption, waste water generation and water
balance details will be presented in EIA report.
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EQMS India Pvt. Ltd. 58
2.5.1 Power Requirement
Existing Plant Load 800 kWA; Additional plant load 3000 kVA
Total Plant load after expansion= 3800kVA. Power is supplied by Rajasthan
RajyaVidut Vitran Nigam.
DG set
Existing DG is 400 kVA and proposed 500 kVA (2 Nos)/ 1X1000 kVA, fuel: HSD, as
and when required during power failure during emergencies.
Power requirement due to amendment of ToR product will be cater in proposed power
requirement.
2.5.2 Fuel
S. No
Particulars Fuel used Fuel consumption (Approximate)
(PER HOUR) Existing
1 Boilers LDO 42 ltr.
2 DG HSD 80 ltr. (During Power failure only)
Proposed
1 Boilers (3 Nos @ each 4 Ton)
Briquette/LDO For briquette - 700 - 900 Kg / Hr For LDO -220 ltrs/hr
2 DG (500 kVA) – 2 nos HSD 106 Ltrs / hr (During Power failure only)
LDO / HSD Storage—5 KL each; Briquette Storage —500 MT
Ash generated from uses of Briquette (~ 0.98 MT/day ;(~ 30 MT / month) will be
disposed off to Brick/Cement manufacturers/ or for road development.
2.5.3 Employment / Manpower
During the construction phase, around 100 workers and during operational phase
around 330 workers (including contractors) will be required. Local skilled and semi-
skilled workers will be engaged during construction phase of the project to extent
possible as per their eligibility. The positives impact includes enhanced direct
employment for technical/ administrative works and in direct employment opportunities
for transporters of raw materials and finished goods.
Manpower
Total Skilled 170
Total Semi – skilled 50
Total Unskilled 210
Grand total 430
2.5. Environmental Aspects:
2.5.1. Liquid Effluent Management
Effluent Treatment Facility
Entire quantity of generated wastewater will be treated in 30.9 KLD ETP.
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EQMS India Pvt. Ltd. 59
Wastewater will be segregated into two streams as High TDS / High COD (HTDS) and
Low TDS / Low COD (LTDS). The HTDS Effluent stream generated from process.
HTDS effluent will be collected in equalization tank and thereafter sent to
neutralization, Settling and solvent stripper will be sent to Multi Effect Evaporator
(MEE). The distillate water will be treated in ETP along with LTDS effluent. The
concentrate will be sent to ATFD for drying. The dried salt will be sent to approved
TSDF for final disposal. The ETP treated effluent will be passed through RO for
recovery of water for recycling. The RO reject will be send to MEE.No process effluent
will be discharged outside the plant premises. There is provision of stripper for
recovery of solvent (VOC) from HTDS effluent before MEE. The inorganic hazardous
residues will be sent to TSDF.
The other source of wastewater generation will be domestic Sewage of 16 KL/day;
which will be treated in STP. Treated water from STP will be used for greenbelt
development, Thus, there will not be any major impact on the water environment due
to proposed activities.
ETP flow diagram is given below:
Figure 2.4 ETP Flow Diagram
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EQMS India Pvt. Ltd. 60
Table 2.10 Effluent Standards for Pesticide Industry
S. No Parameter Concentration not to
exceed, mg/l (except pH)
1. pH 6.5 – 8.5
2. BOD (3 days at 270C)
Technical grade unit 100
Formulation Unit 30
3. Oil& Grease 10
4. Suspended Solids 100
5. Bioassay test 90% survival of fish after 96
hrs in 100% effluent
6. Arsenic (as As) 0.2
7. Copper 1
8. Manganese 1
9. Mercury 0.01
10. Antimony (as Sb) 0.1
11. Zinc 1
12. Phenol & Phenolic compounds 1
(Source:CPCB )
2.5.2. Emission Control System: -
The sources of air emission in INTECH proposed project are Boilers, DG sets (during
power failure only) and process stacks. Dust can be generated from Drying and
micronizing the product. The product dry material is collected through cyclone
separator and bag filter to control any fine particle contamination in air.
DG SET
Three numbers DG sets are provided with complete CPCB approved acoustic
enclosure and vent pipe (stack) including existing stack
Emission Control Measures
The principal impacts on air environment shall be due to operation of flue gas stacks
and process stacks – Briquettes / LDO shall be used as fuel in the boilers & DG sets.
To minimize the impacts due to emission from boilers, cyclone separators & bag filter
shall be provided as air pollution control equipment. The process vents shall be
attached to efficient adequate Acidic or alkali scrubber to remove pollutant from
process emission.
The details of stacks and vents along with height, type of fuel, fuel consumption rate,
control measure etc. is referred in Table2.11.
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EQMS India Pvt. Ltd. 61
Table 2.11 Stacks for Proposed Projects
SN Stack Attached
Stack Height in Meter;(From Ground)
Stack Dia
Flow in Nm3/hr; /Temp in 0C
Pollutants Concentration in mg/Nm3
Remarks
1 Boilers (3Nos each of 4 T capacity; Briquette/ LDO fired)
30 (Three Stacks)
700 mm (At Top)
7800/ 115 SPM<150 SO2 <50 NOx < 150
(Separate stacks for each boiler of 4TPH)
2 Process Stack Alkaline Scrubbers
10 0.3 ~940/37 PM < 20
HBr< 05
Common stack for all alkaline scrubbers
3 Process Stack Water Scrubbers
30 0.3 ~940/65 PM < 20
P2O5 (as H3PO4) < 10
Common stack for all acidic scrubbers
Air Pollution Control Systems with Stack Details
Gaseous emission from fuel burning, consist of common pollutants like SO2, NO2,
and PM would be discharged into atmosphere through Stack of suitable height.
Green belt will be developed covering >33% of the total project area, around the
plant boundary as dust preventive barrier.
Odour Control System: All the vents of the batch tanks and solvents are connected to
scrubber to absorb any pollutant / odour producing gases and chemicals. Green belt
around the plant boundary will absorb the odour to some extent.
The operation of centrifuging/ filter will be done in closed equipment to avoid any
vapours coming out in the local atmosphere. The vents of centrifuges / filters will be
connected to scrubbers.
The drying of the product (if required) is done in a closed type continuous Fluidized
Bed dryer/ Nudge filter to avoid the exposure of any chemicals to human being.
Volatile organic solvents are carefully handled in a closed system, thereby preventing
any discharge of these chemicals into the air.
Odour Control Measures
Adequate systems shall be provided to capture the odour /emissions from process
plants & maintain the emission quality as per recommended guidelines with central
scrubber having caustic solution, before venting it in to the atmosphere.
Control Measures.
All liquid raw materials and intermediates are charged into Reactors with pumps or
under gravity through closed pipes.
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1. All vents of holding tanks and dosing vessels are connected to a Vent Scrubber
system comprising of a suction Blower, Acid Scrubber, Alkali Scrubber before
venting through a tall stack.
2. Suction Hoods are placed near the Man-holes & Charging funnels of Reactors &
Filters so that chemical vapours and dust do not escape into the Plant
&surroundings, when the man-hole covers are opened for inspection or charging
of RM.
3. All storage tanks of low boiling solvents / chemical are provided with Conservation
Vents.
4. Vents of acid storage tanks are provided with a Water filled trap to prevent Acid
fumes from escaping out.
5. All pumps handling hazardous chemicals are provided with mechanical seals to
prevent fugitive emission. Wherever possible magnetic coupled pumps will be
used.
6. Any spillage from drums etc. will be absorbed with saw dust / soda ash and
moped clean. The contaminated absorbent will be safely disposed off along with
hazardous waste.
Fuel combustion: The fuel combustion is from DG sets, boilers (Briquette/LDO fired).
By controlling optimum conditions and in built internal cyclones and bag filters and
also the stack heights the level of particulate matter, SO2 and NOX concentrations are
kept within prescribed limiting standards.
Table 2.12 National Emission Standards for Pesticide Manufacturing and Formulation
Industry
S. No. Parameter Not to exceed (mg/Nm3)
1 HCl 20
2 Cl2 05
3 H2S 05
4 P2O5 (as H3PO4) 10
5 NH3 30
6 Particulate matter within the form of pesticide compounds
20
7 CH3Cl 20
8 HBr 05
(Source:)
The pollution load due to the unit is as given below:
Environmental Impact Assessment Report for Expansion of Existing Pesticide Plant for Manufacturing of Technical Grade Pesticides atVillage – Biratiya Kalan, Tehsil – Raipur, Distt
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EQMS India Pvt. Ltd. 63
Table 2.13 Pollution Load
Sr. No Stack attached to/
Pollutant
Pollutant Load Kg/hr
PM SOx NOx
HBr P2O5 (as H3PO4)
1. Boiler -1 1.17 0.39 1.17 --- ---
2. Boiler 2 1.17 0.39 1.17 --- ---
3. Boiler 3 1.17 0.39 1.17 --- ---
4. Alkali Scrubber
0.188 --- --- 0.047 ---
5. Water Scrubber 0.188 --- --- --- 0.094
The proposed emission control system is adequate to cater the emission load increase
due to additional products and by products, as per application submitted to MoEF&CC
for amendment of ToR.
Note – Henceforth cumulative/ final emission load and stacks details will be presented
in EIA report.
2.5.3. Solid and Hazardous waste
Ash will be main solid waste generated during operation of project. Ash will be
generated from boiler by using briquette. Ash will be stored in Silos (dry handling). Ash
will be disposed off through Cement plant, Brick manufacturing, Road development etc
(As per the guideline of Fly Ash Disposal).
The hazardous waste is generated at various stages of the manufacturing activity. The
disposal methodology generally adopted by INTECH is as stated below: - The
domestic and industrial wastewater generated will be segregated based on pollutant
content. The toxic effluent wastewater will go to the Effluent Treatment Plant (ETP).
Minor quantities of construction waste will be generated in the form of packaging
material and construction waste. Proper care will be taken for handling and reduction
of the solid waste generated during construction phase. During the operation phase
the solid waste is being generated in the form of ETP sludge/ process residue etc.
Hazardous wastes category as per hazardous waste the hazardous wastes
(management, handling and Trans-boundary movement) rules, 2016.
a. Process wastes/ residue b. Chemical sludge containing residue insecticides c. Date expired and off-specification insecticides
In Existing plant INTECH has obtained the membership for Hazardous Waste Disposal
from UCCI (Udaipur Chamber of Commerce and Industry), Udaipur, Rajasthan.
(Membership Certificate Attached as Annexure with final EIA report) For additional
Hazardous waste from proposed project (including additional products) will also be
disposed off through authorized disposal agency and membership for the same will be
obtained accordingly.
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EQMS India Pvt. Ltd. 64
Table 2.14 Hazardous Waste Generation Quantity
S. No
Type of Waste Existing
Qty /Annum
Proposed Qty /
annum
Total Qty
/Annum Remarks
1 Used or Spent oil (cat. 5.1)
50 Ltrs or 0.05 KL
2 KL 2.05 KL Sold to authorized processor.
2 Wastes or residue containing oil (Cat 5.2)
720 Kg/0.72 T
2 T 2.72 T Sold to authorized processor.
4 Sludge containing residual pesticides (Cat. 29.2)
- 600 T 600 T To TSDF site
7 Spent Acids (Cat. 29.6)
- 8500 T 8500 T Sold to authorized processor.
8
Empty containers / barrels / liners contaminated with hazardous chemicals. / wastes (Cat. 33.1)
- 800 T 800 T
sold to authorized recyclers.
9
Contaminated Cotton rags or other cleaning materials (cat. 33.2)
- 10 T 10 T
To TSDF site
10
Chemical Sludge from Waste Water Treatment (cat. 35.3)
- 500 T 500 T
To TSDF site
11
Date expired and off-specifications pesticides (cat. 29.3)
- 50 T 50 T
To TSDF Site
2.5.4. Noise Environment
The proposed project will have various machines and equipment which will generate
noise. The equipment and machines will have adequate provision to minimize the
noise generation. The manufacturing process is batch process.
Plant personnel working in the noisy area will be provided with earplug.
Installation of the plant machinery will be done after due consideration to design
noise levels and noise mitigation measures.
The green belt developed helps in reducing noise levels generated due to plant
operations.
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There will be few major sources of industrial noise; minor noise generated from the
industrial operations will be controlled by proper maintenance.
Proper mitigation measures will be taken in addition to above for the reduction of
noise levels i.e. use of acoustic enclosures and providing personal protective
equipment etc. to the workers.
Periodical monitoring for noise will be carried out on periodical basis.
Proper maintenance, oiling and greasing of machines at regular intervals is done
to minimize generation of noise at source.
The D.G. sets will be provided with acoustic enclosures.
2.5.5. Green Belt Development
The site has some existing tree plantation on periphery of the plant and along the
roads. It will ensure the greenbelt to the extent of 33% of the plot area.
As per approved TOR INTECH will develop greenbelt in an area of 33 % i.e. 14247
m2 out of total area of project 42907 m2, For the proposed expansion project the area
will increase (applied for TOR amendment) hence INTECH will developed a dense
greenbelt in about 3.5 ha (33%) of the area within the plant. About 1150 trees/ha shall
be planted. On an average about 4000 trees shall be planted within the premises as a
greenbelt.
2.5.6. Project Cost:
The overall investment in the project is 2700 lacs About Rs. 382.0 Lac is proposed for
the environment protection program. Details are as given below:
Capital cost and recurring cost/annum for environmental pollution control measures
S. No. Description of Item
Capital Cost
Recurring Cost
(In Lacs) (In Lacs)
1 Air Pollution Control/ Noise 80 7.5
2 Water Pollution Control 200 18
3 Control of Fire and explosion Hazard, safety measures
37 3.9
4 Environmental Monitoring and Management
10 1.5
5 Green Belt Development 55 10
Total 382.00 35.50
2.5.7. Proposed CSR activities and budget
CSR Plan: INTECH has allocated 2.5% of the total project cost towards the Enterprise
Social Commitment (ESC) and item-wise details along with time bound action plan will
be prepared and incorporated after public hearing.
INTECH shall create a CSR Cell under the direct control of Top Management of the
project. The CSR Cell shall implement the CSR programs.
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CHAPTER 3. : DESCRIPTION OF THE ENVIRONMENT
3.1. Background and Salient Environmental Features of the Study Area
Generation of environmental baseline data for a project area is an important phase of
any Environmental Impact Assessment process. Baseline data provide vital
information on the existing environmental quality in which a development is planned. It
is also useful for delineating environmental sensitive areas and for preparing an
Environmental Sensitivity Map for contingency planning. In this study, the
environmental characteristics of the project area (10 km study area) were established
through extensive literature search, field sampling/measurements, laboratory analysis,
consultation and data interpretation.
Initially Baseline study has been carried out by M/s Enkay Enviro Services Pvt. Ltd.
during Oct 2016 to Dec 2016 as per the standard TOR. As per approved ToR dated
15th July-2017, it is mentioned that baseline study carried out from Oct-2016 to Dec-
2016 to be considered for public hearing. M/s Enkay Enviro Services Pvt. Ltd. did not
have NABET accreditation for pesticide (Section 5(b)) sector. INTECH has requested
EQMS to carry out validation of the further work and prepare the EIA Report as per the
EIA Notification dated 14 Sept 2006 and its amendments. EQMS has followed the
MoEF&CC issued Term of reference (TOR) vide file no. J-11011/327/2016-IA. II (I)
dated 15th June 2017 & applied for amendment of ToR for preparing the EIA report.
EQMS has supplemented the existing baseline data (Oct 2016 to Dec 2016) collection
with additional one-month monitoring (1st May to 31th May, 2017) and
prepared/revalidated the baseline data and prepared the EIA report.
Secondary data from literature search were also obtained from the Govt. sources i.e.
Meteorological Department, CPCB publications; Forest Department and other Govt.
Sources. M/s JP Test& Research Center, Sahibabad, Uttar Pradesh with EQMS Field
Team, carried out field sampling and testing work. The study area within a 10 km
radius around the proposed plant site has been considered as impact zone for present
EIA study. Primary and secondary data was collected for 10 km radial study of the
project site.
3.1.1. Environmental Setting and Salient Environmental Features of the Project Area
Proposed Expansion of Existing Pesticide plant for manufacturing of Technical grade
pesticides at Khasra No. 143, 143/1,118,118/1,118/2,119,120,121,122, Village –
This Chapter describes the baseline environmental conditions around the M/s Intech
Pharma Pvt Ltd., project site for various environmental attributes, i.e. physical, biological
and socio-economic conditions, within the 10 km radial zone of the proposed project
site, which is termed as the study area. Topography, drainage, meteorology, air, noise,
water, soil and land constitute the physical environment, where as flora and fauna
constitute the biological environment. Demographic details and occupational pattern in
the study area constitute socio-economic environment.
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Biratiya Kalan, Tehsil – Raipur, District Pali Rajasthan. The proposed expansion
project site is well connected by road network and has advantage of good
infrastructure facilities like national highway (NH-112 & NH-14) roads, water, power
etc; The NH-112 is passing about 1.16 km southwest of the site. NH-14 is passing
about 4.85 km south of the plant site. The plant site is well connected to NH-112 by
MDR roads.
Nearest Railway station is Barlocated about 6.44 km from the site in south east
direction. Beawar Railway station is located about 23 km east of the site. Jodhpur
Airport is around 125 km away from the project site. Dabok Airport (UDR) in Udaipur
located at an aerial distance of ~ 167 km in SSW direction. No major town is located
within the study area of 10 km radius. Road connectivity map is provided in Figure
3.1.
Figure 3.1 Road Connectivity Map
There is no settlement within the 500m area of the project site. Nearest settlement is
Birantiya Kalan village located about 1.2 km in SW direction. Other village located
near to the site are Dhoolkot located about 2.1 km in NNE direction; Birantiya Khurd
village is located at about 3.3 km in SE direction. Other villages are located more than
2 km from the site.
Lilri River and Sukri river are the main surface water bodies located within the study
area. both the rivers are ephemeral and rain fed rivers. Lilri River (Dry River) is located
at about 5.4 km away in northwest direction of the project site. Sukri river is located
about 3.1 km North-East of the plant site. There are no areas protected under
international conventions, national or local legislation for their ecological, landscape,
cultural or other related value. There is no national park, wildlife sanctuary, biosphere
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reserve and wetland is present within the study area. Location map and Google Map
of 10-km radius study area are shown in Figure 3.2 & 3.3. The salient environmental
features of project site within 500 m, 2.0 km and 10 km radius are summarized in
Table 3.1.
Table 3.1 : Salient Environmental Features of Proposed Site
S.
No.
Environmental
Features
Within 500-m
area around
Project Site
Within 2.0-km
area around
Project Site
Within 10-km Radius
area around Project Site
1 Ecological Environment
A Presence of Wildlife
Sanctuary/ National
Park/Biosphere
Reserves
None None None
B Reserved /Protected
Forests
None None
RF near Jaitpura about 8.2
kmESE
C Wetland of state and
national interest
None None None
D Migratory route for
wild animals
None None None
E Presence of schedule-
I Fauna
None Schedule -1 Least
Concern
Schedule -1 Least
Concern
G Critically polluted area None within 10 km study area
2. Physical Environment
H Road Connectivity Link Roads
(Major district
road)
NH-112 (Deana-
Raipur),1.16km,
SW
NH-14 (Beawar-Sirohi-
Radhanpur), ~4.85Km,
(S)
I Rail Connectivity None None None
(Sandera RS ~11 Km SE)
J Defence Installation None None None
K Densely Populated
Area
None None None
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L Village close to plant
site
Birantiya Kalan village ~1.2 km SW, Dhoolkot ~2.1 km NNE,
Birantiya Khurd village ~3.3 km SE.
M Topography (site) Plain, elevation of site ranges between 342 to 345 m amsl
M Seismicity Seismic zone-II ( low risk damage Zone)
N Surface Water
Resources (Rivers)
None None Lilri River (Dry) ~ 5.5 km
NW and Sukri River (Dry)
~3.1 km in NE
O Soil and Land-use Sandy clay loam,
land use is
Industrial
Sandy loam &
Sandy clay loam
land use
agriculture and
settlement
Sandy loam & sandy clay
loam land use agriculture
and settlement
3. Social Environment
S Physical Sensitive
Receptors
None School, Hospitals,
Temple etc.
School, Hospitals, Temple
etc.
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Figure 3.2 Location Map of 10-km Radius Study Area
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Figure 3.3 Google Map of 10-km Radius Study Area
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3.1.2. Primary Data Collection: Monitoring Plan and Quality Assurance Procedures
Initially EIA study has been carried out by M/s Enkay Enviro Services Pvt. Ltd. Since M/s
Enkay Enviro Services Pvt. Ltd. did not have NABET accreditation for pesticide (Section
5(b)) sector. INTECHhas requested EQMS to carry out validation of the further work and
prepare the EIA Report as per the EIA Notification dated 14 Sept 2006. Primary baseline
data has been collected by Enkay Enviro Services Pvt. Ltd. as per the TOR prescribed
by MOEF during Oct-2016 to Dec 2016 (Attached as Annexure-). EQMS has
supplemented the existing baseline data collection with one month 1st May to 31th May
2017 and prepared/revalidated the EIA report. The study period and methodology for
primary data collection is summarized in Table 3.2.
Table 3.2 : Summary of Methodology for Primary/Secondary Baseline Data Collection
Parameters
No. of
Sampling
Locations
Frequency/
Season Remark
Ambient Air Quality
PM (10), PM(2.5), SO2,Nox
NH3, CO, VOC, HF, HBr,H2S
Eight (08)
locations
(Refer Fig.
No.3.5 )
Twice a
Week
for Oct to Dec
2016
&
May 2017
AAQ monitoring was carried out at eight
(08) locations (representing upwind,
downwind and sensitive locations). 24
hours sampling at each location was
carried out as per CPCB guide lines
(CPCB Gazette notification dated
18.11.2009 on AAQ).
Meteorology
Temperature, Humidity, Wind
speed, Direction, Rainfall etc.
One location
Hourly for Oct
to Dec 2016
&
May 2017
Met station was established close to the
site to record the site specific hourly met
data.
Ground Water Quality
Physical, chemical and biological
parameters as per IS:10500
Eight (08)
locations in
study area
(Fig 3.5)
Oct to Dec
2016
&
May 2017
Ground water: Sampling was conducted
at eight (08) locations. Samples were
preserved, transported and analyzed for
different parameters based on APHA
methods. Temp, conductivity and pH
which were measured intently at site
itself.
Surface Water Quality
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Parameters
No. of
Sampling
Locations
Frequency/
Season Remark
Physical, chemical and biological
parameters as per IS:10500
Three (03)
locations in
study area
(Fig 3.5)
Oct to Dec
2016
&
May 2017
Surface water: Sampling was conducted
at three (03) locations. Samples were
preserved, transported and analyzed for
different parameters based on APHA
methods. Temp, conductivity, DO and pH
which were measured intently at site
itself.
Soil
Texture, bulk density, pH,
conductivity, cation exchange
capacity, organic matter, Total
N,P,K, and Heavy metals etc
Eight (08)
locations in
study area
(Fig 3.5)
Oct to Dec
2016
&
May 2017
Soil samples were collected at eight (08)
locations within the study area and
analyzed as per IARI method
Noise
Noise profiling for 24 hrs
Eight (08)
locations in
study area
(Fig 3.5)
Oct to Dec
2016
&
May 2017
Noise monitoring was conducted within
the 10-km area of project site for noise
profiling for 24 hrs using integrated
sound level meter, as per CPCB
guidelines.
Ecology (Flora & Fauna)
Flora & Fauna -
Oct to Dec
2016
&
May 2017
Primary field survey and secondary
sources
Demography & Socio-economic Features
Demography & Socio-economic -
Oct to Dec
2016
&
May 2017
Primary field survey and secondary
sources
Standard methods and procedures have been strictly adhered to in the course of this
study. QA/QC procedures were strictly followed which covers all aspects of the study,
and includes sample collection, handling, laboratory analyses, data coding, statistical
analyses, presentation and communication of results. All analysis was carried out in
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NABL/MoEF accredited/recognized laboratory. Environment sampling Map is provided in
Figure 3.5.
Close view Map of Project site: Close view map of project site showing coordinates of
four corners of the site is presented in Figure 3.4.
Figure 3.4 Close view Map with Project Site coordinates
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Figure 3.5 Environment Sampling Location Map
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3.2. Physical Environment
3.2.1. Topography
The study area falls in Pali district. The district has undulated plains with scattered hills.
The general topographic elevation in the district ranges broadly between 150 m to 300 m
above mean sea level. The lowest elevation of 149.3 m amsl is noticed in Rohat block in
the western part of the district whereas the highest elevation of 1,068 m above mean sea
level in Bali in southern part of the district.
Topography of the Site & Study area: The study area falls in Raipur tehsil of the Pali
district. The general topography of the study area is flat. The mean elevation of the study
area ranges between 309 m to 429 m above mean sea level. The topography of project
site is flat and the elevation of the site ranges between 342 m to 345 m above mean sea
level. The slope of the project site is southeast and south side.
3.2.2. Drainage
The drainage of the study area is controlled by Lilri and Sukri river. Both the river is
ephemeral and rain fed river. The drainage pattern of the study area is dendritic in
nature. The area is sloping slightly towards south eastern side hence all the drainage of
the study area is drains towards south eastern part along the river channel. Drainage
map of the study area is presented in Figure 3.6.
Figure 3.6 Drainage Map of Study Area
3.2.3. Geology
Geologically, the district belongs to Delhi Super Group and Marwar Super Group. The
Delhi Super Group comprises of Kumbhalgarh, Phulad Ophiolite sute, Sendra-
Ambajigranite, Sirohi and Punagarh Group. The Delhi Super Group is overlaid by a
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sequence of unmetamorphosed sedimentary rocks consisting of sandstone, limestone,
siltstone and gypsum beds. The MarwarSuper Group is divided into Jodhpur and Bilara
Group which consists of sandstone, shale and limestone rocks. The Delhi Super Group
rocks are intruded by granites and rhyolite. The predominant intrusive is the Erinpura
Granite. The Delhi Super Group is mainly exposed in NNE parts of the district while
Marwar Super Group is exposed in northern parting Jaitaran and Sojat blocks. Erinpura
granite & gneiss occupied almost 50 % area of the district and exposed mainly in central,
southern and southeaster parts of the district. Geological succession of the Pali district is
given in Table 3.3.
Table 3.3 Geological Sequence
Super group Group Formation
Marwar Recent to Sub-
Recent
Alluvium & wind blown
Bhilara Lime stone
Jodhpur Sandstone, shale, boulders and chert.
Intrusive (Post
Delhi)
Malani Igneous
Suite
Granite and gneiss
Erinpura Granite Basic volcanic with pillow lava, meta tuff, quartzite,
shale, slate phyllite, bedded chert
Delhi Punagarh Basic volcanic with pillow lava, meta tuff, quartzite,
shale, slate phyllite, bedded chert
Sirohi Phyllite, mica schist, biotite schist, dolomitic marble,
migmatite& gneisses epidiorite, Hornblende
Sendra-Ambaji
Granite
Granite and gneiss
PhuladOphiolite
Suite
Hornblendes schist, amphibolite, pyroxene granulite,
gabbro &ultramafic
Kumbhalgarh Calc schist, marble, granite schist/amphibolite, biotite
schist, quartzite, mica schist and migmatite
3.3. Hydrogeology
The main hydrogeological formation encountered in the study area is as Quaternary
Alluvium (Younger and Older), Bilara limestone (Marwar Super group), Jodhpur
Sandstone (Marwar Super group), Malani Suite of Ignious rocks (Post Delhi and Delhi
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Super group), Calcareous Schist, Slate, Phylite, and Granite Gneiss (Aravali Super
group).
3.3.1. Stage of Ground Water Development
The study area falls in Raipur block of Pali district. As per the CGWB categorization of
blocks the study area falls in over exploited category which means that the dynamic
ground water resources are already exhausted. The ground water development in the
study area is more than 100% and the ground water is largely saline hence categorized
as over exploited category.
3.3.2. Depth to Ground Water Table
The study area falls in Raipur block of Pali District. During pre-monsoon period (May,
2010), depth to water level in Raiur block varied from 10 mbgl to 60 mbgl and during post
monsoon period (November, 2010), depth to water level in Raipur block varied from 2
mbgl to 40 mbgl.
3.3.3. Seismicity of the Study Area
Based on tectonic features and records of past earthquakes, a seismic zoning map of
India has been prepared by a committee of experts under the auspices of Bureau of
Indian Standard (BIS Code: IS: 1893: Part I 2002. According to the seismic-zoning map
of India, the project area falls in Zone II (Low risk zone) of seismicity. Thus, lies among
the low-risk earthquake areas. The seismicity map of study area is shown in Figure 3.9.
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Figure 3.7 Seismic Zones Map
3.4. Land use
Land use analysis was carried out using remote Sensing Data. Interpretation approach
based on systematic digital imaging was used for delineating the land use classes. The
demarcation of boundaries falling under different land use/land cover units is done using
different colors assigned to different land use/land cover units of satellite imagery1.
The site is located in the existing industrial area. Most of the land within the 10 km area
of the project site is agricultural land. As per the land use based on satellite image, about
54% of the land is Agricultural land, 33%% of the land is Open Forest, about 7% land is
under Dense forest & 6% of the land is under other uses (Refer Figure 3.9 and Table
3.4).
Table 3.4 : Land use of the Study Area
Sl. No. Class Area( SQ KM) Percentage (%)
1 Agricultural Land 175.85 54
2 Dense Forest 21.54 7
3 Open forest 105.13 33
4 Settlement 12.18 4
5 Dry River Bed 6.33 2
6 Water body 0.56 0.001
Total 321.59 100
Source: Satellite Image analysis
1The satellite Imagery of Indian Remote Sensing Satellite (IRS- ID, sensor P6, LISS III) of 24 m resolution
was used. The Swath of the imagery is 141 Km x 141 Km. Band used are 4, 3, 2 and 5. LANDSAT imagery of
30meter resolution and 185 x 185 km swath is also used for the comparative and overall analysis of the
area. LISS III imagery and LANDSAT 4-5 TM imagery were used for the complete coverage of the study area
Agricultural Land54%
Dense Forest7%
Open forest33%
Settlement4%
Dry River Bed2%
Water body0.001%
Landuse Pattern
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Figure 3.8 : Graph Showing Land Use of the Study Area (10 km Radius)
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Source: Interpretation of Satellite image
Figure 3.9 Land use/Land Cover Map of 10 Km Radial Study Zone
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3.5. Meteorology
Historical meteorological data was obtained from nearest IMD station located at Ajmer.
The predominant wind direction is from west and northwest direction in all season. Details
provided in Table 3.5.
Table 3.5 Long Term Meteorological Data of Ajmer (30 years’ average)
Month
Temperatur
e
(o C) daily
Relative
Humidity
(%) Rainfall
(mm)
Predomina
nt Wind
Direction
(From)
Calm Period Cloud
Amounts
Oktas
Wind
Speed
Km/hr Max Min Max Min 08:30 17:30 08:30 17:30
January 23.8 7.2 65 34 6.1 NE, NW 61 21 1.6. 1.6 3.5
February 26.5 10.2 56 28 7.5 SW, NW 54 13 1.7 2.0 4.3
March 32.0 15.7 41 21 4.4 SW, NW 41 9 1.6 1.9 5.8
April 37.5 21.9 35 22 5.4 SW, W 28 5 1.6 2.1 7.3
May 40.4 26.4 38 22 18.7 SW, W 12 4 0.9 1.7 10.3
June 39.1 26.9 57 36 57.5 SW, W 6 3 2.5 2.7 12.1
July 34.3 25.3 75 58 214.3 SW, W 7 9 5.0 5.1 10.2
August 32.0 24.3 80 67 156.1 SW, W 10 11 5.4 5.3 8.9
September 33.6 23.6 69 53 81.2 SW, W 18 11 2.8 3.2 7.2
October 34.6 18.8 54 34 8.1 SW, NW 50 25 0.8 1.3 4.1
November 29.8 12.8 56 37 6.1 SW, NE 67 35 1.1 1.3 3.3
December 25.2 8.2 64 40 3.6 NE, SW 63 31 1.5 1.7 3.2
Annual
Total or
Mean
32.4 14.8 58 38 569.0 SW, W 35 15 2.2 2.5 6.7
Source: Indian Meteorological Department, Ajmer
Temperature– December, January and February constitutes winter months with daily
mean minimum temperature around 7.20C and daily mean maximum temperature around
26.50C. May are the hottest month with daily mean maximum temperature at 40.40C and
daily mean minimum temperature at 26.40C.
Relative Humidity– The air is generally dry in the region except during monsoon. April
and May are driest with relative humidity ranges between 22-38%. The maximum
humidity during rainy season is 80%.
Rainfall– The annual total rainfall is 569 mm. Over 80% of the total annual rainfall is
received during the monsoon period between July to September.
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Cloud Cover – In the study area, clear weather prevails in most of the time during post
monsoon, winter and summer seasons. Only during monsoon months of July, August and
September, moderate to heavy clouds are observed. Relevant details about the number
of days with zero oktas of cloud cover (all clouds) for all months are presented in Table
3.5.
Table 3.6 No. of days with zero oktas of cloud cover (Ajmer)
Cloud Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Time
08:30 19 17 18 18 23 14 4 3 11 25 21 19
17:30 18 14 17 16 17 12 3 3 8 20 20 17
Wind Speed– The mean wind speed ranges from 3.2 to 4.1 kmph during post-monsoon,
7.2 to 12.1 kmph during monsoon and 5.8 to 10.3 kmph in pre-monsoon season.
Wind Direction– The predominant wind direction at Ajmer is from south west in all year
and second most predominant wind direction is from west.
Calm Periods – The calm period constitutes an important factor in the dispersion of air
pollution. The calm period is more during morning (08:30) compared to Evening (17:30).
The maximum calm period occurs during October to February months. Monthly calm
period values obtained from nearest IMD is shown in Table 3.7.
Table 3.7 Monthly Percentages of Calm Periods (IMD Ajmer)
Calm (%) Jan Feb Mar Apr May Jun Jul Aug Sept Oct Nov Dec
Time
08:30 61 54 41 28 12 6 7 10 18 50 67 63
17:30 21 13 9 5 4 3 9 11 11 25 35 31
Special Weather Phenomena- The occurrence of thunderstorm is 14.5 days per year,
mostly spread across the months of May to September. Annual Dust Storm is 4.3 days
during summer. Annually 4 days have visibility less than 1 km, 61 days has visibility in the
range of 1 - 4 km, 185 days have visibility in the range of 4 -10 km, 95 days between 10 -
20 km and 20 days have visibility above 20 km.
3.5.2. Met Data Generated at Site
Met data for post monsoon season Oct 2016 to Dec2016 was generated at site by Enkay
Enviro Services Pvt. Ltd. met data was again generated for month of May 2017 by EQMS.
An automatic weather monitoring station was installed at Project site, keeping the sensors
free exposed to the atmosphere and with minimum interference with the nearby
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structures. The micro-meteorological data like wind speed, wind direction, temperature,
relative humidity and atmospheric pressure were collected using the weather stationed
cloud cover was recorded manually for the study period. The wind directions, wind speed,
temperature, rainfall and humidity recorded at site during post monsoon season 2016 and
summer season 2017 are presented in Table 3.7and Table 3.8 respectively. Site specific
wind rose diagram is presented in Figure 3.10 and Figure 3.11. Graphical representation
of wind frequency distribution patter is provided in Figure 3.11.
Table 3.8 Site Specific Meteorological Data (Oct 2016 to Dec2016)
Month
Temperature
(0C)
Relative Humidity
(%) Rainfall in mm
Wind Speed
Kmph
Max Min Max Min Max Total Max Min
October- 2016 39.40 18.00 75.30 16.40 0 0 10.40
0
November-2016 35.60 12.00 79.30 17.00 0 0 14.20 0
December- 2016 35.40 7.10 84.10 12.30 0 0 8.40 0
Table 3.9 Site Specific Meteorological Data (May 2017)
Month
Temperature
(0C)
Relative
Humidity (%)
Wind speed
m/s Direction
Calm
period
Max Min Max Min Min Max From %
May 2017 44.0 24.0 74 11 0.5 >3 SW, W 13.04
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Figure 3.10 Wind Frequency Distribution (Post monsoon Season 2016)
Figure 3.11 Wind Frequency Distribution (May 2017)
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Figure 3.12 Wind Frequency distribution (May 2017)
3.6. Ambient Air Quality
AAQ monitoring was done for post monsoon season 2016 (1st Oct 2016 to 31st Dec 2016)
and repeated for one month in May 2017 (1st May to 31st May 2017). Date wise AAQ
results for May 2017 is attached as Annexure. CPCB guidelines were applied for
selecting the appropriateness of monitoring locations. The location and height of the
stations were so selected (>5 m from base) to avoid the capture of re-suspended road
dust and fugitive domestic emissions due to burning. All the ambient air analysis with
respect to each parameter were analyzed as per CPCB guidelines. AAQ monitoring was
done at eight locations within the study area considering dominant wind direction,
populated area and sensitive receptors. Details of monitoring locations are shown in
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Table 3.10. Monitoring Location map is shown in Figure 3.4. The summary of Ambient
Air quality results is presented in Table 3.10and Table 3.11.
Table 3.10 Ambient Air Quality Monitoring Locations
S.N.
Station
Direction &
Direction wrt
site
Terrain features
Coordinates
1 Project site - Flat terrain. Industrial setting
N 26O
07'08.8"
E 74o
05'33.9
2 Dhulkot 1.9 km,NE Flat terrain, rural, located in
downwind direction for
summer season
N 26o
08'05.5" E 74
o06'27.5"
3 Birantiya Khurd 3.1 km,E Flat terrain, rural, located in
downwind direction for
summer
N 26o
07'12.8"
E 74o
08'12.9"
4 Birantiya Kalan 1.3 km,SW Flat terrain, rural, located in
upwind direction for summer
N 26o
05'45.7"
E 74o
06'27.5"
5 Lakshmangarh 1.8 km,NW Flat terrain, rural, located in
downwind direction for post
monsson season
N 26o
07'59.6"
E 74o
04'37.1"
6 Road junction of Birantiya Kalan and Purthigarh
3.9 km,W Flat terrain, mixed use area,
located in upwind direction
for summer season
N 26o
07'45.1" E 74
o03'08.7"
7 Road junction of Birantiya Kalan and Dhulkot
0.2 km,SW Flat terrain, mixed use area,
located in upwind direction
for summer season
N 26o
07'02.3"
E 74o
05'19.9"
8 Hajiwas 2.3km,N Flat terrain, rural, located in
crosswind direction for
summer
N 26o
08'30.8" E 74
o05'34.4"
Table 3.11 Ambient Air Quality Monitoring Results (24-hour average)
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Location PM10 (mg/m3) PM2.5 (mg/m3)
Min Max Mean 98 %tile Min Max Mean 98 %tile
Project site 74.32 87.45 79.89 86.28 37.05 46.25 41.83 46.01
Dhoolkot 54.96 80.21 68.86 79.28 24.71 37.91 30.78 37.05
Birantiya Khurd 58.08 77.5 68.65 75.7 28.22 34.29 30.88 34.25
Birantiya Kalan 62.58 81.39 73.28 80.98 19.16 39.15 29.99 38.65
Lakshmangarh 60.58 89.92 68.25 84.13 25.15 41.83 31.2 39.66
Road junction of Birantiya
Kalan and Purthigarh
61.38 80.14 67.88 79.23 18.1 39.73 29.45 39.61
Road juction of Birantiya
Kalan and Dhoolkot
47.38 79.05 66.69 78.24 17.19 40.1 30.25 39.66
Hajiwas 40.57 68.07 56.6 66.33 23.12 33.47 29.15 28.31
Source: Primary Data Collection and analysis during Oct 2016 to Dec 2016
Table 3.11 continued ........
Location SO2 (mg/m3) NOx(mg/m3)
Min Max Mean 98 %tile Min Max Mean 98 %tile
Projet site 7.83 10.8 9.44 10.74 12.29 16.34 14.38 16.24
Dhoolkot 6.31 10.16 7.81 9.73 11.48 15.57 13.52 15.5
Birantiya Khurd 6.36 9.87 7.82 9.6 11.43 15.67 13.54 15.5
Birantiya Kalan 5.83 9.68 7.68 9.64 8.14 15 12.06 14.76
Lakshmangarh 4.09 8.33 6.21 8.28 8.97 15.62 12.38 15.56
Road junction of Birantiya
Kalan and Purthigarh
4.89 10.02 6.96 9.57 9.1 13.39 11.68 13.23
Road junction of Birantiya
Kalan and Dhoolkot
4.17 9.48 6.67 9.01 7.64 14.8 11.24 14.78
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Hajiwas 3.77 6.62 4.99 6.47 8.79 12.93 10.51 12.87
Source: Primary Data Collection and analysis during Oct 2016 to Dec 2016
Table 3.11 continued ........
Location CO(mg/m3)
8 hrs.
Min Max Mean 98 %tile
Project site 0.20 0.70 0.36 0.65
Dhoolkot 0.10 0.80 0.35 0.70
Birantiya Khurd 0.10 0.60 0.30 0.55
Birantiya Kalan 0.10 0.60 0.32 0.55
Lakshmangarh 0.20 0.60 0.40 0.60
Road junction of Birantiya Kalan and Purthigarh 0.20 0.60 0.36 0.60
Road junction of Birantiya Kalan and Dhoolkot 0.30 0.60 0.44 0.60
Hajiwas 0.30 0.60 0.38 0.60
Source: Primary Data Collection and analysis during Oct 2016 to Dec 2016
Observation on Ambient Air Quality (Oct 2016 to Dec 2016)
PM10: The 98thpercentile value of PM10 was maximum 86.28μg/m3 observed at Project
Site and minimum 66.33 μg/m3 observed at Hajiwas. The 24 hours’ applicable limit for
industrial, Residential Rural and Other Areas is 100 µg/m3.
PM2.5: The 98th percentile value of PM2.5maximum46.01 μg/m3 observed at Project site
and minimum 28.31 μg/m3 at Hajiwas. The 24 hours applicable limit for industrial,
Residential Rural and Other Areas is 60µg/m3.
SO2: The 98th percentile value ofSO2 was maximum (10.74 μg/m3) observed at Project
site and minimum (6.47 μg/m3) at Hajiwas. The 24 hours’ applicable limit for industrial,
Residential Rural and Other Areas is 80 µg/m3.
NO2: The 98th percentile value off Nitrogen Dioxide (16.24 μg/m3) observed at project site
and minimum 12.87 μg/m3 at Hajiwas. The 24 hours’ applicable limit for industrial,
Residential Rural and Other Areas is 80 µg/m3.
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CO: The concentration of CO at all locations was ranges between 0.1to 0.8mg/m3. The 8
hours’ applicable limit for Industrial, Residential Rural and other areas is 2mg/m3.
HC & VOCs: The value of VOCs and HC found below Detection Limit at project site
Ambient Air Quality (May 2017)
Table 3.12 Ambient Air Quality Monitoring Results (24-hour average)
Location PM10 (mg/m3) PM2.5 (mg/m3)
Min Max Mean 98 %tile Min Max Mean 98 %tile
Project site 70 85 77 84 28 36 31 34
Dhoolkot 54 74 65 74 20 31 26 31
Birantiya Khurd 55 73 63 72 22 32 27 32
Birantiya Kalan 58 80 68 79 21 35 26 35
Lakshmangarh 60 81 69 80 25 35 30 35
Road juction of Birantiya Kalan and
Purthigarh
57 75 65 74 22 32 27 35
Road juction of Birantiya Kalan and
Dhoolkot
56 71 62 70 21 30 25 30
Hajiwas 38 61 51 61 17 27 22 27
Source: Primary Data Collection and analysis during May 2017
Table 3.12 continued……
Location SO2 (mg/m3) NOx(mg/m3)
Min Max Mean 98 %tile Min Max Mean 98 %tile
Projet site 5.0 8.5 6.5 8.3 12.0 16.4 13.9 16.3
Dhoolkot 4.8 8.0 6.4 7.8 10.0 14.7 12.2 14.5
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Birantiya Khurd 4.3 7.8 5.9 7.7 10.4 14.6 12.5 14.5
Birantiya Kalan 4.1 7.4 5.8 7.3 10.5 15.5 13.0 15.3
Lakshmangarh 4.0 6.4 5.3 6.3 8.1 12.2 10.5 12.2
Road juction of Birantiya Kalan
and Purthigarh
4.7 9.0 7.3 8.9 9.0 12.4 11.0 12.4
Road juction of Birantiya Kalan
and Dhoolkot
4.5 8.4 6.5 8.3 8.2 13.5 10.8 13.3
Hajiwas 4.0 7.0 5.8 6.9 8.8 12.5 10.3 12.3
Source: Primary Data Collection and analysis during May 2017
Table 3.12 continued……
Location NH3 (mg/m3) CO(mg/m3)
8 hrs.
Min Max Mean 98 %tile Min Max Mean 98 %tile
Projet site 9 15 12 15 <0.1 <0.1 <0.1 <0.1
Dhoolkot 10 14 12 14 <0.1 <0.1 <0.1 <0.1
Birantiya Khurd 8 13 11 13 <0.1 <0.1 <0.1 <0.1
Birantiya Kalan 8 14 11 14 <0.1 <0.1 <0.1 <0.1
Lakshmangarh 8 13 11 13 <0.1 <0.1 <0.1 <0.1
Road junction of Birantiya Kalan
and Purthigarh
8 15 12 15 <0.1 <0.1 <0.1 <0.1
Road junction of Birantiya Kalan
and Dhoolkot
10 14 11 14 <0.1 <0.1 <0.1 <0.1
Hajiwas 7 12 10 12 <0.1 <0.1 <0.1 <0.1
Source: Primary Data Collection and analysis during May 2017
Table 3.12 continued……
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Location VOC
(µg/m³)
HF
(µg/m³) HBr (µg/m³)
H2S
(ppb)
Project site <0.01 <0.1 <0.1 <1
Dhoolkot <0.01 <0.1 <0.1 <1
Birantiya Khurd <0.01 <0.1 <0.1 <1
Birantiya Kalan <0.01 <0.1 <0.1 <1
Lakshmangarh <0.01 <0.1 <0.1 <1
Road junction of Birantiya Kalan
and Purthigarh
<0.01 <0.1 <0.1 <1
Road junction of Birantiya Kalan
and Dhoolkot
<0.01 <0.1 <0.1 <1
Hajiwas <0.01 <0.1 <0.1 <1
Source: Primary Data Collection and analysis during May 2017
3.6.2. Observations on Ambient Air Quality (May 2017):
Particulate Matter (PM10): The highest PM10 level were found at project site (85 µg/m3)
and lowest PM10 level at Hajiwas (38 µg/m3) while the 98%conc. of all location ranges
between 61-85 µg/m3. The PM10 level in all the monitoring locations is within permissible
limit i.e. NAAQMS level 100µg/m3
Particulate Matter (PM2.5): The highest PM2.5 level were found at project site(36 µg/m3)
and lowest PM2.5 level were observed at Hajiwas(17 µg/m3) while the 98%. of all location
ranges between 27-34 µg/m3. The PM2.5 level in all the monitoring locations is within
permissible limit i.e. NAAQMS level 60µg/m3
Sulphur Dioxide (SO2): The highest SO2 level were found at project site (8.5 µg/m3) and
lowest SO2 level were observed also at Hajiwas (4.0 µg/m3) while the 98%conc. of all
location ranges between 6.9-8.3µg/m3. The SO2 level in all the monitoring locations is
within permissible limit i.e. NAAQMS level 80µg/m3
Oxides of Nitrogen (NOx): The highest NOx level were found at Project site (16.4 µg/m3)
and lowest NOx level were observed at HajiwasVillage (8.8 µg/m3) while the 98%conc. of
all location ranges between 12.3 to 16.3 µg/m3. The NOx level in all monitoring location
are under permissible limit i.e. NAAQMS level 80µg/m3
Other Parameters: NH3 were found in the rage of 7 to 15 µg/m3. The 8-hour
concentration of CO was found below 0.1mg/m3. VOC, H2S, HBr and HF were found
below detection limit.
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Overall the ambient air quality of the study area during post monsoon season (as
monitored by Enkay Enviro Services Pvt. Ltd.) and during May 2017 (as monitored by
EQMS) was found to be within the NAAQS.
3.7. Noise Environment
Noise after a certain level can have a very disturbing effect on the people and animals
exposed to it. Hence, it is important to assess the present noise quality of the area in
order to predict the potential impact of future noise levels due to the proposed project.
Ambient noise measurements were taken at 8 locations during Post monsoon season
2016 and repeated in May 2017. Noise monitoring locations are represented in Table
3.13. The Noise level recorded in study area during post monsoon season 2016 and May
2017 is represented in Table 3.14 &Table 3.15.
The monitored levels were compared against the The Noise Pollution (Regulation and
Control) Rules 2000, as amended through the Noise Pollution (Regulation and Control)
Amendment Rules 2010 dated 11th January 2010. The project site falls in designated
industrial area and the noise levels at all the locations were found within the ambient
noise standards.
Table 3.13 Ambient Noise Quality Monitoring Locations
S.N. Station Code Distance, Direction Coordinates
1
Project site
N1
-
N 26o
07'08.80" E
74o
05'33.9"
2 Dhulkot N2 2.1km,NE N 26o
08'05.5" E
74o
06'27.5"
3 Birantiya Khurd N3 5.0km,E N 26o
07'16.8" E
74o
08'40.3"
4 Birantiya Kalan N4 2.9km,SW N 26°6'31.15" E 74° 5'1.05"
5 Lakshmangarh N5 1.8 km,NW N 26o
07'59.6" E
74o
04'38.4"
6 Road junction ofBirantiya Kalan andPurthigarh
N6 3.2km,W N 26o
07'33.7" E
74o
03'26.7"
7 Road junction ofBirantiya Kalan andDhulkot
N7 0.16km,SW N 26o
07'02.3" E
74o
05'19.9"
8 Hajiwas N8 2.3 km,N N 26o
08'26.8" E
74o
05'40.3"
Table 3.14 Ambient Noise Quality in the Study Area (Post Monsoon Season)
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Location
Code
Location Name Present
Category
Day Time
Leq dB(A)
National
Standard
Day Time
Leq
dB(A)
Night
Time Leq
dB(A)
National
Standard
Night Time
Leq dB(A)
N-1 Project site Industrial 58.15 75.0 44.93 70.0
N-2 Dhoolkot Residential 52.34 55.0 48.89 45.0
N-3 Birantiya Khurd Residential 52.05 55.0 38.76 45.0
N-4 Birantiya Kalan Residential 51.98 55.0 39.15 45.0
N-5 Lakshmangarh Residential 54.23 55.0 38.26 45.0
N-6 Road junction of
Birantiya Kalan
and Purthigarh
Commercial
(Mixed Use)
50.98 65.0 39.49 55.0
N-7 Road junction of
Birantiya Kalan
and Dhoolkot
Commercial
(Mixed use)
62.80 65.0 51.50 55.0
N-8 Hajiwas Residential 54.30 55.0 40.0 45.10
Source: Analysis during study periodByWolkem)
Table 3.15 Ambient Noise Quality in the Study Area (May 2017)
Location
Code
Location Name Present
Category
Day
Time
Leq
dB(A)
National
Standard
Day Time
Leq dB(A)
Value
Night
Time Leq
dB(A)
National
Standard
Night Time
Leq dB(A)
N-1 Project site Industrial 61.3 75.0 48.3 70.0
N-2 Dhoolkot Residential 56.6 55.0 45.8 45.0
N-3 Birantiya Khurd Residential 52.4 55.0 42.4 45.0
N-4 Birantiya Kalan Residential 53.8 55.0 43.1 45.0
N-5 Lakshmangarh Residential 52.6 55.0 42.5 45.0
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N-6 Road junction of
Birantiya Kalan and
Purthigarh
Commercial
(Mixed
Use)
49.8 65.0 41.4 55.0
N-7 Road junction of
Birantiya Kalan and
Dhoolkot
Commercial
(Mixed use)
63.0 65.0 53.4 55.0
N-8 Hajiwas Residential 51.3 55.0 42.7 45.0
Source: Analysis during study period by EQMS
3.7.2. Observation on Ambient Noise Quality:
The ambient noise quality of the study area is within the prescribed National Ambient
Noise Quality Standards prescribed for industrial (Standards - 75 dBA during day time
and 70dBA during night time) residential area (Standards - 55 dBA during day time and
45 dBA during night time) and commercial area (Standards - 65 dBA during day time and
55 dBA during night time).
3.8. Water Quality
To assess the water quality of the study area the surface and Ground water sampling was
conducted during post monsoon season (Oct-Dec 2016) and revalidated during May
2017.
3.8.1. Ground Water Quality
Eight ground water samples and three surface water sample were collected from different
locations around the site during post monsoon season (Oct-Dec 2016) and revalidated
during May 2017. The water samples were examined for physico-chemical parameters
and bacteriological parameters. The samples were collected and analyzed as per the
procedures specified in Standard Methods. Samples for chemical analyses were collected
in polyethylene carboys. Samples for bacteriological analyses were collected in sterilized
bottles. Temperature, pH, conductivity and dissolved oxygen were measured at site itself.
Surface water sample were analyzed for various parameters and assessed using the
CPCB’s BDU Criteria.
The name of ground and surface water sampling locations is presented in Table 3.16and
Table 3.17 respectively. The analysis results of ground and surface water for Post -
Monsoon season 2016 is attached as Annexure X. The analysis results of groundwater
for May 2017 are presented in Table 3.18. The analysis results of surface water for May
2017 are presented in Table 3.19
Table 3.16 Ground Water Sampling Locations
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S.no. Station Source Distance, Direction Coordinates Sample
code
1. Near Project Site Hand Pump 0.4 km,E
N 26o07'02.3"
E 74o05'45.7"
GW1
2.
Dhulkot
Hand Pump 1.9 km,NE
N 26o08'03.6"
E 74o06'14.7"
GW2
3.
Birantiya Khurd
Hand Pump 3.9 km,E
N 26o07'11.4"
E 74o07'58.4"
GW3
4.
Biratiya Kalan
Open Well 0.6 km,SW
N 26o06'47.2"
E 74o05'16.2"
GW4
5.
Lakshmangarh
Well Water 1.7km,NW
N 26o07'54.5"
E 74o04'35.3"
GW5
6.
Road Junction Of
Kalan & Purthigarh
Hand Pump 3.3km,W
N 26o07'33.7"
E74o03'26.7"
GW6
7.
Road Junction of
Biratiya Kalan &
Dhulkot
Hand Pump 0.2 km,SW
N 26o07'02.3"
E74o05'19.9"
GW7
8.
Hajiwas
Open Well 3.0km,N
N 26o08'53.2"
E74o05'50.6"
GW8
Table 3.17 Surface Water Sampling Locations
S.no. Station Source Distance, direction Coordinates Sample
code
1 Hajiwas Sukari River
Up Stream
3.1 km,N N 26o08'53.6"
E 74o05'50.4"
SW1
2
Biratiyan
Kalan
Pond Water
Sample
0.8 km,S N 26o06'42.9"
E 74o05'16.1"
SW2
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3
Chattar
Sagar
Reservoir
6.6 km,W N 26o06'47.6"
E 74o01'24.3"
SW3
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Table 3.18 Ground Water Quality in the Study Area (May-2017)
S.N. Parameters GW1
GW2
GW3
GW4
Method Desired Limit
/Permissible Limit
1 pH Value 8.27 7.98 8.18 7.38 APHA-4500 6.5-8.5/No relaxation
2 Temperature 0C 25.2 25.2 25.3 25.3 IS:3025:Part 9 --
3 Conductivity, mhos/cm 6736 1895 2258 1530 APHA-4500 --
4 Turbidity (NTU) <1 <1 <1 <1 APHA-2030B 1-5
5 Total Dissolved solids mg/l 4240 1188 1425 962 APHA-2540B 500/2000
6 Total Suspended solids mg/l <2 <2 <2 <2 APHA-2540D --
7 Total Hardness as CaCO3
mg/l
1568 384 410 298 APHA-2340C 200/600
8 Chloride as Cl mg/l 1406 272 478 244 APHA-4500B 250/1000
9 Total Alkalinity mg/l 568 430 412 348 IS:3025:Part -23 200/600
10 Sulphates as SO4 mg/l 1398 196 118 142 APHA-4500E 200/400
11 Nitrates as NO3 mg/l 37 23 25 19 APHA-4500 45/No relaxation
12 Fluoride as F mg/l 2.28 2.88 1.14 1.20 APHA-4500D 1/1.5
13 Iron as Fe mg/l 0.52 0.60 0.22 0.18 APHA-3111B 0.3/No relaxation
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14 Zinc as Zn mg/l 2.53 1.85 0.94 0.72 APHA-3111B 5/15
15 Calcium as Ca mg/l 252 58.4 88.8 68 APHA-3500B 75/200
16 Magnesium as Mg mg/l 277.9 57..8 45.6 31.1 APHA-3500B 30/100
17 Sodium as Na mg/l 1276 397 554 265 APHA-3500 --
18 Potassium as K mg/l 98 12.8 25.8 15 APHA-3500 KB --
19 Cadmium as Cd mg/l <0.01 <0.01 <0.01 <0.01 APHA-3111B 0.003/No relaxation
20 Copper as Cu mg/l <0.01 <0.01 <0.01 <0.01 APHA-3111B 0.05/1.5
21 Nickel as Ni mg/l <0.01 <0.01 <0.01 <0.01 APHA-3111B 0.02/No relaxation
22 Lead as Pb mg/l 0.09 0.07 0.05 0.04 APHA-3111B 0.01/No relaxation
23 Mercury as Hg mg/l <0.001 <0.001 <0.001 <0.001 APHA-3112 0.001/0.001
24 Chromium (Total as Cr) mg/l <0.05 <0.05 <0.05 <0.05 APHA-3111B 0.5/No relaxation
25 Arsenic as As mg/l <0.025 <0.025 <0.025 <0.025 APHA-3114 0.01/0.05
26 Phenolic compound mg/l <0.001 <0.001 <0.001 <0.001 IS:3025:Part 43 0.001/0.002
27 Total coliform MPN/100ml Nil Nil Nil Nil APHA-9230B Nil
Source: Water Analysis during study period
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Table 3.18 continued, .......Ground Water Quality in the Study Area (May-2017)
S.N. Parameters GW5
GW6
GW7
GW8
Method Desired Limit
/Permissible Limit
1 pH Value 7.48 7.68 8.10 8.22
APHA-4500 6.5-8.5/No relaxation
2 Temperature 0C 24.8 25.0 24.9 25.1
IS:3025:Part 9 --
3 Conductivity, mhos/cm 1498 6478 2596 3057
APHA-4500 --
4 Turbidity (NTU) <1 <1 <1 <1
APHA-2030B 1-5
5 Total Dissolved solids mg/l 890 4088 1632 1918
APHA-2540B 500/2000
6 Total Suspended solids mg/l <2 <2 <2 <2
APHA-2540D --
7 Total Hardness as CaCO3
mg/l
286 422 448 262 APHA-2340C 200/600
8 Chloride as Cl mg/l 252 1290 512 488
APHA-4500B 250/1000
9 Total Alkalinity mg/l 336 1166 448 576
IS:3025:Part -23 200/600
10 Sulphates as SO4 mg/l 130 195 152 194
APHA-4500E 200/400
11 Nitrates as NO3 mg/l 18 32 30 69
APHA-4500 45/No relaxation
12 Fluoride as F mg/l 1.16 1.22 1.22 2.32
APHA-4500D 1/1.5
13 Iron as Fe mg/l 0.18 0.48 0.25 0.06
APHA-3111B 0.3/No relaxation
14 Zinc as Zn mg/l 0.88 1.16 0.99 2.10
APHA-3111B 5/15
15 Calcium as Ca mg/l 64.8 37.6 82.4 60
APHA-3500B 75/200
16 Magnesium as Mg mg/l 30.1 79.7 58.8 27.2
APHA-3500B 30/100
17 Sodium as Na mg/l 258 1276 612 585
APHA-3500 --
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EQMS India Pvt. Ltd. 101
18 Potassium as K mg/l 13 20 29 11.2
APHA-3500 KB --
19 Cadmium as Cd mg/l <0.01 <0.01 <0.01 <0.01
APHA-3111B 0.003/No relaxation
20 Copper as Cu mg/l <0.01 <0.01 <0.01 <0.01
APHA-3111B 0.05/1.5
21 Nickel as Ni mg/l <0.01 <0.01 <0.01 <0.01
APHA-3111B 0.02/No relaxation
22 Lead as Pb mg/l 0.08 0.10 0.08 0.07
APHA-3111B 0.01/No relaxation
23 Mercury as Hg mg/l <0.001 <0.001 <0.001 <0.001
APHA-3112 0.001/0.001
24 Chromium (Total as Cr) mg/l <0.05 <0.05 <0.05 <0.05
APHA-3111B 0.5/No relaxation
25 Arsenic as As mg/l <0.025 <0.025 <0.025 <0.025
APHA-3114 0.01/0.05
26 Phenolic compound mg/l <0.001 <0.001 <0.001 <0.001 IS:3025:Part 43 0.001/0.002
27 Total coliform MPN/100ml Nil Nil Nil Nil
APHA-9230B Nil
Source: Water Analysis during study period
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Observation on Ground Water Quality
The pH value of ground water is an important index of acidity or alkalinity. pH value of
the sample varies from 7.38 to 8.27 in all locations, which is well within the specified
standard of 6.5 to 8.5. In general, the pH of the ground water is slightly basic in nature.
Electric Conductivity levels vary from 1498 to 6736 µmho/cm. High Electric
Conductivity was found at two locations i.e. project site and Road Junction of Biratiya
Kalan & Purthigarh site.
Total dissolved solids ranges from 890 to 4240 mg/l. The TDS values were found
within permissible limit of Indian Standard IS: 10500-2012 at all locations except two
locations i.e. project site and Road Junction of Biratiya Kalan & Purthigarh site.
The hardness values in ground water of the study area ranges between 262 to 1568
mg/l. Hardness values is well within the permissible limit of Indian Standard IS: 10500-
2012 at all locations except two locations i.e. project site and Road Junction of
Biratiya Kalan & Purthigarh site
The chloride values in ground water of the study area ranges between 244 to 1406
mg/l. Chloride values is well within the permissible limit of Indian Standard IS: 10500-
2012 at all locations except two locations i.e. project site and Road Junction of
Biratiya Kalan & Purthigarh site
The fluoride content was found high at project site, Dhulkot and Hajiwas, which not
suitable for drinking purpose. In other locations Fluoride contents were found within the
range.
Nitrate value was exceeding the limit at Hijawas which is not suitable for agriculture
purpose.
No biological and metallic contamination has been found in any of the ground water
sample of the study area.
The analysis results of ground water samples of study area indicate that ground water of
Dulkot, Hajiwas is not suitable for drinking due to presence of high fluoride. Overall the
ground water of Hajiwas, Dhulkot, project site and Road Junction of Biratiya Kalan &
Purthigarh site is not meeting the permissible limit of Indian Standard IS: 10500-2012.
The ground water quality of other locations except Hajiwas, Dhulkot, project site and
Road Junction of Biratiya Kalan & Purthigarh site is meeting the permissible limit of Indian
Standard IS: 10500-2012.
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Table 3.19 Surface Water Quality in the Study Area (May-2017)
S.N. Parameters SW1
SW2
SW3 Method
1 pH Value 8.10 8.26 8.32
APHA-4500
2 Temperature 0C 25.0 25.2 25.5
Part 9
3 Conductivity, mhos/cm 257
386 868 APHA-4500
4 Turbidity (NTU) <5 <5 <5
APHA-2030B
5 Total Dissolved solids
mg/l
158 238 552 APHA-2540B
6 Total Suspended solids
mg/l
4 7 6 APHA-2540D
7 Total Hardness as CaCO3
mg/l
104 152 280 APHA-2340C
8 Chloride as Cl mg/l 19 30 82
APHA-4500B
9 Total Alkalinity mg/l 86 128 310
Part -23
10 Sulphates as SO4 mg/l 8.2 12.0 18 APHA-4500E
11 Fluoride as F mg/l 0.28
0.32 0.46 APHA-4500D
12 Iron as Fe mg/l 0.22
0.26 0.38 APHA-3111B
13 Zinc as Zn mg/l 0.09
0.12 0.22 APHA-3111B
14 Calcium as Ca mg/l 37.6
54.4 74 APHA-3500B
15 Magnesium as Mg mg/l 2.4
3.9 23 APHA-3500B
16 Cadmium as Cd mg/l <0.01 <0.01 <0.01 APHA-3111B
17 Copper as Cu mg/l <0.01 <0.01 <0.01 APHA-3111B
18 Nickel as Ni mg/l <0.01 <0.01 <0.01 APHA-3111B
19 Lead as Pb mg/l <0.01 <0.01 <0.01 APHA-3111B
Environmental Impact Assessment for Expansion of Existing pesticide plant for manufacturing of technical grade pesticides in village – Biratiya Kalan, Tehsil – Raipur, Distt – Pali, Rajasthan
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20 Mercury as Hg mg/l <0.001 <0.001 <0.001 APHA-3112
21 Chromium (Total as Cr)
mg/l
<0.05 <0.05 <0.05 APHA-3111B
22 Arsenic as As mg/l <0.025 <0.025 <0.025 APHA-3114
23 Oil & Grease mg/l Nil Nil Nil Part -39
24 Chemical Oxygen
Demand as COD mg/l
10 20 14 Part -58
25 Bio- Chemical Oxygen
Demand as BOD (for 3
Days 27 ˚C) mg/l
2.8 6 3.4 Part -44
26 Dissolved Oxygen mg/l 5.8 4.8 5.8 APHA
27 Total coliform MPN/100ml 2600 5280 1850 APHA-9230B
Observation on Surface water Quality
The Sukri river and Chatar Sagar pond water quality is meeting the Best Designated Use
– ‘C’ Criteria of CPCB (i.e Drinking water source after conventional treatment and
disinfection). No metallic contamination was found in the river water. Bacterial and
metallic contamination was observed in the Biratiyan Kalan pond water quality. The water
quality of Pond was found to meet the Best Designated Use – ‘D’ Criteria of CPCB (i.e fit
for fish propagation).
3.9. Soil Quality
Soils may be defined as a thin layer of earth's crust that serves as a natural medium for
the growth of plants. It is the unconsolidated mineral matter that has been subjected to
and influenced by genetic and environmental factors. Soils serve as a reservoir of
nutrients for plants and crops and also provide mechanical anchorage and favorable tilts.
Soil is our most important natural resource and a natural resource is anything that comes
from the earth and is used by us. We depend on the soil for food, clothing, shelter,
minerals, clay & water. Soil is the seat of many macro and micro flora like algae, fungi,
earthworms, bacteria etc. These are very beneficial in promoting soil reactions and
decomposing the organic matter by which essential nutrients for plants are liberated. Most
of the soils are made-up of two main parts:
Tiny bits of mineral particles which come from larger rocks, and humus, which is
dark brown in colour and consists of decaying remains of plants and animals.
Environmental Impact Assessment for Expansion of Existing pesticide plant for manufacturing of technical grade pesticides in village – Biratiya Kalan, Tehsil – Raipur, Distt – Pali, Rajasthan
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Soil also contains water, air and living organisms, such as fungi, bacteria,
earthworms, roundworms, insects, etc. Actually, more living organisms live in the
soil than above it.
For general characterization of soil a few random samples from the study area to the
depth of about 15-cm may sufficient. Deeper soil samples may be needed only for the
study of soil Profile.
3.9.1. General Characteristics of the Soil in the District2
The Pali soils occur on nearly level to gently sloping plain at an elevation of 200 to 250m
above mean sea level under semi-arid to arid sub-tropical climate conditions. The soils
have developed on unconsolidated weathered granite and rhyolite material, and are well
drained with moderately permeable conditions. The runoff loss is estimated at 15 to 20 %
of total rainfall. Brown to dark brown loamy, moderate fine to medium granular structure;
slightly hard, friable, slightly sticky and plastic; and moderately alkaline nature of soil is
commonly found in the study area as well as in the district.
Soil map of Rajasthan (Pali) district is shown as Figure 3.13.
2(Source-http://library.wur.nl/isric/fulltext/isricu_i11161_001.pdf)
Environmental Impact Assessment for Expansion of Existing pesticide plant for manufacturing of technical grade pesticides in village – Biratiya Kalan, Tehsil – Raipur, Distt – Pali, Rajasthan
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Figure 3.13 : Soil Map of Rajasthan (Pali) District
3.9.2. Methodology
The soil samples were collected from Eight (08) selected locations during post monsoon
season (Oct-Dec 2016) and revalidated in May 2017. The samples collected from all the
locations were homogeneous representative of each location. At random five sub-
locations were identified at each location and soil samples were collected from 5 to15-cm
below the surface. It was uniformly mixed before homogenizing the soil samples. The
samples about 500-gms were packed in polythene bags labeled in the field with location &
number and sent to the laboratory for the analysis of physicochemical parameters. Soil
sampling locations were selected based on the local geological formation and the
agricultural practices. Soil sampling locations with their distance & directions with respect
to the proposed expansion project site are presented in Table: 3.20& shown in Figure:
3.4.
Table 3.20 Soil Sampling Locations
Pali
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Location
Code
Sampling Locations Coordinates Location
Remark
S-1 Project Site 260 07' 08.8" N, 0740 05' 33.9" E Commercial
/ Industrial
S-2 Dhulkot 260 08' 03.5" N, 0740 06' 14.7" E Agricultural
S-3 Birantiya Khurd 260 07' 16.80" N, 0740 08' 11.2" E Agricultural
S-4 Birantiya Kalan 260 06' 50.8" N, 0740 05'16.0" E Agricultural
S-5 Lakshmangarh 260 07' 54.1" N, 0740 04' 35.3" E Agricultural
S-6 Road Junction of Birantiya
Kalan and Purthigarh
260 07' 33.7" N, 0740 03' 26.7" E
Agricultural
S-7 Road Junction of Birantiya
Kalan and Dhulkot
26007' 05.20" N, 0740 05' 28.0" E
Agricultural
S-8 Hajiwas 260 08' 30.8" N, 0740 05' 34.4" E Agricultural
3.9.3. Analysis of Soil Samples
The soil samples were examined for various physicochemical parameters, to determine
the existing soil characteristics of the study area. Soil samples were collected from the
vicinity of proposed project site during post Monsoon season (Oct-Dec 2016) and
repeated in May 2017. Physicochemical characteristics of soil for post monsoon season
and May 2017 are presented in Table 3.21& Table 3.22.
Table 3.21 Physicochemical Characteristics of Soil Oct-Dec 2016)
S. No.
Parameter Unit S1 S2 S3 S4 S5 S6 S7 S8
1 pH - 8.62 8.26 8.06 8.01 7.65 7.96 8.02 8.22
2 Electrical Conductivity
274 186.9 1184 380.6 202.5 207.5 321.3 110.6
3 Moisture % 10.96 22.61 6.17 8.84 2.2 7.49 9.56 7.76
4 Calcium Carbonate % 0.8 1.2 2.8 5.6 6.4 2.8 5.2 2
5 Sp. Gravity gm/cc 2.382 3.552 2.395 2.447 2.435 2.453 2.342 2.478
6 B.D. Taped gm/cc 0.948 1.216 0.981 0.797 1.308 1.414 1.378 1.099
7 Chlorides as Cl % 0.0071 0.0062 0.0052 0.0075 0.0082 0.0079 0.0081 0.0078
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8 Porosity % 60.2 52.35 59.03 67.42 46.28 42.35 41.16 55.64
9 Organic Carbon % 0.516 0.672 0.536 0.551 0.521 0.604 0.611 0.703
10 Organic Matter % 0.889 1.158 0.924 0.950 0.898 1.041 1.053 1.211
11 Available Nutrients
i) Nitrogen as "N" kg/ha 260 260 240 220 290 178 172 340
ii) Phosphorous as "P" kg/ha 72 38 31 42 42 35 33 45
iii) Potassium as "K" kg/ha 212 220 180 186 178 226 230 192
12 Copper as 'Cu' % 0.0048 0.0044 0.004 0.0043 0.0041 0.0041 0.044 0.0037
13 Iron As 'Fe' % 1.835 13 1.735 1.52 1.84 1.87 1.43 1.656
14 Sodium as 'Na' % 0.0376 0.038 0.025 0.0269 0.0334 0.0335 0.0291 0.0274
15 Zinc as Zn % 0.0089 0.0062 0.0087 0.0069 0.0054 0.0069 0.0092 0.0096
16 Cadmium as Cd % 0.0037 0.0033 0.0039 0.004 0.0037 0.0038 0.0035 0.004
17 Boron as B % 0.0033 0.0042 0.0027 0.0031 0.0028 0.0026 0.0028 0.0029
18 Water Holding Capacity
% 35.12 28.12 17.83 32.76 22.01 25.73 19.40 31.50
19 Particle Size Distribution
i) Sand % 66.1 66.65 66.83 66.44 66.63 66.86 65.78 65.91
ii) Silt % 14.6 13.9 13.72 14.35 13.9 14.07 14.8 14.87
iii) Clay % 19.3 19.45 20.75 20.21 19.47 19.07 19.42 20.22
3.9.4. Observation on Soil Quality (Post Monsoon season 2016)
Physical Parameters
The important physical characteristics of soil are bulk density, moisture content, water
holding capacity and texture. A brief summary of physical characteristics is given below:
Moisture Content: Moisture content of soil samples along with project site is ranged
between 2.2 to 22.61%.
Water Holding Capacity (WHC): Water holding capacity (WHC) of soil samples are
ranged between 17.83 to 35.12%.
Bulk Density: Bulk Density of soil is found to be in the range between 0.797 to 1.414
gm/cc.
Chemical Parameters
A brief summary of chemical characteristics is given below:
pH: pH is determined by taking 1:2.5 ratio of soil and distilled water. pH of soil in the
area is found to be in the range between 7.65 – 8.62. The soil of this area is moderately
alkaline nature.
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CalciumCarbonate:Carbonate Calcium is a highly essential nutrient to plants and
affects the activities of certain enzymes. The calcium carbonate contents as CaCO3 in
the collected soil samples found in the range between 0.8 to 6.4%.
AvailablePhosphorous: Available phosphorous as P of collected soil samples along
the proposed project ranges from 31 to 72-kg/ha and Available Phosphorus are present
in medium range.
TotalOrganicCarbon:Total organic carbon content in soil samples along the proposed
project is found from 0.516 to 0.703% in the range which is very less for plant growth.
Potassium:Potassium content as K in soil samples along the proposed is found in the
range of 178 to 230-kg/ha.
Kjeldahl Nitrogen: Kjeldahl nitrogen content in soil samples along the proposed is
found in the range between 172 to 340-kg/ha. Available Nitrogen in these soil samples is
found satisfactory. Porosity in these soil samples vary from 41.16 to 67.42% which is
average to plant growth.
Environmental Impact Assessment for Expansion of Existing pesticide plant for manufacturing of technical grade pesticides in village – Biratiya Kalan, Tehsil – Raipur, Distt – Pali, Rajasthan
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Table 3.22 Physicochemical Characteristics of Soil (May 2017)
S.
No.
Parameters Unit S-1 S-2 S-3 S-4 S-5 S-6 S-7 S-8
Physical Characteristics
1. Color - Yellowish
Brown
Yellowish
Brown
Yellowish
Brown
Yellowish
Brown
Yellowish
Brown
Yellowish
Brown
Yellowish
Brown
Yellowish
Brown
2. Textural Class USDA
System
Sandy Clay
Loam
Sandy
Clay
Loam
Sandy Clay
Loam
Sandy Clay
Loam
Sandy Clay
Loam
Sandy
Loam
Sandy Clay
Loam
Sandy
Loam
3. Particle Size Distribution
i) Sand (0.02 to 0.20-mm)
% 62 64 58 56 54 57 58 55
ii) Silt (0.002 to 0.02-mm)
% 20 21 22 21 20 19 16 18
iii) Clay (< 0.002-mm) % 18 15 20 23 26 24 26 27
4. Porosity % 45.7 48.7 47.6 46.4 45.3 44.1 46.8 47.2
5. Bulk Density gm/cc 1.44 1.36 1.39 1.42 1.45 1.48 1.41 1.40
6. WHC % 28.8 28.5 29.4 30.8 29.2 29.6 28.7 29.1
7. Permeability cm/hr 0.91 1.33 0.73 0.53 0.40 0.48 0.38 0.36
Chemical Characteristics
8. pH 20% Slurry 7.58 7.86 7.46 8.15 7.66 7.74 7.52 7.86
9. Conductivity µmhos/cm 156.2 166.4 145.6 157.5 162.6 174.5 156.8 175.2
10. Cation Exchange
Capacity
Meq/100-
gm
18.8 19.5 17.6 15.8 17.5 19.2 17.8 18.5
11. Organic Matter % 0.78 0.66 0.62 0.71 0.74 0.85 0.78 0.83
12. Organic Carbon % 0.45 0.38 0.36 0.41 0.43 0.49 0.45 0.48
13. Zinc as Zn mg/kg 0.52 0.38 0.44 0.56 0.48 0.55 0.47 0.51
14. Iron as Fe mg/kg 2.26 2.58 3.12 3.25 2.88 3.95 2.78 3.45
15. Copper as Cu mg/kg 0.85 0.75 0.62 0.58 0.65 0.54 0.46 0.62
16. Manganese as Mn mg/kg 3.48 2.88 3.36 3.55 2.95 3.68 2.84 3.44
17. Chloride as Cl mg/kg 425.5 396.8 468.2 458.8 345.6 415.9 346.5 410.8
18. Carbonate mg/kg <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01
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19. Bi-Carbonate mg/kg 226.5 306.8 350.2 255.6 238.7 288.5 244.5 274.5
20. Available Nutrients
i) Nitrogen as N kg/ha 265.8 275.6 256.5 268.2 275.4 272.5 268.5 262.8
ii) Phosphorus as P kg/ha 18.6 21.8 18.4 16.8 20.7 18.2 18.5 19.4
iii) Potassium as K kg/ha 156.4 145.9 153.6 147.2 139.2 145.5 138.5 141.7
Source: Primary Data Collection and analysis during study period by Laboratory
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3.9.5. Observation on Soil Quality (May 2017)
Physical property
Yellowish Brown colour soils are observed in the study area. Texturally the soils of study
area are observed as Sandy Clay Loam and Sandy Loam Soils. The bulk density of the
soils was found in the range of 1.36 to 1.48-gm/cm3. Water Holding Capacity of study
area soils was observed as 28.5 to 30.8%.
Chemical Properties
Soil Reaction Classes and Critical Limits for Macro & Micro Nutrients in Soil: According to
According to Soil Survey Manual (IARI, 1970), the soils are grouped under different soil
reaction classes viz; extremely acidic (pH<4.5), very strongly acidic (pH 4.5-5.0 ), strongly
acidic (pH 5.1-5.5), moderately acidic (pH 5.6-6.0), slightly acidic (pH 6.1-6.5), neutral (pH
6.6-7.3), slightly alkaline (pH 7.4-7.8), moderately alkaline (pH 7.9-8.4), strongly alkaline
(pH 8.5-9.0).The soils are rated as low (below 0.50 %), medium (0.50-0.75 %) and high
(above 0.75 %) in case of organic carbon, low (<280-kg/ha), medium (280 to 560-kg/ha)
and high (>560-kg/ha) in case of available Nitrogen, low (<10-kg/ha), medium (10 to 25-
kg/ha) and high (>25-kg/ha) for available Phosphorus, low (<108-kg/ha), medium (108 to
280-kg/ha) and high (>280-kg/ha) for available Potassium and low (<10-mg/kg), medium
(10-20-mg/kg) and high (>20-mg/kg) for available Sulphur (Singh et. al. 2004, Mehta et.
al.1988). Critical limits of Fe, Mn, Zn, Cu and B, which separate deficient from non-
deficient soils followed in India are, 4.5, 2.0, 0.5, 0.2 & 0.5-mg/kg respectively. (Follet &
Lindsay-1970 and Berger & Truog-1940)
The soil pH ranges from 7.46 to 8.15, thereby indicating the soils are slightly alkaline to
moderately alkaline. The organic carbon content of soil varied from 0.36 to 0.49% (0.62 to
0.85% as organic matter), thereby implying that soils are low in organic carbon contents.
Available nitrogen content in the surface soils ranges between 256.5 & 275.6-kg/ha
thereby indicates that soils are low in available nitrogen content. Available phosphorus
content ranged between 18.2 & 21.8-kg/ha thereby indicating that soils are having
medium in available phosphorus. Available potassium content in these soils ranges
between 139.2 & 156.4-kg/ha thereby is indicating that the soils are with medium levels of
available potassium content. Thus, the soil of the study area is moderate fertile.
The available manganese content in surface soils were recorded as 2.88 to 3.68-mg/kg,
as the critical limit of available manganese is <2.0-mg/kg. The available zinc in surface
soils of the study area ranges from 0.38 to 0.56-mg/kg. As per the critical limit of available
zinc is <0.5-mg/kg, Soil conditions more often associated with Zinc deficiency in the study
area soil.
3.9.6. Cropping Pattern
The western part of Rajasthan is having less productivity but Pali district enjoys
comparatively more favorable condition for agricultural activities than other districts of
western Rajasthan. Pali District Sojat and Raipur tehsil is famous for Mahandi crop and it
crop depends on rain only. The main crops of the district are Kharif and Rabi. Kharif crops
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are primarily supported by rainy water whereas Rabi crops are irrigated by other water
resources. The Kharif crops are shown prior to monsoon in the month of June-July
whereas Rabi crops are shown in the month of October-November and harvested in
February-March. The main crops of Kharif are – Jowar, Bajra, Maize, Chillies, Groundnut,
Til and Cotton. The main crops of Rabi are wheat, Barley, Grams, Rai and Mustard.
Cropping Pattern of Pali District for Kharif and Rabi season is presented in Table
3.23&3.24.
Table 3.23 Area under Major Field Crops3&Horticulture, 2010-11
Major Cultivated Field Crops
Area, ha
Kharif Rabi Summer Total
Irrigated Rain fed Total Irrigated Rain fed
Total
Pearl Millet 13295 93131 106426 - - - - 106426
Cluster bean 5290 10190 15480 - - - - 15480
Moth bean 220 6700 6920 - - - - 6920
Green gram 1600 10300 11900 - - - - 11900
Sorghum 2000 4515 6515 - - - - 6515
Sesame 150 8900 9050 - - - - 9050
Cowpea 120 7200 7320 - - - - 7320
Groundnut 50 250 300 - - - - 300
Castor 1200 920 2120 - - - - 2120
Cotton 1395 1015 2410 - - - - 2410
Mustard - - - - 275 9450 - 9450
Wheat - - - - 120 11092 - 11092
Cumin - - - - 90 7390 - 7390
Barley - - - - 1500 10000 - 10000
Gram - - - - 1710 7805 - 7805
Taramira - - - - 1276 1871 - 1871
Fenu greek (Methi)
- - - - 150 3350 - 3350
Fennel - - - - 350 2070 - 2070
Total Irrigated Rain fed
Ber 1500 - -
3(Source-http://www.nicra-icar.in/nicrarevised/images/statewiseplans/Rajastan%20(Pdf)/MPUA&T,%20Udaipur/RAJ31-
Pali-28.08.12.pdf)
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Aonla 910 250 660
Lemon 1610 476 1134
Guava 767 50 717
Lisoda 1200 200 1000
Pomegranate 75 10 65
Papaya 720 200 520
Horticultural Crops
Total Irrigated Rain fed
Chillies 4200 3200 1000
Onion 911 700 211
Carrot 920 620 300
Tomato 1176 1000 176
Brinjal 1309 875 434
Cole crops 1678 1276 402
Melon-Musk 1302 120 1182
Medicinal and Aromatic
Total Irrigated Rain fed
Isabgol 421 421 0
Sua 221 95 126
Plantation Crops
Total Irrigated Rain fed
Mahandi (Henna)
4000 - 4000
Fodder Crops Total Irrigated Rain fed
Sorghum 1621 200 1421
Pearl Millet
(Fodder)
920 200 720
Cluster bean (Fodder)
1720 406 1314
Lucern Fodder 2295 1195 1100
Table 3.24 Production and Productivity of Major Crops, 2010-11
S. No.
Major Cultivated
Crops
Kharif Rabi
Summer
Total
Prodn. (,000-t)
Prodty. ( Kg/ha)
Prodn. (,000-t)
Prodty. ( Kg/ha)
Prodn. (,000-t)
Prodty. ( Kg/ha)
Major Field Crops (Crops to be identified based on total acreage)
1 Pearl Millet 467610 540 - - - 467610 540
2 Green gram 303530 310 - - - 303530 310
3 Moth Bean 14170 201 - - - 14170 201
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4 Cluster Bean 358740 166 - - - 358740 166
5 Groundnut 252021 1740 - - - 252021 1740
6 Castor 30312 635 - - - 30312 635
7 Sesame 458820 280 - - - 458820 280
8 Cotton 26410 2100 - - - 26410 2100
9 Sorghum 546660 510 - - - 546660 510
10 Chilies 271115 620 - - - 271115 620
11 Cow pea 282110 199 - - - 282110 199
12 Mustard - - 915990 1390 - 915990 1390
13 Wheat - - 1382710
1789 - 1382710
1789
14 Isabgol - - 2011 421 - 2011 421
15 Cumin - - 25630 642 - 25630 642
16 Taramira - - 275920 1120 - 275920 1120
17 Gram - - 293690 862 - 293690 862
18 Barley - - 73110 1799 - 73110 1799
19 Onion - - 104520 1520 - 104520 1520
20 Garlic - - 92150 1621 - 92150 1621
21 Funnel - - 17900 1820 - 17900 1820
22 Fenugreek - - 16110 1615 - 16110 1615
3.10. Traffic Study
The proposed plant is located about 1.16 km away from the National Highway NH-112.
The plant site is well connected through a major district road to NH-112. All inward and
outgoing materials movement from the plant shall be donethrough this road. To access
the traffic volume on NH 112 near plant site a traffic study was conducted by Enkay enviro
services during post monsoon season. Outcome of the study is depicted in Table 3.25.
The PCU factor applied for the calculation is provided in Table 3.26. Total PCU calculated
is shown in Table 3.27.
Table 3.25 Traffic survey near the plant site
S.N. Time Vehicle movement Total
No of Two wheeler
No of Four wheeler
No of Heavy vehicles
1. 07.00 AM - 08.00 AM 16 8 16 40
2. 08.00 AM - 09.00 AM 39 19 18 76
3. 09.00 AM - 10.00 AM 25 33 12 70
4. 10.00 AM - 11.00 AM 23 15 21 59
5. 11.00 AM - 12.00 PM 22 28 16 66
6. 12.00 PM - 13.00 PM 20 29 19 68
7. 13.00 PM - 14.00 PM 15 12 34 61
8. 14.00 PM - 15.00 PM 15 8 22 45
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9. 15.00 PM - 16.00 PM 21 13 31 65
10. 16.00 PM - 17.00 PM 34 18 36 88
11. 17.00 PM - 18.00 PM 28 24 28 80
12. 18.00 PM - 19.00 PM 22 31 33 86
13. 19.00 PM - 20.00 PM 36 24 16 76
14. 20.00 PM - 21.00 PM 28 18 12 58
15. 21.00 PM - 22.00 PM 18 28 8 54
16. 22.00 PM - 23.00 PM 9 18 11 38
17. 23.00 PM - 24.00 AM 2 6 21 29
18. 24.00 AM - 01.00 AM 1 10 9 20
19. 01.00 AM - 02.00 AM 2 8 12 22
20. 02.00 AM - 03.00 AM 1 2 6 9
21. 03.00 AM - 04.00 AM 3 2 28 33
22. 04.00 AM - 05.00 AM 7 12 16 35
23. 05.00 AM - 06.00 AM 15 18 11 44
24. 06.00 AM - 07.00 AM 21 21 24 66
Table 3.26 : PCU Factors Applied for Different Class of Vehicles
Type of Vehicles PCU Factors
1 Two-wheelers 0.5
2 Car, Jeep, Taxi, Utility Vehicles, Auto-Rickshaw (3-wheelers), Tempo, etc 1.0
3 Bus, Truck, etc 3.0
4 Tractors 4.5
5 Multi-axle truck, dumpers, etc 4.5
Table 3.27 Total PCU on single Lane Road near Plant Site
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Type of Vehicles No of Vehicles Total PCU
1 Two-wheelers 423 211
2 Car, Jeep, Taxi, Utility Vehicles, Auto-
Rickshaw (3-wheelers), Tempo
405 405
3 Bus, Truck, etc 460 1380
4 Tractors - -
5 Multi-axle truck, dumpers, etc - -
Total PCU 1288 1996
At present the Total PCU load on the existing road is 1996 PCU. As per the Indian Road
Congress (IRC: 64 – Guidelines for Capacity of Roads in Rural Area – Code of Practice,
1990) indicates the design service value of 15000 PCU/day for a 2-lane road (7.5 m
width) and 2000 PCU/day for a single-lane road (3.5 m width) on plain rural terrain.
Existing capacity of the double lane (NH 112) road under mixed traffic conditions were
studied and the PCU estimated as per guidelines of IRC is 1996. Based on above
guidelines and code of practice it has been ascertained that the NH 112 is well within the
design service value of 15000 PCU/day, as prescribed by the Indian Road Congress.
3.11. Ecological Environment
The Botanical and wildlife species in an area depend on the availability of suitable habitat
for survival. Habitat loss and increasing habitat fragmentation are the primary causes of
species decline in these environments. This section provides an overview of flora and
fauna observed in study area during site visit.
3.11.1. Flora
There is no tree cutting is required on identified land. No major vegetation is present
within the core zone hence no wildlife exists within the core zone. At present only shrub
species like Calotropis procera, Argemone maxicana acacia species and Prosopis
juliflora.
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Site Photograph Site Photographs
Flora in Core Zone
Most of the vegetation within the core zone is in the form of plantation done by INTECH
Pharma under the green belt plantation. The common trees observed within the core zone
are Neem (Azadirachta indica), Siris (Albizia lebbeck), Shisham (Dalbergia sissoo) Ashok
(Polyalthia longifolia), Gulmohar (Delonix regia) and Kachnar (Bauhinia variegata). The
list of the flora observed within the core zone is presented in Table 3.28.
Table 3.28 List of Flora within Core zone
Trees
S. No. Common Name Species Name Family
1 Neem Azadirachta indica Meliaceae
2 Gulmohar Delonix regia Caesalpiniaceae
3 Siris Albizia lebbeck Fabaceae
4 Pipal Ficus religiosa Moraceae
5 Khejari Prosopis cineraria Fabaceae
6 Amaltash Cassia fistula Fabaceae
7 Karanj Pongamia pinnata Fabaceae
8 Ficus Ficus benjamina Moraceae
9 Desi Babool Acacia nilotica Fabaceae/Mimosoideae
Shrubs
1 Kaner Nerium oleander Apocynaceae
2 Peeli Kaner Thevetia peruviana Apocynaceae
3 Aak Calotropis procera Asclepiadaceae
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4 Khimp Leptadenia pyrotechnica Asclepiadaceae
5 Ker Capparis deicuda Capparidaceae
6 Kikar Acacia jacquemontii Fabaceae
7 Phog Calligonum polygonoides Polygonaceae
8 Senna Senna auriculata Fabaceae
9 Raimuniya Lantana camara Verbenaceae
Herbs & Grass
1 Satyanashi Argemone maxicana Papavaraceae
2 Bui Aerva tomentosa Amaranthaceae
3 Senia Crotalaria burhia Fabaceae
4 Unth kantalo Echinops echinatus Asteraceae
5 Bhurat Cenchrus biflorus Poaceae
6 Sharpunkha Tephrosia purpurea Fabaceae
7 Doob ghas Cynodon dactylon Poaceae
8 Daabh Desmostachya bipinnata Poaceae
Flora in Buffer Zone
Most of the land around thestudy area (10 km radius around the project site) is under
agriculture and residential uses. No national parks, wild life sanctuary, biosphere reserve
is present within 10 km area of the project site. However, few patches of Reserve Forest
are present within the study area in east and south east direction. The forest patched are
located more than 5 km away from the project site. As per the land use classification
about 7 % of the land in study area is under dense forests and about 33% of the land is
under open forest. The forest in the study area are scattered and mostly in hills and
ridges. In general, the vegetation is dry deciduous type. The structure and composition of
vegetation was studied by observing each and every individual plant species growing in a
habitat.
The vegetation in the study area is open mixed type and mostly restricted in areas like
river banks, gullies and hills and ridges. The vegetation in study area is dominated by
Acacia species and Prosopis cineraria. The most characteristic tree in the study area
areAzadirachta indica), Siris (Albizia lebbeck), Shisham (Dalbergia sissoo) Ashok
(Polyalthia longifolia), Gulmohar (Delonix regia), Kachnar (Bauhinia variegata), Ficus
benghalensis, Ficus religiosa,Acacia nilotica and Prosopis cineraria.
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The Ground vegetation dominated by the herbs and shrub species like Zyziphus
mauritiana, Calotropis procera, Ipomoea carnea,Ricinus communis, Argemone mexicana,
Solanum surattense, Xanthium strumarium, Dhatura metal, Sida cordifolia, Polygonum
glabrum, Cassia tora, Canabis sativa, Chenopodium album, Cyanodon dactylon,
Parthenium hysterophorus and Achyranthus aspera. The list of the plant species
observed in the study area is given Table 3.29.
Table 3.29 List of Common Plant Species Present in Study Area
S.
No.
Vernacular Name Scientific Name Family
Trees
1. Ronjh Acacia leucopholea Fabaceae (Mimosoideae)
2. Babool Acacia nilotica Fabaceae (Mimosoideae)
3. Ardu Ailanthus excelsa Simaroubaceae
4. Siris Albizia lebbeck Mimosaceae
5. Neem Azadirachta indica Meliaceae
6. Dhak Butea monosperma Fabaceae (Papilionaceae)
7. Amaltash Cassia siamea Caesalpiniaceae
8. Shesham Dalbergia sissoo Fabaceae (Papilionaceae)
9. Lasoda Cordia dichotoma Boraginaceae
10. Gulmohar Delonix regia Caesalpiniaceae
11. Bargad Ficus benghalensis Moraceae
12. Pipal Ficus religiosa Moraceae
13. Kankera Maytenus emarginata Celastraceae
14. Ashok Polyalthia longifolia Annonaceae
15. Karanj Pongamia pinnata Fabaceae (Papilionaceae)
16. Khejari Prosopis cineraria Mimosaceae
17. Imli Tamarindus indica Fabaceae (Leguminosae)
18. Rohida Tecomella undulata Bignoniaceae
19. Ber Ziziphus mauritiana Rhamnaceae
20. Aamla Phyllanthus emblica Euphorbiaceae
21. Safeda Eucalyptus globolus Myrtaceae
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22. Vilayati Babool Prosopis juliflora Fabaceae
23. Kikar Acacia jacquemontii Fabaceae
Shrubs
1 Aakra Calotropis gigantean Asclepiadaceae
2 Aak Calotropis procera Asclepiadaceae
3 Kair Capparis decidua Capparidaceae
4 Behaya Ipomoea carnea Convolvulaceae
5 Kaner Nerium oleander Apocynaceae
6 Nag phani Opuntia elatior Cactaceae
7 Vilayati babool Prosopis juliflora Mimosaceae
8 Arandi Ricinus communis Euphorbiaceae
9 Kans Saccharum spontaneum Poaceae (Gramineae)
10 Jharberi Ziziphus nummularia Rhamnaceae
11 Champa Plumeria alba Apocynaceae
12 Dandathor Euphorbia caducifolia Euphorbiaceae
Herbs
1 Bui Aerva tomentosa Amaranthaceae
2 Pili Kantili Argemone Mexicana Papaveraceae
3 Kala bhangra Anisomeles indica Lamiaceae
4 Jangli chaulai Amaranthus spinosus Amaranthaceae
5 Latjira Achyranthes aspera subsp. argentea Amaranthaceae
7 Muktajhuri Acalypha indica Euphorbiaceae
8 Punarnava Boerhavia diffusa Nyctaginaceae
9 Survali Celosia argentea Amaranthaceae
10 Chitraa Citrullus colocynthis Cucurbitaceae
11 Ban Tulsi Croton bonplandianum Euphorbiaceae
12 Kachari Cucumis melo ssp. Agrestis Cucurbitaceae
13 Dhatura Datura metel Solanaceae
14 Latmahuria Digera muricata Amaranthaceae
15 Motha Cyperus rotundus Cyperaceae
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16 Unthkanta Echinops echinatus Asteraceae
17 Oldman'S Cap Polycarpaea corymbosa Caryophyllaceae
18 Gulpankhi Polygala erioptera Polygalaceae
19 Laptuna Setaria verticillata Poaceae (Gramineae)
20 Baraira (bala) Sida acuta Malvaceae
21 Khareti Sida rhombifolia Malvaceae
22 Asiatic witchweed Striga asiatica Scrophulariaceae
23 Marigold Tagetes minuta Asteraceae
24 Yellow Bell Tecoma gaudichaudi Bignoniaceae
25 Sarphonk Tephrosia purpurea Fabaceae (Papilionaceae)
26 Sharpunkha Tephrosia villosa Fabaceae (Papilionaceae)
27 Peeli Kaner Thevetia peruviana Apocynaceae
28 Badi Dudhi Euphorbia hirta Euphorbiaceae
29 Gokhru Indigofera cordifolia Fabaceae (Papilionaceae)
30 Nili Indigofera linnaei Fabaceae (Papilionaceae)
31 Raimuniya Lantana camera Verbenaceae
32 Tikiokra Melochia corchorifolia Sterculiaceae
33 Jharasi Mollugo pentaphylla Molluginaceae
34 Dudhi Sonchus oleraceus Asteraceae
35 Damanpaper Oldenlandia corymbosa Rubiaceae
36 Bada Gokhru Pedalium murex Pedaliacae
Grass
1 Jhuhi ghas Alysicarpus monilifer Fabaceae (Papilionaceae)
2 Bristle grass Aristida adscensionis Poaceae (Gramineae)
3 Doob ghas Cynodon dactylon Poaceae (Gramineae)
4 Sheda Grass Dichanthium annulatum Poaceae (Gramineae)
5 Makra Dactyloctenium aegyptium Poaceae (Gramineae)
6 Panghas Eragrostis japonica Poaceae (Gramineae)
7 Chinese Love Grass Eragrostis unioloides Poaceae (Gramineae)
9 Asian crab grass Digitaria bicornis Poaceae (Gramineae)
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10 jangli-jowar Sorghum halepense Poaceae (Gramineae)
12 Okrich (Mauritania). Sporobolus helvolus Poaceae (Gramineae)
13 Thread Sprangletop Leptochloa panicea Poaceae (Gramineae)
Medicinal Plants:The study area shows many medicinal plants. Many medicinal plants
are also observed in which Azadirachta indica; Aegle marmelos, Emblica officinalis,
Ocimumsanctum are the important one. List of medicinally important trees, shrubs and
herbs and their uses with their natural orders are presented in Table 3.30.
Table 3.30 List of Medicinal Plants and their Medicinal Value
Sr.
No. Name of Species Family Medicinal Use
Trees
1. Aegle marmelos Rutaceae
Antidiuratic, antithetmintic, antipyretic, carminative tonic
Furit used in chronic diarrhoea & dysentery
2. Azadirachta indica Meliaceae
Oil extracted from seed as local stimulant, insecticide and antiseptic
3. Cassia fistula Caesalpiniaceae
Control fever and gas trouble
Laxative
4. Emblica offcinalis Euphorbiaceae
Fruit powder coolent and laxative
Rich source of vitamin C
5. Ficus religiosa Moraceae
Quenches thirst
6. Syzygium cumini Mystaceae
Stem bark is used to treat sore throat, bronchitis, ulcer, dysentery
Seed powder for diabetes
7. Acacia nilotica Mimosaceae
In pharmacy, used in preparing emulsions, tablets, pills etc.
8. Calatropis procera Asclepiadaceae
Root bark used for leprosy
9. Argemone
Mexicana
Papaveraceae Latex is laxative and used in cataract
Seed oil used in asthma
Rare and Endangered Plant Species in the Study Area: In the study area, no rare and
endangered plant species was observed (Source: Red Data Book of Indian Plants, N.P
Nayar and A. P. K. Sastry, B.S.I. 1988).
3.11.2. Fauna
No national parks, wild life sanctuary, biosphere reserve is present within 10 km area of
the project site. However, few patches of Reserve Forest are present within the study
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area in east and south east direction. The forest patched are located more than 5 km
away from the project site. As per the land use classification about 7 % of the land in
study area is under dense forests and about 33% of the land is under open forest. The
forest in the study area are scattered and mostly in hills and ridges. The wild fauna is
restricted only to the forest areas.
The information on fauna was collected by visual observations, random survey at different
locations and discussion with the local people. The secondary data from different Govt.
Sources and available literature was also referred in this study. The fauna study is carried
for corezone as well as for buffer zone i.e. 10 km area around the project site, which is
describes in following sections.
A. Fauna in Core zone: The land identified for the proposed expansion is under process
of possision in possession of the INTECH No tree cutting is required. No major
vegetation is present within the core zone hence no wildlife exists within the core
zone. However, the presence of reptiles and amphibian species has been reported by
the local people. Common avifaunal species has also been observed in the core
zone.
B. Fauna in Buffer Zone: List of fauna found in buffer zone (10 km study area) is
provided in Table 3.31. The listed fauna found in study area has been cross-checked
with Red Data Book of Indian Animals (Zoological Survey of India). There is no
endangered or Schedule-I faunal species in the study area except Peafowl (Pavo
Cristatus) which is schedule –I species but is of least concern category.
C. The Indian Peafowl is categorized as ‘Least Concerned’ in the International Union for
Conservation of Nature’s (IUCN) Red List. However, in India this species was
declared a ‘National Bird’ in1963 and has been provided utmost protection by
including it in Schedule I of the Indian Wildlife Act, 1972. Though this charismatic
species is not considered under potentially threatened category as of now. A least
concern (LC) species is a species which has been categorized by the International
Union for Conservation of Nature as evaluated but not qualified for any other
category. As such they do not qualify as threatened, near threatened, or (before
2001) conservation dependent. Though a conservation plan for Pavo cristatus has
been prepared by Enkay Enviro and approved by DFO Paliwhich is attached as
Annexure- VII. Application has already been submitted to Chief Wildlife Warden for
Schedule – I fauna conservation plan approval.
Mammals:
No significant carnivorous and herbivorous wild animals are found in the area. Blue bull
(Boselaphus tragocamelus), Mongoose (Herpestes edwards) and Jungle Cat (Felis
chaus) are the common mammals observed in the area. List of mammals observed in the
study area is provided in Table 3.32.
Amphibian & Reptiles (Herpetofauna)
Frog, Indian bull frog, snake like Indian cobra (Naja naja); Dhaman (Lycodon aulicus), and
\lizard are encountered at various places in study area (refer Table 3.33).
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Table 3.31 Mammalian Fauna reported in study area
S.N
o.
Family Zoological name Local Name English Name Schedule
Class-Mammalia (Order: Primates)
1 Colobidae Presbytia entellus Langur Common langur II
2 Pteropodidae Cynopterus sphinx Chamgader Short nosed fruit bat V
3 Pteropodidae Manis crassicandata Shehi Indian pangolin IV
4 Felidae Felis chaus Jangli Billi Wild cat II
5 Herpestidae Herpestes edwardsi Newala Mangoose II
6 Canidae Vulpes benglensis Lomadi Indian fox II
7 Sciuridae Funambulus pennant Gilhaari Common squirrel IV
8 Muridae Bandicota
bengalensis
Chuha Field rat V
9 Hystricidae Hystrix Indica Shahi Common Porcupine IV
10 Leporidae Lepus nigricollis Khargosh Common Indian
hare
IV
11 Cetartiodactyla Boselaphus
tragocamelus
Neelgai Blue bull III
Table 3.32 : Reptiles and Amphibian observed in Study Area
S. N. Common Name Scientific Name Vernacular
Name Family
Feeding
Status
Schedule
Amphibians
1 Frog Rana tigrina - - C IV
2 Indian bull frog Hoplobatrachus
tigerinus
- - C IV
Reptiles
3 Binocellate cobra Naja naja Nag Elapidae C II
4 Indian Krait Bungarus coeruleus - Elapidae C IV
5 Russell’s Viper Vipera russellis - Crotalidae C II
6 Rat snake Ptyas mucosus Dhaman Colubridae C II
7 Forest Lizard Calotes versicolor - Agamidae C II
8 House geeko Hemidactylis brukaii - Gekkonidae C II
Avifauna
Avifauna is an important part of the ecosystem playing the various roles as scavengers,
pollinators, predators of insect, pest, etc. They are also one of the bio indicators of
different status of environment and affected by urbanization, industrialization and human
interference. They can be used as sensitive indicators of pollution and malfunction of
ecosystem.
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Due to presence of the favorable habitats for avifauna, wide range of avifauna observed
in the study area.The study area is inhabited by forty species of birds. Among the birds
recorded in this study, were insectivores and other dominating types. The list of avifauna
observed in the study area is given in Table 3.33.
Table 3.33 Avifauna Sighted during the primary survey
S. No. Common Name Scientific Name Family Status
(IWPA 1972)
1 Red-wattled lapwing Vanellus cinereus Charadriidae -
2 Baya weaver Ploceus philippinus Ploceidae Schedule IV
3 Variable wheatear Oenanthe picata sub sp.
Opistholeuca
Muscicapidae No mention
4 Grey francolin Francolinus pondicerianus Phasianidae Schedule IV
5 Indian peafowl Pavo cristatus Phasianidae Schedule I
(Least
Concern)
6 Indian Roller Coracias benghalensis Coraciidae Schedule IV
7 White-throated kingfisher Halcyon smyrnensis Alcedinidae Schedule IV
8 Green bee-eater Merops orientalis Meropidae -
9 Pied cuckoo Clamator jacobinus Cuculidae Schedule IV
10 Lesser coucal Centropus bengalensis Cuculidae Schedule IV
11 Rose-ringed parakeet Psittacula krameri Psittacidae Schedule IV
12 House swift Apus affinis sub sp. affinis Apodidae No mention
13 Rock Pigeon Columba livia Columbidae Schedule IV
14 Laughing dove Streptopelia senegalensis Columbidae Schedule IV
15 Collared dove Streptopelia decaocto Columbidae Schedule IV
16 Red Collared dove Streptopelia tranquebarica Columbidae Schedule IV
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17 Cattle egret Bubulcus ibis Ardeidae Schedule IV
18 Long-tailed shrike Lanius schach Laniidae -
19 House crow Corvus splendens Corvidae Schedule V
20 Black drongo Dicrurus macrocercus Dicruridae Schedule IV
21 White-bellied drongo Dicrurus caerulescens Dicruridae Schedule IV
22 Indian robin Saxicoloided fulicata Turdinae No mention
23 Common myna Acridotheres tristis Sturnidae Schedule IV
24 Bank myna Acridotheres ginginianus Sturnidae Schedule IV
25 Wire-tailed swallow Hirundo smithii Hirundinidae No mention
26 White-eared bulbul Pycnonotus leucotis Pycnonotidae Schedule IV
27 Red-vented bulbul Pycnonotus cafer Pycnonotidae Schedule IV
28 Jungle babbler Turdoides striatus Timaliinae Schedule IV
29 Purple sunbird Nectarinia asiatica Nectariniidae Schedule IV
30 House sparrow Passer domesticus Passerinae Schedule IV
31 Common Hoopoe Upuca epops Upupidae Schedule IV
Threatened and Endangered Mammals
The listed fauna found in study area has been cross-checked with Red Data Book of
Indian Animals (Zoological Survey of India). There is no endangered or critical faunal
species in the study area.
3.12. Socio-Economic Environment
Demographic and Socio-Economic Features4
Demography is one of the important indicators of environmental health of an area. It
includes population, number of households, literacy, population density, etc. In order to
assess the ‘Demographic and Socio-economic Features’ of the study area, census data of
4
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2011, forthe concerned District Pali, in Rajasthan State was compiled and placed in the
form of tabulation and graphical representation.
Demography of the District
As per the district census handbook of 2011 records, the total population of Pali district is
observed as 2037573 persons comprising with 1025422 males and 1012151 females. It
shares almost 2.97% of the state population. The population density of the district is
observed as164 persons/sq.km. Nearly 77.4% population of the district lives in rural areas
where proportion of urban population to the total population is observed as 22.6%. The
sex ratio of the district is observed as 987 females for every 1000 males. The district has
high child (age group 0 to 6 years) sex ratio i.e. 899 females for every 1000 males. Pali
district has mainly Hindu & Muslim population. As per 2011 census the proportions of
Hindu and Muslim population in total population are 91.8% and 7.0% respectively. The
proportion of Jain population in the district is too meagre as 0.9%. The district has
registered a percentage decadal variation of 12.0% during the decade, 2001-11. The rural
areas of the district have attained a lower decadal variation of 10.4% as compared to that
of urban area at 17.7%.
Population Distribution in the Study Area
Population Distribution within 2.0-km radial Zone of the Study Area: As per the
census records 2011, the total population of the 2.0-km radial zone of study area was
recorded as 4916 persons of four (04) revenue villages named Birantiya Kalan, Hajiwas,
Dhoolkot and Lawamali of Raipur Tahsil in Pali district of Rajasthan. Total number of
‘Households’ was observed as 1070 in the 2.0-km radius study zone. Male-female wise
total population was recorded as 2381 males and 2535 females respectively. Caste-wise
population distribution of the study area revenue villages/towns, is shown in Table 3.34.
Table 3.34 : Caste-wise Population Distribution of 2.0-km Radial Zone
Name of the
Village
No of
Households
Total Population
Scheduled
Castes
Scheduled
Tribes
Persons Male Female Male Female Male Female
Birantiya
Kalan 478 2445 1229 1216 741 710 4 6
Hajiwas 302 1217 567 650 231 231 5 14
Dhoolkot 272 1172 539 633 166 172 0 0
Lawamali 18 82 46 36 2 3 0 0
TOTAL 1070 4916 2381 2535 1140 1116 9 20
Source-Census Records 2011
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Population Distribution within 10.0-km radial Zone of the Study Area: As per the
census records 2011, the total population of the 10-km radius study area was recorded as
66012 persons of 42 revenue villages of Pali district of Rajasthan state. Three (3) villages
named, Beerbasni, Beesawas Kalan and Beesawas Khurd are uninhabited villages in the
study area. All the study area villages are falling mainly under two (02) Tehsil namely
Raipur and Jaitran of Pali district in Rajasthan. Total number of ‘Households’ was
observed as 14115 in the study area. Male-female wise total population was recorded as
32940 males and 33072 females respectively. Caste wise male-female population
breakup of the entire study area is shown in Table 3.35.
Table 3.35 Caste-wise Population Distribution of 10-km radial Study Area
Name of the
Village
No of
Household
s
Total Population
Scheduled
Castes
Scheduled
Tribes
Tehsil
Person Male
Femal
e Male
Femal
e Male
Femal
e
Birantiya Kalan 478 2445 1229 1216 741 710 4 6 Raipur
Hajiwas 302 1217 567 650 231 231 5 14
Dhoolkot 272 1172 539 633 166 172 0 0
Lawamali 18 82 46 36 2 3 0 0
Rampura Kalan 376 1585 752 833 261 235 0 0
Aakeli 229 896 407 489 127 139 0 0
Leelamba 586 2605 1273 1332 410 397 0 0
Malni 114 566 273 293 0 0 0 0
Makarwali 74 422 223 199 6 10 0 0
Asan Tiloriya 166 757 390 367 28 30 0 0
Fata Khera 158 792 419 373 12 20 0 1
Megarda 254 1231 656 575 279 248 0 0
Kaya Bheela 361 1840 943 897 10 7 0 1
Bar 1386 6777 3516 3261 704 643 10 7
Dholi Dhed 151 690 339 351 13 17 0 0
Bogasani Khurd 22 100 44 56 7 4 0 1
Beerbasni 0 0 0 0 0 0 0 0
Beesawas
Kalan 0 0 0 0 0 0 0 0
Beesawas
Khurd 0 0 0 0 0 0 0 0
Kheramamawa
s 227 1080 529 551 103 104 0 0
Khokhari 188 981 490 491 35 38 1 1
Giri 619 3011 1532 1479 536 516 0 0
Mesiya 343 1418 723 695 190 168 0 0
Chanwadiya 77 360 189 171 9 10 0 0
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Kalan
Nanana 460 2253 1144 1109 125 110 0 0
Shahpura 64 294 169 125 0 0 0 0
Chainpura 112 557 293 264 0 0 0 0
Jheentra 274 1432 738 694 0 0 1 0
Birantiya Khurd 792 3349 1613 1736 337 315 2 0
Kesarpura 214 1102 574 528 17 22 0 0
Jaitpura 233 1084 581 503 25 20 0 1
Jhala Ki Chauki 201 965 521 444 60 56 4 3
Sendara 550 2731 1396 1335 210 172 7 4
Kurantiya 58 264 146 118 0 0 0 0
Nimaj 3226 15071 7341 7730 1330 1309 4 6 Jaitran
Khera Ramgarh 153 630 292 338 64 60 0 0
Khera Deogarh 330 1444 712 732 158 149 0 0
Nimbera Khurd 164 819 407 412 167 164 1 1
Samokhi 207 868 414 454 70 72 32 40
Birampuri 120 559 270 289 85 70 0 0
Mohrai 402 1898 945 953 255 238 0 0
Dagla 154 665 305 360 43 50 0 0
TOTAL 14115 66012 32940 33072 6816 6509 71 86
Source-Census Records 2011
Sex Ratio
The ‘Sex Ratio’ is a numeric relationship between females and males of an area and
bears paramount importance in the present-day scenario where the un-ethnic pre-
determination of sex and killing of female foetus during pregnancy is practiced by
unscrupulous medical practitioners against the rule of the law of the country. It is evident
that by contrast the practice of female foeticide is not prevalent in the study area.
As per the census records 2011, the entire study area is falling mainly in Pali district of
Rajasthan state. The ‘Sex Ratio’ was observed as 987 females per 1000 males in the Pali
District. The same was recorded as 1004 females for every 1000 males in the study area.
The child sex ratio of the district was observed as 881 female children per 1000 male
children. The village wise male-female population distribution for the study area is
depicted and shown by graphical representation in Figure3.14.
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Figure 3.14 Male-Female Wise Population Distribution
Scheduled Caste &Scheduled Tribe Population: On the basis of the village wise SC &
ST population distribution of the study area during 2011, the ‘Scheduled Castes’
population was observed as 13325 persons consisting of 6816 males and 6509 females
respectively in the study area which accounts as 20.2% to the total population (66012
persons) of the study area. ‘Scheduled Tribes’ population was observed too meagre as
157 persons, accounting as 0.2% to the total population of the study area consisting of 71
males and 86 females. It implies that the rest 79.6% of the total population belongs to the
general category. Male-female wise distribution of SC & ST population in the study area is
graphically shown in Figure 3.15& 3.16.
Figure 3.15 : Scheduled Caste Population in Study Area
0
10000
20000
30000
40000
50000
60000
70000
Total Population Male Population Female Population
Total Population
0
2000
4000
6000
8000
10000
12000
14000
Total SC Population Male SC Population Female SC Population
Total SC Population
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Figure 3.16 Scheduled Tribes Population in Study Area
Literacy Rate
Literacy level is quantifiable indicator to assess the development status of an area or
region. Male-Female wise literates and ill-literate’s population is represented in Table
3.36. Total literate’s population was recorded as 34597 persons (52.4%) in the study
area. Table 3.36 reveals that Male-Female wise literates are observed as 21562 & 13035
persons respectively, implies that the ‘Literacy Rate’ is recorded as 52.4% with male-
female wise percentages being 32.7% &19.7% respectively. The total illiterate’s
population was recorded as 31415 persons (47.6%) in the study area. Male-Female wise
illiterates were 11378 (17.2%) and 20037 (30.6%) respectively. The Male-Female wise
graphical representation of literates &ill-literate’s population in study area villages/town is
shown in Figure 3.17.
Figure 3.17 : Male-Female Wise Distribution of Literates &Illiterates
0
50
100
150
200
Total ST Population Male ST Population Female ST Population
Total ST Population
0
5,000
10,000
15,000
20,000
25,000
30,000
35,000
TotalLiterates
MaleLiterates
FemaleLiterates
TotalIlliterates
MaleIlliterates
FemaleIlliterates
Literates and Illiterates Population
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Table 3.36 Male-female wise Literates & Illiterates
Name of Village
Total
Population
Literates Illiterates
Person Male Female Person Male Female
Birantiya Kalan 2445 1259 797 462 1186 432 754
Hajiwas 1217 592 336 256 625 231 394
Dhoolkot 1172 540 306 234 632 233 399
Lawamali 82 47 32 15 35 14 21
Rampura Kalan 1585 843 506 337 742 246 496
Aakeli 896 435 261 174 461 146 315
Leelamba 2605 1227 767 460 1378 506 872
Malni 566 256 156 100 310 117 193
Makarwali 422 255 163 92 167 60 107
Asan Tiloriya 757 355 233 122 402 157 245
Fata Khera 792 305 210 95 487 209 278
Megarda 1231 677 452 225 554 204 350
Kaya Bheela 1840 748 519 229 1092 424 668
Bar 6777 4265 2608 1657 2512 908 1604
Dholi Dhed 690 379 225 154 311 114 197
Bogasani Khurd 100 42 24 18 58 20 38
Beerbasni 0 0 0 0 0 0 0
Beesawas
Kalan 0 0 0 0 0 0 0
Beesawas
Khurd 0 0 0 0 0 0 0
Kheramamawas 1080 485 323 162 595 206 389
Khokhari 981 358 246 112 623 244 379
Giri 3011 1661 1075 586 1350 457 893
Mesiya 1418 629 405 224 789 318 471
Chanwadiya
Kalan 360 128 97 31 232 92 140
Nanana 2253 1066 730 336 1187 414 773
Shahpura 294 98 73 25 196 96 100
Chainpura 557 246 176 70 311 117 194
Jheentra 1432 487 359 128 945 379 566
Birantiya Khurd 3349 1624 969 655 1725 644 1081
Kesarpura 1102 589 398 191 513 176 337
Jaitpura 1084 596 394 202 488 187 301
Jhala Ki Chauki 965 477 317 160 488 204 284
Sendara 2731 1700 1056 644 1031 340 691
Kurantiya 264 170 106 64 94 40 54
Nimaj 15071 8798 5194 3604 6273 2147 4126
Khera Ramgarh 630 330 184 146 300 108 192
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Khera Deogarh 1444 708 452 256 736 260 476
Nimbera Khurd 819 395 255 140 424 152 272
Samokhi 868 405 245 160 463 169 294
Birampuri 559 260 169 91 299 101 198
Mohrai 1898 936 613 323 962 332 630
Dagla 665 226 131 95 439 174 265
TOTAL 66012 34597 21562 13035 31415 11378 20037
Source-Census Records 2011
3.12.2. Economic Structure
The majority of people in rural sector are cultivators & agricultural labors which indicates
dominant agricultural economy. A small section of people are engaged as workers in
household industries. But in urban sector the existing scenario is completely reversed as
most of the people there are engaged in non-agricultural activity especially in local
hotels/restaurants and as drivers some people also operates their vans/jeeps/cars as
tourist vehicle.
Annual income helps in identifying families below poverty line. During the field survey,
income of a household through all possible sources was recorded. Agriculture and allied
activities was reported to be the major source of income followed by non-farm wage labor,
business, Government and Private Service etc. The other important sources of income
include government pension and income from selling of fodder.
Economy of the District
Agriculture is an important sector of the Indian economy and vital for the food and
nutritional security of the nation. As per the district census handbook of Pali, the economy
of Pali district is mainly dependent on agriculture as 57.1% workers in the district are
either cultivators or agricultural labourers. However, the district percent of such workers is
lower than the state average of 62.1%.
The mineral wealth of the district is largely non-metallic. The chemical grade limestone,
Quartz, Feldspar and Calcite produced in the district is also known for their quality. Other
minerals are Asbestos, Soap stone, Magnetite, Gypsum, Marble and Barites. The district
has substantial resources of Quartz Feldspar, Asbestos. Lime Stone, Marble and Granite.
3.12.3. Workers Scenario
‘Occupational Pattern: Occupational pattern was studied to assess the skills of people in
the study area. Occupational pattern helps in identifying major economic activities of the
area. The main and marginal-workers population with further classification as casual,
agricultural, households and other workers is shown in Table 37. In the study area the
Main and Marginal Workers population was observed as 19105 (28.9%) and 9567
(14.5%) respectively of the total population (66012) while the remaining 37340 (56.6%)
persons were recorded as non-workers. Thus it implies that the semi-skilled and non-
skilled work-force required in study area for the project is available in aplenty.
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Occupation Pattern wise distribution of Population and Graphical representation of
‘Workers Scenario’ of the study area are shown as Table 3.37& Figure 3.18 respectively.
Table 3.37 Village wise Occupational Pattern in the Study Area
Name of
Village
MAIN
WORK_
P
MAIN_
CL_P
MAIN
_AL_
P
MAIN_
HH_P
MAIN_
OT_P
MARG
WORK_
P
MARG
_CL_P
MARG
_AL_P
MARG
_HH_P
MARG
_OT_P
Birantiya Kalan 304 132 19 3 150 629 18 286 7 318
Hajiwas 379 181 79 13 106 156 19 29 1 107
Dhoolkot 497 266 59 0 172 88 11 26 0 51
Lawamali 25 10 0 0 15 0 0 0 0 0
Rampura Kalan 342 223 40 2 77 348 52 266 3 27
Aakeli 184 55 9 8 112 242 18 208 2 14
Leelamba 1132 367 286 110 369 52 1 11 3 37
Malni 167 68 5 0 94 46 5 10 0 31
Makarwali 105 34 8 0 63 44 0 39 0 5
Asan Tiloriya 331 20 144 0 167 13 0 11 0 2
Fata Khera 371 175 3 0 193 0 0 0 0 0
Megarda 301 84 18 11 188 308 19 142 7 140
Kaya Bheela 340 72 49 0 219 596 287 210 0 99
Bar 1633 126 224 64 1219 917 59 574 31 253
Dholi Dhed 111 9 1 1 100 141 4 18 0 119
Bogasani
Khurd 8 1 2 1 4 22 1 14 0 7
Beerbasni 0 0 0 0 0 0 0 0 0 0
Beesawas
Kalan 0 0 0 0 0 0 0 0 0 0
Beesawas
Khurd 0 0 0 0 0 0 0 0 0 0
Kheramamawa
s 574 494 64 7 9 83 54 19 4 6
Khokhari 269 56 56 2 155 188 95 87 1 5
Giri 958 226 203 111 418 191 3 85 2 101
Mesiya 552 372 62 8 110 294 60 207 7 20
Chanwadiya
Kalan 164 148 13 0 3 27 26 0 0 1
Nanana 992 392 439 10 151 32 17 13 0 2
Shahpura 133 106 0 3 24 3 1 2 0 0
Chainpura 194 114 1 4 75 5 0 0 0 5
Jheentra 597 304 211 34 48 104 13 65 17 9
Birantiya Khurd 980 440 215 17 308 471 121 196 3 151
Kesarpura 267 224 7 0 36 224 101 117 0 6
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Jaitpura 261 122 85 0 54 264 200 30 1 33
Jhala Ki Chauki 218 46 78 4 90 281 19 12 5 245
Sendara 346 50 29 11 256 760 49 224 12 475
Kurantiya 55 32 0 0 23 51 26 24 0 1
Nimaj 4065 990 970 169 1936 2063 308 1314 162 279
Khera Ramgarh 221 114 32 19 56 117 9 30 21 57
Khera Deogarh 253 125 19 1 108 423 21 379 1 22
Nimbera Khurd 361 53 302 0 6 3 3 0 0 0
Samokhi 445 189 45 2 209 32 22 5 0 5
Birampuri 258 144 79 1 34 27 1 19 0 7
Mohrai 436 194 115 7 120 247 21 192 4 30
Dagla 276 222 19 7 28 75 35 17 21 2
TOTAL 19105 6980 3990 630 7505 9567 1699 4881 315 2672
Abbreviations:
MAIN WORKERS POPULATION: MAIN WORK_P: Main worker’s total population, MAIN_CL_P: Main
cultivated labour population, MAIN_AL_P: Main agricultural labour population, MAIN_HH_P: Main worker’s
population involved in household industries, MAIN_OT_P: Main other worker’s population
MARGINAL WORKERS POPULATION:
MARG WORK_P : Marginal workers total population, MARG_CL_P : Marginal cultivated labors total
population, MARG_AL_P : Marginal agricultural labors population, MARG_HH_P : Marginal workers involved in
household industries, MARG_OT_P : Marginal other workers Population
Source: Census of India Records, 2011
Distribution of work participation rate of the study area population is shown in Table 3.38.
Table 3.38 Distribution of Work Participation Rate
Occupation Class 2011
Main Workers 19105 (28.9 %)
Male 13037 (68.2 %)
Female 6068 (31.8 %)
Marginal Workers 9567 (14.5 %)
Male 3250 (34.0 %)
Female 6317 (66.0 %)
Non-Workers 37340 (56.6 %)
Male 16653 (44.6 %)
Female 20687 (55.4 %)
Total Population 66012
Source: Census of India Records, 2011
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Figure 3.18 : Workers Scenario
Composition of Main Workers: The ‘Main Workers’ were observed as 19105 persons
(28.9%) to the total population of the study area and its composition is made-up of Casual
laborers as 6980 (36.5%), Agricultural laborers as 3990 (20.9%), Household workers 630
(3.3%) and other workers as 7505 (39.3%) respectively. Composition of Main workers is
shown below as Figure 3.19.
Composition of Marginal Workers: The total marginal workers are observed as 9567
which constitute 14.5% of the total population (66012) comprises of Marginal Casual
Laborers as 1699 (17.8%), Marginal Agricultural Laborers as 4881 (51.0%), Marginal
Household laborers as 315 (3.3%) and marginal other workers were also observed as
2672 (27.9%) of the total marginal workers respectively. Details about marginal workers in
the study area are tabulated in Table 3.39. Composition of Marginal workers is shown as
follows in Figure 3.20.
Main Workers28.9%
Marginal Workers14.5%
Non-Workers56.6%
Workers Scenario
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Figure 3.19 : Composition of Main Workers Population
Figure 3.20 : Composition of Marginal Workers
Composition of Non-Workers: The total Non-worker’s population was observed as
37340 which constitute 56.6% to the total population (66012) of study area. Male-female
wise Non-worker’s population was recorded as 16653 Males (44.6%) and 20687 Females
(55.4%) respectively. Details about total Non-workers of the study area with Graphical
representation are compiled in Table 3.39and shown by Figure 3.21.
MAIN_CL_P36.5%
MAIN_AL_P20.9%
MAIN_HH_P3.3%
MAIN_OT_P39.3%
Composition of Main Workers Population
MARG_CL_P17.8%
MARG_AL_P51%MARG_HH_P
3.3%
MARG_OT_P27.9%
Composition of Marginal Workers Population
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Table 3.39 Composition of Non-Workers
Non-Workers Population
Persons Males Females
37340 16653 (44.6%) 20687 (55.4%)
Figure 3.21 Composition of Non-Workers
3.12.4. Basic Infrastructure Facilities Availability (as per the Census records of 2011)
A review of basic infrastructure facility and amenities available in the study area villages
has been done on the basis of the field survey and Census Records 2011. All the revenue
villages of study area are mainly under two (2) tehsils namely Raipur and Jaitaran of Pali
district, in Rajasthan. Three (3) villages named Beerbasni, Beesawas Kalan and
Beesawas Khurd, are uninhabited villages in the study area. The study area has
moderate level of basic infrastructure facilities like educational, medical, potable water,
power supply, and transport & communication network. Entire study area is predominantly
rural and no town is observed in the study area.
Education Facilities: As per the Census Records of India 2011, there are a total forty-
two (42) revenue villages of Pali district of Rajasthan. All the revenue villages are mainly
under two (2) tehsils namely Raipur and Jaitran of Pali district of Rajasthan. There are
about forty-four (44) Primary Schools existing in the revenue villages as rural part of the
study area. Middle schools are twenty-two (22 no’s) in the rural part of the study area.
Only twelve (12 no’s) Higher Secondary Schools are available in the rural part of the
study area. Senior Secondary School facility is available in five (05) revenue villages of
the study area as rural part. The educational facilities have been further strengthening
now and a number of private public schools and colleges are also functioning in the
surroundings of the study area. Besides, there are Engineering and Medical colleges
available in Towns and District headquarters only. Higher education facilities are available
in Towns of the area. There is considerable improvement in educational facility. The
0
5000
10000
15000
20000
25000
30000
35000
40000
Total Non-Workers Male Non-Workers Female Non-Workers
Non-Workers Population
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villages/towns of the study area have no such facilities can reach within5.0 to 10.0-km
range. Majority of the villages are little far from their nearest town.
Out of total forty-two (42) revenue villages/towns of the study area eight (08) revenue
villages including three (03) uninhabited villages namely Beerbasni, Beesawas Kalan and
Beesawas Khurd do not have primary school facility and children of these villages have to
travel less than 5.0-km for their primary schooling. Mamta Bal Vidya Mandir is located at a
distance of 4.97 Km from the site in South-Southwest. One government school is also
located at 1.42km in SW direction to the proposed site.
Medical Facilities: The medical facilities are provided by different agencies like Govt. &
Private individuals and voluntary organizations in the study area. As per the district
census handbook information of 2011, only one (01) village named Nimaj has community
health centre (CHC) and two (02) villages named Giri and Nimaj are with primary health
centre (PHC) exists in the study area; most of the study area villages depend upon the
towns / district HQ of the study area having such facility. Eighteen (18) Primary Health
Sub Centres (PHSC) are exists in the rural part of the study area. Mother & Child Welfare
Centre (MCWC) are available in Six (06) revenue villages of the study area. Family
welfare centre (FWC) exists only in three (03) villages namely Bar, Nimaj of the study
area. Hospital facility was not observed in any villages of the study area rest of the
villages are depending upon towns of the district for such type of medical facility. Medical
dispensary facility was available only in five (05) revenue villages. Overall study area
villages are served by average medical facilities. Specialized medical facilities are
available in towns and District Headquarter (HQ) only.
Potable Water Facilities: Potable water facility is available in most of the villages/towns
of the study area. The entire study area has plenty of good potable water facilities. Tap
water facility was observed in nineteen (19) revenue villages of the study area. Most of
the villages (about 81.0%) having Hand Pumps (HP) water as potable water facility. Out
of total forty-two (42) revenue villages only one (01) village named Birantiya Khurd of
Raipur Tehsil in Pali district is served with River/Canal water as drinking water in the
study area. As per the census records of 2011, about Twenty-two (22) villages (52.4%)
are being served with Tank/Pond/Lake facility in the study area. Good potable water
facilities are available in the study area. There are two major surface water bodies exists
in the study area named Sukari River (dry river) at a distance of 2.68-km in NE direction
and another one is Lirli river at a distance of 5.29-km in NW direction to the proposed
project site.
Communication, Road, Transport and Banking Facilities: The district is well
connected by the North Western Railway. The Delhi-Ahmedabad broad-gauge railway
line passes from Sendra railway station to Nana via Sojat Road, Marwar Junction,
Phalana and Mori Bera. A part of this district is also served by the north western railway
from Marwar Junction to Phulad. There are thirty-one (31) railway stations in the district.
Another railway line also passes through the district from Marwar Junction to Rohat. All-
important places of the district are connected with bus routes.
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At the year 2010-11, the district has 374 post offices and 2 telegraph offices, beside, the
services of 146 telephone exchanges and 2648 STD/PCO were also available.
Apart from Post &Telegraph (P & T) services, transport is the main communication
linkage in the study area. Out of forty-two (42) villages of the study area, only three (03)
villages named Bar, Nimaj and Mohrai are served with Post Office facilities in the study
area, remaining villages are depending upon this villages and towns of the study area.
The study area has good road network, passes from the area. The site is well connected
to NH-65 A (Degana - Raipur), and NH-14 (Beawar-Sirohi-Radhanpur) at an aerial
distance of ~1.16 km in SW and ~4.85 km in South direction of the site respectively.
Out of the total forty-two (42) revenue villages of the study area there are only two (02)
villages named Birantiya Kalan, Bar respectively, which are served with railway station
facility in the study area and rest of the villages are depending upon this village and towns
with this facility. Railway station for public transportation is Bar & Pali railway station
located at an aerial distance of ~ 6.44 km in ESE direction and 86.0-km in WSW direction
respectively from the project site.
Nearest airport from the project site is Dabok Airport (UDR) in Udaipur located at an aerial
distance of ~ 167 km in SSW direction. Jodhpur Airport is around 125 km away from the
project site. No major town is observed in the study area of 10km radius.
About eleven (11) villages (26.2%) are served with Pucca road facility in the study area.
The study area has almost all the schedule commercial banks with ATM facility in urban
areas and the district HQ.
Power Supply: It is revealed from the compiled information on amenities availability as
per the census records of 2011; twenty-three (23) villages (about 54.8%) are electrified for
all purpose in the study area. About 38 villages (90.5%) of the study area are electrified
for Agriculture purpose. About 23 villages (54.8%) were also electrified for commercial
purpose in the study area. Village wise information on basic infrastructure and amenities’
availability for the entire study area is compiled and presented in Table 3.40.
Historical place of Archeological Importance: There is no historical place of archeological
importance is present within 300 m of the proposed site.
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Table 3.40 Village wise Basic Amenities Availability in the Study Area
Village Name Educational Medical Drinking Water Communication &
Transport
Approach to
the Village
Co.
Bank
Power Supply
P M SS SS
S
C
H
C
P
H
C
P
H
S
C
M
C
W
C
D F
W
C
T W H
P
T
W
S R T
k
O P
O
P
&
T
T
e
l
e
.
M
o
b.
B
S
R
S
PR KR FP E
D
E
A
g.
E
C
E
A
Birantiya Kalan 2 1 1 0 0 0 1 0 0 0 1 1 1 2 2 2 1 2 2 2 1 1 2 1 1 1 1 2 1 1 1 1
Dhoolkot 1 1 0 0 0 0 1 0 0 0 2 1 1 1 2 2 2 1 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Hajiwas 1 1 1 0 0 0 1 0 0 0 1 2 1 1 2 2 1 2 2 2 1 1 2 2 1 1 1 2 1 1 1 1
Lawamali 0 0 0 0 0 0 0 0 0 0 2 2 2 2 2 2 2 1 2 2 2 1 2 2 2 1 1 2 1 1 2 2
Rampura Kalan 1 1 1 0 0 0 1 0 0 0 1 1 1 1 2 2 1 1 2 2 1 1 2 2 1 1 1 2 1 1 2 2
Aakeli 1 0 0 0 0 0 0 0 0 0 1 1 2 2 2 2 1 1 2 2 1 1 2 2 2 1 1 2 1 1 2 2
Leelamba 2 1 1 0 0 0 1 1 1 0 1 1 1 1 2 2 1 1 2 2 1 1 2 2 1 1 1 1 1 1 1 1
Malni 1 0 0 0 0 0 1 0 0 0 2 2 1 2 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Makarwali 0 0 0 0 0 0 0 0 0 0 2 2 2 1 2 2 1 1 2 2 2 1 2 2 2 1 1 2 1 1 2 2
Asan Tiloriya 1 0 0 0 0 0 0 0 0 0 2 2 1 1 2 2 1 1 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Fata Khera 1 0 0 0 0 0 0 0 0 0 2 2 1 1 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 2 2
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Megarda 1 1 0 0 0 0 1 0 0 0 1 2 1 1 2 2 1 2 2 2 1 1 2 2 2 1 1 2 1 1 2 2
Kaya Bheela 1 1 0 0 0 0 0 0 0 0 1 1 1 1 2 2 2 1 2 2 1 1 2 2 2 1 1 2 1 2 2 2
Bar 2 1 1 1 0 0 1 1 1 1 1 1 1 1 2 2 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1
Dholi Dhed 1 0 0 0 0 0 0 0 0 0 2 1 1 2 2 2 1 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Bogasani Khurd 0 0 0 0 0 0 0 0 0 0 2 2 2 2 2 2 2 2 2 2 2 1 2 2 2 1 1 2 1 1 2 2
Beerbasni Un-Inhabited Village
Beesawas Kalan Un-Inhabited Village
Beesawas Khurd Un-Inhabited Village
Kheramamawas 1 1 0 0 0 0 0 0 0 0 2 1 1 2 2 2 1 1 2 2 1 1 2 2 2 1 1 2 1 1 2 2
Khokhari 1 0 0 0 0 0 0 0 0 0 2 2 1 2 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 2 2
Giri 1 1 1 1 0 1 0 1 0 0 1 1 1 1 2 2 1 1 2 2 1 1 1 2 1 1 1 1 1 1 2 2
Mesiya 1 1 0 0 0 0 0 0 0 0 1 1 1 2 2 2 1 2 2 2 1 1 1 2 2 1 1 2 1 1 1 1
Chanwadiya
Kalan 0 0 0 0 0 0 0 0 0 0 2 2 2 2 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Nanana 2 1 1 0 0 0 1 0 0 0 1 2 1 2 2 2 2 1 2 2 1 1 1 2 1 1 1 2 1 1 2 2
Shahpura 0 0 0 0 0 0 0 0 0 0 2 2 1 1 2 2 2 2 2 2 2 1 2 2 2 1 1 2 1 1 2 2
Chainpura 1 0 0 0 0 0 0 0 0 0 2 2 1 2 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
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Jheentra 1 1 0 0 0 0 1 0 0 0 2 2 1 2 2 2 1 2 2 2 2 1 2 2 2 1 1 2 1 1 2 2
Birantiya Khurd 3 1 1 0 0 0 1 1 1 0 1 1 1 1 2 1 1 1 2 2 1 1 1 2 1 1 1 1 1 1 2 2
Kesarpura 1 1 0 0 0 0 0 0 0 0 2 2 1 1 2 2 1 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Jaitpura 1 1 0 0 0 0 0 0 0 0 1 2 1 2 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Jhala Ki Chauki 1 0 0 0 0 0 1 0 0 0 2 2 1 1 1 2 2 2 2 2 1 1 1 2 2 1 1 2 1 1 1 1
Sendara 2 2 1 1 0 0 1 1 1 1 1 1 1 1 2 2 1 1 2 2 1 1 1 1 1 1 1 1 1 1 1 1
Kurantiya 0 0 0 0 0 0 0 0 0 0 2 2 1 2 2 2 1 2 2 2 1 1 2 2 2 1 1 2 1 1 2 2
Nimaj 5 2 2 2 1 1 0 1 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1
Khera Ramgarh 1 0 0 0 0 0 1 0 0 0 1 2 1 2 2 2 1 1 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Khera Deogarh 1 1 0 0 0 0 1 0 0 0 1 2 1 2 2 2 2 1 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Nimbera Khurd 1 0 0 0 0 0 0 0 0 0 2 2 1 2 2 2 2 2 2 2 1 1 1 2 2 1 1 2 1 1 1 1
Samokhi 1 0 0 0 0 0 1 0 0 0 2 2 1 1 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Birampuri 1 0 0 0 0 0 0 0 0 0 1 2 1 2 2 2 2 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
Mohrai 1 1 1 0 0 0 1 0 0 0 1 1 1 1 1 2 1 1 1 1 1 1 2 2 1 1 1 2 1 1 1 1
Dagla 1 0 0 0 0 0 1 0 0 0 2 2 1 2 2 2 1 2 2 2 1 1 2 2 2 1 1 2 1 1 1 1
TOTAL
4
4
2
2
1
2
0
5
0
1
0
2
1
8
0
6
0
5
0
3 Status for Availability and Non-Availability is shown as A (1) & NA (2) respectively
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Abbreviations
Educational Facilities: P-Primary School, M-Middle School, SS-Higher Secondary Schools, SSS-Senior Secondary School
Medical Facilities: CHC-Community Health Centre, PHC-Primary Health Centre, PHSC-Primary Health Sub-Centre, MCWC-Maternity and Child Welfare
Centre, H-Hospital, D-Dispensary, FWC-Family Welfare Centre
Drinking Water Facilities: T-Tap Water, W-Well Water, HP-Hand Pump, TW-Tube Well Water, R-River Water, Tk-Tank Water, O-Other Drinking Water
Facility
Communication and transport Facilities: PO- Post Office,SPO-Sub-Post Office, PTO- Post & Telegraph Office, Tel. - Telephone Connection, Mob.-
Mobile Phone Coverage, BS- Bus Services, RS- Railways Services
Approach to Village: PR- Paved Roads, KR- Kuchha Road, FP- Foot Path
Power Supply: ED- Power Supply for Domestic use, E Ag.- Power Supply for Agricultural use, EC- Power supply for Commercial use, EA- Electricity for
All Purposes
Source-http://www.censusindia.gov.in/2011census/dchb/DCHB.html
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CHAPTER 4. IMPACTS ASSESSMENT AND PREDICTION
4.1. General
Impacting activities are defined as elements of organization's activities that can interact
with the environment. These include activities during normal and abnormal actions of
Residential, commercial and education units. Environmental impacts are defined as any
change in environment, whether adverse or beneficial, wholly or partially, resulting from
impacting activities. The environmental indices (or parts of the receiving environment on
which impacts are being predicted) are ambient air, water, noise, land, flora and fauna,
infrastructure, and socio-economic environment. Thus, we predict the environmental
impacts of the impacting activities on the environmental indices. In this chapter we
covered the cummulative impact considering approved TOR and applied amendemnt of
TOR.
The possible impact on various components of environment due to the proposed INTECH
project can be assessed in terms of:
Beneficial or detrimental
Naturally reversible or irreversible
Repairable via management practices or irreparable
Short term or long term
Temporary or continuous
Occurring during construction phase or operational phase
Local, regional, national or global
Accidental or planned (recognized beforehand)
Direct (primary) or Indirect (secondary)
Cumulative or single
Significant
And on:
Physical
Biological Environment and
Demographic and Socio-economic Environment.
For proper assessment of significance and magnitude of environmental changes due to
construction and operational phases of the plant, the impacts are analyzed on the 10 km
radius study area around the proposed plant site for each environmental parameter.
Impact assessment study for the existing INTECH unit is carried out by predicting net
contribution of pollutants (qualitative as well as quantitative) on overall qualitative
This chapter details the inferences drawn from the Environmental Impact Assessment of the
proposed project. It describes the overall impacts of the project activities and underscores the
areas of concern, which need mitigation measures.
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assessment of various environmental indicators. Prediction of impacts is an important
component in environmental impact assessment process. Several techniques and
methodologies are in vogue for predicting the impacts due to existing and proposed
industrial development on physico-ecological and socio-economic components of
environment. Such predictions delineate contribution in existing baseline data for the
operational project and superimpose over the baseline (pre-project) status of
environmental quality to derive the ultimate (post-project) scenario of the environmental
conditions due to the proposed project. The quantitative prediction of impacts leads to
delineation of suitable environmental management plan needed for implementation during
the construction, commissioning and operational phases of the proposed project in order
to mitigate the adverse impacts on environmental quality.
4.2. Construction Phase
The activities of proposed expansion program will be confined to the project site within the
boundary of Plant complex. The present project activities will not cause any significant
loss of any important flora.
Emission /Gaseous pollution
Due to different vehicular movement, construction machineries and project construction
activities (Bulk solids handling), the concentration of air pollutants can be increased.
These pollutants can affect the surrounding vegetation and nearby agricultural crops.
There will be limited construction activities at INTECH.
Dust / Fumes (from machineries) Generation
Terrestrial flora can be affected by the dusty/ fumes environment to be created due to
vehicular movement/ machineries during construction phase. Increment in the density of
the dust particles (SPM)/ fumes having SOx/NOx/HC in the atmosphere can affect the
surrounding plant/ vegetation in following ways:
a) Blockage and damage to stomata
b) Reduction in chlorophyll content
c) Abrasion of leaf surface or cuticle
All these disturbances ultimately affect photosynthesis process and plant metabolism that
leads to reduction in plant growth up to some extent.
Noise Pollution
Noise level of the project area will be increased during construction phase. Although there
is no specific noise-sensitive fauna has been recorded near to project site but limited
avifauna and small animals in the industrial area can be affected by increased noise level.
In such cases they can change their habitat.
Congregation of Labour
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Construction activities often require a considerable workforce and associated support
services. The livelihood activities of this increased human population may contribute to
local environmental impacts in terms of collecting firewood and food as well as enhancing
recreational activities.
The impacts during construction phase normally are:
Detrimental
Naturally reversible
Short term
Temporary
Local
Direct
Mitigation Measures:
Gaseous pollution
The pollutants (SPM, SOX,NOX, HC and others) in ambient air of the study area are low.
Development of multi-layer plantation (green belt) around the proposed project area will
further help to mitigate gaseous pollution within and around the project area.
Dust Generation
Dust generation during construction period will be managed through:
Water spraying on rough roads, on powdery construction materials etc.
Land / Soil
As this is an expansion project, there will be construction activities to be carried out.
There will also be installation of new machineries and equipment. But all this would not
make a huge damage to the present condition of land. Further the area of the plant is flat.
Much leveling would not be required. Thus, topography will also remain unchanged after
execution of the proposal.
Thus, the impact on the land/soil during the construction will for short terms and
insignificant.
Effluent discharge
There will be a negligible discharge of effluent from the proposed plant due to
construction activities, which will be directly sent to Soak pit through septic tank. Safe
guard for rainy season runoff will be taken to prevent any direct discharge from the plant
to nearby water body. As such the water ecology will not be affected, the domestic
effluent will be discharged through septic tank into soak pit.
Congregation of Labour
The impacts will be managed through:
No permanent camping in vegetation rich area and riverside
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A provision of fuel for labourers engaged in construction activities
Restriction on poaching/hunting and removal of any vegetation
Based on the field observations and interaction with local people and forest officials, it
was noticed that the project area is not associated with any National Park/Wildlife
Sanctuary/Conservation Reserve and there are no wildlife migratory routes present in the
project area. Improvement in the green cover under a regular plantation program
(Greenbelt Development Program) will not only increase the plant diversity in the area but
also enhance the habitat for wildlife especially for avifauna.
4.3. Operation Phase
4.3.1. Air Environment
The pre-project (baseline) ambient air quality status in the study area indicates that all the
general as well as specific to project pollutants are well within the prescribed National
Ambient Air Quality Standards (NAAQS) for industrial, residential, rural and other areas.
The principal impacts on air environment shall be due to operation of flue gas stacks and
process stacks – Briquettes /LDO shall be used as fuel in the boilers & DG sets. To
minimize the impacts due to emission from boilers, cyclone separators & bag filter shall
be provided as air pollution control equipment. The process vents shall be attached to
efficient adequate water scrubbers followed by alkali / acid scrubbers to remove pollutant
from process emission.
To assess the impact of air emissions from various continuous point sources, air
dispersion modelling study has been conducted with the help of ISCST3 (USEPA
dispersion model). Detailed description has been given in the following sub-sections:
4.3.2. Model Details
Air dispersion modelling can be used to predict atmospheric concentrations of pollutants
at specific locations (receptors) over specific averaging times (i.e. annual, daily, and
hourly). An atmospheric dispersion model accounts for the emissions from a source;
estimates how high into the atmosphere they will go, how widely they will spread and how
far they will travel based on temporal meteorological data; and outputs the pattern of
concentrations that will occur for various exposure periods, thereby providing the
exposure risks for different receptors.
In the proposed project, prediction of impacts on air environment has been carried out
employing mathematical model based on a Steady State Gaussian Plume Dispersion
Model designed for multiple points sources for short term. In the present case, Industrial
Source Complex Short-term [ ISCST3] dispersion model based on steady state Gaussian
Plume Dispersion, designed for multiple points sources for short term and developed by
United States Environmental Protection Agency (USEPA) has been used for simulations
from point sources.
The predictions for air quality during operation phase were carried out for particulate
matter (PM) SOx, NOx, Hydrogen Bromide (HBr) and P2O5 using ISCST3.
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A uniform polar grid was used for the computation and extended to 10 km from the centre
of the proposed project. In addition to that, receptors were also placed at the sampling
locations
4.3.3. Predicted GLC due to INTECH Expansion Project
The main sources of air pollution due to the operation of the plant are the Boiler, Process
vent and other stacks. The contribution to GLCs for the pollutants i.e. particulate matter,
SOx, NOx, HBr and P2O5 were predicted over the study area proposed project
considering the worst scenario. The emission load from proposed project is given in Table
below. The prediction (maximum) is based on the expected total emission rate from each
stack and are given in isopleths Figure 4.1 (A, B, C and D) for proposed project. The
additional contribution to GLC is also given below in Table 4.1.
Table 4.1 Stack Parameters and Emission Details from Proposed Expansion Project
(Process)
SN Stack Attached
Stack Height in Meter;(From Ground)
Stack Dia (m)
Flow in Nm3/hr; /Temp in 0C
Pollutants Concentration in mg/Nm3
Remarks
1 Boilers (3Nos each of 4 T capacity ; Briquette/ LDO fired)
30 (Three Stacks)
0.07 (At Top)
7800/ 115 SPM<150 SO2<50 NOx < 150
(Separate stacks for each boiler of 4TPH)
2 Process Stack Alkaline Scrubbers
10 0.3 ~940/37 PM < 20
HBr< 05
All alkaline scrubbers are attached in single stack.
3 Process Stack Water Scrubbers
30 0.3 ~940/65 PM < 20
P2O5 (as H3PO4) < 10
All Acidic scrubbers are attached in single stack.
Table 4.2 Emission Load Proposed Expansion Project (Process)
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Sr. No Stack attached to/
Pollutant
Pollutant Load
Kg/hr
PM SOx NOx
HBr P2O5 (as H3PO4)
1. Boiler -1 1.17 0.39 1.17 --- ---
2. Boiler 2 1.17 0.39 1.17 --- ---
3. Boiler 3 1.17 0.39 1.17 --- ---
4. Alkali Scrubber
0.188 --- --- 0.047 ---
5. Water Scrubber 0.188 --- --- --- 0.094
4.3.4. Meteorological Data
The meteorological data consists of wind speed, direction, temperature, humidity, solar
radiation, cloud cover and rainfall recorded during the months of 1st May, 2017 through
31st May 2017, on an hourly basis. Wind speed, wind direction and temperature have
been processed to extract the 24–hour mean meteorological data for application in
ISCST3.
4.3.5. Receptor Locations
A total of about 186 receptors – 180 receptors of which were generated with a polar grid
from the centre of the proposed project and extended to 10 km. Apart from these
receptors, the sampling locations were also taken into account to assess the incremental
load on the baseline environmental scenario.
4.3.6. Summary of Predicted GLC’s
The summary of maximum ground level concentrations (GLC) for the proposed project is
listed in Table 4.2.
Table 4.3 Summary of Maximum 24-hour Incremental GLC due to the Proposed
Expansion Project Stacks
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Parameters Maximum incremental GLC(µg/m³) Distance (Km) Direction
PM 5.58 1.9 NE
SO2 1.30 1.9 NE
NOx 3.89 1.9 NE
P2O5 0.259 1.9 NE
HBr 8.6E-0.2 1.9 NE (Source: Modelling output results)
Maximum 24 hourly average incremental in GLCs of particulate matter, SOx, NOx, HBr
and P2O5 due to expansion project during operation phase are predicted and given in
Table 4.2. The isopleths of the pollutant concentration due to the impacts associated with
the operation of the proposed project are shown in Figures 4.1 through 4.5 for, Particulate
matter, SOx, NOx, HBr and P2O5 respectively. Contours of the incremental GLCs depict
that the travel of emissions from the proposed project would be mainly in NE direction.
Besides the worst GLC (maximum) predictions the GLC incremental at the sensitive
receptors (where the ambient air monitoring was carried out) was also predicted. The
predicted incremental GLC for pollutants are given in underneath Table 4.3.
Table 4.4 : Summary of Maximum GLC at Monitoring Locations due to the Proposed
ProjectAmbient Air Quality Monitoring Results (24-hour average)
Location Wind Direction PM(µg/m3)
Existing baseline Mean
Incremental Glcs
Net Incremental Glcs
Project site Flat terrain.
77 0.50 77.50
Dhoolkot downwind
direction for
summer season
65 5.0 70.00
Birantiya Khurd downwind
direction for
summer
63 00 63
Birantiya Kalan upwind direction
for summer
68 1.00 69
Lakshmangarh downwind
direction for
post monson
69 1.0 70
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season
Road junction of Birantiya Kalan and Purthigarh
upwind direction
for summer
season
65 1.0 66
Road junction of Birantiya Kalan and Dhoolkot
upwind direction
for summer
season
62 1.0 63
Hajiwas crosswind
direction for
summer
51 1.0 52
Table 3.12 continued……
Location Wind Directio
n
SO2 (µg/m3) NOx(µg/m3)
Existing
baseline Mean
Incremental Glcs
Net Incrementa
l Glcs
Existing baseline
Mean
Incremental Glcs
Net Incrementa
l Glcs
Project site
Flat
terrain.
6.5 00 6.5 13.9 00 13.9
Dhoolkot downwin
d
direction
for
summer
season
6.4 1.00 7.4 12.2 3.00 15.20
Birantiya Khurd
downwin
d
direction
for
summer
5.9 00 5.8 12.5 00 12.50
Birantiya Kalan
upwind
direction
5.8 00 5.3 13.0 00 13.00
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for
summer
Lakshmangarh
downwin
d
direction
for post
monson
season
5.3 00 7.3 10.5 1.00 11.50
Road junction of Birantiya Kalan and Purthigarh
upwind
direction
for
summer
season
7.3 00 6.5 11.0 1.00 12.00
Road junction of Birantiya Kalan and Dhoolkot
upwind
direction
for
summer
season
6.5 00 5.8 10.8 1.00 11.80
Hajiwas crosswin
d
direction
for
summer
5.8 00 5.9 10.3 1.00 11.30
Location Wind Direction HBr(µg/m3)
Existing
baseline Mean Incremental
Glcs Net Incremental
Glcs
Project site Flat terrain.
<0.1 8.6E-.02 8.6E-.02
Dhoolkot downwind direction for
summer season
<0.1 8.0E-.02 8.0E-.02
Birantiya Khurd downwind direction for
summer
<0.1 1.0E-.02 1.0E-.02
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Birantiya Kalan upwind direction for
summer
<0.1 1.0E-.02 1.0E-.02
Lakshmangarh downwind direction for
post monsoon season
<0.1 1.0E-.02 1.0E-.02
Road junction of Birantiya Kalan and Purthigarh
upwind direction for
summer season
<0.1 1.0E-.02 1.0E-.02
Road junction of Birantiya Kalan and Dhoolkot
upwind direction for
summer season
<0.1 1.0E-.02 1.0E-.02
Hajiwas crosswind direction for
summer
<0.1 1.0E-.02 1.0E-.02
(Source: Modelling output results with base line)
4.3.7. Discussion of the Cumulative Impacts at monitoring locations:
The nearest settlement in downwind direction is Dhoolkot (1.9 km NE). As per baseline
data of AAQ maximum GLC for PM at Dhoolkot is 65µg/m³ with this proposed expansion
project, 5.00 µg/m³ rise in GLCs so PM level will be 70 µg/m³. The Particulate Matter in
the study area is contributed mainly by commercial activities and traffic movement
(vehicular emissions), re-suspended dust from paved and unpaved roads and open
uncovered areas as well as from industrial activities.
Maximum baseline GLC for SO2 (Process) at downwind direction Dhoolkot (1.9 km NE)
was as 6.4 µg/m³ are observed. With the expansion project SOx level may increase by
1.0 µg/m³ so post project level of SOx is 7.4 µg/m³. Maximum baseline GLC for NOx in
downwind direction atDhoolkot (1.9 km NE) as 12.2 µg/m³. With the expansion project
NOx concentration is 3 µg/m³ so rise in GLC of NOx concentration is 15.20 µg/m³. It can
be concluded that with the expansion of project all the AAQ parameters will remain within
the NAAQ norms.
As is evident from the table and discussion above, there will be no adverse impacts on
the surrounding area (all pollutants post project GLC will be well within NAAQ norms
except PM which is already high due to natural and other commercial and traffic causes).
Highly efficient air pollution control systems have been adopted to mitigate particulate
matter as well as gaseous emissions in the ambient environment.
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(A) Isopleth for PM incremental GLC due to Proposed Expansion Project
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(B) Isopleth for SOx incremental GLC due to Proposed Expansion Project
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(C) Isopleth for NOx incremental GLC due to Proposed Expansion Project
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(D) Isopleth for P2O5 incremental GLC due to Proposed Expansion Project
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(D) Isopleth for HBr incremental GLC due to Proposed Expansion Project
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Mitigation Measures:
The ambient air quality with respect to air pollutants will change during the operation
phase of the proposed project. However, adequate stack height has been provided for
better dispersion of flue gas as per the guidelines of CPCB. In addition, all process
stacks have been provided with high efficiency scrubbing system to control the emission
within norms. In addition to that, adequate greenbelt will be developed for further control
of air pollution.
Compliance with the existing ambient air quality standards will be achieved by process
system selection as outlined above, proper system operation and implementation of the
measures as outlined in EMP. This needs to be coupled with the continuous monitoring
of air pollutants within and around the project site as well as in adjoining areas.
Environmental impacts (AAQ) resulting from proposed project can be grouped into
following
Categories:
Beneficial or detrimental--detrimental
Naturally reversible or irreversible---Reversible
Repairable via management practices or irreparable—Repairable to some extent
through Green Belt development
Short term or long term Short term
Temporary or continuous-- Continuous
Occurring during construction phase or operational phase—Operation Phase
Local, regional, national or global--Local
Accidental or planned (recognized beforehand) --Planned
Direct (primary) or Indirect (secondary)-- Direct
Cumulative or single-- Single
4.4. Noise Environment
The sources of noise during the operational phase of the plant are mainly from Boilers,
air compressors, blowers, pumps, vacuum pumps, ejectors and furnaces and other
process equipment. The other sources of noise are the movement of vehicles along the
road. Moving machineries will be selected with caution as regard to low noise generation
as well as low energy consumption.
4.4.1. Impacts due to Transportation
Noise level contributed from increased movement of light medium and heavy vehicles on
the roads both within and outside the plant can be considerable depending upon the
traffic density. The heavy commercial vehicles traffic is limited depending upon the
material receipt and dispatch of products through road transport. The major quantity of
pesticides will be dispatched through roads.
4.4.2. Impact of noise on community
Equivalent sound levels are often used to describe community exposures to noise. Noise
survey was also carried out at eight locations outside the plant area but within the study
area. Ambient noise level of the study area is within the prescribed National Ambient
Noise Quality Standard for respective residential, commercial and industrial category at
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all the monitored locations which is well within the day and night time standard
(commercial).
The operation of proposed expansion project will have the noise level not much
exceeding the present noise level and as such will not have any adverse impact on the
human settlement around it. The noise will not be audible beyond its boundary limit,
particularly due to natural green belt and other attenuators.
Mitigation Measures:
Noise from the plant is to be limited through:
a. High noise machineries (DG sets etc.) should have acoustic enclosures.
b. Proper / regular maintenance of machineries.
Regular noise monitoring in work area. Any abnormal noise level to be investigated and
noise source attended.
Green belt development to arrest noise from going outside the plant.
Environmental impacts (Noise) resulting from proposed project can be grouped into
following
Categories:
Beneficial or detrimental--detrimental
Naturally reversible or irreversible---Reversible
Repairable via management practices or irreparable—Repairable to some extent
through Green Belt development
Short term or long term Short term
Temporary or continuous-- Continuous
Occurring during construction phase or operational phase—Operation Phase
Local, regional, national or global--Local
Accidental or planned (recognized beforehand) -- Planned
Direct (primary) or Indirect (secondary)-- Direct
Cumulative or single-- Single
4.5. Water Environment
Impact on water environment due to INTECH proposed project scheme will be in terms
of additional water consumption {water demand} and waste water generation after
treatment will be recycled and reused.
4.5.1. Water Demand
Since the INTECH proposed project will have water requirement both during construction
period as well as during operation. The requirement during construction period will be
much less. as compared to that during operation and will be met from Surface water and
ground water or both.
Water during operational phase is normally required for:
Process and washing
Cooling Water
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Boiler Feed Water
Domestic and Green Belt
Total water requirement after expansion will be around limited (221.46 KLD). The total
fresh water requirement after the proposed expansion project will be 102.14 KLD and
119.32 KLD water will recycled and used. The water balance for the proposed project is
given in the Figure 2.4.
The domestic wastewater generated from the toilets, washrooms and canteen of the
plant shall be sent to STP (Sewage Treatment Plant). No wastewater will be discharged
outside the plant premises during non-monsoon and under normal operating conditions,
unit followed the zero discharge concepts.
4.5.2. Effluent Generation and Discharge
Wastewater will be segregated into two streams as High TDS / High COD (HTDS) and
Low TDS / Low COD (LTDS). The HTDS Effluent stream generated from process. HTDS
effluent will be collected in equalization tank and thereafter sent to neutralization, Settling
and solvent stripper will be sent to Multi Effect Evaporator (MEE). The distillate water will
be treated in ETP along with LTDS effluent. The concentrate will be sent to ATFD for
drying. The dried salt will be sent to approved TSDF for final disposal. The ETP treated
effluent will be passed through RO for recovery of water for recycling. The RO reject will
be send to MEE. No process effluent will be discharged outside the plant premises.
There is provision of stripper for recovery of solvent (VOC) from HTDS effluent before
MEE. The inorganic hazardous residues will be sent to TSDF.
The other source of wastewater generation will be domestic Sewage of 16 KL/day; which
will be treated in STP. Treated water from STP will be used for greenbelt development,
Thus, there will not be any major impact on the water environment due to proposed
activities.
Hazardous wastes will be stored, managed and handles as per hazardous wastes rules.
All bulk chemicals and fuel storage areas will be provided with dyke wall / bunds to
eliminate chances of any spillages/ leakages entering into the storm water drain.
No significant adverse impact on the surface and ground water or soil quality is
envisaged in view of the proposed mitigate measures.
Mitigation Measures:
Water consumption to be controlled though eliminating / reducing any water wastage –
leakages/ spillage.
a. Process control
Regular monitoring of effluent sources to ETP will show process conditions and deviation
from optimum water consumption.
ETP – performance for maximum recycle of treated water.
Environmental impacts (Water) resulting from proposed project can be grouped into
following
Categories:
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Beneficial or detrimental--detrimental
Naturally reversible or irreversible---Reversible
Repairable via management practices or irreparable—Repairable to some extent
Short term or long term Short term
Temporary or continuous--continuous
Occurring during construction phase or operational phase—Operation Phase
Local, regional, national or global--Local
Accidental or planned (recognized beforehand) -- Planned
Direct (primary) or Indirect (secondary)—Direct
Cumulative or single--cumulative
4.6. Land/Soil Environment
Essentially, the two major impacts normally faced in impact on land environment due to
any development project are:
Diversion of land from designated use to the Project Use.
Deterioration of land / soil in terms of soil fertility and toxicity.
4.6.1. Land Diversion
Proposed expansion for manufacturing of technical grade pesticide is adjacent to existing
plant and is being converted for industrial use. Existing plant land is already for industrial
use.
4.6.2. Land Deterioration
The hazardous waste is generated at various stages of the manufacturing activity. The
mode of disposal is mentioned for each category of waste as per hazardous wastes
(management, handling and trans -boundary movement) rules, 2016.
Hazardous wastes will be stored at earmarked area with impervious flooring, shed and
spillage/ leakage collection system to eliminate rainwater contamination, chances of
overflow / spillages going on to the land and thus land/ soil contamination.
SOLID WASTE: The total steam requirement will be met from boiler. briquettes/LDO will
be used as fuel in proposed boilers. Ash generated from use of Briquette (~ 0.98 MT/day
;( ~ 30 MT / month) will be disposed off to Brick/Cement manufacturers/ or for road
development and to comply the Fly ash management rules.
4.6.3. SOLID/HAZARDOUS WASTE
Hazardous/solid waste generation will be the main source of impact on the soil
environment. Entire quantity of hazardous waste will be handled and disposed as per
Hazardous Waste (Management, Handling and Trans boundary movement) Rules 2016,
Most of the hazardous waste will be collected, stored and sent /will be disposed off as
per the hazardous waste management rules.
4.7. Biological Environment
Though the concentrations of the emitted pollutants will be kept within permissible levels
through the various engineering controls, it is essential to have eco-management in the
Likely Impact Zone for safeguard and enhanced of ecological environment of the project
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area. The likely impacts and mitigation measures associated with different phases due to
various project activities area describes in following Table.
Project Aspect
Description
Likely Impacts on
Ecology and
Biodiversity (EB)
Impact Consequence -
Probability Description
/ Justification
Mitigation measures Type
Pre-Construction Stage Impacts
Removal of site
vegetation like herbs,
shrubs and grasses
site specific loss of common floral diversity
Site specific loss of associated faunal diversity
Site specific loss of habitat / habitat diversity
No major vegetation is present on site.
Site possesses common floral species; This will be site specific impact.
.
Subject to periodic
monitoring
/surveillance. However,
greenbelt / plantation
will be developed in
project site and in
periphery of the project
boundary, which will
improve floral diversity
of the area.
Short term
Construction Stage Impacts
Dust and Noise
Generation due to
movement
of JCBs, other
machinery, and other
construction activities
Site specific
disturbance to faunal
species
Dust settlement on
vegetation
No endangered fauna
reported from the site as
well as in study area.
The species reported
from project site and
buffer zone are common
/ generalist species and
not very sensitive to the
routine activities, so
there will be no threat of
facing disturbance.
However, its site specific
and temporary impact.
Subject to periodic
monitoring and
surveillance.
Water sprinkling for
Dust suppression.
Construction activities
shall be restricted in
night time.
Short term
Operation Stage Impact
Emission of PM, NOx,
Sox, HBr, P2O5 due to
operation (Indirect
impact on crops, trees
and shrubs of vicinity
due to contamination
Impact on surrounding
vegetation and
associated biodiversity.
Though the emission
levels of all pollutants
will be kept within
permissible limits. APCD
shall be used to control
dust emissions from
Operation subject to
management by
operational controls.
Emission levels of all
pollutants will be kept
within permissible
Long term
(insignificant
)
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of ambient air, dust
emission, vehicular
exhaust)
various sections of plant.
The incremental air
pollution will not violate
the air quality standards.
Proposed plant is zero
liquid discharge basis so
no waste water will be
discharged.
Greenery development
will be done in and
around the plant site.
Such measures will be
adequate to protect the
noise and air pollution
impacts.
levels through various
engineering control
measures. However,
green belt development
with suitable species
will help to mitigate
likely cumulative
impacts.
Noise Generation
(Disturbance to
sensitive terrestrial
fauna due to
noise pollution)
Construction Stage Impacts
Excavation and filling up operation may result in fugitive dust emission. The dust
deposition on pubescent leaves of the surrounding vegetation may leads to temporary
reduction of photosynthesis. Such impacts would however be confined mostly to the
initial period of the construction phase and would minimized through paving of roads,
surface treatment, regular water sprinkling in dust generating areas and greenbelt
development. The impact on the ecology of the surrounding area during the construction
stage will be insignificant in nature. Greenbelt development along the plant boundary,
development of gardens and lawns will mitigate the residual impact on natural resources.
Operation stage Impacts
No national park, wildlife sanctuary, biosphere reserve exists within 10 km area of the
project. No endangered or rare or threatened plant or animal species was observed
within 10 km area of the project site (Except Peafowl). However, one small patches of
forest are present within the study area which is located more than 5 km away from the
site. The impact on the surrounding ecology during the operation of the project will
mainly occur from the deposition of air pollutants. Air pollution affects the biotic and
abiotic components of the ecosystem individually and synergistically with other
pollutants. Chronic and acute effects on plants and animals may be induced when the
concentration of air pollutants exceeds threshold limits. Particulate emission and other
gaseous emissions from the proposed plant are the major pollutant that may affect the
ecology of the area. The incremental emission of air pollutants is not likely to induce any
significant changes in the ecology because the national ambient air quality standards will
remain within the limits. The incremental MGLC of PM, Sox, NOx, HBr, P2O5generated
from the proposed plant will be very less and overall incremental GLC will remains within
the NAAQS. Therefore, impact of PM, NOx, HBr, P2O5 emission on the surrounding
vegetation will be insignificant.
CREP Guidelines: I NTECH has good corporate company committed to abide by CREP
guide lines for pesticide industry as give below:
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The guidelines enunciated by CPCB are very helpful to mitigate environment pollution,
improve human health and benefit of cost savings by cutting cost of valuable solvent by
efficient recovery system. We (INTECH) will adopt all the guidelines as stated here
under.
Table 4.5 CREP Guidelines Compliance
Sr. No CREP Point INTECH Compliance
1
Segregation waste streams: Waste streams
should be segregated into COD waste, toxic
waste, low COD waste, inorganic waste etc, for
the purpose of providing appropriate treatment.
Waste streams will be segregated and treated in well-designed ETP
2
Detoxification and treatment of high COD
waste streams: Streams should be detoxified and
treated in CTP or thermally destroyed in
incinerator, as per CPCB guidelines. The waste
streams should be treated suitably before taking to
evaporation ponds.
INTECH will have three stage ETP followed by RO system. All the treated effluents will be recycled in the process.
3
Improvement in solvent recovery:
– Solvent recovery should be improved and
attempts should be made to achieve at least 90%
recovery wherever possible.
– Rest of the solvents which cannot be recovered
shall be incinerated.
INTECH will follow norms
4
Hazardous air pollutant control:
– For air pollution control from processes,
scrubber efficiency will be improved and
maintained as per the best practicable technology
for control of CI2, Bromine and VOCs. – An
incinerator will be installed, where necessary.
An incinerator will be installed, where
necessary
High efficiency scrubber and stacks for reducing the Air pollution will be provided. Stack emissions will be kept well within the prescribed limits.
Not applicable
5
Control of fugitive emissions/ VOCs: For control
of fugitive emissions (particularly for hazardous air
pollutions). The industries will adopt standard
engineering practices. System of leak detection
and repair (LDAR) program especially for solvents
Condenser with brine chilling shall be provided to the vent to minimize vapour losses. LDAR system will be followed to prevent any liquid/vapour leakages.
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4.8. Socio – Economic Environment
INTECH proposed project will generate employment opportunities some through direct
employment and more so indirectly through services for the plant. Pesticides
manufactured by INTECH proposed plant are indirectly going to contribute food grain
availability by preventing loss due to insects (to crop) and rodents (during storage) etc.
INTECH project will have some impacts also on socio – economic environment of the
study area- some are as given below:
Proposed project will result in handling of product and raw material, which will increase
manpower requirement at various stages directly, or indirectly resulting in more income
of people.
INTECH project would increase requirement from ancillary and auxiliary industries in
the vicinity.
should be developed industries.
6
Upgrade of incinerators: Incinerators will be
upgraded to meet CPCB norms hazardous waste
incinerators. This is necessary for Halogenated
compound and POPs.
Not Applicable.
7
Replacement of Bio Assay test by toxicity
Factor: The present bio-assay test will be
replaced by Toxicity Factor test method developed
by CPCB. Toxicity factor of four (TF-4) will be
achieved and industries will improve their system
to achieve TF-
2. TF test method will be implemented by
PCBs/CPCB/ MoEF. The CPCB will organize
workshops on “Toxicity Factor” for industry.
INTECH will abide by the
rules.
8
Minimum scale of production to afford cost of
pollution load: To be decided, as industries view
point is that this cannot be done as few products
are costly and made in small volume. The matter
will be studied in detail by MoEF/ CPCB.
INTECH will abide by norms.
9
Non-complying Units (as identified by SPCB)
should meet the notified standards
Not Applicable
10
Bank guarantee to be submitted to SPCB by
Non-complying units: The submissions from
pesticides industry regarding speedy clearance
and other will be considered by MoEF/CPCB for
examination.
Not Applicable
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With more load on infrastructure facilities – roads and rails; these facilities would need
improvement.
More income to Government through more taxes on higher amount of production.
4.9. INFRASTRUCTURE
The proposed plant is located about 1.16 km away from the National Highway NH-112.
The plant site is well connected through a major district road to NH-112. All inward and
outgoing materials movement from the plant shall be done through this road. To assess
the traffic volume on NH 112 near plant site a traffic study was conducted (given in
Chapter 3.). At present the total PCU as per traffic study is 1996. With the proposed
expansion project additional load will be around 15 trucks /day (20 tonner) outgoing for
products/by products and around 10 to15 trucks is coming per day. Based on IRC
guidelines and code of practice it has been ascertained that the NH 112 road stretches is
well within the design service value of 15000 PCU/day, as prescribed by the Indian Road
Congress.
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CHAPTER 5. ENVIRONMENTAL MANAGEMENT PLAN
This chapter describes the administrative aspects for ensuring that mitigation measures
are implemented and their effectiveness monitored, after approval of the EIA.
Environmental Management Plan provides a logical framework within which identified
environmental impacts are managed. Technical methods to be used to mitigate (prevent,
control and reduce) negative impacts and working practices are described in Chapter 5.
In this chapter we covered the environmental management plan considering impact
assessment of approved TOR and applied amendemnt of TOR.
5.1. Environment Management Plan (Construction and Operation Phase)
The management of INTECH is quite conscious of its responsibility for maintaining clean
and a healthy environment. The management is also keen to modify and make more
efficient measures towards suppression of pollution sources. Lot of adequate funds for
pollution control measures are provided as a part of overall project financing to ensure
the availability of proper treatment facilities before the commissioning of the unit. The
proposed Environment Management Plan for the proposed expansion is summarized in
the below Table 51.
Table 5.1 Environment Management Plan
Environment
Elements
Stages and Source Impact Area Management Plan
Air
Environment
Construction Phase:
Construction activity is limited
may cause by emission of
dust such as the movements
of vehicles, speed, soil
stripping, excavation, back
filling and reinstatement
Within Plant boundary Water sprinkling in
construction area;
Asphalting the main
approach road;
Proper maintenance
of vehicles and
construction
equipment; and
Tree plantation in the
area earmarked for
greenbelt
development
Operational Phase:
Handling and storage of raw
material
Within Plant boundary
Adequate water sprinkling
system
Conveying of the raw material Transfer points Dust
extraction/suppression
This Chapter provides mitigation and control measures to attenuate and/or eliminate
environmental impacts, which are likely to be caused by the proposed project. An
Environmental Management Plan (EMP) has been developed to mitigate the potential
impacts and to strengthen the beneficial impacts during the construction and operation
phase.
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system shall be provided.
Truck Movements Within Plant boundary Truck mounted vacuum
cleaning system.
Asphalting the road within
the plant area.
Process emission
Boiler& DG Stack within study area Adequate stack height for wider dispersion
Green belt development around the plant to arrest the fugitive emission.
Design of control equipment to meet the standard stipulated by CREP.
Process stack Within study area Adequate stack height for wider dispersion
Green belt development around the plant to arrest the fugitive emission.
Design of control equipment to meet the standard stipulated by CREP.
Noise
Environment
During Construction Phase:
Movement of heavy
equipment’s
Within Project Boundary
Good maintenance of
vehicles and
construction
equipment;
Restriction of
construction activities
to day time only to
extent possible;
Plantation of
trees around the
plant boundary to
attenuate the noise;
and
Provision of earplugs
and earmuffs to
workers.
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During Operation Phase:
Increase in ambient Noise
level from equipment’s,
pump, DG sets and
compressors. However
incremental level is
insignificant due to provision
of acoustic enclosures for
noise generation sources.
Within Plant Boundary Equipment will be
designed to confirm to
noise level prescribed by
regulatory authority.
Provision of rubber
padding/ noise isolators.
Provision of silencers to
modulate the noise
generated by machines
Provision of protective
devices like ear muff/plugs
to the employee &workers.
Greenbelt development in
and around the plant
periphery
Water
Environment
During Construction Phase:
Water will be needed mainly
for construction and domestic
purpose i.e. for drinking and
sanitation
Within Project Boundary
Domestic waste water will
be disposed off through
septic tank or soak pits.
During Operation Phase:
Generation of high TDS and
High COD effluent. Zero
Discharge
Within Plant Boundary
Proposed ETP to achieve
ZLD (Zero Liquid
Discharge to extent
possible. And reuse the
treated effluent in the
process.
Domestic waste water will
be treated in proposed
STP. Treated STP water
will be used for green belt
development.
Land
Environment
During Construction Phase:
Soil Excavation
Within project boundary Top soil generated from
various activities like
excavation etc. will be
stored and preserved to
use in greenbelt
development.
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During Operation Phase:
Solid waste disposal and
Hazardous waste generation
storage.
Within plant boundary Hazardous waste shall be
disposed off as per HWM
rules 2016.
Periodic monitoring shall
be carried out.
Zero liquid discharge will
be maintained.
In order to effectively manage the environmental management (including social
management) of the project, following management plans are required.
1. Creation of Environmental Management Department
2. Institutionalized Management Structure
3. Green Belt Development
4. CSR Management
5. Budget for Environmental Management Plan
5.2. Fly ash Management plan
Utilization of ash produced by Boiler as a thrust area of its activities and all possible
actions will be taken to enhance level of ash utilization. In the proposed boilers, various
avenues for ash utilization will be explored as delineated in the above sections. In
particular, supply of quality ash for manufacture of cement will be taken as there are
some cement units. Some of the actions planned for the project are as given in below
Table 5.2 : Ash utilization plan
Item description 1st Year 2nd Year 3rd Year 4th Year
Total Production of Ash
(Maximum)TPA
314 314 314 314
Fly Ash use in brick
manufacture
20 30 40 50
Fly Ash use in Cement
plant
80 120 155 204
Ash used on road
development in
surrounding Area
15 20 25 30
Ash use in mine fill 10 15 20 30
Total Consumption 125 185 240 314
Utilization (%) 40% 58% 76% 100%
Note: The figures derived at about the ash utilization in the area are only rough estimates and may be
considered as a guideline only.
• INTECH will make efforts to motivate and encourage entrepreneurs to set up units for
manufacture of ash based products such as fly ash bricks, lightweight aggregates,
cellular concrete products etc as ancillary industries in the region. INTECH would be
providing all possible infrastructure facilities to these entrepreneurs in accordance with
its policy;
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• INTECH would request State Government to make mandatory to utilize ash/ash based
products in Works Department and other Government/State sponsored projects to
enhance ash utilization;
• INTECH would also continue to encourage utilization of available ash based products in
all its construction activities;
• INTECH will encourage the use for Backfilling of abandoned coal mines will depend on
the allocation of abandoned mines by Government
The ash will be utilized in various construction materials to the maximum extent and
100% utilization will be achieved. All efforts will be made for maximum utilization of ash.
INTECH is committed to explore possibilities for ash utilization considering new
technologies and avenues and try to achieve the target fixed by MoEF in this regard.
INTECH is committed to comply with the Fly Ash Utilization Notification, 1999 and as
amended thereof.
5.3. Rain Water Harvesting Plan
INTECH realizes the importance of rainwater harvesting however it will be prudent that
rain water harvesting is not taken up in INTECH plant area. This is because if some
hazardous dust (in spite of all possible precautions) gets mixed with rainwater and enter
the ground water and the ground water will get contaminated. If required INTECH may
do rain water harvesting at alternate place with due approval from authorities.
5.4. Environment Management Cell (EMC)
First of all, EMC shall be modified in the expansion unit. The organizational structure of
Environment Management Cell (EMC) responsible for routine environmental
management and monitoring measures, implementing the EMP and complying with the
conditions stipulated by SPCB and MOEF is shown in Figure 5.1.
The Head of EMC shall directly report to the top management of the Plant. The Head of
Safety and Health shall also directly report to the top management of the Plant. In case
the HOD notes any non-compliance or violation of environmental, safety or health law/
regulations, the same shall be brought to the notice of the Production in Charge (during
the weekly review meeting). In case the non-compliance or violation is of manageable
nature, Production in Charge will issue instruction and sanction budget and resources to
rectify the same. Otherwise Production in Charge will obtain financial approval from the
Board of Directors (Top Management) and then address the problem. In any case all
matters of non-compliance and violations shall be brought to the notice of the Top
Management / Board of Directors, action taken report shall be submitted on regular
basis, till the problem is rectified.
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Figure 5.1 Structure of Environmental Management Department
Functions of EMC: Head of the EMC shall form a Consultative Working Group by
involving responsible citizens from the surrounding community and develop action plans
to address any grievances of the public related to environmental performance of the
project and develop targets for addressing the grievances. The Cell shall thoroughly
study each activities and suggest additional mitigation measures (if required) for
improvement of environmental performance and discuss them in monthly meetings with
the departmental HOD for implementation. The EMC shall co-ordinate all related
activities such as safety, worker’s health, and health of surrounding community and
prepare statistical records.
Regular monitoring of fugitive emissions and report any abnormalities for immediate corrective measures.
Regular monitoring of ambient air quality within the plant and around the plant.
Regular monitoring of wastewater quality, water quality of the storage ponds, ground water quality and surface water quality.
Regular noise monitoring of the work zone and surrounding area.
Green belt plantation, maintenance, development of other forms of greenery like lawns, nursery, gardens, etc. in the plant premises.
Regular monitoring of the used oil and sell it out to the authorized recycler approved by the Central Pollution Control Board / SPCB.
In addition to above the environment management Cell shall conduct environmental audit
every year.
5.5. Institutional Arrangement
INTECH shall ensure following action items to be complied with throughout the life cycle
of the project:
FACTORY MANAGER
MANAGER (EHS)
Asst. Manager
(Housekeeping, Horticulture and
landscaping)
Asst. Manager
(Health)
Asst. Manager
(Safety)
Lab Assistants
(Environ. Sampling and Monitoring work)
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Formulate Environmental Health & Safety Policy
Document the organization structure, roles and responsibilities for implementation and for functioning of Environmental Management System (EMS) and Safety Management System (SMS) Procedures.
Develop standard operating process and procedures to bring into focus any infringement / deviation / violation of the environment or forest norms/conditions.
Carry out regular inspections, monitoring and auditing;
Carry out periodical review and issuing amendments;
Reporting and communication (including internal and external reporting);
Documentation and record keeping;
An effective system of management is a key technique for ensuring that all pollution
prevention and control techniques, monitoring plan & mitigation measures are delivered
reliably and on an integrated basis. INTECH shall operate a formal Environmental
Management System for the proposed project. INTECH shall document the Standard
Operating Procedures to bring in any deviation / violation of the environmental norms as
prescribed. The SOP shall address the system of reporting of non-compliances /
violations of environmental norms to the Board of Directors of the Company including all
shareholders and stakeholders. The salient features of Environmental Management
System (EMS) are listed below:
Effective operational and maintenance systems shall be employed on all aspects of
the process whose failure could impact on the environment:
Documented procedures to control operations that may have an adverse impact on
the environment
Define procedure for identifying, reviewing and prioritizing items of plant for which a
preventative maintenance regime is appropriate
Documented procedure for monitoring impacts
Preventative maintenance program, whose failure could lead to impact on the
environment
The maintenance system includes auditing of performance against requirements
arising from the above and reporting the result of audits to top management.
The skills and competencies necessary for key posts shall be documented and
records of training needs and training received for these post maintained.
The potential environmental risks posed by the work of contractors shall be assessed
and instructions provided to contractors about protecting the environment while
working on site.
Written procedures for handling, investigating, communicating and reporting actual or
potential non-compliance with operating procedures.
Written procedures for handling, investigating, communicating and reporting
environmental complaints and implementation of appropriate actions.
Written procedures for investigating incidents, (and near misses) including identifying
suitable corrective action and following up
The company shall conduct audits, annually, to check that all activities are carried out
in conformity with the above requirements.
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The company shall report and publish annual report on environmental performance,
objectives and targets, and future planned improvements.
The company shall have demonstrable procedures (eg. written instructions) which
incorporate environmental considerations into the following areas:
o The control of process and engineering change on the installation;
o Design, construction and review of new facilities and other capital projects
o Capital approval; and
o Purchasing policy
The company shall have a clear and logical system for keeping records of policies, roles
and responsibilities, targets, procedures
Training Requirement of Staff: Training systems, covering the following items, shall be
in place for all staff of EC and other staff of various departments, which cover the
following:
Awareness of the regulatory implications of the Environmental Permits for the activity
and their work activities;
Awareness of all potential environmental effects from operation under normal and
abnormal circumstances.
Awareness of the need to report deviation from the Permit.
Prevention of accidental emissions and action to be taken when accidental emissions
occur.
The staff of the EMC will be trained every year by arranging in house training programs
by inviting experts or faculty members from reputed institutes.
Periodical Review: INTECH will annually review the EMP and identified management
action plans to address any changes in the organization, process or regulatory
requirements.
Documentation and Record Keeping: The EMC will maintain following documents for
effective implementation of the EMP:
Master management system document;
Legal Register;
Operation control procedures;
Work instructions;
Incident reports;
Emergency preparedness and response procedures;
Training records;
Monitoring reports;
Auditing reports; and
Complaints register and issues attended/closed.
5.6. Resource Conservation/ Waste Minimization
Additional key measures taken for natural resource and energy conservation are as
given below: -
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• Used oil will be stored in covered storages / hard flooring to preventanycontamination
in soil/ ground water.
• Proper scheduling of preventive maintenance of critical machines will minimize used
oil generation.
• Energy efficient drives / LED lights to be used.
• Reduction of lighting power consumption by optimum use of electrical lights in plants.
• Use of variable frequency drive in plant.
• Enough care will be taken to prevent/minimize energy losses at each stage.
• Zero liquid discharge will be maintained for reduction in fresh water consumption.
Also use of Energy Efficient Lighting, Transformers, HVAC system, Use of Energy
Efficient Motors, electrical appliances to minimize the energy consumption in addition to
Process Planning.
5.7. Facilities for Employees
Company will give preference to local people (Skilled People) for employment. The
Company is more concern for the safety and health of its people, including the larger
community outside of the company and the environment as a whole. All employees will
be trained to work on sites in the safest possible manner and shall be made aware of the
consequences of unsafe act. Company will also provide the shelter, safe drinking
water, sanitation facility. The company will allocate adequate budget for safety and
Occupational health management of the employees.
5.8. Environment Policy
An effective system of management is a key technique for ensuring that all pollution
prevention and control techniques, monitoring plan and mitigation measures are
delivered reliably and on an integrated basis. INTECH has a well laid down Corporate
Occupational Health, Safety and Environment Policy approved by its Board of Directors.
Objectives of Environmental Policy
“To be a role model in protection of environment for sustainable development, INTECH is
committed to implement best global practices in its operations through prevention /
mitigation of pollution, proper disposal / reclamation of wastes and bringing awareness
among all the stakeholders for continuous improvement in environmental performance”
To take account of environment concerns in planning and decision making.
Compliance of conditions imposed in Environmental Clearance and all other statutory
clearances issued by the Regulatory Authorities.
To prevent pollution of surrounding habitation by monitoring & measurement of
environmental parameters.
Identification of significant impacts and preparation of environment management
system for implementation.
To reduce waste generation and promote recycling of materials, wherever possible.
Optimum utilization of resources i.e. Electricity, Oil and Water.
To take up development works in surrounding villages as a part of corporate social
responsibility.
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To provide appropriate training and disseminate information to enable all employees to
implement best practices and work in partnership to create a culture of continuous
improvement.
The company shall document the Standard Operating Procedures to bring in any
deviation / violation of the environment norms as prescribed.
Figure 5.2 : Corporate Occupational Health, Safety and Environmental Policy
5.9. EMP for Biological Environment Quality
Ecological base line surveys in the core and buffer zones, reveals no exceptional
features of wildlife interest. The survey based on following criteria.
Table 5.3 Table: Ecological criteria & Observations
Land use The site proposed for the expansion is already under process of possession of INTECH. No tree cutting is required. No major vegetation is present within the core zone hence no wildlife Zone exists within the core zone. At present only shrub species like Calotropisprocera, Argemonemaxicana, Acacia species and Prosopisjuliflora are present.
No sensitive ecosystem is present within 10 km area of the project site. However, one small Forest patches is present but located more than 5 km away from the project site.
Diversity Species diversity of flora as well as fauna species is restricted to agro ecosystem.
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Rarity There is no endemic, rare or threatened species in site as well as in study area. There is no endangered or schedule-I faunal species in the study area except Peafowl (Pavo Cristatus) which is schedule –I species but is of least concern category
Proximity There are no Biosphere Reserve, National Park, Wildlife Sanctuary, present within 10 km area of the site
Potential value After developing a wide and dense greenbelt in plant area will increase habitat condition especially for avifauna.
Based on the ecological baseline study following mitigation measures have been
suggested:
Regeneration / restoration of rare plants and animals: No rare plants and wildlife
species exists in the core and buffer zone, there are no endangered or Schedule-I faunal
species in the study area except Peafowl (Pavo Cristatus) which is schedule –I species
but is of least concern category. Though a conservation plan for Pavo cristatus has been
prepared by Enkay Enviro and approved by DFO Pali.
Improvement of biodiversity: Environment management cell of the project proponent
will look after the day to day environment monitoring requirement and Greenbelt
development in and around the project site.
Green Belt development plan
In order to mitigate and minimize the environmental impacts, arising due to project
especially from air pollution, noise pollution, soil erosion etc. the Greenbelt development
in the area delineated can provide the best mitigation option. The green canopy not only
absorbs some of these pollutants as carbon sink but also improves the aesthetic
environment, besides attenuating the noise levels.
INTECH will develop 5-10 m wide greenbelt (as space available) all around the plant
premises. As per CPCB/MoEF& CC guidelines 33% of the total land area (35364 m2)
shall be kept as greenbelt.
Development of Greenbelt
The strategy worked out for development of green belt consists of following:
The species selected should be capable of growing fast,
The species should be wind firm and long lived.
Broad leaf trees growing above 10 m in height should be planted along the
roads, offices and infrastructure facilities.
The species should form a dense crown cover.
The species should form a litter in abundance on the plantation floor.
Generally local/indigenous fast growing trees/ shrubs should be planted.
For protection against biotic interference thorn fencing around the plantation,
circular trench around the planting pit and sown with fast growing thorny shrubs
on the ridge should be followed.
Guidelines and Techniques for Green Belt Development
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Based on environmental conditions suitable indigenous plants species shall be planted
under green belt development plan. The requirement of plants sapling for development of
green belt shall be made from the nearby forest nursery. The soil characteristics shall
also be kept in mind. As advance work the area to be planted shall be demarcated and
pit locations marked. Pits shall be dug out and semi-filled with good and loose weathered
soil before planting with the commencement of good monsoon rains sometime in month
of July. The digging operation of the pit should be completed before the end of June so
as to allow thoroughly weathering of the dugout soil. Prior to the commencement of the
rains, pits shall be refilled with the dugout soil and FYM added. Planting shall be done
when heavy showers causing run-off occurs sometime between July and August. The
saplings should be 9 to 12 months old. Immediately after planting the pits shall be
watered with 20 liters / pit and in case of failure of rainfall it should be watered @ 20
liters / pit at fortnight interval. The mortality of plants has been considered @ 20% and
re-digging of pit should be carried out before replacement of the individual plant.
Precautions During Plantation
Some important precautions should be taken during the plantation, which are as under:
Indigenous species recommended should be planted in sufficient numbers to increase their population size in the area.
Multipurpose species should be planted in large numbers.
Selection of species for plantation: The species selected under this plantation will be
moderately high, good foliage bearing and are able to trap dust and noise. The following
species along with hedge plant have been proposed for plantation under green belt.
(Table 5.3.
Table 5.4 Species suggested for plantation under Greenbelt Development Programmed
Scientific Name Family Habit/ Height
Evergreen (E)/ Deciduous (D)
Crown Shape
Azadirachtaindica Mileaceae Tree, 20m E Spreading
Bauhinia racemosa Caesalpinaceae Tree, 5m D Oblong
Bougainvillea spectabillis
Nyctagianceae Shrub, 8 m E Oblong
Emblicaofficinalis Euphorbaeceae Tree, 12m D Oblong
Murayapaniculata Rutaceae Shrub, 3m E Round
Neriumindicum Apocyanaceae Shrub, 3m E Round
Thevetiaperuviana Apocynacea Shrub. 5m E Round
Bougainvilliea Nyctaginaceae Shrub, 10m E Spreading
Syzygiumcumini Myrtaceae Tree, 20m E Oblong
Tamarindusindica Caesapinaceae Tree 20 m E Round
Dalbergiasisoo Fabacea Tree, 15 m D Spreading
AlbiziaLebback Mimosaceae Tree, 20 m D Oblong
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Meliaazidarch Mileaceae Tree, 15 m D Spreading
Delonixregia Fabaceae Tree, 20 m D Spreading
Pongamiapinnata Fabacea Tree, 15 m E Round
Budget for Greenbelt:
INTECH will be developed a dense greenbelt in about 3.5 ha (33%) of the area within the
plant. About 1150 trees/ha shall be planted. On an average about 4000 trees shall be
planted within the premises as a greenbelt. The capital cost for Greenbelt development
(5 Year budget) of the project is estimated to be Rs 55.46 Lakh. The yearly greenbelt
budget for the proposed plant is discussed in following.
Table 5.5 Greenbelt Budget for 5 Year
Total area available for Greenbelt 3.5 ha (35365 m2)
No of trees to be planted 4000
Cost per plant
Total cost for 1st Year
Plantation
2nd Year recurring
cost (assuming
80% survival of
plant )
2nd Year onward
recurring cost
Purchase cost of the per sapling Rs. 20 0.8 Lach 0.16 lakh Nil
Tree planting cost Rs. 50 2.0 Lach 0.40 lach Nil
Watering cost (per year) Rs. 150 6.0 Lach 6.0 Lach 6.0 Lach
Maintenance cost (per year) Rs. 60 2.4 Lach 2.4 Lach 2.4 Lach
Manure/pesticides (per year) Rs. 50 2.0 Lach 2.0 lach 2.0 lach
Misc. cost (lump sum) for lawn and other form of greenery (per year) --
0.50 Lach -
Total expenses - 12.8 Lach 11.46 Lach 10.4 lach
Total Budget for 5 year =55.46 (12.8+11.46+10.4+10.4+10.4Lach)
Note – Schedule for plantation is tentative, it depends on the construction activities.
Table 5.6 Proposed Environmental Monitoring Program
Discipline Location Parameter Frequency Remarks
Micro - Meteorology One Temp.{max.; min.};
Relative humidity;
Rain fall; Wind speed
and direction.
Daily
Ambient Air Quality Five HCl, Cl2, SOx; NOx, Once in a Parameters as
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CO, HBr, HC
Particulate matter
(with pesticide
compounds)
month applicable /as per
products being
manufactured
Boiler Stacks One PM, SOx; NOx, CO Once in a
month
Scrubber Stack All continuous
stacks
HBr, SOx; NOx;P2O5
(as H3PO4)
Particulate matter
(with pesticide
compounds; As per
stack design)
Once in a
month
Parameters as
applicable /as per
products being
manufactured
Effluents Final Treated
effluents
As per process /
plant requirement
Once in a
month
Parameters as
applicable /as per
products being
manufactured
Sewage Sanitary TSS; BOD Once in a
month
Ground Water
Quality (One
peizometric wells)
One peizometric
wells
Pesticides- etc. [in
association with
SPCB]
Pre-monsoon &
Post-monsoon
Parameters as
applicable /as per
products being
manufactured
Soil Plant premises As per CPCB norms Once in year
Noise Plant area
&periphery
Day & Night time
noise level
Quarterly
Health Check Up All Plant Personnel Diseases related to
pesticides
Annually
5.10. Budget for EMP
The overall investment in the project is 2700 lacs About Rs. 382.0 Lac is proposed for
the environment protection program. Details are as given below:
Table 5.7 : EMP Budget
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Capital cost and recurring cost/annum for environmental pollution control measures
S. No. Description of Item Capital Cost Recurring Cost
(In Lacs) (In Lacs)
1 Air Pollution Control/ Noise 80 7.5
2 Water Pollution Control 200 18
3 Control of Fire and explosion Hazard,
safety measures 37 3.9
4 Environmental Monitoring and
Management 10 1.5
5 Green Belt Development 55 10
Total 382.00 35.50
5.11. Conclusion
Environmental Management plan will be dynamic, flexible and subject to periodic review.
For project where the major environmental impacts are associated, EMP will require
regular review. Senior management responsible for a project should conduct a review of
EMP and its implementation to ensure that the EMP remains effective and appropriate.
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CHAPTER 6. RISK ASSESSMENT& DISASTER MANAGEMENT PLAN
6.1. Introduction
Industrial plants deal with materials, which are generally hazardous in nature by virtue of
their intrinsic chemical properties or their operating temperatures or pressures or a
combination of these. Fire, explosion, toxic release or combinations of these are the
hazards associated with industrial plants using hazardous chemicals. More
comprehensive, systematic and sophisticated methods of Safety Engineering, such as,
Hazard Analysis and Quantitative Risk Assessment have now been developed to
improve upon the integrity, reliability and safety of industrial plants. In this chapter risk
assessment and disaster management is mentioned the cummulative (approved ToR
and applied amendemnt of ToR).
The primary emphasis in safety engineering is to reduce risk to human life, property and
environment. Some of the more important methods used to achieve this are:
Quantitative Risk Analysis: Provides a relative measure of the likelihood and
severity of various possible hazardous events by critically examining the plant
process and design.
Work Safety Analysis: The technique discerns whether the plant layout and
operating procedures in practice have any inherent infirmities.
Safety Audit: Takes a careful look at plant operating conditions, work practices
and work environments to detect unsafe conditions.
Together, these three broad tools attempt to minimize the chances of accidents
occurring. Yet, there always exists, no matter how remote, probability of occurrence of a
major accident. If the accident involves highly hazardous chemicals in sufficiently large
quantities, the consequences may be serious to the plant, to surrounding areas and the
populations residing therein.
6.2. Risk Assessment
A three ‘levels’ risk assessment approach has been adopted for the Intech Pharma Pvt
Ltd (henceforth INTECH) for proposed expansion project considering both condition i.e.
approved TOR and applied for amended TOR. The risk assessment levels are generally
consistent with the practices encountered through various assignments for medium and
large chemical complexes. The brief outline of the three-tier approach is given below:
Level 1 – Risk Screening
This is top-down review of worst- case potential hazards/risks, aimed primarily at
identifying plant sites or areas within plant, which pose the highest risk. Various
screening factors considered include:
This Chapter provides the details about the Risk Assessment, Disaster Management
Plan (DMP) and on-site emergency plan as proposed for the proposed project.
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Inventory of hazardous materials;
Hazardous Materials properties;
Storage conditions (e.g. temperature and pressure);
Location sensitivity (distance to residential areas / populace).
The data / information are obtained from plant. The results provide a relative indication of
the extent of hazards and potential for risk exposure.
Level 2 – Major Risk Survey (Semi - Quantitative)
The survey approach combines the site inspection with established risk assessment
techniques applied both qualitative as well quantitative mode. The primary objective is to
identify and select major risks at a specific location in the plant considering possible soft
spots / weak links during operation / maintenance. Aspects covered in the risk usually
include:
Process Hazards;
Process Safety Management Systems;
Fire Protection and Emergency response equipment and programs.
Security Vulnerability;
Impact of hazards consequences (equipment damage, business interruption,
injury, fatalities);
Qualitative risk identification of scenarios involving hazardous materials;
Risk reduction measures.
Selection of critical scenarios and their potential of damage provide means of prioritizing
mitigate measures and allocate the resources to the areas with highest risks.
Level 3 – Quantitative Risk Assessment (Deterministic)
This is the stage of assessment of risks associated with all credible hazards (scenarios)
with potential to cause an undesirable outcome such as human injury, fatality or
destruction of property. The four basic elements include:
i. Hazards identification utilizing formal approach (Level 2, HAZOP etc.);
ii. Frequency Analysis. Based on past safety data (incidents / accidents);
Identifying likely pathway of failures and quantifying the toxic / inflammable
material release;
iii. Hazards analysis to quantify the consequences of various hazards
scenarios (fire, explosion, BLEVE, toxic vapour release etc.). Establish
minimum value for damage (e.g. IDLH, over pressure, radiation flux) to
assess the impact on environment.
iv. Risk Quantification: Quantitative techniques are used considering effect /
impact due to weather data, population data, and frequency of occurrences
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and likely hood of ignition / toxic release. Data are analyzed considering
likely damage (in terms of injury / fatality, property damage) each scenarios
is likely to cause.
QRA provides a means to determine the relative significance of a number of undesired
events, allowing analyst and the team to focus their risk reduction efforts where they will
be beneficial most.
INTECH shall manufacture some new technical grade pesticides chemicals at the
existing plantsite. Table2.6 in Chapter 2 gives the list of raw materials. Solid raw
materials are stored in ware house while liquid and gaseous raw materials are stored in
tank farms and covered area. The list of bulk liquid storages of raw materials is as given
below:
Table 6.1 Liquid/Gaseous Bulk Storages
S. No Material Capacity Remarks
RAW MATERIAL
1. Methanol 2X 25 MT Underground storage in tanks
2. Sulphuric acid 50 MT Above ground storage in tanks
3. Nitromethane 50 MT In drums / ISO Tankers, Well ventilated covered storage
4. Fuel (LDO /HSD) 5 KL each In drums, Well ventilated covered storage
6.3. Risk Screening Approach
Proposed Plant: Risk screening of INTECH proposed project was undertaken through
data / information provided by INTECH. Data of major / bulk storages of raw materials,
intermediates and other chemicals were collected. MSDS of hazardous chemicals were
studied vis avis their inventories and mode of storage. INTECH plant will be using
number of hazardous chemicals and also producing pesticides chemicals – all hazardous
in nature. The chemicals stored in bulk (liquid or gaseous) and defined under MSHIC
Rule will be considered for detailed analysis.
Hazardous materials have been defined under MSIHC Rules (1989) - 2 (e) which means.
(i) Any chemical which satisfies any of the criteria laid down in Part I of
Schedule I and is listed in Column 2 of Part II of this Schedule;
i. Toxic Chemicals: Chemicals having the following values of acute toxicity and
which owing to their physical and chemical properties, are capable of producing
major accident hazards:
S.
No
Toxicity Oral Toxicity
LD50 (mg/kg)
Dermal
Toxicity LD50
(mg/kg)
Inhalation
Toxicity LC50
(mg/l)
Remarks
1 Extremely >5 < 40 < 0.5
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Toxic
2 Highly Toxic >5 – 50 > 20 – 200 < 0.5 – 2.0
3 Toxic >50 – 200 > 200 - 1000 > 2 – 10
Flammable chemicals:
(i) Flammable gases; 20 0C and at standard pressure of 101.3 KPa are:
Ignitable when in a mixture of 13% or less by volume with air, or;
Have a flammable range with air of at least 12% points regardless of the lower
flammable limits.
(ii) Extremely flammable liquids: chemicals which have a flash point lower than or
equal to 230C and the boiling point less than 350C;
(iii) Very Highly flammable liquids: chemicals which have a flash point lower than or
equal to 230C and the boiling point higher than 35 0C;
(iv) Highly Flammable Liquid: Chemicals, which have a flash point lower than or equal
to 60 0C but higher than 23 0C.
(v) Flammable liquids: chemicals, which have a flash point higher than 60 0C but
lower than 90 0C.
Explosives: Explosive means a solid or liquid or pyrotechnics substance (or a mixture of
substances) or an article.
a) Which is in itself capable by chemical reaction of producing gas at such a temperature and pressure and at such a speed as to cause damage to surroundings;
b) Which is designed to produce an effect by heat, light, sound, gas or smoke or a combination of these as the result of non-detonative self-sustaining exothermic chemical reaction.
I. any chemical listed in Column 2 of Schedule 2; II. any chemical listed in Column 2 of Schedule 3;
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Table 6.2 : Hazardous Analysis of Products
S.
No
Material S. No & Threshold Quantity
(TQ in MT) as per MSHIC
Rules
Hazards Potential Remarks
Schedu
le- 1,
Part-II
Schedu
le-2,
Part-I
Schedule-
3, Part-I
Hazards Toxic
DT->---mg/Kg; OT----
mg/Kg; IT----mg/l; (Rats)
Chloropicrin
Cl3CNO2
CAS: 76-06-2
UN No: 1397
Clear to light green/brown
liquid, slightly oily
Odour: Intensely irritating
odor
--- ---- --- Toxic if swallowed. Causes
skin irritation. May Cause an
allergic reaction.
Causes serious eye irritation.
Fatal if inhaled.
IDLH 2.0 ppm HT
ACGIH (TLV)-0.1 ppm
(0.67 mg/m3)
Aluminum Phosphide
CAS: 20859-73-8
UN No: 1397
Grey-green powder or
pellet / tablet.
Odour: Strong garlic smell.
63 --- ---- Product gives off toxic
Phosphine gas when exposes
to atmospheric
moisture.
Oral, rat: LD50 = 11.8
mg/kg;
Skin, rabbit: LD50 =
>2000 gm/kg;
Eyes: cause
irritation.
Skin: cause
irritation
Ingestion
Extremely toxic
by ingestion
Methyl Bromide (MBr)
CH3Br
CAS: 74-83-9
UN No.
Toxic, flammable, corrosive
liquid and gas under
pressure.
--- --- --- Toxic, flammable, liquid and gas
under pressure, may be fatal if
inhaled, harmful if absorbed
through the skin,
Rat oral LD50 liquid MBr in
corn oil - 104 mg/kg
LC50- 302 ppm (Rat, 8
Hours)
TLV-TWA (ACGIH) – 1 ppm
Eye – May cause
moderate
conjunctivitis,
Inhalation –
Irritating to the
respiratory tract.
Skin – Itching
dermatitis.
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Zinc Phosphide
CAS: 1314-84-7
UN No: 1397
Form: solid
Color: Grey/black
Odor: Garlic odor.
--- ---- --- Harmful or fatal if swallowed. Oral, rat: LD50 = 910
mg/kg;
Inhalation, rat: LC50 =
15.3 mg/Kg
Additional Products
N-PROPYL BROMIDE
CAS: 106-94-5
Clear colorless to pale
yellow liquid with sweetish
odor
--- ---- --- Highly flammable liquid;
Harmful if swallowed
Oral, rat: LD50 = 2000-
3600;
LD50 (skin)-2000
Inhalation, rat: LC50 =
35000 mg/m3
ISO PROPYL BROMIDE
CAS: 75-26-3
Clear liquid
--- ---- --- Highly flammable. Harmful:
danger of serious damage to
health by prolonged exposure
through inhalation.
DT->---mg/Kg;
OT----mg/Kg;
IT----36000 mg/m3
Repeated
exposure may
cause skin
dryness or
cracking.
VINYL BROMIDE
CAS: 593-60-2
colorless
liquefied gas
with pleasant odor
671 ---- --- Harmful if swallowed, eye
irritation, central nervous
system depression
DT->---mg/Kg;
OT---- 500 mg/Kg;
IT-------- mg/m3
Flammable gas.
May cause flash
fire.
2-CYNO 4-
BROMOMETHYLBI-
PHENYL
CAS: 114772-54-2
Off-white crystalline
powder
--- ---- --- Skin: Causes skin irritation.
Ingestion: Toxic if swallowed.
Inhalation: May be harmful if
inhaled. Causes respiratory
tract irritation.
DT->---mg/Kg;
OT----mg/Kg;
IT-------- mg/m3
[Not available]
TMSOBr (Tri-Methyl
Sulfoxonium Bromide)
--- ---- --- Skin corrosion/irritation:
Serious eye damage/irritation:
DT->------- mg/Kg;
OT---- 14500 mg/Kg;
Data not
available
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CAS No: 25596-24-1
Solid -crystal Powder
IT---- ---- mg/m3
ETHYL
BROMIDE
CAS: 74-96-4
UN No:1605
Colorless liquid with
Ethereal odour; burning
taste
--- ---- --- Hazardous in case of skin
contact (irritant, permeate), of
eye contact (irritant), of
ingestion. Slightly hazardous
in case of
inhalation.
.
DT->-------mg/Kg;
OT---- 1350 mg/Kg (Rat);
IT----8115 ppm [4 hrs.
mouse]
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Table 6.3 : Hazardous Analysis Raw materials stored in Bulk
S. No Material S. No & Threshold Quantity (TQ in MT) as per MSHIC Rules
Hazards Potential Remarks
Schedule- 1, Part-II
Schedule-2, Part-I
Schedule-3, Part-I
Hazards Toxic DT->---mg/Kg; OT----mg/Kg; IT----mg/l; (Rats)
1. Methanol CAS No:67-56-1 UN No:1230 A colorless fairly volatile liquid with a faintly sweet pungent odor like that of ethyl alcohol.
377 --- --- Highly Flammable; Behavior in Fire: Containers may explode. Health Hazards: Exposure to excessive vapor causes eye irritation, head- ache, fatigue and drowsiness. High concentrations can produce central nervous system depression and optic nerve damage. 50,000 ppm will probably cause death in 1 to 2 hrs. Can be absorbed through skin. Swallowing may cause death or eye damage.
ERPG-1: 200 ppm ERPG-2: 1000 ppm ERPG-3: 5000 ppm IDLH: 6000 ppm
2. Sulphuric Acid CAS No: 7664-93-9 UN No: 1830
591 Flammability: Will not burn Health Hazard: Extremely hazardous - use full protection; Reactivity: Violent chemical change possible
ERPG-1: 2.0 mg/m3 ERPG-2: 10 mg/m3 ERPG-3: 30 mg/m3 IDLH: 15 mg/m3
3. Bromine CAS No:7726-95-6 UN No:1744
84 17 TQ-1: 10 50 MT TQ-2:
500 MT
106 TQ-1: 40 MT TQ-2:
500 MT
Stable. Incompatible with reducing agents, alkali metals, powdered metals, steel, iron, copper, organic materials. Toxicology May be fatal if inhaled. Highly toxic by inhalation, ingestion or skin contact. Causes severe burns. Lachrymator. Typical TLV 0.1 ppm. Typical STEL 0.3 ppm
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4. Phosphorus UN No: 1381 Colorless or white, transparent, crystal solid, waxy appearance.
503 ---- ---- Very toxic if swallowed Acute - Eye: Causes burns. Acute - Skin: Causes burn in contact with skin.
Acute - Inhaled: Very toxic by inhalation. May cause severe injury or
death.
5. Sodium Hydroxide CAS No: 1310-730-2 UN No: 1823
571 Not flammable; Corrosive to metals and tissue. Hazardous.
ERPG-1: 0.5 ppm ERPG-2: 5.0 ppm ERPG-3: 50 ppm IDLH: ---- ppm
6. Nitro Methane CAS No: 75-52-5 Colorless Oily Liquid with disagreeable-Choking Odour
---- ---- ---- Very hazardous in case of ingestion. Hazardous in case of eye contact (irritant). Slightly hazardous in case of inhalation
DT----- OT—940 (Rat) IT------
7. Sodium Hypo chloride (3—20%) CAS No:7681-52-9 Greenish- Yellow Clear liquid with strong Chlorine Odour
---- ---- ---- Irritant of the nose and throat, causing coughing, difficulty breathing, and pulmonary edema.
DT------ OT—8910 (Rat/ Undiluted) IT-----
Causes severe skin irritation with blistering and ulceration.
8. Methylene Dichloride CAS No:75-09-2
---- ---- ---- Very hazardous in case of eye contact (irritant), of ingestion, of inhalation. Hazardous in case of skin
DT------ OT—1600 (Rat)
Not much data available
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Liquid; Odour –not available
contact (irritant, permeate). Inflammation of the eye is characterized by redness, watering, and itching.
IT----- Acute toxicity of the vapor (LC50): 52000 1 hours [Rat]
9. Sulphur CAS No 7704-34-9 Solid Odourless, Tasteless, faint taste
-- --- --- Hazardous in case of eye contact (Irritant), Slightly hazardous in case of skin contact. Toxic if inhale or injection.
LD50 - Acute: >8437 mg/kg
[Rat] LC50 – 10000 ppm 96 hours (Fish)
-
TQ-I: Threshold quantity (for application of rules 4,5,7 to 9 and 13 to 15)TQ-II: Threshold quantity (for application of
rules 10 to 12)
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Note:
1. Oral Toxicity (OT) in LD50 (mg/kg) 2. Dermal Toxicity (DT) in LD50 (mg/kg) 3. Inhalation Toxicity in LC50 (mg/l) [4 hrs.]
INTECH proposes production of new technical3 products and expansion of existing
formulation product. All products are hazardous in nature and limited data are available
for these. However, hazards potential (for damage) of products and other materials to
plant personnel, environment and off-site area is different for different materials See
Table 6.3. Among technical products only one is liquid. Among the products one product
namely Chloropicrin is” highly toxic” as per MSIHC rules. None is “extremely toxic”.
Among six additional products only one product (Vinyl Bromide) is mentioned in MSIHC
Rules. However, all are toxic in nature. Limited data are available for the products.
Though INTECH will be using a number of raw materials however it will be storing nearly
2 liquid raw materials (in bulk). Bromine will not be stored. It will be used immediately on
receipt in bulk tankers; no storage The raw materials coming under hazardous category
as specified by MSIHC Rules, 1989 (including subsequent amendments) is given in
Table 6.2 above
All pesticides products are hazardous in nature and many of them are new compounds
with little data available. The products are produced as per market demand and packed
and stored in saleable packing.
6.4. Hazardous Materials Storage
The solid raw materials will be received in bags or drums and will be stored in chemicals
go-downs. The products (liquid or solid) will be packed in drums and stored in product
go-downs as per market demand. The bulk storages of liquid hazardous materials are
given in the Table 6.1.
The solid materials powder or granules spillage can result in polluting small area only.
The damage to personnel can be through ingress- dermal (if individual come in contact),
oral (if individual food gets infected through fugitive dust) or inhalation (fugitive dust). The
main route is fugitive dust which in covered area will move to short distance only. Some
of the raw materials are though stored in bulk (quantity) but in drums only.
The pesticide product will be both as liquid and solid. The product storage for liquid will
be in drums and ISO containers and for solid in bags depending upon client requirement
The risk is through liquid and gaseous materials which are volatile/gaseous material
(toxic) and inflammable/explosive materials. The toxic vapours due to spillage of such
material can travel to some distance (as they are stored in covered go-downs) and cause
damage. The liquid products will be packed in drums (Approx 200 liters’ drums).
6.5. QRA Approach
Identification of hazards and likely scenarios (based on Level-1 and Level-2 activities)
calls for detailed analysis of each scenario for potential of damage, impact area (may
vary with weather conditions / wind direction) and safety system in place. Subsequently
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each incident is classified according to relative risk classifications provided in Table
below as Table 6.4:
Table 6.4 Risk Classification
Stage Description
High
(> 10-2/yr.)
A failure which could reasonably be expected to occur within the expected life time of the plant.
Examples of high failure likelihood are process leaks or single instrument or valve failures or a human error which could result in releases of hazardous materials.
Moderate
(10-2 --10-
4/yr.)
A failure or sequence of failures which has a low probability of occurrence within the expected lifetime of the plant.
Examples of moderate likelihood are dual instrument or valve failures, combination of instrument failures and human errors, or single failures of small process lines or fittings.
Low
(<10-4)
A failure or series of failures which have a very low probability of occurrence within the expected lifetime of plant.
Examples of ‘low’ likelihood are multiple instruments or valve failures or multiple human errors, or single spontaneous failures of tanks or process vessels.
Minor Incidents
Impact limited to the local area of the event with potent for ‘knock – on- events’
Serious Incident
One that could cause: Any serious injury or fatality on/off site; Property damage of $ 1 million offsite or $ 5 million onsite.
Extensive Incident
One that is five or more times worse than a serious incident.
Assigning a relative risk to each scenario provides a means of prioritizing associated risk
mitigation measures and planned actions.
6.6. Thermal Hazards
In order to understand the damages produced by various scenarios, it is appropriate to
understand the physiological/physical effects of thermal radiation intensities. The thermal
radiation due to tank fire usually results in burn on the human body. Furthermore,
inanimate objects like equipment, piping, cables, etc. may also be affected and also need
to be evaluated for damages. Table 6.5, Table 6.6and Table 6.7(below), respectively
give tolerable intensities of various objects and desirable escape time for thermal
radiation.
Thermal hazards could be from fires or explosion. Fire releases energy slowly while
explosion release energy very rapidly (typically in micro seconds). Explosion is rapid
expansion of gases resulting in rapidly moving shock wave. Explosion can be confined
(within a vessel or building) or unconfined (due to release of flammable gases).
BLEVE (boiling liquid expanding vapour explosion) occurs if a vessel containing a liquid
at a temperature above its atmospheric boiling point ruptures. The subsequent BLEVE is
the explosive vaporisation of large fraction of its vapour contents; possibly followed by
combustion or explosion of the vaporised cloud if it is combustible range.
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Thermal hazards have been considered for various scenarios including:
Fire in inflammable chemicals storage tanks.
Table 6.5 Effects due to Incident Radiation Intensity
Incident Radiation
kW/m2 Damage Type
0.7 Equivalent to Solar Radiation
1.6 No discomfort on long duration
4.0 Sufficient to cause pain within 20 sec. Blistering of skin (first degree burn are likely).
9.5 Pain threshold reached after 8 sec. Second degree burn after 20 sec.
12.5 Minimum energy required for piloted ignition of wood, melting of plastic tubing etc.
25
Minimum Energy required for piloted ignition of wood, melting, plastic tubing etc.
37.5 Sufficient to cause damage to process equipment.
62.0 Spontaneous ignition of wood.
Table 6.6 Thermal Radiation Impact to Human
Exposure
Duration
Radiation Energy {1%
lethality; kW/m2}
Radiation Energy
for 2nd degree
burns; kW/m2
Radiation Energy
for 1st degree
burns; kW/m2
10 sec 21.2 16 12.5
30 Sec. 9.3 7.0 4.0
Table 6.7 Tolerable Intensities for Various Objects
Sl. No Objects Tolerable Intensities (kw/m2)
1 Drenched Tank 38
2 Special Buildings (No window, fire proof doors)
25
3 Normal Buildings 14
4 Vegetation 10-12
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5 Escape Route 6 (up to 30 sec.)
6 Personnel in Emergencies 3 (up to 30 sec.)
7 Plastic Cables 2
8 Stationary Personnel 1.5
6.7. Damage due to Explosion
The explosion of a dust or gas (either as a deflagration or detonation) results in a
reaction front moving outwards from the ignition source preceded by a shock wave or
pressure front. After the combustible material is consumed the reaction front terminates
but the pressure wave continues its outward movement. Blast damage is based on the
determination of the peak overpressure resulting from the pressure wave impacting on
the object or structure.
As a safety measure INTECH is storing highly hazardous raw materials in isolated places
with full safety measures. Damage estimates based on overpressure are given in Table
6.8below:
Table 6.8 Damage due to Overpressure
Sl. No Overpressure (psig / bar)
Damage
1. 0.04 Loud Noise / sonic boom glass failure
2. 0.15 Typical pressure for glass failure
3. 0.5 – 1 Large and small windows usually shattered
4. 0.7 Minor damage to house structure
5. 1 Partial demolition of houses, made
uninhabitable.
6. 2.3 Lower limit of serious structure damage
7. 5 – 7 Nearly complete destruction of houses
8. 9 Loaded train box wagons completely
demolished
9. 10 Probable total destruction of houses
10. 200 Limits of crater lip
In INTECH case explosion not likely.
6.8. Toxic Release
Hazardous materials handled and stored in bulk in INTECH complex are toxic liquids (as
detailed in Table 6.1) and other raw materials as defined in MSHIC rules and indicated in
Table 6.3. Some of these chemicals are stored in bulk (in tank farm).
Damage criteria: For toxic release the damage criteria considered is IDLH concentration
(if data are available). In the absence of non-availability of IDLH, ‘Inhalation Toxicity (IT)
data for rats’ are considered. ‘IT’ data are used for the products as IDLH are not
available for these chemicals.
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6.9. Data Limitations
It is also observed that very little data or information (regarding physical properties
required for modelling) is available about the products.
6.10. Likely Failure Scenarios
Few likely failure scenarios have been selected after critical appraisal of raw materials
and storage inventories. Failure scenarios selected are as given in Table 6.9 below:
Table 6.9 Different Failure Scenarios
S. No. Scenario Remark
Raw materials
Case -1 Methanol Spillage Toxic Impact
Case -2 Nitromethane Spillage Toxic / Thermal Impact
6.11. Weather Effect
The effect of ambient conditions on the impact of fire / heat radiation and GLC of
hazardous / toxic material can be beneficial as well as harmful. A high wind (turbulence)
can dilute the toxic material while stable environment can extend the reach of IDLH or IT
(inhalation LC50 rats for products) concentration to long distance. Any inflammable gas /
vapour release in turbulent weather will soon dilute the hazardous gases below LEL and
thus save the disaster.
6.12. Incidents Impacts
The identified failure scenarios (Table 6.9) have been analysed (Using ALOHA and
EFFECT Modules) for the impact zones considering damage due to thermal and toxic
impacts. Similar impacts are considered for expansion units. Each incident will have
Impact on the surrounding environment which in extreme case may cross plant
boundary. The impact zones for various scenarios are given in Table 6.10.
Table 6.10 : Hazards Scenario Impact
Scenario No. Scenario Impact Zone (m) Remarks
Scenario Raw Material
Case -1 Methanol Spillage <10
IDLH; Stability Class D;
Case -2 Nitromethane Spillage <18
11
IDLH; Stability Class D;
Template-1
1st Degree Burn
Template-2
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Templates of Scenario
Template 1. Nitro Methane Spillage—Toxic Impact Zone (Class D)
Template 2. Nitro Methane Spillage; Pool Fire—Thermal Impact Zone
6.13. Consequential Impacts
The consequential impacts from each incident scenario can be though thermal, over
pressure wave and toxic route. The damage can be on plant personnel (and neighboring
residents in case incident crosses boundary), property and also loss in production.
6.14. Thermal and Explosion Hazards
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Incidents involving thermal hazards are mainly due to fuel fire (due to spillage). However,
the material stored is drums in small quantity. The impact due to nitromethane spillage
and fire (1st degree burn) is limited to ~11 m (2nd case) only (i.e. within plant boundary).
However, the consequences can go to worse if the incidents lead to domino effect to
other tanks.
6.15. Toxic Hazards
Toxic hazards are mainly due to Nitromethane and other toxic chemicals leakage and its
impact is also within the plant boundary (< 18 m).
Other hazardous chemicals including products their impact will be limited to spillage
area. The acid spillage if comes in contact with metal parts will produce hydrogen which
is highly flammable gas. Any person moving in area and getting splash will get the injury.
In addition, the spillage will cause pollution problem. The spillage is to be collected and
neutralized for toxic contents before disposal.
6.16. General Control Measures
Since some of the substances in use at INTECH are hazardous with fire potential and
also toxic in nature, it is necessary to use appropriate control measures recommended
for such substances:
6.17. Flammable Gas Fires
Fire control generally consists of directing, diluting and dispersing the inflammable
gas/vapor to prevent contact with persons, to prevent it from infiltrating structures if the
leak is out door, and to avoid its contact with ignition sources while, if possible,
simultaneously stopping the flow of gas. Water in the form of spray, applied from hoses
or monitor nozzles or by fixed water spray system cools the burning vapors / gas.
6.18. Process Safety System
Process & Plant Safety:
Conducting Preliminary Safety Analysis (A1), Basic Safety Review (A2), Detailed Safety
Review (A3), Pre Start-Up Safety Review (A4) & Pre Start-Up Safety audit according to
PPS directive (details mentioned in following flow diagram)
Every change in the process, procedure, equipment, etc. will be done through robust
management of change (MOC) procedure
Pre-Start up Safety Reviews for all modification
Pressure testing of pipelines and replacement of fragile pipelines and tanks by
prevention project
Hazardous area classification
Internal safety rounds for P&PS
Control P&IDs, and Lock opened (LO)/ Lock closed (LC) procedures are in place
TOPPS (Top Performance in Process & Plant Safety) training to all employees
Root Cause Analysis of all incidents
Pre-Start up Safety Reviews for all modification
Occupational Safety:
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Permit to Work procedure and Monthly monitoring of all filled permit for continual
improvement
Mobilized Near- Miss Reporting and award scheme
HSE rounds: PMT (Plant Management Team) of one plant takes HSE round of
another plant. Exchange of best practices among plants
MSDS Management
Tool Box talk with contractors
Central Safety Committee
Departmental Safety Committees
HSE Coordinator and Monitor program: Shop floor employees’ participation in
Safety activities
Celebration of theme based Safety days/ weeks at site
Safety Induction program for new joiners (both company & contract employees)
Emergency Preparedness:
On-Site Emergency Plan for the site
Training on On-Site Emergency Action Plan
Regular Site Level Mock drills and Plant Specific Fire Drills and Leak, spill drills
Availability of First aiders, Fire Fighters and Rescue members in each shift
Maintenance of Fire hydrant system, sprinkler system and portable fire
extinguishers
Periodic testing of fire hydrant and sprinkler systems
Fire Tenders and Ambulances kept ready
Occupational Health:
Pre-employment & Annual Medical Examination
Quarterly/Periodical Physical Examinations
Canteen Employees Examination
Fork lift operators Examination
Recall services & Follow-Up
Return to work assessment
Exit Examination
Training on Counselling, Hearing Conservation Program, Hazardous Chemical
Awareness Program, Shop floor training, First-aid (Adequate numbers of Certified
First Aiders/employees), etc.
Legal records: All medical records of employees to be maintained.
Emergency Medical services: Ambulance services, First-aid boxes,
Decontamination facility etc.
Health Promotional Activities: Awareness on Medical issues, Ergonomics awareness
programs, Stress management, De-addiction program, etc.
Decontamination facility is provided
Breathing air provision is provided at toxic chemical handling area.
Safety System for Toxic Material Handling
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Following precaution Taken while handling Toxic materials
Highly Toxic chemical is stored in storage room with lock and key.
Inventory records are maintained.
Toxic material is stored in well ventilation and out of sunlight
It is stored away from incompatible chemicals.
Keeping containers tightly & securely closed when not in use
Toxic chemical charging is done inside the closed room in presence of shift in-
charge.
Local Ventilation system is provided to avoid exposure at work place.
Vent gas is passing through scrubber system for absorption & reduction of pollution.
Standby pump provision is available for LEV & scrubber system. Training to employees
is providing for manual handling of toxic chemicals.
First aid training also provided to concern employees.
Antitoxic kit is maintaining inside OHC.
Safety PPE’s is providing during charging.
First aid kit provision is available at work place area.
Eye wash/Safety shower stations are readily available nearby and are tested regularly
To avoid fire and explosion nitrogen blanketing, earthling& bonding, electrical flame proof
equipment’s, pressure rated equipment’ are provided.
Suitable fire extinguisher and spill cleanup equipment are maintained.
Dyke provision is available where liquid toxic chemicals are stored.
Appropriate spill control equipment and procedures is available.
MSDS is maintained inside the concern plant / department.
Precautionary placard is displayed nearby the work place.
Toxic chemicals sign board is displayed on container.
Avoiding any welding, cutting, soldering or other hot work on an empty container of
toxic chemicals.
Good housekeeping is maintaining.
Toxic gas detector also provided at workplace.
Toxic chemical waste is collecting in separate pit and transferring to ETP for its
treatment.
Always ensuring that the waste container used is compatible with the waste material
Ensuring that the waste container is properly and accurately labelled.
Unauthorized person entry is restricted.
Restricted for eating, drinking & smoking at work place.
Employees are trained for emergency of toxic chemicals.
Toxic chemical spill, leak drills are conducting for awareness, preparedness &
response during an emergency.
Work place area monitoring is to be carried out for ensuring exposure at workplace.
Process is performed in closed conditions.
Regular pressure testing for pipelines and equipment to ensure tightness
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WORKPLACE MONITORING PLAN
Work zone monitoring is carried out by HSE department every month for gaseous
pollutants and dusts. Records are to be kept in standard Form as per Factories Rules.
Location for samplings shall be identified. Samples are analyzed for Air borne
concentration of hazardous chemicals in ppm.
The analyzed results are compared with the threshold limit values (TLV) of international
organizations. The monitoring program is based on the Action Level Concentration (ALC)
which is 50% of the TLV. If the analyzed concentration is < ALC, no regular monitoring is
required, only occasional checks (once in a year) to ensure the acceptability of the
system.
If the analyzed concentration is > ALC < TLV then the monitoring is carried out at regular
interval (once in two months). Incase analyzed concentration is > TLV then corrective
actions are decided by Plant Manager, General Manager - works and Engineering
Manager and they are implemented. After implementation again monitoring is carried
out.
The sampling for gaseous pollutants and air pollutants are done by Air sampling pump.
Arrangement for ensuring health and safety of workers engaged in handling of toxic
materials
All persons working in manufacturing units are surveyed by regular medical
examinations.
Pre-employment Medical examination to be carried out for all employees prior to
employment at well-known multispecialty hospital.
Checkups & tests carried out as per Factory rules / SPCB guidelines.
6.19. Safety Recommendations
6.20. Commonly Recommended Control Measures
A number of preventive control measures for hazardous occurrences have been
analyzed and discussed above. Some more salient points are enumerated below:
All storage tanks in the tank farm should be dyked. Other operation and maintenance features shall be based on established best safety practices.
Concentration detectors for hazardous chemical vapours (e.g. Chlorine/ bromine/ other chemicals etc.) fire Smoke / heat detectors and fire alarm should be installed at all strategic locations in the plant.
A schedule for preventive maintenance including health survey of all plant equipment should be adhered to as far as possible.
Ensure the absence of ignition sources in storage area.
Ensure placement of firefighting facilities, such as, carbon dioxide, dry chemical powder and foam type fire extinguishers in addition to fire hydrant system, at strategic locations. Spill control measures, such as, removal of all ignition sources from the spill area and ventilating the area as well as soaking the spilled material with paper, towel or mud and letting the volatile substance evaporate slowly in a safe area.
Compulsory use of protective clothing, non-sparking tools and warning signs during critical operations and maintenance.
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Training / refresher courses on safety information’s / norms.
Eyewash and showers should be put up at strategic places for use during emergencies.
A group of plant personnel should be trained in first aid, rescue, firefighting and
emergency control measures. These personnel will form core group/emergency squad
who will fight the emergency and also act as rescue and first aid team.
In order to ensure communication from isolated places/locations Walkie-Talkie be made
available to persons working in these areas. This will considerably improve the
effectiveness of emergency management.
There is no substitute for training-mock drills and these must be held at regular interval
keeping the following objectives in mind:
Real time mock-drill should be carried out for probable/likely hazardous situation (after
the plant is successfully commissioned).
Target to be set up for various tasks and events during an emergency.
Weak links should be marked and corrective action taken to improve effectiveness during
emergency.
6.21. Occupational Health and Safety
Occupational Health and Safety (OHS) are of prime importance more so in hazardous
industries. Industries have various types of hazards and QRA is carried out to
understand the hazards potential from various incidents. Pre-emptive steps can be
planned to safeguards from likely causes. Some of the
Frequent causes of accidents
Fire and explosion: explosives, flammable material
Hazards from Toxic Materials
Mechanical Hazards such as:
Being struck by falling objects
Caught in between machine parts
Snapping of cables, ropes, chains, slings
Handling heavy objects
Electricity Hazards
o Electrocution o Short circuits and consequential fire. o Poor illumination etc.
Other Hazards:
o Falls from height inside industrial units or on the ground o Struck by moving objects; Slipping on wet surfaces o Sharp objects
Oxygen deficiency in confined spaces; Lack of personal protective equipment (PPE),
housekeeping practices, safety signs
Consequential hazards due to extreme Temperatures;
Consequential hazards due to vibration
Consequential hazards due to radiation;
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Many more hazards.
Hazardous substances and wastes
Heavy and toxic metals
Lack of hazard communication (storage, labelling, material safety data sheets)
Batteries, fire-fighting liquids
Welding fumes
Volatile organic compounds (solvents)
Inhalation in confined and enclosed spaces
Repetitive strain injuries, awkward postures, repetitive and monotonous work, excessive workload
Ergonomic and psychosocial hazards
Many of the hazards are as result of working environment.
Long working hours, shift work, night work, temporary employment (Long working hours, shift work, night work, temporary employment, Mental stress, human relations) which results in less attention at work place and consequential incidents and accidents.
Lack of education and training / awareness is another prime cause of accidents.
Considering above, QRA analysis and also the nature of activities at INTECH the
following steps for OHS activities have been suggested:
Employee’s health check-up: pre-employment and periodic check-up during employment. The health check-up observations should be informed to employees.
The health should include any impact due to hazards at work place including (but not limited to) due to noise, heat, illumination, dust, any other chemicals, metals being suspected in environment and going into body of workers either through inhalation, ingestion or through skin absorption and steps taken to avoid muscular-skeletal disorders (MSD), backache, pain in minor and major joints, fatigue etc.
Training and refresher courses on safety to all employees.
Employees should be made aware of the hazards in the plant and the preventive actions to be safe from such hazards.
Response to Injuries: Based on a survey of possible injuries, a procedure for response to
injuries or exposure to hazardous substances should be established. All staff should
have minimum training to such response and the procedure ought to include the
following:
Immediate first aid, such as eye splashing, cleansing of wounds and skin, and
Bandage etc.
Immediate reporting to a responsible designated person
If possible, retention of the item and details of its source for identification of
possible hazards.
Medical surveillance
Recording of the incident
Investigation, determination and implementation of remedial action
6.22. Emergency Management Plan
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INTECH should develop an Emergency Management Plan (EMP) and regularly carry out
Mock drills to check the effectiveness of the EMP. Ergonomic and psychosocial hazards
6.23. Many of the hazards are as result of working environment
Repetitive strain injuries, awkward postures, repetitive and monotonous work, excessive
workload
Long working hours, shift work, night work, temporary employment (Long working hours,
shift work, night work, temporary employment, Mental stress, human relations) which
results in less attention at work place and consequential incidents and accidents.
Lack of education and training / awareness is another prime cause of accidents.
Considering above, QRA analysis and also the nature of activities at INTECH the
following steps for OHS activities have been suggested:
Employee’s health check-up: pre-employment and periodic check-up during employment.
The health check-up observations should be informed to employees.
The health should include any impact due to hazards at work place including (but not
limited to) due to noise, heat, illumination, dust, any other chemicals, metals being
suspected in environment and going into body of workers either through inhalation,
ingestion or through skin absorption and steps taken to avoid musculo-skeletal disorders
(MSD), backache, pain in minor and major joints, fatigue etc.
Training and refresher courses on safety to all employees.
Employees should be made aware of the hazards in the plant and the preventive actions
to be safe from such hazards.
Response to injuries: Based on a survey of possible injuries, a procedure for response to
injuries or exposure to hazardous substances should be established. All staff should
have minimum training to such response and the procedure ought to include the
following:
Immediate first aid, such as eye splashing, cleansing of wounds and skin, and
Bandage etc.
Immediate reporting to a responsible designated person
If possible, retention of the item and details of its source for identification of possible
hazards.
Medical surveillance
Recording of the incident
Investigation, determination and implementation of remedial action
6.24. Key Process Safety Measures
Flameproof equipment’s and fittings are provided for handling of hazardous
chemicals.
Tanks and all pump motors are earthed.
Road tanker earthling lines have been provided near the unloading pumps.
Dykes have been provided for hazardous chemicals storage to contain leakages.
Floors of the dyke area have impervious finish.
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Housekeeping of the plant is as per prescribed norms. Floors, platforms, staircases,
passages are kept free of any obstruction.
All hazardous operations are explained to the workers. They are periodically trained
on the hazardous processes.
Dedicated supply of firewater is available in the plant.
Only authorized persons are allowed inside the plant.
All instrument and safety devices are checked and calibrated during installation.
They are also calibrated, checked at a frequent interval. Calibration records are
maintained.
All electrical equipment’s are installed as per prescribed standards.
All the equipment’s of the plant are periodically tested as per standard and results
are documented. All equipment’s undergo preventive maintenance schedule.
Hydrant system is pressured with a Jockey Pump.
Flame arrestor is provided on each tank.
Pressure gauge is provided on each tank.
In addition to fire hydrant system, nos. of fire extinguishers are also installed at different
locations within premises.
Retention basin is provided to collect the contaminated water used during firefighting.
6.25. Transportation:
Class A petroleum products (equivalent raw materials) will be received through road
tanker and stored in underground storage tank as per petroleum Act & Rules.
Road tanker unloading procedure will be in place and will be implemented for safe
unloading of road tanker.
Static earthing provision will be made for tanker unloading.
Earthed Flexible Steel hose will be used for solvent unloading from the road tanker.
Fixed pipelines with pumps will be provided for solvent transfer up to Day
tanks/reactors.
Double mechanical seal type pumps will be installed.
NRV provision will be made on all pump discharge line.
Table 6.11 Transportation, Unloading and Handling Safety Measures
Activity Type of possible Hazard
Mitigation measures
1 Transportation of Chemicals
Bromine Leakage& Spillage
Isolate the area
Isolate the container
Check the source of leakage point.
Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
Do the necessary containment by cordoning and neutralize by neutralizing agent
• Training will be provided to driver and cleaner regarding the safe
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driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Instructions will be given not to stop road tanker in populated area. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE.
• Appropriate PPEs will be kept with tanker
Fire,& explosion,
Possibility of Fire & Expulsion is unlikely
Toxic release
• Isolate the area • Isolate the container • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Instructions will be given not to stop road tanker in populated area. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker .
Acid s
Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
Do the necessary containment by cordoning and neutralize by neutralizing agent • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Instructions will be given not to stop road tanker in populated area. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker
Fire,& explosion,
Possibility of Fire & Expulsion is unlikely
Toxic release
• Isolate the area • Isolate the container . Attend the source of release and mitigate with appropriate P.P.E.s • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. •• Instructions will be given not to stop road tanker in populated area. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker
Solvent Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
Use water spray to avoid any possibility of fire • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • • Instructions will be given not to stop road tanker in populated area.
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• Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker
Fire,& explosion,
• Use water spray to reduce vapors; • Keep combustibles (wood, paper, oil, etc.) away from spilled material. • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • • Instructions will be given not to stop road tanker in populated area. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker
Toxic release
• Isolate the area • Isolate the container • Check the source of leakage point. • Spray the water on leakage • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Fire extinguishers will be kept with tanker. • Flame arrestor will be provided to tanker exhaust. • Instructions will be given not to stop road tanker in populated area. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker
2 Acids, Bromine and& Solvents Road tanker unloading at project site.
Bromine Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Do the necessary containment by cordoning and neutralize by neutralizing agent
• Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker Priority will be given to Tanker to immediately enter the storage premises at site and will not be kept waiting near the gate or the main road. • Security person will check License, TREM CARD, Fire extinguisher condition; Antidote Kit, required PPEs as per SOP laid down. • Store officer will take sample as per sampling SOP from sampling point. • After approval of QC department unloading procedure will be allowed be started.
Fire,& explosion,
Possibility of Fire & Expulsion is unlikely
Toxic • Isolate the area
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release • Isolate the container • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker. Priority will be given to Tanker to immediately enter the storage premises at site and will not be kept waiting near the gate or the main road. • Security person will check License, TREM CARD, Fire extinguisher condition; Antidote Kit, required PPEs as per SOP laid down. • Store officer will take sample as per sampling SOP from sampling point. • After approval of QC department unloading procedure will be allowed be started.
Acid Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
Do the necessary containment by cordoning and neutralize by neutralizing agent • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker Priority will be given to Tanker to immediately enter the storage premises at site and will not be kept waiting near the gate or the main road. • Security person will check License, TREM CARD, Fire extinguisher condition; Antidote Kit, required PPEs as per SOP laid down. • Store officer will take sample as per sampling SOP from sampling point. • After approval of QC department unloading procedure will be allowed be started.
Fire,& explosion,
Possibility of Fire & Expulsion is unlikely
Toxic release
• Isolate the area • Isolate the container . Attend the source of release and mitigate with appropriate P.P.E.s • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. •• • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker Priority will be given to Tanker to immediately enter the storage premises at site and will not be kept waiting near the gate or the main road.
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• Security person will check License, TREM CARD, Fire extinguisher condition; Antidote Kit, required PPEs as per SOP laid down. • Store officer will take sample as per sampling SOP from sampling point. • After approval of QC department unloading procedure will be allowed be started.
Solvent Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
Use water spray to avoid any possibility of fire • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker Priority will be given to Tanker to immediately enter the storage premises at site and will not be kept waiting near the gate or the main road. • Security person will check License, TREM CARD, Fire extinguisher condition; Antidote Kit, required PPEs as per SOP laid down. • Store officer will take sample as per sampling SOP from sampling point. • After approval of QC department unloading procedure will be allowed be started. Following precautions will be adopted during unloading • Wheel stopper will be provided to tanker at unloading platform. • Static earthing will be provided to road tanker. • Tanker unloading procedure will be followed according to check list and implemented. • Flexible SS hose connection will be done at tanker • The quantity remaining in the hose pipeline will be drained to a small underground storage tank, which will be subsequenTanker y transferred by nitrogen pressure to the main storage tank thus ensuring complete closed conditions for transfer from road tanker. • All tanker valves will be closed in tanker. • Only day time unloading will be permitted. Dyke wall will be provided to storage tank. • Level transmitter will be provided with low-level high level auto cut-off provision. • Vent will be connected to water trap and vent of water trap will be provided with flame arrestor.
Fire,& explosion,
• Use water spray to reduce vapors; • Keep combustibles (wood, paper, oil, etc.) away from spilled material. Priority will be given to Tanker to immediately enter the storage premises at site and will not be kept waiting near the gate or the main road. • Security person will check License, TREM CARD, Fire extinguisher condition; Antidote Kit, required PPEs as per SOP laid down.
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• Store officer will take sample as per sampling SOP from sampling point. • After approval of QC department unloading procedure will be allowed be started. Dyke wall will be provided to storage tank. • Level transmitter will be provided with low-level high level auto cut-off provision. • Vent will be connected to water trap and vent of water trap will be provided with flame arrestor.
Toxic release
• Isolate the area • Isolate the container • Check the source of leakage point. • Spray the water on leakage • Training will be provided to driver and cleaner regarding the safe driving, hazard of Flammable chemicals, emergency handling. • TREM card will be kept with tanker. • Fire extinguishers will be kept with tanker. • Flame arrestor will be provided to tanker exhaust. • Clear Hazard Identification symbol and emergency telephone number will be displayed as per HAZCHEM CODE. • Appropriate PPEs will be kept with tanker Priority will be given to Tanker to immediately enter the storage premises at site and will not be kept waiting near the gate or the main road. • Security person will check License, TREM CARD, Fire extinguisher condition; Antidote Kit, required PPEs as per SOP laid down. • Store officer will take sample as per sampling SOP from sampling point. • After approval of QC department unloading procedure will be allowed be started. Following precautions will be adopted during unloading • Wheel stopper will be provided to tanker at unloading platform. • Static earthing will be provided to road tanker. • Tanker unloading procedure will be followed according to check list and implemented. • Flexible SS hose connection will be done at tanker. • The quantity remaining in the hose pipeline will be drained to a small underground storage tank, which will be subsequenTanker y transferred by nitrogen pressure to the main storage tank thus ensuring complete closed conditions for transfer from road tanker. • All tanker valves will be closed in tanker. • Only day time unloading will be permitted. Dyke wall will be provided to storage tank. • Level transmitter will be provided with low-level high level auto cut-off provision. • Vent will be connected to water trap and vent of water trap will be provided with flame arrestor.
3 Bromine, fuels and acid& Solvents Storage tank safety
Bromine Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
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Do the necessary containment by cordoning and neutralize by neutralizing agent Dyke wall will be provided to storage tank.
Fire,& explosion,
Possibility of Fire & Explosion is unlikely
Toxic release
• Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Do the necessary containment by cordoning and neutralize by neutralizing agent Dyke wall will be provided to storage tank.
Acid Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Do the necessary containment by cordoning and neutralize by neutralizing agent . Dyke wall will be provided to storage tank.
Fire,& explosion,
Possibility of Fire & Exposlision is unlikely
Toxic release
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Do the necessary containment by cordoning and neutralize by neutralizing agent Dyke wall will be provided to storage tank.
Methanol Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing.
Use water spray to avoid any possibility of fire Dyke wall will be provided to storage tank.
Fire,& explosion,
• Use water spray to reduce vapors; • Keep combustibles (wood, paper, oil, etc.) away from spilled material. Dyke wall will be provided to storage tank.
Toxic release
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• Isolate the area • Isolate the container • Check the source of leakage point. Dyke wall will be provided to storage tank.
4 Bromine and acid& Solvents transfer from storage tank to Day tank.
Bromine Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Proper training to operator, regular calibration of equipment’s, Proper flange guard to be available at applicable points
Fire,& explosion,
Not possible
Toxic release
Isolate the area Isolate the container Check the source of leakage point. Proper training to operator, regular calibration of equipment’s, Regular inspection and safety rounds Proper flange guard to be available at applicable points
Acid Leakage& Spillage
Isolate the area Isolate the container Check the source of leakage point. Proper training to operator, regular calibration of equipment’s Regular inspection and safety rounds Proper flange guard to be available at applicable points
Fire,& explosion,
Not possible
Toxic release
Isolate the area Isolate the container Check the source of leakage point. And attend leak Proper training to operator, regular calibration of equipment’s, Regular inspection and safety rounds Proper flange guard to be available at applicable points
Solvent Leakage& Spillage
• Double mechanical seal type FLP type pump will be provided. • Double on / off switch will provided at tank farm and process area near day tank. Pump auto cut off with day tank high level will be provided. • Flame arrestor will be provided on day tank vent. • Over flow will be provided for additional safety and it will be connected to main storage tank. • NRV will be provided on pump discharge line. • Double Jumper clip will be provided to all solvent handling pipeline. Double static earthing will be provided to day tank.
Fire,& explosion,
• Double mechanical seal type FLP type pump will be provided. • Double on / off switch will provided at tank farm and process area near day tank. Pump auto cut off with day tank high level will be provided. • Flame arrestor will be provided on day tank vent. • Over flow will be provided for additional safety and it will be connected to main storage tank.
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• NRV will be provided on pump discharge line. • Double Jumper clip will be provided to all solvent handling pipeline. Double static earthing will be provided to day tank.
Toxic release
• Double mechanical seal type FLP type pump will be provided. • Double on / off switch will provided at tank farm and process area near day tank. Pump auto cut off with day tank high level will be provided. • Flame arrestor will be provided on day tank vent. • Over flow will be provided for additional safety and it will be connected to main storage tank. • NRV will be provided on pump discharge line. • Double Jumper clip will be provided to all solvent handling pipeline. Double static earthing will be provided to day tank.
5 Transportation of Chemicals transfer from Day tank to reactor.
Bromine Leakage& Spillage
• Gravity transfer. Total quantity of day tank material will be charged in to reactor at a time.
Check the source of leakage point. And attend leak Proper training to operator, regular calibriation of equipments, Regular inspection and safety rounds Proper flange guard to be available at applicable points
Fire,& explosion,
Not applicable
Toxic release
• Gravity transfer. Total quantity of day tank material will be charged in to reactor at a time.
Check the source of leakage point. And attend leak Proper training to operator, regular calibriation of equipments, Regular inspection and safety rounds Proper flange guard to be available at applicable points
Leakage& Spillage
• Gravity transfer. Total quantity of day tank material will be charged in to reactor at a time.
Check the source of leakage point.and attend leak Proper training to operator, regular calibriation of equipments, Regular inspection and safety rounds
Proper flange guard to be available at applicable points
Fire,& explosion,
Not applicable
Toxic release
• Gravity transfer. Total quantity of day tank material will be charged in to reactor at a time.
Check the source of leakage point. And attend leak Proper training to operator, regular calibration of equipment’s, Regular inspection and safety rounds
Proper flange guard to be available at applicable points
Solvent Leakage& Spillage
Gravity transfer. Total quantity of day tank material will be charged in to reactor at a time. • Static earthing will be provided to storage tank. • Double Jumpers will be provided to pipeline flanges Proper flange guard to be available at applicable points
Fire,& explosion,
Check the source of leakage point. And attend leak, • Static earthing will be provided to storage tank. • Double Jumpers will be provided to pipeline flanges, Proper flange guard to be available at applicable points
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Toxic release
Proper training to operator, regular calibration of equipment’s, Regular inspection and safety rounds • Static earthing will be provided to storage tank. • Double Jumpers will be provided to pipeline flanges, Proper flange guard to be available at applicable points
6.26. Emergency facilities
Emergency Management Planning (EMP) should be developed considering the likely
hazards in the plant and sincerely implemented. Mock drills for various scenarios should
be carried out and results of the drills should be recorded. Weal links in the mock drills
should be strengthened.
6.27. Objectives
The Emergency Management Plan (EMP) is developed to make the best possible use of
the resources available at INTECH and the nearby agencies to provide help/assistance
in case of an emergency in the plant. The activities will include:
Rescue the victims and give them the necessary medical attention in the shortest
possible time.
Safeguard other person (evacuate them to a safer place).
Contain the incident and control it with minimum damage to human and life and
property.
Provide necessary information to families/relatives of affected persons, outside
agencies including media and statutory bodies.
6.28. Emergency Management Plan [EMP]
An outline of EMP organizational set-up necessary for chain of commands during
emergency situation in the plant is as given below. INTECH should develop EMP in the
organization and send it statutory authorities for approval and integration in District
Disaster Management Plan. A sample EMP is enclosed for reference.
In-charge – Production of the INTECH is the Chief Emergency Coordinator and he shall
be the main guiding person directing the emergency operations. He shall be assisted by:
Chief Shift Coordinator. Asst. Manager (Production)
Coordinate and direct all the activities from
Emergency site.
In absence of Asst. Manager (Prod.), Shift in
charge (Prod. I/II) will act as Chief Site
Coordinator.
Chief Maintenance Coordinator Manager-Maintenance
Coordinate all the maintenance activities from the
Emergency Control Center.
In absence of Manager (Maint.), Asst. Manager will
act as Chief Maintenance Coordinator.
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Chief Service Coordinator Manager (HR)
Coordinate with local administration take care of
transport, medical, canteen arrangements, and
evacuation of people if required.
In absence of Manager (HR), Asst. Manager (P&A)
will act as Chief Service Coordinator.
Chief Material Coordinator Manager (Commercial)
In absence of Manager (Commercial), Asst.
Manager (Commercial) will act as commercial
Coordinator.
Chief Operation Coordinator Manager (Admin) is the Incident
Controller for Vehicle Control & Security
Personnel Security Officer
In absence of Security Officer, SecuritySupervisor
will act for Vehicle Control & Security Personnel
deployment.
Fire & Safety Controller In-charge (F&S)
In absence of In-charge (F&S), Supervisor. (F & S)
will act as Fire & Safety Controller and also for first
aid.
Chief Medical Controller In-charge / Manager First Aid
In absence of In-charge (Medical), Supervisor.
(Medical) will act as Chief Medical Controller and
also for first aider.
Two “Assembly Points” will be identified (based on wind direction and away from
hazardous areas) and duly marked.
Chief Service Coordinator shall contact the following senior officers stationed at Barr
during emergency.
Format for Telephone Numbers of the Authorities:
Help Line
1 Emergency Services Helpline 108
2 Rajasthan Tourism Department ,Barr 02937-284224
1.1.1.
Ambulance
3 Ambulance 102/108
4 Red Cross , Mahavir Rajkiya Hospital. 02937-284-801
Hospital
5 Govt. Community Centre ,Barr 02937-284801
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6 Govt. Community Centre ,Raipur 02937-221122
7 Govt. Community Centre ,Sojat City 02932-222030
Govt Office
8 Factories and Boilers 0145-2427091
9 RPCB 02932-231616
10 RSEB 02937-284500
Fire
11 Fire Head Quarters 101
12 Fire Brigade Jaitarn 02939-222248
Police
13 Police 100
14 Barr 02937-220107
15 Raipur 02937-220777
16 Jaitaran 02939-222232
17 Sojat City 02960-222024
6.29. Responsibilities & Role of Key Personnel
6.30. Over all In-charge –In charge Production / Manager Production)
On getting the information about emergency from In-Charge (Prod.)/ First Viewer of Incident /
Supervisor rush to incident site/. Assess the overall situation and provide guidance in critical
decision-making.
6.31. Chief Site Coordinator- Manager (Prod.)
On getting the information about emergency from Supervisor Plant, inform over all
In-charge Plant (Operation).
Rush to the emergency site to assess the situation and decide to:
o Declare emergency based on amount/extent of hazards and water/air
analysis (toxic / flammable material release) and advise in charge (F&S) for
sounding emergency siren.
o Review if plant shutting down is required to contain / control the hazard.
o Review, evacuation from affected areas and sending the affected person to
a safe place.
o Advise Incident Controller and other key personnel to take necessary action.
o He will interact with Chief Service Coordinator and advise him on possible
effects on areas inside and outside the factory to initiate Off- Site Emergency
Response Plan.
o Remain in touch with Overall in-charge and inform about the situation &
actions being taken and seek his advice for the critical decisions.
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6.32. Chief Maintenance Coordinator- Manager (Maintenance)
After getting information about emergency from manager concerned Plant. Inform all
concerned personnel to be on alert.
Rush to the ECC (Emergency Control Cell), assess the situation and facilitate Chief
Site Coordinator-Manager (Prod.), Maintenance support needed to tackle the
emergency.
Facilitate elect. isolation of the affected area, if required through Supervisor (E&I)
Facilitate lighting arrangements at (a) affected locations and (b) Assembly points if
required through Supervisor (E&I)
Facilitate work-shop facilities with adequate manpower if required through Manager
(Maintenance). Remain in touch with Chief Site Controller.
6.33. Chief Service Coordinator - Manager (HR)
On getting information from the Medical Coordinator rush to the Emergency Control
Centre.
Assess the situation in consultation with Chief Site Coordinator and Incident
Controller and ensure that casualties get adequate transport / medical help.
Make arrangement to shift all the persons to the safest place if called for.
Assess 'Law and Order' situation.
Inform press, TV / Radio, local authorities about the severity of situation in close co-
ordination with Chief Site Coordinator and in consultation with Over All In-charge
Inform the District Authority / local police station in case their help is required for
evacuation of personnel / preserving law and order.
Evacuation of adjoining areas and villages, if required.
Remain in touch with over all In-charge and seek his advice for the critical decisions.
6.34. Chief Material Coordinator- Manager (Materials)
Rush to the emergency control centre on receipt of the message from Chief Service
Coordinator / on hearing the emergency siren and inform Supervisor. (Store) about
the emergency.
Get the stores opened for requirement of the Firefighting/safety and other materials,
which may be required during emergency.
Assess the situation in consultation with Chief site coordinator & incident controller
for any material requirement /help at the affected site.
He will be responsible for the arrangements of trucks for movement of bulk material if
required.
Remain in touch with Chief site coordinator, Incident controller, and Chief
maintenance coordinator.
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6.35. Incident Controller Concerned Plant -Manager Concerned Plant
Rush to the site of emergency after getting information from Shift In-charge assesses
the situation and immediately inform to Manager production
Take over charge from shift in charge.
Ensure that persons working in the area are safe and isolate source of toxic release
if possible.
Advise and assist in charge (F&S) for providing water curtains to contain toxic
release with in the plant battery.
Remain in touch with Chief Site Controller and other concerned officers.
Coordinate with Chief Maintenance / Chief Material coordinators for assistance
required at site.
Depending upon the severity of incident, ensure that adequate emergency services
like Medical/ Laboratory/ Mechanical/ Electrical etc. Are summoned.
Preservation of evidence as far as possible without affecting the operation of
emergency procedures to facilitate any subsequent inquiries into the causes and
circumstances, which led to the emergency.
6.36. Shift In-charge (Concerned Plant):
Immediately proceed to the site of emergency and assess the situation:
Immediately informed to Emergency Control Room (with name and location of
emergency)
During odd hours/till arrival of Fire shift I/C should act as chief fire coordinator.
Initiate the shutting down operations for controlling the hazard if unavoidable.
Cordon off the area and do not allow any body to enter the affected area without
respiratory protection (In case of toxic gas leakage).
Direct rescue operations with the help of fire and safety staff.
Open safety Almira for the use of plant personnel.
Have regard to the need for preserving evidence that could facilitate subsequent
inquiry.
Advise Supervisor of the plant to take roll call and account for missing personnel.
Hand over charge of the operation to the Manager when he arrives at site.
Ensure service agencies like Electrical, mechanical, instrumentations are mobilized
to handle the emergencies.
6.37. Security Officer Vehicle Control and Security Personnel Deployment at the Locations
Rush to the spot of emergency on getting information from Security Officer on duty
and inform Manager (HR) about emergency.
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Arrange one emergency vehicle immediately for ECC.
Keep in touch with Chief Service Coordinator, Chief Site Coordinator and In-charge
(F&S).
He will act as a special rescue Coordinator at the time of evacuation of employees
and others if required.
Alerts complete staff under his control and make it available at a known point, as per
the guidance of Chief Site Coordinator / Chief Service Coordinator.
Anticipate and arrange vehicles required at emergency site in consultation with in
charge (F&S) and Chief Site Coordinator and Chief Service Coordinator.
On request send vehicles for getting plant personnel / fire personnel required for
emergency.
Arrange vehicle in consultation with Medical Coordinator / Chief Service Coordinator
for shifting injured to city hospital.
During emergency arrange for opening of relevant gates/ barriers for easy movement
of vehicles. Security Guards should be posted on these gates / barriers to prevent
unauthorized entry.
Arrange transport and temporary shelters for evacuated personnel and inform the
relatives of the affected personnel if required.
6.38. Fire & Safety Controller- In charge (F&S)
Rush to the spot of emergency after getting information from ECC and inform to
Supervisor (F&S).
Direct rescue operations under the guidance of Chief Site Coordinator/ Incident
controller if required
Ask additional help from C.S.O. for cordoning off the area and advise fire personnel
for rescue / firefighting if required
Arrange to provide water curtains, water monitors, at affected locations if required.
Organize and supervise fire-fighting operations if called or.
Provide necessary respiratory equipment to plant personnel for emergency use.
Advise Chief Site Coordinator to arrange additional help Mutual aid group /
neighbouring industries if required.
Give safety precautions to the personnel at rescue work.
6.39. Fire Control Room In-Charge
On receiving emergency message from the in charge(F&S)/ on hearing siren. Rush to
ECC and take charge of Fire Control Centre from the fire operator / fire supervisor.
Assess the situation and Call fire staff from fire barrack.
Immediately rush fire crew to emergency spot.
Inform Medical Centre for sending ambulance to emergency site.
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6.40. Fire Supervisor should also ensure the following:
Supervisor to look for the wind direction and cordon off the area.
Use water monitors/hydrants/water curtains in consultation with incident/Chief site
controller.
Provide respiratory equipment’s to the plant personnel.
In case of toxic spillage at site, put foam (HAZMAT)/ sand on the spillage area.
Remain in touch with in charge(F&S).
Chief Site Co-coordinator will instruct Fire Control Room In-charge for operation of
“All Clear Siren” when the disaster is contained / controlled.
However, regular testing of siren & emergency buzzer plant control rooms for 2
minutes on every Week in afternoon is being done. All clear siren will sound for 2
minutes with a continuous sound.
6.41. Post Emergency Recovery
The post-emergency procedures discussed briefly below are designed to successfully
manage the damage / losses of an emergency event. The focus of these procedures is
to move the plant back into normal operating mode as quickly and efficiently as possible.
Immediately after the “ALL CLEAR” an emergency meeting will be held in emergency
control center to assess the loss both for men & materials, where in following will be
present with attendance records, details of injured, outside situation and preparation of
press release (if felt necessary)
Overall in charge
Chief Site Coordinator
Chief Maintenance Coordinator
Chief Service Coordinator
Incident Controller
Material Coordinator
Medical co-ordinator
Security
Fire & Safety Controller
6.42. Accident Investigation
a. As soon as possible after the emergency is over and plant operation has become normal, the investigation and analysis is to be carried out to determine the cause of the event.
b. Representatives from various disciplines will be members of the investigation and analysis team.
c. The areas of the events are to be sealed off so that tempering or alterations of the physical evidence are not likely to occur.
d. Key components are to be photographed and logged with time, place, direction etc.
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e. Statements are to be taken from those who were involved with the operation or who witnessed the event.
6.43. Damage Assessment
This phase of recovery establishes the quantum of replacement machinery considered
necessary for bringing back plant to normal operation; property and personnel losses
accounted and culminates in a list of necessary repair, replacement and construction
work.
Insurance companies will be informed of the damage and requested to pay the
compensation as per claim.
6.44. Clean-up and Restoration
This phase will only begin once the investigation is complete. Reporting documentations
are to be prepared and forwarded to appropriate authorities. Repair, clean up and
restoration work to begin.
6.45. Conclusion &Recommendations
The hazard analysis and risk assessment incident scenarios indicates that incidents
mostly are not limited to plant battery limits but covers surrounding area also then. There
are possibilities of domino effect and the secondary scenario not predictable can be
worse than the primary one. The scenarios (specifically toxic hazards scenarios) are
crossing the INTECH plant boundaries. the direction of impact will be in down wind
direction (wind direction and speed varies with season).
Some of the recommendations for Tank farm storage system are as given below:
Provision of flame detectors/ thermal sensors at strategic locations in the
tank farm area.
Auto water deluge system on each bulk storage tank for inflammable liquids.
The system should automatically start taking signal from flame detectors or
thermal relay.
Fixed foam system with adequate capacity.
Human Factors: Company is having well equipped fire station and also safety
department – safety practices. Human factors role in safety cannot be ignored. Odd
hours working and over / long hours, work can drain out individual. It shows in lack of
efficiency and also the lack of paper attention the modern which chemical complex
demand. They are to be closely looked into and avoided.
‘Safety’ has unique features:
If no accident has happened so far probability of incident / accident occurring increases.
‘No accident’ / good safety record develops complacency inertia/ over confidence in the
team. This attitude gives rise to gaps / soft spots in the system giving chances to
incidents / accidents.
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Safety requires novelty. Routine training practices get stale with no positive results. Look
for novel scheme of training/ safety practices to build up fresh impetus in safety.
Involvement of employees with refreshed outlook for safety is to be achieved.
INTECH will strength their safety system by introducing SOP’s, work instruction followed
by mock drill with proper intervals, fire escape routes will be marked with all fire
extinguishers putting in place with proper trained fire team. It is proposing to install fire
hydrant system also as the storage and handling of flammable material will increase.
Above all it is attitude and practice which always help in handling the incident/ accident
occurs at anywhere especially regular, fire drills and induction training program at plant
before starting the day helps in avoiding the risk. It is also going to made mandatory to
use PPE at site. Company has policy to achieve zero accident rewards system for
employs to motivate and maintain safe environment.
The hazard potential of chemicals and estimation of consequences in case of their
accidental release during storage, transportation and handling has been identified and
risk assessment has been carried out to quantify the extent of damage and suggest
recommendations for safety improvement for the proposed facilities. Risk mitigation
measures based on MCA analysis and engineering judgments are incorporated in order
to improve overall system safety and mitigate the effects of major accidents.
An effective Disaster Management Plan (DMP) to mitigate the risks involved has been
prepared. This plan defines the responsibilities and resources available to respond to the
different types of emergencies envisaged. Training exercises will be held to ensure that all
personnel are familiar with their responsibilities and that communication links are functioning
effectively.
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CHAPTER 7. SUMMARY AND CONCLUSION
7.1. Prelude
The present study was aimed at identifying the potential environmental impacts due to
the various project activities, assessment of impact, mitigation measures, and at
developing an environmental management and monitoring plans for proper mitigation of
any adverse environmental impact. In this study, the various activities likely to take place
during the construction and operation phases of the project have been analyzed in
relation to the baseline condition of different environmental components. The mitigation
measures proposed for the construction and operation stages have been proposed and
the potential residual impacts discussed. The key points considered in this study are
described in the following sections:
7.2. Regulatory Compliance
The project is yet at its technical investigation stage. Prior to its implementation, it will be
necessary to acquire all the necessary clearance from the Government of India, as per
the applicable national regulations. Key clearances include obtaining No Objection
Certificate from the Rajasthan State Pollution Control Board (RPPCB) under The Water
(Prevention and Control of Pollution) Act, 1974 and Rules, 1975; The Air (Prevention and
Control of Pollution) Act, 1981 and Rules, 1982. In addition to that Manufacture, Storage
and Import of Hazardous Chemicals (MSIHC) Rules, 1989 and amendments thereafter,
Hazardous Waste (Management, Handling and Trans-Boundary Movement) Rules,
2016, Bio Medical Waste (Management & Handling) Rules, 1998 and amendments
thereafter, Municipal Solid Waste (Management & Handling) Rules, 2000 and
amendments thereafter will also be applicable to the industry.
7.3. Baseline Conditions
The monitoring of the existing environmental conditions of the proposed project site and
of its close vicinity have been established with respect to physical, biological and human
environment.
The air quality of the area meets the prescribed National Ambient Air Quality Standards
applicable for the Residential & Rural Areas. The background noise levels were also
found well within the standards as at present most of the area is not developed.
The analysis results of ground water samples of study area indicate that ground water of
Dhoolkot, Hajiwas is not suitable for drinking due to presence of high fluoride. Overall
the ground water of Hajiwas, Dhuoolkot, project site and Road Junction of Biratiya Kalan
&Purthigarh site is not meeting the permissible limit of Indian Standard IS: 10500-2012.
7.4. Environmental Impacts and Mitigation Measures
The project entails various impacts on the study area, some negative and some positive.
This chapter concludes on the findings that emerged from the environmental assessment study and summarizes the key points to be addressed to ensure the environmental sustainability of the project during the construction and operation phases.
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There is going to no adverse impact on water quality or water demand due to proposed
project. Rather overall fresh water demand will get reduced from the present level due to
treated effluent recycle.
The impact (incremental GLC) due to the new stacks were computed and all pollutants
post project GLC will be well within NAAQ norms.
There will be no adverse impact on land or noise level due to proposed project.
INTECH has taken adequate measures for EHS aspects for the proposed project. In
addition, recommendations have been made to further strengthen the EHS measures,
energy conservation and other EMP aspects.
7.5. Project Benefits
Proposed expansion project will result in considerable growth of stimulating the
industrial and commercial activities in the state. Small and medium scale industries may
be further developed as a consequence.
The project will be beneficial in govt’s target of increase the production capacity and
yield in the field of agriculture.
Increased revenue to the state by way of royalty, taxes and duties; ear foreign
exchange for our country as the primary market for all these product is export.
Overall Growth of the neighbouring area viz.: Agriculture and animal husbandry, Health
and family welfare; Watershed development; Sustainable livelihood and strengthening
of village Self Help Groups; and Infrastructure development.
In operation phase, the proposed plant would require significant workforce of non-
technical and technical persons.
Migration of persons with better education and professional experience will result in
increase of population and literacy in the surrounding villages.
Civic amenities will be substantial after the commencement of project activities. The
basic requirement of the community needs will be strengthened by extending
healthcare, educational facilities to the community, building/strengthening of existing
roads in the area.
The local population will be given preference to employment on the basis of their
eligibility and company requirement. The employment potential will ameliorate
economic conditions of these families directly and provide employment to many other
families indirectly who are involved in business and service oriented activities. The
employment of local people in primary and secondary sectors of project shall upgrade
the prosperity of the region. This in-turn will improve the socio-economic conditions of
the area.
About 100 people will be deployed temporarily during construction of the project and
about 430 people will be employed during operational stage of the project (direct or in
direct).
7.6. Conclusion and Recommendations
Based on the environmental impact assessment conducted, the following
recommendations are made:
Since regulations are fast changing in India, the project proponent must keep himself or
herself updated with respect to applicable laws and take appropriate actions in case the
provisions in some regulations undergo change.
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The impacts envisaged due to construction activities will be for short limited period.
Impact due to operational activities, systems of periodic auditing and reporting shall be
adopted during the operation period to ensure that the system adheres to the EMP.
The project proponent and its team of consultants and contractors are urged to develop
a strategy for effective communication with local people. The construction team/
developer should effectively follow the suggestions made in the EMP and/ or any other
environmental measures so as not to damage the environment of the project area.
CSR activities should be further strengthened.
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CHAPTER 8. DISCLOSURE OF CONSULTANT
Declaration by Experts Contributing to the Environmental Impact Assessment for Expansion of
Existing pesticide plant for manufacturing of technical grade pesticides in village – Biratiya
Kalan, Tehsil – Raipur, Distt – Pali, Rajasthan by M/s Intech Pharma Pvt Ltd.I, hereby, certify
that I was a part of the EIA team in the following capacity that developed the above EIA.
EIA Coordinator:
Name P K Srivastava
Signature
Period of involvement June 2017 to finalization of report
Contact Information: 011-30003200
Functional Area Experts
Functional Areas
Name of the Expert
Involvement
(Period and Task**)
December 2016 to finalization of report
Signature
Air Pollution Monitoring &
Control (AP)*
Y Bordia
Air pollution monitoring.
Meteorological parameter
measurement.
Identification & assessment of quantum of emission and its
Mitigation measures.
Air Quality Modeling and Prediction
(AQ)**
Sanjeev Sharma
Ambient Air Quality monitoring
network designing.
Processing of micrometeorological data for
using in model.
Air quality modelling through
ISC- Aermod for proposed
prediction of impact
Noise
Sanjeev Sharma
Monitoring of noise levels of the project site and surrounding
area.
Assessment of noise level and vibration potential due to proposed project and its
mitigation measures.
Water Pollution
(WP)*
Y Bordia
Water Quality monitoring
network designing.
Sampling of water samples
(surface and ground water).
Monitoring of water quality.
Water Balance
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Functional Areas
Name of the Expert
Involvement
(Period and Task**)
December 2016 to finalization of report
Signature
Identification & assessment of quantum of water pollution and
its Mitigation measures.
ETP Suggestion.
Ecology and
Bio-diversity
Conservation
(EB)
Ratnesh Kotiyal
Conducted Ecological survey &
preparation of status report.
Application of taxonomy in
resource inventory (Flora &
Fauna)
List of species animals and
plants report.
Identification & assessment of ecological impact due to proposed project and its
Mitigation measures.
Solid and Hazardous Waste Management
(SHW)
Y Bordia
Identification of hazardous and
non-hazardous wastes.
Reuse and recycling of solid
wastes.
Handling and disposal of Non-
Hazardous solid waste &
Hazardous waste.
Risk and
Hazards (RH)
P K Srivastava
Identification of hazards due to
proposed project.
Identification of hazardous substances in the proposed
project.
Preparation of risk assessment report and onsite emergency
plan.
Land use (LU) Anil Kumar
Development of land use maps of study area using GIS / related tools, site visit for ground truth survey, finalization of land use maps
*Following category ‘B’ FAEs have worked as support FAE to category ‘A’ FAEs. Mr. Om
Prakash for Air and Water Environment
Ms. Shweta Gupta for Noise and Vibration.
** Mr. Om Prakash worked as team member in Air Quality Modelling and Prediction (AQ)
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Declaration by the Head of the Accredited Consultant Organization/authorized person
I, S.K.Jain, hereby confirm that the above-mentioned experts the Environmental Impact
Assessment for Expansion of Existing pesticide plant for manufacturing of technical grade
pesticides in village – Biratiya Kalan, Tehsil – Raipur, Distt – Pali, Rajasthan by M/s Intech
Pharma Pvt Ltd. I also confirm that the consultant organization shall be fully accountable
for any mis-leading information mentioned in this statement.
Name: S.K.Jain
Signature
Designation: Director, Technical
Name of the EIA Consultant organization EQMS India Pvt. Ltd.
NABET Certificate No. and date NABET/EIA/RA11/007, 19th May, 2014