draft environmental impact assessment report rakamcherla, vikarabad... · rakamcherla ip -eia i...
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Rakamcherla IP - EIA
i
DRAFT ENVIRONMENTAL IMPACTASSESSMENT REPORT
FOR THE
“PROPOSED INDUSTRIAL PARK”(112.48Acres)
[Project termed under Schedule (7C) Category ‘B’ - Industrial Park as per EIANotification 2006 and it’s Amendments]
AT
VILLAGES: RAKAMCHERLA & PUDUR
MANDAL: PUDUR
DISTRICT: VIKARABAD
STATE: TELANGANA
PROPOSED BY
TELANGANA STATE INDUSTRIAL INFRASTRUCTURE CORPORATION LTD.
6th Floor, Parisrama Bhavan,
Fateh Maidan Road, Basheerbagh, Hyderabad – 500 004
REPORT PREPARED BY
(NABET Accredited vide Certificate No: NABET/EIA/1618/SA0015 &
MoEF Recognized Lab vide F.No Q-15018/29/2007-CPW)
HUBERT ENVIRO CARE SYSTEMS PVT LTD., CHENNAI
February 2017
Rakamcherla IP - EIA
i
DRAFT ENVIRONMENTAL IMPACTASSESSMENT REPORT
FOR THE
“PROPOSED INDUSTRIAL PARK”(112.48Acres)
[Project termed under Schedule (7C) Category ‘B’ - Industrial Park as per EIANotification 2006 and it’s Amendments]
AT
VILLAGES: RAKAMCHERLA & PUDUR
MANDAL: PUDUR
DISTRICT: VIKARABAD
STATE: TELANGANA
PROPOSED BY
TELANGANA STATE INDUSTRIAL INFRASTRUCTURE CORPORATION LTD.
6th Floor, Parisrama Bhavan,
Fateh Maidan Road, Basheerbagh, Hyderabad – 500 004
REPORT PREPARED BY
(NABET Accredited vide Certificate No: NABET/EIA/1618/SA0015 &
MoEF Recognized Lab vide F.No Q-15018/29/2007-CPW)
HUBERT ENVIRO CARE SYSTEMS PVT LTD., CHENNAI
February 2017
Rakamcherla IP - EIA
i
DRAFT ENVIRONMENTAL IMPACTASSESSMENT REPORT
FOR THE
“PROPOSED INDUSTRIAL PARK”(112.48Acres)
[Project termed under Schedule (7C) Category ‘B’ - Industrial Park as per EIANotification 2006 and it’s Amendments]
AT
VILLAGES: RAKAMCHERLA & PUDUR
MANDAL: PUDUR
DISTRICT: VIKARABAD
STATE: TELANGANA
PROPOSED BY
TELANGANA STATE INDUSTRIAL INFRASTRUCTURE CORPORATION LTD.
6th Floor, Parisrama Bhavan,
Fateh Maidan Road, Basheerbagh, Hyderabad – 500 004
REPORT PREPARED BY
(NABET Accredited vide Certificate No: NABET/EIA/1618/SA0015 &
MoEF Recognized Lab vide F.No Q-15018/29/2007-CPW)
HUBERT ENVIRO CARE SYSTEMS PVT LTD., CHENNAI
February 2017
Rakamcherla IP - EIA
ii
Hubert Enviro Care Systems (P)Ltd.Client: TELANGANA STATE INDUSTRIAL INFRASTRUCTURE
CORPORATION LTDProject: DRAFT EIA FOR PROPOSED
INDUSTRIAL PARKProject No.:
Title: ENVIRONMENTAL IMPACTASSESSMENT REPORT
Document No.: Rev.:
R1This document is the property of Hubert Enviro Care Systems (P) Ltd. and mustnot be passed on to any person or body not authorised by us to receive it nor becopied or otherwise made use of either in full or in part by such person or bodywithout our prior permission in writing.
File path:c:\users\hecs\desktop\report format.docx
Notes:
1. Executive summary in Telugu and English.
2. Draft EIA Report
Revision Details:
4
3
2
1 09/02/2017 Second Revision Varadarajan AkhilaChandran
0 20/08/2016 First Revision Varadarajan Vamseekrishna
Rev. Date DetailsInit. Sign. Init. Sign
. Init. Sign.
Prepared Checked Approved
Rakamcherla IP - EIA
ii
Hubert Enviro Care Systems (P)Ltd.Client: TELANGANA STATE INDUSTRIAL INFRASTRUCTURE
CORPORATION LTDProject: DRAFT EIA FOR PROPOSED
INDUSTRIAL PARKProject No.:
Title: ENVIRONMENTAL IMPACTASSESSMENT REPORT
Document No.: Rev.:
R1This document is the property of Hubert Enviro Care Systems (P) Ltd. and mustnot be passed on to any person or body not authorised by us to receive it nor becopied or otherwise made use of either in full or in part by such person or bodywithout our prior permission in writing.
File path:c:\users\hecs\desktop\report format.docx
Notes:
1. Executive summary in Telugu and English.
2. Draft EIA Report
Revision Details:
4
3
2
1 09/02/2017 Second Revision Varadarajan AkhilaChandran
0 20/08/2016 First Revision Varadarajan Vamseekrishna
Rev. Date DetailsInit. Sign. Init. Sign
. Init. Sign.
Prepared Checked Approved
Rakamcherla IP - EIA
ii
Hubert Enviro Care Systems (P)Ltd.Client: TELANGANA STATE INDUSTRIAL INFRASTRUCTURE
CORPORATION LTDProject: DRAFT EIA FOR PROPOSED
INDUSTRIAL PARKProject No.:
Title: ENVIRONMENTAL IMPACTASSESSMENT REPORT
Document No.: Rev.:
R1This document is the property of Hubert Enviro Care Systems (P) Ltd. and mustnot be passed on to any person or body not authorised by us to receive it nor becopied or otherwise made use of either in full or in part by such person or bodywithout our prior permission in writing.
File path:c:\users\hecs\desktop\report format.docx
Notes:
1. Executive summary in Telugu and English.
2. Draft EIA Report
Revision Details:
4
3
2
1 09/02/2017 Second Revision Varadarajan AkhilaChandran
0 20/08/2016 First Revision Varadarajan Vamseekrishna
Rev. Date DetailsInit. Sign. Init. Sign
. Init. Sign.
Prepared Checked Approved
Rakamcherla IP - EIA
i
TABLE OF CONTENTSAnnexures………………………………………………………….......................xi
Acknowledgement………………………….……………………………...….…xii
Declaration of experts contributing to the EIA ......…………………………..xii
Declaration by the head of the accredited consultantorganization…………………………………………...……….………….....…..xv
Compliance to Terms of Reference (ToR)......................................……….…...xvi
1 Introduction....................................................................................21.1 Purpose of the Report.................................................................................................................... 2
1.2 Project Proponent.......................................................................................................................... 2
1.3 EIA Requirement .......................................................................................................................... 3
1.4 Rationale of the Study................................................................................................................... 4
1.5 Applicability of Environmental Clearance.................................................................................... 5
1.6 Objectives and Scope.................................................................................................................. 13
1.6.1 Objectives of this EIA Report .............................................................................................13
1.7 Methodology Adopted for the Study .......................................................................................... 14
1.7.1 EIA Process.........................................................................................................................14
2 Project Description ......................................................................172.1 Type of the Project...................................................................................................................... 17
2.2 Project Location .......................................................................................................................... 17
2.3 Need for the Project .................................................................................................................... 22
2.4 Project Site .................................................................................................................................. 23
2.5 Existing Site Conditions.............................................................................................................. 23
2.6 Approach to the Site.................................................................................................................... 24
2.7 Proposed Development ............................................................................................................... 25
2.7.1 Plotted Area & Bulk Allotments .........................................................................................26
2.7.2 Access Road and Internal Roads.........................................................................................27
2.7.3 Green Belt Development.....................................................................................................28
2.8 Utilities........................................................................................................................................ 28
Rakamcherla IP - EIA
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TABLE OF CONTENTSAnnexures………………………………………………………….......................xi
Acknowledgement………………………….……………………………...….…xii
Declaration of experts contributing to the EIA ......…………………………..xii
Declaration by the head of the accredited consultantorganization…………………………………………...……….………….....…..xv
Compliance to Terms of Reference (ToR)......................................……….…...xvi
1 Introduction....................................................................................21.1 Purpose of the Report.................................................................................................................... 2
1.2 Project Proponent.......................................................................................................................... 2
1.3 EIA Requirement .......................................................................................................................... 3
1.4 Rationale of the Study................................................................................................................... 4
1.5 Applicability of Environmental Clearance.................................................................................... 5
1.6 Objectives and Scope.................................................................................................................. 13
1.6.1 Objectives of this EIA Report .............................................................................................13
1.7 Methodology Adopted for the Study .......................................................................................... 14
1.7.1 EIA Process.........................................................................................................................14
2 Project Description ......................................................................172.1 Type of the Project...................................................................................................................... 17
2.2 Project Location .......................................................................................................................... 17
2.3 Need for the Project .................................................................................................................... 22
2.4 Project Site .................................................................................................................................. 23
2.5 Existing Site Conditions.............................................................................................................. 23
2.6 Approach to the Site.................................................................................................................... 24
2.7 Proposed Development ............................................................................................................... 25
2.7.1 Plotted Area & Bulk Allotments .........................................................................................26
2.7.2 Access Road and Internal Roads.........................................................................................27
2.7.3 Green Belt Development.....................................................................................................28
2.8 Utilities........................................................................................................................................ 28
Rakamcherla IP - EIA
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TABLE OF CONTENTSAnnexures………………………………………………………….......................xi
Acknowledgement………………………….……………………………...….…xii
Declaration of experts contributing to the EIA ......…………………………..xii
Declaration by the head of the accredited consultantorganization…………………………………………...……….………….....…..xv
Compliance to Terms of Reference (ToR)......................................……….…...xvi
1 Introduction....................................................................................21.1 Purpose of the Report.................................................................................................................... 2
1.2 Project Proponent.......................................................................................................................... 2
1.3 EIA Requirement .......................................................................................................................... 3
1.4 Rationale of the Study................................................................................................................... 4
1.5 Applicability of Environmental Clearance.................................................................................... 5
1.6 Objectives and Scope.................................................................................................................. 13
1.6.1 Objectives of this EIA Report .............................................................................................13
1.7 Methodology Adopted for the Study .......................................................................................... 14
1.7.1 EIA Process.........................................................................................................................14
2 Project Description ......................................................................172.1 Type of the Project...................................................................................................................... 17
2.2 Project Location .......................................................................................................................... 17
2.3 Need for the Project .................................................................................................................... 22
2.4 Project Site .................................................................................................................................. 23
2.5 Existing Site Conditions.............................................................................................................. 23
2.6 Approach to the Site.................................................................................................................... 24
2.7 Proposed Development ............................................................................................................... 25
2.7.1 Plotted Area & Bulk Allotments .........................................................................................26
2.7.2 Access Road and Internal Roads.........................................................................................27
2.7.3 Green Belt Development.....................................................................................................28
2.8 Utilities........................................................................................................................................ 28
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2.8.1 Power Requirement.............................................................................................................28
2.8.1.2 Electrical Substation ...........................................................................................................29
2.8.2 Water Requirement .............................................................................................................29
2.8.3 Rain Water/Storm Water Drain...........................................................................................31
2.8.4 Solid and Hazardous Wastes...............................................................................................31
2.9 Project Cost................................................................................................................................. 33
3 Description of Environment .......................................................353.1 Scope of Study ............................................................................................................................ 35
3.2 Location ...................................................................................................................................... 35
3.3 Climate........................................................................................................................................ 37
3.4 Rainfall........................................................................................................................................ 38
3.5 Micrometeorology....................................................................................................................... 41
3.6 Air Environment ......................................................................................................................... 43
3.6.1 Reconnaissance Survey.......................................................................................................44
3.6.2 Baseline Status ....................................................................................................................48
3.7 Noise Environment ..................................................................................................................... 52
3.7.1 Reconnaissance Survey.......................................................................................................52
3.7.2 Baseline Status ....................................................................................................................54
3.7.3 Limits Set by CPCB ............................................................................................................55
3.8 Water Environment ..................................................................................................................... 56
3.8.1 Reconnaissance Survey.......................................................................................................56
3.8.2 Baseline Status ....................................................................................................................59
3.8.3 Hydrogeology .....................................................................................................................62
3.8.4 Drainage and water Bodies of the Study Area ....................................................................64
3.8.5 Irrigation Practices ...................................................................................................................64
3.9 Land Environment ...................................................................................................................... 67
3.9.1 Reconnaissance Survey.......................................................................................................67
3.9.2 Geology...............................................................................................................................67
3.9.3 Geomorphology ..................................................................................................................68
3.9.4 Physiography.......................................................................................................................69
3.9.5 Land Use/ Land Cover Classification .................................................................................70
3.10 Soil Environment ........................................................................................................................ 73
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2.8.1 Power Requirement.............................................................................................................28
2.8.1.2 Electrical Substation ...........................................................................................................29
2.8.2 Water Requirement .............................................................................................................29
2.8.3 Rain Water/Storm Water Drain...........................................................................................31
2.8.4 Solid and Hazardous Wastes...............................................................................................31
2.9 Project Cost................................................................................................................................. 33
3 Description of Environment .......................................................353.1 Scope of Study ............................................................................................................................ 35
3.2 Location ...................................................................................................................................... 35
3.3 Climate........................................................................................................................................ 37
3.4 Rainfall........................................................................................................................................ 38
3.5 Micrometeorology....................................................................................................................... 41
3.6 Air Environment ......................................................................................................................... 43
3.6.1 Reconnaissance Survey.......................................................................................................44
3.6.2 Baseline Status ....................................................................................................................48
3.7 Noise Environment ..................................................................................................................... 52
3.7.1 Reconnaissance Survey.......................................................................................................52
3.7.2 Baseline Status ....................................................................................................................54
3.7.3 Limits Set by CPCB ............................................................................................................55
3.8 Water Environment ..................................................................................................................... 56
3.8.1 Reconnaissance Survey.......................................................................................................56
3.8.2 Baseline Status ....................................................................................................................59
3.8.3 Hydrogeology .....................................................................................................................62
3.8.4 Drainage and water Bodies of the Study Area ....................................................................64
3.8.5 Irrigation Practices ...................................................................................................................64
3.9 Land Environment ...................................................................................................................... 67
3.9.1 Reconnaissance Survey.......................................................................................................67
3.9.2 Geology...............................................................................................................................67
3.9.3 Geomorphology ..................................................................................................................68
3.9.4 Physiography.......................................................................................................................69
3.9.5 Land Use/ Land Cover Classification .................................................................................70
3.10 Soil Environment ........................................................................................................................ 73
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2.8.1 Power Requirement.............................................................................................................28
2.8.1.2 Electrical Substation ...........................................................................................................29
2.8.2 Water Requirement .............................................................................................................29
2.8.3 Rain Water/Storm Water Drain...........................................................................................31
2.8.4 Solid and Hazardous Wastes...............................................................................................31
2.9 Project Cost................................................................................................................................. 33
3 Description of Environment .......................................................353.1 Scope of Study ............................................................................................................................ 35
3.2 Location ...................................................................................................................................... 35
3.3 Climate........................................................................................................................................ 37
3.4 Rainfall........................................................................................................................................ 38
3.5 Micrometeorology....................................................................................................................... 41
3.6 Air Environment ......................................................................................................................... 43
3.6.1 Reconnaissance Survey.......................................................................................................44
3.6.2 Baseline Status ....................................................................................................................48
3.7 Noise Environment ..................................................................................................................... 52
3.7.1 Reconnaissance Survey.......................................................................................................52
3.7.2 Baseline Status ....................................................................................................................54
3.7.3 Limits Set by CPCB ............................................................................................................55
3.8 Water Environment ..................................................................................................................... 56
3.8.1 Reconnaissance Survey.......................................................................................................56
3.8.2 Baseline Status ....................................................................................................................59
3.8.3 Hydrogeology .....................................................................................................................62
3.8.4 Drainage and water Bodies of the Study Area ....................................................................64
3.8.5 Irrigation Practices ...................................................................................................................64
3.9 Land Environment ...................................................................................................................... 67
3.9.1 Reconnaissance Survey.......................................................................................................67
3.9.2 Geology...............................................................................................................................67
3.9.3 Geomorphology ..................................................................................................................68
3.9.4 Physiography.......................................................................................................................69
3.9.5 Land Use/ Land Cover Classification .................................................................................70
3.10 Soil Environment ........................................................................................................................ 73
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3.10.1 Soil Type .............................................................................................................................73
3.10.2 Soil Monitoring ...................................................................................................................74
3.11 Terrestrial Ecology...................................................................................................................... 79
3.11.1 Flora in the Study Area .......................................................................................................79
3.11.2 Fauna...................................................................................................................................88
3.12 Socio Economic Environment .................................................................................................... 92
3.12.1 Social Indicators..................................................................................................................92
3.12.2 Economy of the District ....................................................................................................102
3.12.3 Industries...........................................................................................................................102
3.12.4 Social Survey – Interaction with People ...........................................................................103
3.12.5 Outcome of Socio Economic Survey ................................................................................111
4 Anticipated Environmental Impacts & Mitigation Measures1144.1 Impact Identification and Evaluation ........................................................................................ 114
4.1.1 Nature of Impact ...............................................................................................................114
4.1.2 Duration of Impact ............................................................................................................114
4.1.3 Aerial Extent of Impact.....................................................................................................115
4.1.4 Intensity of Impact ............................................................................................................115
4.2 Impacts due to Development of Industrial Park........................................................................ 116
4.2.1 Construction Phase............................................................................................................116
4.2.2 Operation Phase Impacts and Mitigation Measures.................................................................. 122
4.2.3 Impacts on Quality of Life ................................................................................................127
4.2.4 Impacts on Land Use.........................................................................................................128
4.2.5 Impacts on Standard of Living and Economic Opportunities ...........................................128
4.3 Impact Assessment.................................................................................................................... 131
5 Analysis of Alternatives.............................................................1385.1 Introduction............................................................................................................................... 138
5.2 Site Selection ............................................................................................................................ 138
5.3 Alternative I - prepare the site on an as-needed basis ............................................................... 138
5.4 Alternative II - Proposed Development .................................................................................... 139
5.5 Future Review and Approval .................................................................................................... 139
5.6 Comparison of Alternatives ...................................................................................................... 140
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3.10.1 Soil Type .............................................................................................................................73
3.10.2 Soil Monitoring ...................................................................................................................74
3.11 Terrestrial Ecology...................................................................................................................... 79
3.11.1 Flora in the Study Area .......................................................................................................79
3.11.2 Fauna...................................................................................................................................88
3.12 Socio Economic Environment .................................................................................................... 92
3.12.1 Social Indicators..................................................................................................................92
3.12.2 Economy of the District ....................................................................................................102
3.12.3 Industries...........................................................................................................................102
3.12.4 Social Survey – Interaction with People ...........................................................................103
3.12.5 Outcome of Socio Economic Survey ................................................................................111
4 Anticipated Environmental Impacts & Mitigation Measures1144.1 Impact Identification and Evaluation ........................................................................................ 114
4.1.1 Nature of Impact ...............................................................................................................114
4.1.2 Duration of Impact ............................................................................................................114
4.1.3 Aerial Extent of Impact.....................................................................................................115
4.1.4 Intensity of Impact ............................................................................................................115
4.2 Impacts due to Development of Industrial Park........................................................................ 116
4.2.1 Construction Phase............................................................................................................116
4.2.2 Operation Phase Impacts and Mitigation Measures.................................................................. 122
4.2.3 Impacts on Quality of Life ................................................................................................127
4.2.4 Impacts on Land Use.........................................................................................................128
4.2.5 Impacts on Standard of Living and Economic Opportunities ...........................................128
4.3 Impact Assessment.................................................................................................................... 131
5 Analysis of Alternatives.............................................................1385.1 Introduction............................................................................................................................... 138
5.2 Site Selection ............................................................................................................................ 138
5.3 Alternative I - prepare the site on an as-needed basis ............................................................... 138
5.4 Alternative II - Proposed Development .................................................................................... 139
5.5 Future Review and Approval .................................................................................................... 139
5.6 Comparison of Alternatives ...................................................................................................... 140
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3.10.1 Soil Type .............................................................................................................................73
3.10.2 Soil Monitoring ...................................................................................................................74
3.11 Terrestrial Ecology...................................................................................................................... 79
3.11.1 Flora in the Study Area .......................................................................................................79
3.11.2 Fauna...................................................................................................................................88
3.12 Socio Economic Environment .................................................................................................... 92
3.12.1 Social Indicators..................................................................................................................92
3.12.2 Economy of the District ....................................................................................................102
3.12.3 Industries...........................................................................................................................102
3.12.4 Social Survey – Interaction with People ...........................................................................103
3.12.5 Outcome of Socio Economic Survey ................................................................................111
4 Anticipated Environmental Impacts & Mitigation Measures1144.1 Impact Identification and Evaluation ........................................................................................ 114
4.1.1 Nature of Impact ...............................................................................................................114
4.1.2 Duration of Impact ............................................................................................................114
4.1.3 Aerial Extent of Impact.....................................................................................................115
4.1.4 Intensity of Impact ............................................................................................................115
4.2 Impacts due to Development of Industrial Park........................................................................ 116
4.2.1 Construction Phase............................................................................................................116
4.2.2 Operation Phase Impacts and Mitigation Measures.................................................................. 122
4.2.3 Impacts on Quality of Life ................................................................................................127
4.2.4 Impacts on Land Use.........................................................................................................128
4.2.5 Impacts on Standard of Living and Economic Opportunities ...........................................128
4.3 Impact Assessment.................................................................................................................... 131
5 Analysis of Alternatives.............................................................1385.1 Introduction............................................................................................................................... 138
5.2 Site Selection ............................................................................................................................ 138
5.3 Alternative I - prepare the site on an as-needed basis ............................................................... 138
5.4 Alternative II - Proposed Development .................................................................................... 139
5.5 Future Review and Approval .................................................................................................... 139
5.6 Comparison of Alternatives ...................................................................................................... 140
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5.6.1 Alternative Location ................................................................................................................. 140
5.6.2 Comparison of Alternatives and the Preferred Alternative....................................................... 141
5.7 Conclusion ................................................................................................................................ 141
6 Environmental Monitoring Programme .................................1436.1 Introduction............................................................................................................................... 143
6.2 Environmental Effects Monitoring in EIA................................................................................ 143
6.3 Environmental Monitoring Program – Construction and Operation Phase: ............................. 144
6.4 Budget for Environmental Monitoring ..................................................................................... 146
6.5 Monitoring Methodologies ....................................................................................................... 146
6.6 Reporting & Documentation..................................................................................................... 147
7 Environmental Management Plan ...........................................1497.1 Introduction............................................................................................................................... 149
7.2 Environmental Management Plan............................................................................................. 151
7.3 Objectives of EMP.................................................................................................................... 152
7.4 EMP Structure and Organization .............................................................................................. 153
7.4.1 Roles and Responsibilities for EMP ......................................................................................... 154
7.4.2 Environmental Management Cell ............................................................................................. 155
7.4.3 Responsibilities of Environment Management Cell ................................................................. 156
7.4.4 Monitoring of Environment ...................................................................................................... 157
7.5 Corporate Social Responsibility (CSR) .................................................................................... 158
7.6 Environmental Aspects -Construction Phase ............................................................................ 158
7.6.1 Air Environment ....................................................................................................................... 161
7.6.2 Water Environment ................................................................................................................... 161
7.6.3 Noise Environment ................................................................................................................... 162
7.6.4 Social Environment................................................................................................................... 163
7.7 Environment Management Plan - Operation Phase .................................................................. 163
7.7.1 Air Environment ....................................................................................................................... 165
7.7.2 Water Environment ................................................................................................................... 167
7.7.3 Noise Environment ................................................................................................................... 169
7.7.4 Land Environment and Solid/Hazardous Waste Management ................................................. 170
7.7.5 Green Belt Design Methodology and Approach....................................................................... 171
7.7.6 Material Management ............................................................................................................... 171
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5.6.1 Alternative Location ................................................................................................................. 140
5.6.2 Comparison of Alternatives and the Preferred Alternative....................................................... 141
5.7 Conclusion ................................................................................................................................ 141
6 Environmental Monitoring Programme .................................1436.1 Introduction............................................................................................................................... 143
6.2 Environmental Effects Monitoring in EIA................................................................................ 143
6.3 Environmental Monitoring Program – Construction and Operation Phase: ............................. 144
6.4 Budget for Environmental Monitoring ..................................................................................... 146
6.5 Monitoring Methodologies ....................................................................................................... 146
6.6 Reporting & Documentation..................................................................................................... 147
7 Environmental Management Plan ...........................................1497.1 Introduction............................................................................................................................... 149
7.2 Environmental Management Plan............................................................................................. 151
7.3 Objectives of EMP.................................................................................................................... 152
7.4 EMP Structure and Organization .............................................................................................. 153
7.4.1 Roles and Responsibilities for EMP ......................................................................................... 154
7.4.2 Environmental Management Cell ............................................................................................. 155
7.4.3 Responsibilities of Environment Management Cell ................................................................. 156
7.4.4 Monitoring of Environment ...................................................................................................... 157
7.5 Corporate Social Responsibility (CSR) .................................................................................... 158
7.6 Environmental Aspects -Construction Phase ............................................................................ 158
7.6.1 Air Environment ....................................................................................................................... 161
7.6.2 Water Environment ................................................................................................................... 161
7.6.3 Noise Environment ................................................................................................................... 162
7.6.4 Social Environment................................................................................................................... 163
7.7 Environment Management Plan - Operation Phase .................................................................. 163
7.7.1 Air Environment ....................................................................................................................... 165
7.7.2 Water Environment ................................................................................................................... 167
7.7.3 Noise Environment ................................................................................................................... 169
7.7.4 Land Environment and Solid/Hazardous Waste Management ................................................. 170
7.7.5 Green Belt Design Methodology and Approach....................................................................... 171
7.7.6 Material Management ............................................................................................................... 171
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5.6.1 Alternative Location ................................................................................................................. 140
5.6.2 Comparison of Alternatives and the Preferred Alternative....................................................... 141
5.7 Conclusion ................................................................................................................................ 141
6 Environmental Monitoring Programme .................................1436.1 Introduction............................................................................................................................... 143
6.2 Environmental Effects Monitoring in EIA................................................................................ 143
6.3 Environmental Monitoring Program – Construction and Operation Phase: ............................. 144
6.4 Budget for Environmental Monitoring ..................................................................................... 146
6.5 Monitoring Methodologies ....................................................................................................... 146
6.6 Reporting & Documentation..................................................................................................... 147
7 Environmental Management Plan ...........................................1497.1 Introduction............................................................................................................................... 149
7.2 Environmental Management Plan............................................................................................. 151
7.3 Objectives of EMP.................................................................................................................... 152
7.4 EMP Structure and Organization .............................................................................................. 153
7.4.1 Roles and Responsibilities for EMP ......................................................................................... 154
7.4.2 Environmental Management Cell ............................................................................................. 155
7.4.3 Responsibilities of Environment Management Cell ................................................................. 156
7.4.4 Monitoring of Environment ...................................................................................................... 157
7.5 Corporate Social Responsibility (CSR) .................................................................................... 158
7.6 Environmental Aspects -Construction Phase ............................................................................ 158
7.6.1 Air Environment ....................................................................................................................... 161
7.6.2 Water Environment ................................................................................................................... 161
7.6.3 Noise Environment ................................................................................................................... 162
7.6.4 Social Environment................................................................................................................... 163
7.7 Environment Management Plan - Operation Phase .................................................................. 163
7.7.1 Air Environment ....................................................................................................................... 165
7.7.2 Water Environment ................................................................................................................... 167
7.7.3 Noise Environment ................................................................................................................... 169
7.7.4 Land Environment and Solid/Hazardous Waste Management ................................................. 170
7.7.5 Green Belt Design Methodology and Approach....................................................................... 171
7.7.6 Material Management ............................................................................................................... 171
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7.7.7 Hazardous Waste Management................................................................................................. 172
7.7.8 Energy Conservation Measures Proposed................................................................................. 174
7.7.9 Fire Safety Facility.................................................................................................................... 174
7.7.10 Occupational Health and Safety................................................................................................ 174
7.7.11 Safety and Emergency Plan ...................................................................................................... 177
7.7.12 Fire Protection........................................................................................................................... 178
7.7.13 Green belt Development ........................................................................................................... 180
7.7.14 Corporate Social Responsibility................................................................................................ 180
7.7.15 Budget for Environmental Management................................................................................... 181
8 Additional Studies......................................................................1848.1 Risk Assessment ....................................................................................................................... 184
8.2 Disaster Management Plan........................................................................................................ 184
8.2.1 Major Activities .................................................................................................................184
8.2.5 Emergency Plan.................................................................................................................186
8.2.6 Service & Control .............................................................................................................187
8.3 Public Hearing .......................................................................................................................... 188
9 Project Benefits ..........................................................................190
10 Summary and Conclusion.........................................................192
11 Disclosure of Consultants Engaged..........................................195
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7.7.7 Hazardous Waste Management................................................................................................. 172
7.7.8 Energy Conservation Measures Proposed................................................................................. 174
7.7.9 Fire Safety Facility.................................................................................................................... 174
7.7.10 Occupational Health and Safety................................................................................................ 174
7.7.11 Safety and Emergency Plan ...................................................................................................... 177
7.7.12 Fire Protection........................................................................................................................... 178
7.7.13 Green belt Development ........................................................................................................... 180
7.7.14 Corporate Social Responsibility................................................................................................ 180
7.7.15 Budget for Environmental Management................................................................................... 181
8 Additional Studies......................................................................1848.1 Risk Assessment ....................................................................................................................... 184
8.2 Disaster Management Plan........................................................................................................ 184
8.2.1 Major Activities .................................................................................................................184
8.2.5 Emergency Plan.................................................................................................................186
8.2.6 Service & Control .............................................................................................................187
8.3 Public Hearing .......................................................................................................................... 188
9 Project Benefits ..........................................................................190
10 Summary and Conclusion.........................................................192
11 Disclosure of Consultants Engaged..........................................195
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7.7.7 Hazardous Waste Management................................................................................................. 172
7.7.8 Energy Conservation Measures Proposed................................................................................. 174
7.7.9 Fire Safety Facility.................................................................................................................... 174
7.7.10 Occupational Health and Safety................................................................................................ 174
7.7.11 Safety and Emergency Plan ...................................................................................................... 177
7.7.12 Fire Protection........................................................................................................................... 178
7.7.13 Green belt Development ........................................................................................................... 180
7.7.14 Corporate Social Responsibility................................................................................................ 180
7.7.15 Budget for Environmental Management................................................................................... 181
8 Additional Studies......................................................................1848.1 Risk Assessment ....................................................................................................................... 184
8.2 Disaster Management Plan........................................................................................................ 184
8.2.1 Major Activities .................................................................................................................184
8.2.5 Emergency Plan.................................................................................................................186
8.2.6 Service & Control .............................................................................................................187
8.3 Public Hearing .......................................................................................................................... 188
9 Project Benefits ..........................................................................190
10 Summary and Conclusion.........................................................192
11 Disclosure of Consultants Engaged..........................................195
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LIST OF TABLES
Table 1.1 Applicable Acts and Rules for the Proposed Project .................................................................... 7Table 2.1 Project site and surrounding features ..........................................................................................17Table 2.2 Land use breakup for the project ................................................................................................25Table 2.3 List of Industries Allocated.........................................................................................................26Table 2.4 List of Industries Proposed .........................................................................................................26Table 2.5 Water Requirement during Construction Phase..........................................................................26Table 2.6 Water Requirement for Proposed Industries ...............................................................................30Table 2.7 Municipal Waste generation during construction phase ...........................................................326Table 2.8 Solid & Hazardous Waste details of Allotted & Proposed Industries ........................................32Table 2.9 Project Cost.................................................................................................................................33Table 3.1 Climatic Condition in Vikarabad district in 2014 .......................................................................38Table 3.2 Rainfall distribution during the respective seasons.....................................................................38Table 3.3 Meteorological Observations (March – May).............................................................................42Table 3.4 Ambient Air Quality Monitoring Locations ...............................................................................45Table 3.5 Test methods for the analysis of Ambient Air Quality parameters.............................................48Table 3.6 Average Ambient Air Quality Monitoring data ..........................................................................50Table 3.7 Noise level sampling monitoring locations.................................................................................53Table 3.8 Summary of Noise monitoring in the Study area........................................................................55Table 3.9 Water sampling location details..................................................................................................57Table 3.10 Test methgods used for the analysis of water quality parameters.............................................59Table 3.11 Results of Surface water samples .............................................................................................60Table 3.12 Analytical results on Ground water samples.............................................................................61Table 3.13 Area irrigated different sources (in Ha) ....................................................................................65Table 3.14 Area Irrigated under food & Nonfood crops of RR District (2013-14) ....................................65Table 3.15 Land use classification ..............................................................................................................71Table 3.16 Soil Sampling Locations in the study area................................................................................74Table 3.17 Analytical results of soil samples collected at different sampling stations...............................77Table 3.18 List of Trees in the Study Area .................................................................................................82Table 3.19 Shrubs recorded in the study area .............................................................................................87Table 3.20 Climbers present in the study area ............................................................................................87Table 3.21 Herbs recorded in the study area...............................................................................................87Table 3.22 Aquatic plants recorded in the study area .................................................................................88Table 3.23 List of Mammals recorded in the study area.............................................................................89Table 3.24 Birds recorded in the study area................................................................................................89Table 3.25 Reptiles recorded in the study area ...........................................................................................90Table 3.26 List of Amphibians ...................................................................................................................91Table 3.27 List of Insects recorded in the study area..................................................................................91Table 3.28 Child Population in the District ................................................................................................94Table 3.29 Comparison of Demographic profile 2011 and 2001................................................................96Table 3.30 Comparison of Demographic profile between Rural and Urban ..............................................96
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LIST OF TABLES
Table 1.1 Applicable Acts and Rules for the Proposed Project .................................................................... 7Table 2.1 Project site and surrounding features ..........................................................................................17Table 2.2 Land use breakup for the project ................................................................................................25Table 2.3 List of Industries Allocated.........................................................................................................26Table 2.4 List of Industries Proposed .........................................................................................................26Table 2.5 Water Requirement during Construction Phase..........................................................................26Table 2.6 Water Requirement for Proposed Industries ...............................................................................30Table 2.7 Municipal Waste generation during construction phase ...........................................................326Table 2.8 Solid & Hazardous Waste details of Allotted & Proposed Industries ........................................32Table 2.9 Project Cost.................................................................................................................................33Table 3.1 Climatic Condition in Vikarabad district in 2014 .......................................................................38Table 3.2 Rainfall distribution during the respective seasons.....................................................................38Table 3.3 Meteorological Observations (March – May).............................................................................42Table 3.4 Ambient Air Quality Monitoring Locations ...............................................................................45Table 3.5 Test methods for the analysis of Ambient Air Quality parameters.............................................48Table 3.6 Average Ambient Air Quality Monitoring data ..........................................................................50Table 3.7 Noise level sampling monitoring locations.................................................................................53Table 3.8 Summary of Noise monitoring in the Study area........................................................................55Table 3.9 Water sampling location details..................................................................................................57Table 3.10 Test methgods used for the analysis of water quality parameters.............................................59Table 3.11 Results of Surface water samples .............................................................................................60Table 3.12 Analytical results on Ground water samples.............................................................................61Table 3.13 Area irrigated different sources (in Ha) ....................................................................................65Table 3.14 Area Irrigated under food & Nonfood crops of RR District (2013-14) ....................................65Table 3.15 Land use classification ..............................................................................................................71Table 3.16 Soil Sampling Locations in the study area................................................................................74Table 3.17 Analytical results of soil samples collected at different sampling stations...............................77Table 3.18 List of Trees in the Study Area .................................................................................................82Table 3.19 Shrubs recorded in the study area .............................................................................................87Table 3.20 Climbers present in the study area ............................................................................................87Table 3.21 Herbs recorded in the study area...............................................................................................87Table 3.22 Aquatic plants recorded in the study area .................................................................................88Table 3.23 List of Mammals recorded in the study area.............................................................................89Table 3.24 Birds recorded in the study area................................................................................................89Table 3.25 Reptiles recorded in the study area ...........................................................................................90Table 3.26 List of Amphibians ...................................................................................................................91Table 3.27 List of Insects recorded in the study area..................................................................................91Table 3.28 Child Population in the District ................................................................................................94Table 3.29 Comparison of Demographic profile 2011 and 2001................................................................96Table 3.30 Comparison of Demographic profile between Rural and Urban ..............................................96
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LIST OF TABLES
Table 1.1 Applicable Acts and Rules for the Proposed Project .................................................................... 7Table 2.1 Project site and surrounding features ..........................................................................................17Table 2.2 Land use breakup for the project ................................................................................................25Table 2.3 List of Industries Allocated.........................................................................................................26Table 2.4 List of Industries Proposed .........................................................................................................26Table 2.5 Water Requirement during Construction Phase..........................................................................26Table 2.6 Water Requirement for Proposed Industries ...............................................................................30Table 2.7 Municipal Waste generation during construction phase ...........................................................326Table 2.8 Solid & Hazardous Waste details of Allotted & Proposed Industries ........................................32Table 2.9 Project Cost.................................................................................................................................33Table 3.1 Climatic Condition in Vikarabad district in 2014 .......................................................................38Table 3.2 Rainfall distribution during the respective seasons.....................................................................38Table 3.3 Meteorological Observations (March – May).............................................................................42Table 3.4 Ambient Air Quality Monitoring Locations ...............................................................................45Table 3.5 Test methods for the analysis of Ambient Air Quality parameters.............................................48Table 3.6 Average Ambient Air Quality Monitoring data ..........................................................................50Table 3.7 Noise level sampling monitoring locations.................................................................................53Table 3.8 Summary of Noise monitoring in the Study area........................................................................55Table 3.9 Water sampling location details..................................................................................................57Table 3.10 Test methgods used for the analysis of water quality parameters.............................................59Table 3.11 Results of Surface water samples .............................................................................................60Table 3.12 Analytical results on Ground water samples.............................................................................61Table 3.13 Area irrigated different sources (in Ha) ....................................................................................65Table 3.14 Area Irrigated under food & Nonfood crops of RR District (2013-14) ....................................65Table 3.15 Land use classification ..............................................................................................................71Table 3.16 Soil Sampling Locations in the study area................................................................................74Table 3.17 Analytical results of soil samples collected at different sampling stations...............................77Table 3.18 List of Trees in the Study Area .................................................................................................82Table 3.19 Shrubs recorded in the study area .............................................................................................87Table 3.20 Climbers present in the study area ............................................................................................87Table 3.21 Herbs recorded in the study area...............................................................................................87Table 3.22 Aquatic plants recorded in the study area .................................................................................88Table 3.23 List of Mammals recorded in the study area.............................................................................89Table 3.24 Birds recorded in the study area................................................................................................89Table 3.25 Reptiles recorded in the study area ...........................................................................................90Table 3.26 List of Amphibians ...................................................................................................................91Table 3.27 List of Insects recorded in the study area..................................................................................91Table 3.28 Child Population in the District ................................................................................................94Table 3.29 Comparison of Demographic profile 2011 and 2001................................................................96Table 3.30 Comparison of Demographic profile between Rural and Urban ..............................................96
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Table 3.31 Schools in the District (2013-20104) ......................................................................................100Table 3.32 Dropout rate of Girls and Boys for the district and the State. (2013-14)................................100Table 3.33 Health facilities in the district .................................................................................................101Table 3.34 Livestock population in the district.........................................................................................102Table 4.1 Stack emission details for modeling .........................................................................................123Table 4.2 Predicted GLC for Proposed Stack ...........................................................................................126Table 4.3 Emission details of diesel Engines............................................................................................127Table 4.4 Summary of Findings................................................................................................................128Table 4.5 Summary Matrix of Predicted Impacts and Mitigation Measures ............................................131Table 6.1 Environmental Monitoring Program for Construction and Operation Phase............................144Table 6.2 Budgetary Allocation for Environmental Monitoring...............................................................146Table 7.1 Responsibility for EMP implementation...................................................................................154Table 7.2 Hazardous waste category and disposal method.........................................................................94Table 7.3 Budget for Environmental Management.....................................................................................94Table 11.1 Details of the Consultant.........................................................................................................195
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Table 3.31 Schools in the District (2013-20104) ......................................................................................100Table 3.32 Dropout rate of Girls and Boys for the district and the State. (2013-14)................................100Table 3.33 Health facilities in the district .................................................................................................101Table 3.34 Livestock population in the district.........................................................................................102Table 4.1 Stack emission details for modeling .........................................................................................123Table 4.2 Predicted GLC for Proposed Stack ...........................................................................................126Table 4.3 Emission details of diesel Engines............................................................................................127Table 4.4 Summary of Findings................................................................................................................128Table 4.5 Summary Matrix of Predicted Impacts and Mitigation Measures ............................................131Table 6.1 Environmental Monitoring Program for Construction and Operation Phase............................144Table 6.2 Budgetary Allocation for Environmental Monitoring...............................................................146Table 7.1 Responsibility for EMP implementation...................................................................................154Table 7.2 Hazardous waste category and disposal method.........................................................................94Table 7.3 Budget for Environmental Management.....................................................................................94Table 11.1 Details of the Consultant.........................................................................................................195
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Table 3.31 Schools in the District (2013-20104) ......................................................................................100Table 3.32 Dropout rate of Girls and Boys for the district and the State. (2013-14)................................100Table 3.33 Health facilities in the district .................................................................................................101Table 3.34 Livestock population in the district.........................................................................................102Table 4.1 Stack emission details for modeling .........................................................................................123Table 4.2 Predicted GLC for Proposed Stack ...........................................................................................126Table 4.3 Emission details of diesel Engines............................................................................................127Table 4.4 Summary of Findings................................................................................................................128Table 4.5 Summary Matrix of Predicted Impacts and Mitigation Measures ............................................131Table 6.1 Environmental Monitoring Program for Construction and Operation Phase............................144Table 6.2 Budgetary Allocation for Environmental Monitoring...............................................................146Table 7.1 Responsibility for EMP implementation...................................................................................154Table 7.2 Hazardous waste category and disposal method.........................................................................94Table 7.3 Budget for Environmental Management.....................................................................................94Table 11.1 Details of the Consultant.........................................................................................................195
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LIST OF FIGURES
Figure 1.1 EIA Process Cycle .....................................................................................................................15Figure 2.1 Location of the Project site ........................................................................................................19Figure 2.2 Project Site 15 Km Radius Map ................................................................................................20Figure 2.3 Satellite Imagery of the site Showing 10Km radius ................................................................201Figure 2.4 Google Image showing the Project site boundary with coordinates........................................202Figure 2.5 Site Photos ...............................................................................................................................204Figure 2.6 Site approach road from SH4 ..................................................................................................204Figure 2.7 Access road to site from SH4 ..................................................................................................205Figure 2.8 Water Balance Chart..................................................................................................................31Figure 3.1 Project Site Showing the administrative Setup..........................................................................36Figure 3.2 Topo map showing the project site and its surrounding features ..............................................37Figure 3.3 Monthly and Annual Rainfall of Vikarabad District (Source IMD)..........................................39Figure 3.4 Rainfall pattern in Vikarabad District .......................................................................................40Figure 3.5 Deviation of rainfall from Normal for Vikarabad District .......................................................40Figure 3.6 Wind Rose Diagram in the month of March to May 2014 .......................................................43Figure 3.7 Air quality monitoring Sampling locations Map (10Km Radius) .............................................46Figure 3.8 Sampling Photographs ...............................................................................................................47Figure 3.9 Noise level monitoring locations Map (10Km Radius) .............................................................58Figure 3.10 Water Sampling locations Map (10Km Radius)......................................................................58Figure 3.11 Ground Water Quality of Pudur Area......................................................................................63Figure 3.12 Drainage Map of the Study area ..............................................................................................66Figure 3.13 Geology Map of the Project Site .............................................................................................68Figure 3.14 Physiography of the Study area ...............................................................................................70Figure 3.15 Land Use and Land cover Classification of Study area...........................................................72Figure 3.16 Land Use / Land Cover Map of the Study area .......................................................................72Figure 3.17 Geological formation of the Study Area.................................................................................73Figure 3.18 Soil Classification of the Study Area .....................................................................................74Figure 3.19 Types of soil in the study area .................................................................................................75Figure 3.20 Soil Sampling Locations of the study area ..............................................................................76Figure 3.21 Floral Biodiversity in the study area........................................................................................82Figure 3.22 District-Social Groups in Rangareddy district.........................................................................93Figure 3.23 Sex-Ratio District vs State.......................................................................................................93Figure 3.24 Population of Vikarabad District .............................................................................................94Figure 3.25 Types of workers in the district ...............................................................................................97Figure 3.26 Percapita income of the district ...............................................................................................97Figure 3.27 Operational Land Holding .......................................................................................................98Figure 3.28 Land use pattern 2013 - 2014 ................................................................................................949Figure 3.29 Amenities available in the study area ....................................................................................107Figure 3.30 Living culture of people in the study area .............................................................................108
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LIST OF FIGURES
Figure 1.1 EIA Process Cycle .....................................................................................................................15Figure 2.1 Location of the Project site ........................................................................................................19Figure 2.2 Project Site 15 Km Radius Map ................................................................................................20Figure 2.3 Satellite Imagery of the site Showing 10Km radius ................................................................201Figure 2.4 Google Image showing the Project site boundary with coordinates........................................202Figure 2.5 Site Photos ...............................................................................................................................204Figure 2.6 Site approach road from SH4 ..................................................................................................204Figure 2.7 Access road to site from SH4 ..................................................................................................205Figure 2.8 Water Balance Chart..................................................................................................................31Figure 3.1 Project Site Showing the administrative Setup..........................................................................36Figure 3.2 Topo map showing the project site and its surrounding features ..............................................37Figure 3.3 Monthly and Annual Rainfall of Vikarabad District (Source IMD)..........................................39Figure 3.4 Rainfall pattern in Vikarabad District .......................................................................................40Figure 3.5 Deviation of rainfall from Normal for Vikarabad District .......................................................40Figure 3.6 Wind Rose Diagram in the month of March to May 2014 .......................................................43Figure 3.7 Air quality monitoring Sampling locations Map (10Km Radius) .............................................46Figure 3.8 Sampling Photographs ...............................................................................................................47Figure 3.9 Noise level monitoring locations Map (10Km Radius) .............................................................58Figure 3.10 Water Sampling locations Map (10Km Radius)......................................................................58Figure 3.11 Ground Water Quality of Pudur Area......................................................................................63Figure 3.12 Drainage Map of the Study area ..............................................................................................66Figure 3.13 Geology Map of the Project Site .............................................................................................68Figure 3.14 Physiography of the Study area ...............................................................................................70Figure 3.15 Land Use and Land cover Classification of Study area...........................................................72Figure 3.16 Land Use / Land Cover Map of the Study area .......................................................................72Figure 3.17 Geological formation of the Study Area.................................................................................73Figure 3.18 Soil Classification of the Study Area .....................................................................................74Figure 3.19 Types of soil in the study area .................................................................................................75Figure 3.20 Soil Sampling Locations of the study area ..............................................................................76Figure 3.21 Floral Biodiversity in the study area........................................................................................82Figure 3.22 District-Social Groups in Rangareddy district.........................................................................93Figure 3.23 Sex-Ratio District vs State.......................................................................................................93Figure 3.24 Population of Vikarabad District .............................................................................................94Figure 3.25 Types of workers in the district ...............................................................................................97Figure 3.26 Percapita income of the district ...............................................................................................97Figure 3.27 Operational Land Holding .......................................................................................................98Figure 3.28 Land use pattern 2013 - 2014 ................................................................................................949Figure 3.29 Amenities available in the study area ....................................................................................107Figure 3.30 Living culture of people in the study area .............................................................................108
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LIST OF FIGURES
Figure 1.1 EIA Process Cycle .....................................................................................................................15Figure 2.1 Location of the Project site ........................................................................................................19Figure 2.2 Project Site 15 Km Radius Map ................................................................................................20Figure 2.3 Satellite Imagery of the site Showing 10Km radius ................................................................201Figure 2.4 Google Image showing the Project site boundary with coordinates........................................202Figure 2.5 Site Photos ...............................................................................................................................204Figure 2.6 Site approach road from SH4 ..................................................................................................204Figure 2.7 Access road to site from SH4 ..................................................................................................205Figure 2.8 Water Balance Chart..................................................................................................................31Figure 3.1 Project Site Showing the administrative Setup..........................................................................36Figure 3.2 Topo map showing the project site and its surrounding features ..............................................37Figure 3.3 Monthly and Annual Rainfall of Vikarabad District (Source IMD)..........................................39Figure 3.4 Rainfall pattern in Vikarabad District .......................................................................................40Figure 3.5 Deviation of rainfall from Normal for Vikarabad District .......................................................40Figure 3.6 Wind Rose Diagram in the month of March to May 2014 .......................................................43Figure 3.7 Air quality monitoring Sampling locations Map (10Km Radius) .............................................46Figure 3.8 Sampling Photographs ...............................................................................................................47Figure 3.9 Noise level monitoring locations Map (10Km Radius) .............................................................58Figure 3.10 Water Sampling locations Map (10Km Radius)......................................................................58Figure 3.11 Ground Water Quality of Pudur Area......................................................................................63Figure 3.12 Drainage Map of the Study area ..............................................................................................66Figure 3.13 Geology Map of the Project Site .............................................................................................68Figure 3.14 Physiography of the Study area ...............................................................................................70Figure 3.15 Land Use and Land cover Classification of Study area...........................................................72Figure 3.16 Land Use / Land Cover Map of the Study area .......................................................................72Figure 3.17 Geological formation of the Study Area.................................................................................73Figure 3.18 Soil Classification of the Study Area .....................................................................................74Figure 3.19 Types of soil in the study area .................................................................................................75Figure 3.20 Soil Sampling Locations of the study area ..............................................................................76Figure 3.21 Floral Biodiversity in the study area........................................................................................82Figure 3.22 District-Social Groups in Rangareddy district.........................................................................93Figure 3.23 Sex-Ratio District vs State.......................................................................................................93Figure 3.24 Population of Vikarabad District .............................................................................................94Figure 3.25 Types of workers in the district ...............................................................................................97Figure 3.26 Percapita income of the district ...............................................................................................97Figure 3.27 Operational Land Holding .......................................................................................................98Figure 3.28 Land use pattern 2013 - 2014 ................................................................................................949Figure 3.29 Amenities available in the study area ....................................................................................107Figure 3.30 Living culture of people in the study area .............................................................................108
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Figure 3.31 Interaction with people on Socio - economic aspects............................................................110Figure 4.1Terrain map of the site..............................................................................................................124Figure 4.2 Ground Level Concentration of SOx .......................................................................................125Figure 4.3 Ground Level Concentration of Nox .......................................................................................125Figure 4.4 GLC of PM ..............................................................................................................................126Figure 7.1 Organogram for Environmental Management.........................................................................156
LIST OFABBREVIATIONS
AAQ Ambient Air Quality MonitoringDMP Disaster Management PlanEIA Environmental Impact AssessmentEM Environmental Monitoring
EMP Environmental Management PlanETP Effluent Treatment PlantSTP Sewage Treatment PlantLPG Liquefied Petroleum GasKLD Kilo litres per dayRA Risk analysisHW Hazardous WasteSQ Soil Quality
MTPA Metric Tonne Per AnnumNAAQ National Ambient Air Quality
NQ Noise QualityWQ Water Quality
µg/cu.m Microgram per cubic metermg/litre Milligram/litreng/litre Nanogram/litre
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Figure 3.31 Interaction with people on Socio - economic aspects............................................................110Figure 4.1Terrain map of the site..............................................................................................................124Figure 4.2 Ground Level Concentration of SOx .......................................................................................125Figure 4.3 Ground Level Concentration of Nox .......................................................................................125Figure 4.4 GLC of PM ..............................................................................................................................126Figure 7.1 Organogram for Environmental Management.........................................................................156
LIST OFABBREVIATIONS
AAQ Ambient Air Quality MonitoringDMP Disaster Management PlanEIA Environmental Impact AssessmentEM Environmental Monitoring
EMP Environmental Management PlanETP Effluent Treatment PlantSTP Sewage Treatment PlantLPG Liquefied Petroleum GasKLD Kilo litres per dayRA Risk analysisHW Hazardous WasteSQ Soil Quality
MTPA Metric Tonne Per AnnumNAAQ National Ambient Air Quality
NQ Noise QualityWQ Water Quality
µg/cu.m Microgram per cubic metermg/litre Milligram/litreng/litre Nanogram/litre
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Figure 3.31 Interaction with people on Socio - economic aspects............................................................110Figure 4.1Terrain map of the site..............................................................................................................124Figure 4.2 Ground Level Concentration of SOx .......................................................................................125Figure 4.3 Ground Level Concentration of Nox .......................................................................................125Figure 4.4 GLC of PM ..............................................................................................................................126Figure 7.1 Organogram for Environmental Management.........................................................................156
LIST OFABBREVIATIONS
AAQ Ambient Air Quality MonitoringDMP Disaster Management PlanEIA Environmental Impact AssessmentEM Environmental Monitoring
EMP Environmental Management PlanETP Effluent Treatment PlantSTP Sewage Treatment PlantLPG Liquefied Petroleum GasKLD Kilo litres per dayRA Risk analysisHW Hazardous WasteSQ Soil Quality
MTPA Metric Tonne Per AnnumNAAQ National Ambient Air Quality
NQ Noise QualityWQ Water Quality
µg/cu.m Microgram per cubic metermg/litre Milligram/litreng/litre Nanogram/litre
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ANNEXURES
Annexure 1: ToR letter copy
Annexure 2: ToR extension letter copy
Annexure 3: Land documents
Annexure 4: G.O. copy
Annexure 5: Revised Master Plan of proposed industrial park
Annexure 6: Traffic plan layout
Annexure 7: Water line layout
Annexure 8: Hydrogeology study report
Annexure 9: Storm Water Line Layout
Annexure 10: NAAQS copy
Annexure 11: Drinking water standards
Annexure 12: Noise standards and rules
Annexure 13: Project site contour map
Annexure 14: Project site overlapping layout
Annexure 15: Revenue sketch
Annexure 16: Panchanama of the project site
Annexure 17: Project site layout with survey numbers
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ANNEXURES
Annexure 1: ToR letter copy
Annexure 2: ToR extension letter copy
Annexure 3: Land documents
Annexure 4: G.O. copy
Annexure 5: Revised Master Plan of proposed industrial park
Annexure 6: Traffic plan layout
Annexure 7: Water line layout
Annexure 8: Hydrogeology study report
Annexure 9: Storm Water Line Layout
Annexure 10: NAAQS copy
Annexure 11: Drinking water standards
Annexure 12: Noise standards and rules
Annexure 13: Project site contour map
Annexure 14: Project site overlapping layout
Annexure 15: Revenue sketch
Annexure 16: Panchanama of the project site
Annexure 17: Project site layout with survey numbers
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ANNEXURES
Annexure 1: ToR letter copy
Annexure 2: ToR extension letter copy
Annexure 3: Land documents
Annexure 4: G.O. copy
Annexure 5: Revised Master Plan of proposed industrial park
Annexure 6: Traffic plan layout
Annexure 7: Water line layout
Annexure 8: Hydrogeology study report
Annexure 9: Storm Water Line Layout
Annexure 10: NAAQS copy
Annexure 11: Drinking water standards
Annexure 12: Noise standards and rules
Annexure 13: Project site contour map
Annexure 14: Project site overlapping layout
Annexure 15: Revenue sketch
Annexure 16: Panchanama of the project site
Annexure 17: Project site layout with survey numbers
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ACKNOWLEDGEMENT
The following people are gratefully acknowledged for their fullest support in rendering needful
information regarding the project and kind cooperation in fulfilling the report.
Telangana State Industrial Infrastructure Corporation Ltd. (TSIIC)
Mr. A. Laxmikantha Reddy- Chief Engineer
Mr. Maloth Nanu- Environmental Engineer
Mr. J. Vijay Kumar Reddy- Environmental Engineer
Mrs. Archana - Environmental Engineer
Mr. Raj Kiran – Environmental Engineer
Hubert Enviro Care Systems Pvt. Ltd, Chennai
Dr. J.R.Moses – FAE
Dr. Rajkumar Samuel–FAE
Mr. Abishek Moses – Team Member
Mr. Vamsee Krishna Navooru – EIA Coordinator
Mr. A.Manoharan– FAE
Mr. V.Dhivakar– FAE
Mrs. Ramaa Prakash – FAE
Mr.N.Varadharajan – Team Member
Mr. Chengalvarayan– Team Member
Ms. A. Ragatharani – Team Member
Laboratory Details
Hubert Enviro Care Systems Pvt. Ltd., Ashok Nagar, Chennai – Approved by MoEF&CC
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ACKNOWLEDGEMENT
The following people are gratefully acknowledged for their fullest support in rendering needful
information regarding the project and kind cooperation in fulfilling the report.
Telangana State Industrial Infrastructure Corporation Ltd. (TSIIC)
Mr. A. Laxmikantha Reddy- Chief Engineer
Mr. Maloth Nanu- Environmental Engineer
Mr. J. Vijay Kumar Reddy- Environmental Engineer
Mrs. Archana - Environmental Engineer
Mr. Raj Kiran – Environmental Engineer
Hubert Enviro Care Systems Pvt. Ltd, Chennai
Dr. J.R.Moses – FAE
Dr. Rajkumar Samuel–FAE
Mr. Abishek Moses – Team Member
Mr. Vamsee Krishna Navooru – EIA Coordinator
Mr. A.Manoharan– FAE
Mr. V.Dhivakar– FAE
Mrs. Ramaa Prakash – FAE
Mr.N.Varadharajan – Team Member
Mr. Chengalvarayan– Team Member
Ms. A. Ragatharani – Team Member
Laboratory Details
Hubert Enviro Care Systems Pvt. Ltd., Ashok Nagar, Chennai – Approved by MoEF&CC
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ACKNOWLEDGEMENT
The following people are gratefully acknowledged for their fullest support in rendering needful
information regarding the project and kind cooperation in fulfilling the report.
Telangana State Industrial Infrastructure Corporation Ltd. (TSIIC)
Mr. A. Laxmikantha Reddy- Chief Engineer
Mr. Maloth Nanu- Environmental Engineer
Mr. J. Vijay Kumar Reddy- Environmental Engineer
Mrs. Archana - Environmental Engineer
Mr. Raj Kiran – Environmental Engineer
Hubert Enviro Care Systems Pvt. Ltd, Chennai
Dr. J.R.Moses – FAE
Dr. Rajkumar Samuel–FAE
Mr. Abishek Moses – Team Member
Mr. Vamsee Krishna Navooru – EIA Coordinator
Mr. A.Manoharan– FAE
Mr. V.Dhivakar– FAE
Mrs. Ramaa Prakash – FAE
Mr.N.Varadharajan – Team Member
Mr. Chengalvarayan– Team Member
Ms. A. Ragatharani – Team Member
Laboratory Details
Hubert Enviro Care Systems Pvt. Ltd., Ashok Nagar, Chennai – Approved by MoEF&CC
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Declaration of Experts contributing to the EIA
I, hereby, certify that I was a part of the EIA team in the following capacity that developed theabove EIA.
EIA Coordinator:
Name: Vamsee Krishna Navooru
Signature: Date: February 06, 2017
Period of Involvement: Oct 2016 - On going
Contact Information: Hubert Enviro Care Systems (P) Ltd
# A-21, III Phase, Behind Lions Club School
Thiru Vi Ka Industrial Estate
Guindy, Chennai - 600 032, Tamil Nadu, India.
Email: [email protected]
Website: www.hecs.in
Functional Area Experts:
S. No.Functional
AreasName of the
ExpertDuration of Involvement Signature
1. AP Dr. J. R. Moses October 2014 to Till date
2. WP Ramaa PrakashOctober 2014 to Till date
3. SHWDr. J. R. Moses,Ramaa Prakash
October 2014 to Till date
4.AP,WP,N &SHW
Mr. VamseeKrishna Navooru
October 2014 to Till date
5. SE V DhivakarOctober 2013 to Till date
Rakamcherla IP - EIA
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Declaration of Experts contributing to the EIA
I, hereby, certify that I was a part of the EIA team in the following capacity that developed theabove EIA.
EIA Coordinator:
Name: Vamsee Krishna Navooru
Signature: Date: February 06, 2017
Period of Involvement: Oct 2016 - On going
Contact Information: Hubert Enviro Care Systems (P) Ltd
# A-21, III Phase, Behind Lions Club School
Thiru Vi Ka Industrial Estate
Guindy, Chennai - 600 032, Tamil Nadu, India.
Email: [email protected]
Website: www.hecs.in
Functional Area Experts:
S. No.Functional
AreasName of the
ExpertDuration of Involvement Signature
1. AP Dr. J. R. Moses October 2014 to Till date
2. WP Ramaa PrakashOctober 2014 to Till date
3. SHWDr. J. R. Moses,Ramaa Prakash
October 2014 to Till date
4.AP,WP,N &SHW
Mr. VamseeKrishna Navooru
October 2014 to Till date
5. SE V DhivakarOctober 2013 to Till date
Rakamcherla IP - EIA
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Declaration of Experts contributing to the EIA
I, hereby, certify that I was a part of the EIA team in the following capacity that developed theabove EIA.
EIA Coordinator:
Name: Vamsee Krishna Navooru
Signature: Date: February 06, 2017
Period of Involvement: Oct 2016 - On going
Contact Information: Hubert Enviro Care Systems (P) Ltd
# A-21, III Phase, Behind Lions Club School
Thiru Vi Ka Industrial Estate
Guindy, Chennai - 600 032, Tamil Nadu, India.
Email: [email protected]
Website: www.hecs.in
Functional Area Experts:
S. No.Functional
AreasName of the
ExpertDuration of Involvement Signature
1. AP Dr. J. R. Moses October 2014 to Till date
2. WP Ramaa PrakashOctober 2014 to Till date
3. SHWDr. J. R. Moses,Ramaa Prakash
October 2014 to Till date
4.AP,WP,N &SHW
Mr. VamseeKrishna Navooru
October 2014 to Till date
5. SE V DhivakarOctober 2013 to Till date
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6. EB,WPDr. RajkumarSamuel
March 2015
7. AQ Dr. J. R. Moses October 2014 to Till date
8. RH Dr. J. R .Moses October 2014 to Till date
9. SE, EB, SC A. ManoharanOctober 2014 toDecember 2014
10. HG DR.T.P.Natesan March to May 2014
11. LU DR.T.P.Natesan March to May 2014
12. GEO DR.T.P.Natesan March to May 2014
13. NV Mr.Brijesh Kumar April 2014
*See below the expansion of Functional Areas
Functional AreaCode
Abbreviation of the Functional Areas
LU Land UseAP Air Pollution monitoring, Prevention and ControlAQ Meteorology, Air Quality Modeling & PredictionWP Water Pollution monitoring, Prevention and ControlEB Ecology and BiodiversityNV Noise and VibrationSE Socio-EconomicsHG Hydrology, Ground Water & Water ConservationGEO GeologySC Soil ConservationRH Risk Assessment and Hazards ManagementSHW Solid and Hazardous Waste Management
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6. EB,WPDr. RajkumarSamuel
March 2015
7. AQ Dr. J. R. Moses October 2014 to Till date
8. RH Dr. J. R .Moses October 2014 to Till date
9. SE, EB, SC A. ManoharanOctober 2014 toDecember 2014
10. HG DR.T.P.Natesan March to May 2014
11. LU DR.T.P.Natesan March to May 2014
12. GEO DR.T.P.Natesan March to May 2014
13. NV Mr.Brijesh Kumar April 2014
*See below the expansion of Functional Areas
Functional AreaCode
Abbreviation of the Functional Areas
LU Land UseAP Air Pollution monitoring, Prevention and ControlAQ Meteorology, Air Quality Modeling & PredictionWP Water Pollution monitoring, Prevention and ControlEB Ecology and BiodiversityNV Noise and VibrationSE Socio-EconomicsHG Hydrology, Ground Water & Water ConservationGEO GeologySC Soil ConservationRH Risk Assessment and Hazards ManagementSHW Solid and Hazardous Waste Management
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6. EB,WPDr. RajkumarSamuel
March 2015
7. AQ Dr. J. R. Moses October 2014 to Till date
8. RH Dr. J. R .Moses October 2014 to Till date
9. SE, EB, SC A. ManoharanOctober 2014 toDecember 2014
10. HG DR.T.P.Natesan March to May 2014
11. LU DR.T.P.Natesan March to May 2014
12. GEO DR.T.P.Natesan March to May 2014
13. NV Mr.Brijesh Kumar April 2014
*See below the expansion of Functional Areas
Functional AreaCode
Abbreviation of the Functional Areas
LU Land UseAP Air Pollution monitoring, Prevention and ControlAQ Meteorology, Air Quality Modeling & PredictionWP Water Pollution monitoring, Prevention and ControlEB Ecology and BiodiversityNV Noise and VibrationSE Socio-EconomicsHG Hydrology, Ground Water & Water ConservationGEO GeologySC Soil ConservationRH Risk Assessment and Hazards ManagementSHW Solid and Hazardous Waste Management
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Project Mile StoneS.No Description Date
1 EC Application Submission 8.8.2013
2 ToR Issued 25.9.2013
3 Base Line Monitoring March to May 2014
4 ToR Extension Requested 24.9.2015 & 27.11.2015
5 One year Extension of Additional ToR
submission with Draft EIA Report
6.4.2016
6 Additional ToR Extension Requested 7.11.2016
7 Additional ToR request SEAC Meeting held 30.12.2016
8 Additional ToR Extension Letter Received 3.2.2017
9 Draft EIA Report Submitted 9.2. 2017
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Project Mile StoneS.No Description Date
1 EC Application Submission 8.8.2013
2 ToR Issued 25.9.2013
3 Base Line Monitoring March to May 2014
4 ToR Extension Requested 24.9.2015 & 27.11.2015
5 One year Extension of Additional ToR
submission with Draft EIA Report
6.4.2016
6 Additional ToR Extension Requested 7.11.2016
7 Additional ToR request SEAC Meeting held 30.12.2016
8 Additional ToR Extension Letter Received 3.2.2017
9 Draft EIA Report Submitted 9.2. 2017
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Project Mile StoneS.No Description Date
1 EC Application Submission 8.8.2013
2 ToR Issued 25.9.2013
3 Base Line Monitoring March to May 2014
4 ToR Extension Requested 24.9.2015 & 27.11.2015
5 One year Extension of Additional ToR
submission with Draft EIA Report
6.4.2016
6 Additional ToR Extension Requested 7.11.2016
7 Additional ToR request SEAC Meeting held 30.12.2016
8 Additional ToR Extension Letter Received 3.2.2017
9 Draft EIA Report Submitted 9.2. 2017
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Declaration by the Head of the Accredited Consultant Organization
I, Dr. J.R.MOSES hereby, confirm that the above mentioned experts prepared the EIA for
“Proposed Industrial Park at Rakamcherla” for Telangana State Industrial Infrastructure
Corporation LTD at Rakamcherla village Sy.no. 5/1 and Pudur village Sy. No’s. 243/1, 244/1,
245/1, 246/1, 247/1 & 248/1 of Pudur Mandal, Vikarabad District in the State of Telangana.
I also confirm that I shall be fully accountable for any misleading information mentioned in this
statement.
Signature:
Name: Dr. J.R MosesDesignation: CEOName of the EIA Consultant Organization: Hubert Enviro Care Systems Pvt. Ltd., ChennaiNABET Accredited Serial No. & Issue Date: 78, 6th Feb 2017.
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Declaration by the Head of the Accredited Consultant Organization
I, Dr. J.R.MOSES hereby, confirm that the above mentioned experts prepared the EIA for
“Proposed Industrial Park at Rakamcherla” for Telangana State Industrial Infrastructure
Corporation LTD at Rakamcherla village Sy.no. 5/1 and Pudur village Sy. No’s. 243/1, 244/1,
245/1, 246/1, 247/1 & 248/1 of Pudur Mandal, Vikarabad District in the State of Telangana.
I also confirm that I shall be fully accountable for any misleading information mentioned in this
statement.
Signature:
Name: Dr. J.R MosesDesignation: CEOName of the EIA Consultant Organization: Hubert Enviro Care Systems Pvt. Ltd., ChennaiNABET Accredited Serial No. & Issue Date: 78, 6th Feb 2017.
Rakamcherla IP - EIA
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Declaration by the Head of the Accredited Consultant Organization
I, Dr. J.R.MOSES hereby, confirm that the above mentioned experts prepared the EIA for
“Proposed Industrial Park at Rakamcherla” for Telangana State Industrial Infrastructure
Corporation LTD at Rakamcherla village Sy.no. 5/1 and Pudur village Sy. No’s. 243/1, 244/1,
245/1, 246/1, 247/1 & 248/1 of Pudur Mandal, Vikarabad District in the State of Telangana.
I also confirm that I shall be fully accountable for any misleading information mentioned in this
statement.
Signature:
Name: Dr. J.R MosesDesignation: CEOName of the EIA Consultant Organization: Hubert Enviro Care Systems Pvt. Ltd., ChennaiNABET Accredited Serial No. & Issue Date: 78, 6th Feb 2017.
Rakamcherla IP - EIA
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COMPLIANCE TO TERMS OF REFERENCE (TOR)
Rakamcherla IP - EIA
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COMPLIANCE TO TERMS OF REFERENCE (TOR)
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COMPLIANCE TO TERMS OF REFERENCE (TOR)
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Compliance to Terms of Reference (TOR)
S.No Terms of Reference TOR Compliance
1.Project Location and Layout
The project location details areexplained in chapter 2, 2.2, pg no. 17to 22.
2. A Recent satellite imagery of the project areaand its surroundings
The satellite image is given in Figureno. 2.3, Pg No.21.
3.Topo map and layout drawing of the project site.
The topo map is given in Fig No. 3-1A, pg no. 44.
4. Location of National Park/Wild life sanctuary/Reserve Forest within 10 km radius of theproject.
No wildlife or National park orReserve Forest present in 10KmRadius.
5.
Present land use and cropping pattern based onsatellite imagery for the study area of 10 kmradius.
The land use study for 15Km radiusis done and mentioned in chapter 3,3.9, 3.9.5, pg no. 77-79.
The Cropping pattern details arementioned in chapter 3, 3.12.1.7, Pgno. 98 – 99.
6.Contour map of the project site
The Contour map is given in Figure3.14.
7. Rain water Harvesting details Discussed in chapter 2, 2.8.5.
8.List of Industries Proposed
List of industries allotted list is givenin chapter 2, 2.7.
9. Details of water consumption and source ofwater supply, waste water generation, treatmentand effluent disposal with water Balance.
Water requirement details mentionedin chapter 2, 2.8, 2.8.2 Pg no. 29 to32.
10.Water Conservation measures proposed
Water Conservation detailsMentioned in chapter 7, 7.7. 2.
11.Power requirement & power back up
Power requirement detailsmentioned in chapter 2, 2.8, 2.8.1.
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Compliance to Terms of Reference (TOR)
S.No Terms of Reference TOR Compliance
1.Project Location and Layout
The project location details areexplained in chapter 2, 2.2, pg no. 17to 22.
2. A Recent satellite imagery of the project areaand its surroundings
The satellite image is given in Figureno. 2.3, Pg No.21.
3.Topo map and layout drawing of the project site.
The topo map is given in Fig No. 3-1A, pg no. 44.
4. Location of National Park/Wild life sanctuary/Reserve Forest within 10 km radius of theproject.
No wildlife or National park orReserve Forest present in 10KmRadius.
5.
Present land use and cropping pattern based onsatellite imagery for the study area of 10 kmradius.
The land use study for 15Km radiusis done and mentioned in chapter 3,3.9, 3.9.5, pg no. 77-79.
The Cropping pattern details arementioned in chapter 3, 3.12.1.7, Pgno. 98 – 99.
6.Contour map of the project site
The Contour map is given in Figure3.14.
7. Rain water Harvesting details Discussed in chapter 2, 2.8.5.
8.List of Industries Proposed
List of industries allotted list is givenin chapter 2, 2.7.
9. Details of water consumption and source ofwater supply, waste water generation, treatmentand effluent disposal with water Balance.
Water requirement details mentionedin chapter 2, 2.8, 2.8.2 Pg no. 29 to32.
10.Water Conservation measures proposed
Water Conservation detailsMentioned in chapter 7, 7.7. 2.
11.Power requirement & power back up
Power requirement detailsmentioned in chapter 2, 2.8, 2.8.1.
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Compliance to Terms of Reference (TOR)
S.No Terms of Reference TOR Compliance
1.Project Location and Layout
The project location details areexplained in chapter 2, 2.2, pg no. 17to 22.
2. A Recent satellite imagery of the project areaand its surroundings
The satellite image is given in Figureno. 2.3, Pg No.21.
3.Topo map and layout drawing of the project site.
The topo map is given in Fig No. 3-1A, pg no. 44.
4. Location of National Park/Wild life sanctuary/Reserve Forest within 10 km radius of theproject.
No wildlife or National park orReserve Forest present in 10KmRadius.
5.
Present land use and cropping pattern based onsatellite imagery for the study area of 10 kmradius.
The land use study for 15Km radiusis done and mentioned in chapter 3,3.9, 3.9.5, pg no. 77-79.
The Cropping pattern details arementioned in chapter 3, 3.12.1.7, Pgno. 98 – 99.
6.Contour map of the project site
The Contour map is given in Figure3.14.
7. Rain water Harvesting details Discussed in chapter 2, 2.8.5.
8.List of Industries Proposed
List of industries allotted list is givenin chapter 2, 2.7.
9. Details of water consumption and source ofwater supply, waste water generation, treatmentand effluent disposal with water Balance.
Water requirement details mentionedin chapter 2, 2.8, 2.8.2 Pg no. 29 to32.
10.Water Conservation measures proposed
Water Conservation detailsMentioned in chapter 7, 7.7. 2.
11.Power requirement & power back up
Power requirement detailsmentioned in chapter 2, 2.8, 2.8.1.
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12. Detailed solid waste generation, collection,segregation, its recycling and reuse, treatmentand disposal.
Solid waste details are calculatedbased on manpower and mentionedin chapter 2, 2.8, 2.8.4, Pg no. 33.
13.
Total cost of the project along with total capitalcost and recurring cost/annum for environmentalpollution control measures.
Capital cost given for environmentalpollution control measures isRs.79.85 Lakhs and the break updetails with recurring cost mentionedin chapter 7, 7.7.15, Table 7.3 pg no.183.
14. Site-specific micro-meteorological data fortemperature, relative humidity, hourly windspeed and direction and rainfall for one season atone location.
Discussed in chapter 3, 3.4, 3.5, Pgno. 38 to 43.
15. Ambient air quality monitoring locations within10 Km radius of study area as per the standardsdated 16 November, 2009 for one season at 10locations (Non Monsoon) taking into account thepre-dominant wind direction, population zoneand sensitive receptors.
Air quality monitoring detailsdiscussed in chapter 3, 3.6, pg no. 43- 51.
16.Determination of atmospheric inversion leveland assessment of ground level concentration ofpollutants. Air quality modeling for proposedproject.
The air dispersion modeling hasbeen analyzed and found thatpredicted GLC are well within thelimits as Mentioned in chapter 4,4.2, 4.2.2, Pg no.122-127.
17. Water monitoring including surface & groundwater at 10 locations within 10 Km radius ofstudy area (Non Monsoon).
Water analysis details discussed inchapter 3, 3.8, pg no. 56 - 62.
18. Soil sample analysis at 10 locations within thestudy area (Non Monsoon).
Soil analysis discussed in Chapter 3,3.10, Pg no. 73 to 78.
19. Noise Monitoring at 10 locations within thestudy area for one season (Non Monsoon).
Noise Monitoring discussed inchapter 3, 3.7, Pg no. 52 to 56.
20.Demography & Socio-economics of the studyarea.
Socio Economic studies have beengiven in chapter 3, 3.12, Pg no. 92 –112.
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12. Detailed solid waste generation, collection,segregation, its recycling and reuse, treatmentand disposal.
Solid waste details are calculatedbased on manpower and mentionedin chapter 2, 2.8, 2.8.4, Pg no. 33.
13.
Total cost of the project along with total capitalcost and recurring cost/annum for environmentalpollution control measures.
Capital cost given for environmentalpollution control measures isRs.79.85 Lakhs and the break updetails with recurring cost mentionedin chapter 7, 7.7.15, Table 7.3 pg no.183.
14. Site-specific micro-meteorological data fortemperature, relative humidity, hourly windspeed and direction and rainfall for one season atone location.
Discussed in chapter 3, 3.4, 3.5, Pgno. 38 to 43.
15. Ambient air quality monitoring locations within10 Km radius of study area as per the standardsdated 16 November, 2009 for one season at 10locations (Non Monsoon) taking into account thepre-dominant wind direction, population zoneand sensitive receptors.
Air quality monitoring detailsdiscussed in chapter 3, 3.6, pg no. 43- 51.
16.Determination of atmospheric inversion leveland assessment of ground level concentration ofpollutants. Air quality modeling for proposedproject.
The air dispersion modeling hasbeen analyzed and found thatpredicted GLC are well within thelimits as Mentioned in chapter 4,4.2, 4.2.2, Pg no.122-127.
17. Water monitoring including surface & groundwater at 10 locations within 10 Km radius ofstudy area (Non Monsoon).
Water analysis details discussed inchapter 3, 3.8, pg no. 56 - 62.
18. Soil sample analysis at 10 locations within thestudy area (Non Monsoon).
Soil analysis discussed in Chapter 3,3.10, Pg no. 73 to 78.
19. Noise Monitoring at 10 locations within thestudy area for one season (Non Monsoon).
Noise Monitoring discussed inchapter 3, 3.7, Pg no. 52 to 56.
20.Demography & Socio-economics of the studyarea.
Socio Economic studies have beengiven in chapter 3, 3.12, Pg no. 92 –112.
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12. Detailed solid waste generation, collection,segregation, its recycling and reuse, treatmentand disposal.
Solid waste details are calculatedbased on manpower and mentionedin chapter 2, 2.8, 2.8.4, Pg no. 33.
13.
Total cost of the project along with total capitalcost and recurring cost/annum for environmentalpollution control measures.
Capital cost given for environmentalpollution control measures isRs.79.85 Lakhs and the break updetails with recurring cost mentionedin chapter 7, 7.7.15, Table 7.3 pg no.183.
14. Site-specific micro-meteorological data fortemperature, relative humidity, hourly windspeed and direction and rainfall for one season atone location.
Discussed in chapter 3, 3.4, 3.5, Pgno. 38 to 43.
15. Ambient air quality monitoring locations within10 Km radius of study area as per the standardsdated 16 November, 2009 for one season at 10locations (Non Monsoon) taking into account thepre-dominant wind direction, population zoneand sensitive receptors.
Air quality monitoring detailsdiscussed in chapter 3, 3.6, pg no. 43- 51.
16.Determination of atmospheric inversion leveland assessment of ground level concentration ofpollutants. Air quality modeling for proposedproject.
The air dispersion modeling hasbeen analyzed and found thatpredicted GLC are well within thelimits as Mentioned in chapter 4,4.2, 4.2.2, Pg no.122-127.
17. Water monitoring including surface & groundwater at 10 locations within 10 Km radius ofstudy area (Non Monsoon).
Water analysis details discussed inchapter 3, 3.8, pg no. 56 - 62.
18. Soil sample analysis at 10 locations within thestudy area (Non Monsoon).
Soil analysis discussed in Chapter 3,3.10, Pg no. 73 to 78.
19. Noise Monitoring at 10 locations within thestudy area for one season (Non Monsoon).
Noise Monitoring discussed inchapter 3, 3.7, Pg no. 52 to 56.
20.Demography & Socio-economics of the studyarea.
Socio Economic studies have beengiven in chapter 3, 3.12, Pg no. 92 –112.
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21.Ecological features (Terrestrial & Aquatic) of thestudy area.
The study has been done andenclosed in chapter 3, 3.11, Pg No.79-92.
22.Assessment of impact on air, water, soil, solid/Hazardous waste and noise levels.
The detail study has been done andmentioned in chapter 4, 4.3, Pg No.131- 136.
23. Air pollution control measures proposed for theeffective control of gaseous emissions withinpermissible limits.
Individual industries will install airpollution control measures as pernorms.
24. Risk assessment including Hazard identification,Consequence Analysis, Risk Assessment andpreparation of Disaster Management Plan.
Risk assessment and other detailsmentioned in Chapter 8, Pg no. 185.
25.Details of proposed Occupational HealthSurveillance program for the employees andother labour.
Occupational health surveillancewill be conducted to employees byindividual industries which arediscussed in EMP chapter 7, 7.7.10,Pg no. 175.
26. Detailed Environment management Plan (EMP)with specific reference to Energy conservationand natural resource conservation, details of airpollution control system, water & wastewatermanagement, monitoring frequency,responsibility and time bound implementationplan for mitigation measure will be provided.
EMP is enclosed in chapter 7.
Additional ToR
27. Type and number of industries proposed to beaccommodated
Details are provided in section 2.7,2.7.1, Chapter 2. Proposed Industriesare listed in Table 2.4
28. Undertaking that the projects other thanCategory ‘A’ projects will be accommodated inthe proposed Industrial Park.
Only 7 industries have been allottedso far in the proposed industrial area,namely,
Binjusaria Metal Box Com.
Anil Re-Rolling Mills
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21.Ecological features (Terrestrial & Aquatic) of thestudy area.
The study has been done andenclosed in chapter 3, 3.11, Pg No.79-92.
22.Assessment of impact on air, water, soil, solid/Hazardous waste and noise levels.
The detail study has been done andmentioned in chapter 4, 4.3, Pg No.131- 136.
23. Air pollution control measures proposed for theeffective control of gaseous emissions withinpermissible limits.
Individual industries will install airpollution control measures as pernorms.
24. Risk assessment including Hazard identification,Consequence Analysis, Risk Assessment andpreparation of Disaster Management Plan.
Risk assessment and other detailsmentioned in Chapter 8, Pg no. 185.
25.Details of proposed Occupational HealthSurveillance program for the employees andother labour.
Occupational health surveillancewill be conducted to employees byindividual industries which arediscussed in EMP chapter 7, 7.7.10,Pg no. 175.
26. Detailed Environment management Plan (EMP)with specific reference to Energy conservationand natural resource conservation, details of airpollution control system, water & wastewatermanagement, monitoring frequency,responsibility and time bound implementationplan for mitigation measure will be provided.
EMP is enclosed in chapter 7.
Additional ToR
27. Type and number of industries proposed to beaccommodated
Details are provided in section 2.7,2.7.1, Chapter 2. Proposed Industriesare listed in Table 2.4
28. Undertaking that the projects other thanCategory ‘A’ projects will be accommodated inthe proposed Industrial Park.
Only 7 industries have been allottedso far in the proposed industrial area,namely,
Binjusaria Metal Box Com.
Anil Re-Rolling Mills
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21.Ecological features (Terrestrial & Aquatic) of thestudy area.
The study has been done andenclosed in chapter 3, 3.11, Pg No.79-92.
22.Assessment of impact on air, water, soil, solid/Hazardous waste and noise levels.
The detail study has been done andmentioned in chapter 4, 4.3, Pg No.131- 136.
23. Air pollution control measures proposed for theeffective control of gaseous emissions withinpermissible limits.
Individual industries will install airpollution control measures as pernorms.
24. Risk assessment including Hazard identification,Consequence Analysis, Risk Assessment andpreparation of Disaster Management Plan.
Risk assessment and other detailsmentioned in Chapter 8, Pg no. 185.
25.Details of proposed Occupational HealthSurveillance program for the employees andother labour.
Occupational health surveillancewill be conducted to employees byindividual industries which arediscussed in EMP chapter 7, 7.7.10,Pg no. 175.
26. Detailed Environment management Plan (EMP)with specific reference to Energy conservationand natural resource conservation, details of airpollution control system, water & wastewatermanagement, monitoring frequency,responsibility and time bound implementationplan for mitigation measure will be provided.
EMP is enclosed in chapter 7.
Additional ToR
27. Type and number of industries proposed to beaccommodated
Details are provided in section 2.7,2.7.1, Chapter 2. Proposed Industriesare listed in Table 2.4
28. Undertaking that the projects other thanCategory ‘A’ projects will be accommodated inthe proposed Industrial Park.
Only 7 industries have been allottedso far in the proposed industrial area,namely,
Binjusaria Metal Box Com.
Anil Re-Rolling Mills
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Garg Steels
Arun Ispat Udyog
Neha Steels
All are steel Re-rolling industriesand will be coming under CategoryB.
Gujarat Enviro Protection &Infrastructure Ltd
M.N. Industries
As required by Additional ToRUndertaking the projects Other than“A” Category industries will beallotted in the Industrial Park.
29. Proposal for development of Green belt in anarea of 33% of total area.
It is proposed to develop greenbelt inminimum 33% of total site area inwhich 14.94% of open space areaused for greenbelt and the remaininggreen belt area will be maintained byindividual industries.
Detailed at sections 2.7.3, Chapter 2.
Additional Information
30. Layout Copy with Sy. Nos. The Layout with Survey numbersenclosed as Annexure 17
31. Over lapping layouts showing the previouslayout area and new layout area
The Superimposed Layout (Revised& old) enclosed as Annexure 14
32. Revenue sketch of the land acquired for thepurpose of approach road
Approach road Revenue Sketchenclosed as Annexure 15.
33. Panchanama of the land acquired for the purposeof approach road
Panchanama of the land acquiredenclosed as Annexure 16.
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Garg Steels
Arun Ispat Udyog
Neha Steels
All are steel Re-rolling industriesand will be coming under CategoryB.
Gujarat Enviro Protection &Infrastructure Ltd
M.N. Industries
As required by Additional ToRUndertaking the projects Other than“A” Category industries will beallotted in the Industrial Park.
29. Proposal for development of Green belt in anarea of 33% of total area.
It is proposed to develop greenbelt inminimum 33% of total site area inwhich 14.94% of open space areaused for greenbelt and the remaininggreen belt area will be maintained byindividual industries.
Detailed at sections 2.7.3, Chapter 2.
Additional Information
30. Layout Copy with Sy. Nos. The Layout with Survey numbersenclosed as Annexure 17
31. Over lapping layouts showing the previouslayout area and new layout area
The Superimposed Layout (Revised& old) enclosed as Annexure 14
32. Revenue sketch of the land acquired for thepurpose of approach road
Approach road Revenue Sketchenclosed as Annexure 15.
33. Panchanama of the land acquired for the purposeof approach road
Panchanama of the land acquiredenclosed as Annexure 16.
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Garg Steels
Arun Ispat Udyog
Neha Steels
All are steel Re-rolling industriesand will be coming under CategoryB.
Gujarat Enviro Protection &Infrastructure Ltd
M.N. Industries
As required by Additional ToRUndertaking the projects Other than“A” Category industries will beallotted in the Industrial Park.
29. Proposal for development of Green belt in anarea of 33% of total area.
It is proposed to develop greenbelt inminimum 33% of total site area inwhich 14.94% of open space areaused for greenbelt and the remaininggreen belt area will be maintained byindividual industries.
Detailed at sections 2.7.3, Chapter 2.
Additional Information
30. Layout Copy with Sy. Nos. The Layout with Survey numbersenclosed as Annexure 17
31. Over lapping layouts showing the previouslayout area and new layout area
The Superimposed Layout (Revised& old) enclosed as Annexure 14
32. Revenue sketch of the land acquired for thepurpose of approach road
Approach road Revenue Sketchenclosed as Annexure 15.
33. Panchanama of the land acquired for the purposeof approach road
Panchanama of the land acquiredenclosed as Annexure 16.
Rakamcherla IP - EIA Introduction
1
Chapter 1
Introduction
Rakamcherla IP - EIA Introduction
1
Chapter 1
Introduction
Rakamcherla IP - EIA Introduction
1
Chapter 1
Introduction
Rakamcherla IP - EIA Introduction
2
1 Introduction
1.1 Purpose of the Report
Telangana State Industrial Infrastructure Corporation Limited (TSIIC) proposes to develop an
Industrial Park at Sy.No 5/1 of Rakamcherla village and Sy. Nos. 243/1, 244/1, 245/1, 246/1, 247/1
& 248/1 of Pudur Village, Pudur Mandal, Vikarabad District in the State of Telangana. The total
area for development is 112.48 Acres (45.52 Ha) proposed with related infrastructure, including
green belt, access road, internal roads, storm water drains, water supply and power supply.
The proposed site is strategically situated adjacent to the SH-4 connecting Manneguda and Pargi.
The site is furthermore situated at 12 Km Northwest of Rangareddy – Wadi junction main line.
Currently the project land is predominantly barren, the site is relatively flat on the northern side
with a gradient on the southern side and far away from densely populated human settlements, and
therefore the property has been identified as land suitable for Industrial Development. The purpose
of this project is to promote industrial activity in the region to meet a growing demand in the
services sector, and to enhance future economic growth within the region. The proposed Industrial
Park will accommodate the relocation of Steel rerolling mills. The sub region surrounding the site is
undergoing significant change in recent year as a result of both commercial and industrial activity.
1.2 Project Proponent
Telangana State Industrial Infrastructure Corporation’s Limited (TSIIC), formerly Andhra Pradesh
Industrial Infrastructure Corporation Limited (APIIC) before the bifurcation of the Andhra Pradesh
State, was formed in 1973 by the GO No: 831 dated 10th Sep 1973 issued by Government of
Andhra Pradesh headquartered at 6th Floor, Parisrama Bhavan, Fateh Maidan Road, Basheerbagh,
Hyderabad – 500 004, Telangana, India. TSIIC is an autonomous premier organization in the State,
vested with the objective of providing Industrial Infrastructure through Development of Industrial
Parks and Special Economic Zones. The Industrial Parks and Special Economic Zones are playing
a pivotal role, in attracting investments to the State both domestic & foreign by providing multiple
incentives. TSIIC is spread over in all districts of Telangana having 6 Zonal Offices. The major
responsibility of TSIIC is to promote and undertake infrastructure development in its Industrial
parks and take up regular maintenance. TSIIC is also delegated with Local Authority Powers under
Panchayat Raj & Municipal Act by the Government of Telangana.
Rakamcherla IP - EIA Introduction
2
1 Introduction
1.1 Purpose of the Report
Telangana State Industrial Infrastructure Corporation Limited (TSIIC) proposes to develop an
Industrial Park at Sy.No 5/1 of Rakamcherla village and Sy. Nos. 243/1, 244/1, 245/1, 246/1, 247/1
& 248/1 of Pudur Village, Pudur Mandal, Vikarabad District in the State of Telangana. The total
area for development is 112.48 Acres (45.52 Ha) proposed with related infrastructure, including
green belt, access road, internal roads, storm water drains, water supply and power supply.
The proposed site is strategically situated adjacent to the SH-4 connecting Manneguda and Pargi.
The site is furthermore situated at 12 Km Northwest of Rangareddy – Wadi junction main line.
Currently the project land is predominantly barren, the site is relatively flat on the northern side
with a gradient on the southern side and far away from densely populated human settlements, and
therefore the property has been identified as land suitable for Industrial Development. The purpose
of this project is to promote industrial activity in the region to meet a growing demand in the
services sector, and to enhance future economic growth within the region. The proposed Industrial
Park will accommodate the relocation of Steel rerolling mills. The sub region surrounding the site is
undergoing significant change in recent year as a result of both commercial and industrial activity.
1.2 Project Proponent
Telangana State Industrial Infrastructure Corporation’s Limited (TSIIC), formerly Andhra Pradesh
Industrial Infrastructure Corporation Limited (APIIC) before the bifurcation of the Andhra Pradesh
State, was formed in 1973 by the GO No: 831 dated 10th Sep 1973 issued by Government of
Andhra Pradesh headquartered at 6th Floor, Parisrama Bhavan, Fateh Maidan Road, Basheerbagh,
Hyderabad – 500 004, Telangana, India. TSIIC is an autonomous premier organization in the State,
vested with the objective of providing Industrial Infrastructure through Development of Industrial
Parks and Special Economic Zones. The Industrial Parks and Special Economic Zones are playing
a pivotal role, in attracting investments to the State both domestic & foreign by providing multiple
incentives. TSIIC is spread over in all districts of Telangana having 6 Zonal Offices. The major
responsibility of TSIIC is to promote and undertake infrastructure development in its Industrial
parks and take up regular maintenance. TSIIC is also delegated with Local Authority Powers under
Panchayat Raj & Municipal Act by the Government of Telangana.
Rakamcherla IP - EIA Introduction
2
1 Introduction
1.1 Purpose of the Report
Telangana State Industrial Infrastructure Corporation Limited (TSIIC) proposes to develop an
Industrial Park at Sy.No 5/1 of Rakamcherla village and Sy. Nos. 243/1, 244/1, 245/1, 246/1, 247/1
& 248/1 of Pudur Village, Pudur Mandal, Vikarabad District in the State of Telangana. The total
area for development is 112.48 Acres (45.52 Ha) proposed with related infrastructure, including
green belt, access road, internal roads, storm water drains, water supply and power supply.
The proposed site is strategically situated adjacent to the SH-4 connecting Manneguda and Pargi.
The site is furthermore situated at 12 Km Northwest of Rangareddy – Wadi junction main line.
Currently the project land is predominantly barren, the site is relatively flat on the northern side
with a gradient on the southern side and far away from densely populated human settlements, and
therefore the property has been identified as land suitable for Industrial Development. The purpose
of this project is to promote industrial activity in the region to meet a growing demand in the
services sector, and to enhance future economic growth within the region. The proposed Industrial
Park will accommodate the relocation of Steel rerolling mills. The sub region surrounding the site is
undergoing significant change in recent year as a result of both commercial and industrial activity.
1.2 Project Proponent
Telangana State Industrial Infrastructure Corporation’s Limited (TSIIC), formerly Andhra Pradesh
Industrial Infrastructure Corporation Limited (APIIC) before the bifurcation of the Andhra Pradesh
State, was formed in 1973 by the GO No: 831 dated 10th Sep 1973 issued by Government of
Andhra Pradesh headquartered at 6th Floor, Parisrama Bhavan, Fateh Maidan Road, Basheerbagh,
Hyderabad – 500 004, Telangana, India. TSIIC is an autonomous premier organization in the State,
vested with the objective of providing Industrial Infrastructure through Development of Industrial
Parks and Special Economic Zones. The Industrial Parks and Special Economic Zones are playing
a pivotal role, in attracting investments to the State both domestic & foreign by providing multiple
incentives. TSIIC is spread over in all districts of Telangana having 6 Zonal Offices. The major
responsibility of TSIIC is to promote and undertake infrastructure development in its Industrial
parks and take up regular maintenance. TSIIC is also delegated with Local Authority Powers under
Panchayat Raj & Municipal Act by the Government of Telangana.
Rakamcherla IP - EIA Introduction
3
1.3 EIA Requirement
The Government of India (GOI), Ministry of Environment and Forests & Climate Change (MoEF
& CC), New Delhi, vide Notification No. S.O. 1533 dated 14th September, 2006 (subsequently
amended by S.O. 3067(E) dated 01-12-2009), has made it mandatory to obtain ‘Prior
Environmental Clearance’ for projects or activities within the schedule of that notification from
MoEF & CC (for Category A projects) or from SEIAA (for Category B projects). The proposed
project of Industrial park is classified as Category B, Industrial Estate, <500 Ha falls under schedule
No. 7(C) of the said Notification. As this proposed project is a category B project, requisite
application in prescribed Form-1 was submitted to SEIAA, Telangana. Based on the information
furnished and presentation done before the State Expert Appraisal Committee (SEAC) and after
giving due consideration to various aspects of the project, scoping of the project was done by SEAC
and Terms of Reference (TOR) were assigned for the EIA study. With a view to evaluate likely
impacts on various components of the environment because of the proposed project, TSIIC took
service of Hubert Enviro Care System Pvt. Ltd, Chennai for preparation of Environmental Impact
Assessment Report.
This report will give information about baseline data collected to identify, quantify, predict and
assess impacts on various environmental components like air, water, noise, land etc. for the months
of March, April & May 2014. In line with the requirements of the Environment protection act 1986
as amended in 1991, and the rules there under, this EIA Report provides a detailed description of
the predevelopment environment, specifically in terms of the biophysical and socio-economic
environment of the study area. Furthermore, the report provides a comprehensive description of the
activities as well as numerous specialist studies undertaken for the EIA Phase and Public
Participation Process (PPP), as well as the way forward in the form of conclusions,
recommendations and a draft Environmental Management Plan. To ensure the completeness of the
EIA and Draft EMP, specialists surveyed the area to identify the potential impacts of the project on
the area.
The EIA of the project activities was determined by identifying the environmental aspects and then
undertaking an environmental risk assessment to determine the significant environmental aspects.
The environmental impact assessment has included all phases of the project namely the
construction phase and operational phase. The rating system is applied to the potential impact on
Rakamcherla IP - EIA Introduction
3
1.3 EIA Requirement
The Government of India (GOI), Ministry of Environment and Forests & Climate Change (MoEF
& CC), New Delhi, vide Notification No. S.O. 1533 dated 14th September, 2006 (subsequently
amended by S.O. 3067(E) dated 01-12-2009), has made it mandatory to obtain ‘Prior
Environmental Clearance’ for projects or activities within the schedule of that notification from
MoEF & CC (for Category A projects) or from SEIAA (for Category B projects). The proposed
project of Industrial park is classified as Category B, Industrial Estate, <500 Ha falls under schedule
No. 7(C) of the said Notification. As this proposed project is a category B project, requisite
application in prescribed Form-1 was submitted to SEIAA, Telangana. Based on the information
furnished and presentation done before the State Expert Appraisal Committee (SEAC) and after
giving due consideration to various aspects of the project, scoping of the project was done by SEAC
and Terms of Reference (TOR) were assigned for the EIA study. With a view to evaluate likely
impacts on various components of the environment because of the proposed project, TSIIC took
service of Hubert Enviro Care System Pvt. Ltd, Chennai for preparation of Environmental Impact
Assessment Report.
This report will give information about baseline data collected to identify, quantify, predict and
assess impacts on various environmental components like air, water, noise, land etc. for the months
of March, April & May 2014. In line with the requirements of the Environment protection act 1986
as amended in 1991, and the rules there under, this EIA Report provides a detailed description of
the predevelopment environment, specifically in terms of the biophysical and socio-economic
environment of the study area. Furthermore, the report provides a comprehensive description of the
activities as well as numerous specialist studies undertaken for the EIA Phase and Public
Participation Process (PPP), as well as the way forward in the form of conclusions,
recommendations and a draft Environmental Management Plan. To ensure the completeness of the
EIA and Draft EMP, specialists surveyed the area to identify the potential impacts of the project on
the area.
The EIA of the project activities was determined by identifying the environmental aspects and then
undertaking an environmental risk assessment to determine the significant environmental aspects.
The environmental impact assessment has included all phases of the project namely the
construction phase and operational phase. The rating system is applied to the potential impact on
Rakamcherla IP - EIA Introduction
3
1.3 EIA Requirement
The Government of India (GOI), Ministry of Environment and Forests & Climate Change (MoEF
& CC), New Delhi, vide Notification No. S.O. 1533 dated 14th September, 2006 (subsequently
amended by S.O. 3067(E) dated 01-12-2009), has made it mandatory to obtain ‘Prior
Environmental Clearance’ for projects or activities within the schedule of that notification from
MoEF & CC (for Category A projects) or from SEIAA (for Category B projects). The proposed
project of Industrial park is classified as Category B, Industrial Estate, <500 Ha falls under schedule
No. 7(C) of the said Notification. As this proposed project is a category B project, requisite
application in prescribed Form-1 was submitted to SEIAA, Telangana. Based on the information
furnished and presentation done before the State Expert Appraisal Committee (SEAC) and after
giving due consideration to various aspects of the project, scoping of the project was done by SEAC
and Terms of Reference (TOR) were assigned for the EIA study. With a view to evaluate likely
impacts on various components of the environment because of the proposed project, TSIIC took
service of Hubert Enviro Care System Pvt. Ltd, Chennai for preparation of Environmental Impact
Assessment Report.
This report will give information about baseline data collected to identify, quantify, predict and
assess impacts on various environmental components like air, water, noise, land etc. for the months
of March, April & May 2014. In line with the requirements of the Environment protection act 1986
as amended in 1991, and the rules there under, this EIA Report provides a detailed description of
the predevelopment environment, specifically in terms of the biophysical and socio-economic
environment of the study area. Furthermore, the report provides a comprehensive description of the
activities as well as numerous specialist studies undertaken for the EIA Phase and Public
Participation Process (PPP), as well as the way forward in the form of conclusions,
recommendations and a draft Environmental Management Plan. To ensure the completeness of the
EIA and Draft EMP, specialists surveyed the area to identify the potential impacts of the project on
the area.
The EIA of the project activities was determined by identifying the environmental aspects and then
undertaking an environmental risk assessment to determine the significant environmental aspects.
The environmental impact assessment has included all phases of the project namely the
construction phase and operational phase. The rating system is applied to the potential impact on
Rakamcherla IP - EIA Introduction
4
the receiving environment and includes an objective evaluation of the mitigation of the impact.
During the EIA, the impact of the Industrial park Development on the biophysical and social
environments was assessed. From the assessment, it was determined which parts of the two
environments will be more significantly affected as compared to others. It was this assessment that
allowed the EAP to make an informed analysis & opinion of the proposed development.
With a view to evaluate likely impacts due to the proposed projects on various component of the
environment and propose appropriate management and monitoring plan, TSIIC took services of
NABET Accredited Consultant, Hubert Enviro Care System Pvt. Ltd.
1.4 Rationale of the Study
The development of steel rerolling industries within the Rakamcherla Industrial Park should be
done in such a way that the water resources, biodiversity, health of the local people and visitors will
not get affected. However, on the reverse side, these same industries will become an important
source of revenue for the local people. The adverse impacts caused by industrial expansion within
the zone needs to be identified and assessed to protect the biodiversity of the region by promoting
the sustainable development of the surrounding communities in a deliberate and tactful way.
Furthermore, environmental pollution by the emerging industries around the industrial park needs
to be assessed. In order to assess the situation, comprehensive information about the proposed
industries; multi-dimensional impacts expected by the industries; land use planning for the
promotion of livelihoods of the locals using non-carbon emissions sources of income generation;
and preservation of cultural values of the Pudur Mandal need to be integrated into the conservation
and development plan of the region in order to reduce the environmental degradation.
In this regard, as per the Environment protection act 1986 as amended in 1991, and the rules there
under an Environmental Impact Assessment (EIA) is mandatory for the protection, conservation
and sustainable management of the environment.
The scope of the work mentioned includes an assessment study of proposed industries and their
impact on the region. This study puts forward the most effective ways to protect the environment
from increasing pollution caused by the burgeoning industrial development and recommendations
for environmental-friendly development initiatives in the region.
Rakamcherla IP - EIA Introduction
4
the receiving environment and includes an objective evaluation of the mitigation of the impact.
During the EIA, the impact of the Industrial park Development on the biophysical and social
environments was assessed. From the assessment, it was determined which parts of the two
environments will be more significantly affected as compared to others. It was this assessment that
allowed the EAP to make an informed analysis & opinion of the proposed development.
With a view to evaluate likely impacts due to the proposed projects on various component of the
environment and propose appropriate management and monitoring plan, TSIIC took services of
NABET Accredited Consultant, Hubert Enviro Care System Pvt. Ltd.
1.4 Rationale of the Study
The development of steel rerolling industries within the Rakamcherla Industrial Park should be
done in such a way that the water resources, biodiversity, health of the local people and visitors will
not get affected. However, on the reverse side, these same industries will become an important
source of revenue for the local people. The adverse impacts caused by industrial expansion within
the zone needs to be identified and assessed to protect the biodiversity of the region by promoting
the sustainable development of the surrounding communities in a deliberate and tactful way.
Furthermore, environmental pollution by the emerging industries around the industrial park needs
to be assessed. In order to assess the situation, comprehensive information about the proposed
industries; multi-dimensional impacts expected by the industries; land use planning for the
promotion of livelihoods of the locals using non-carbon emissions sources of income generation;
and preservation of cultural values of the Pudur Mandal need to be integrated into the conservation
and development plan of the region in order to reduce the environmental degradation.
In this regard, as per the Environment protection act 1986 as amended in 1991, and the rules there
under an Environmental Impact Assessment (EIA) is mandatory for the protection, conservation
and sustainable management of the environment.
The scope of the work mentioned includes an assessment study of proposed industries and their
impact on the region. This study puts forward the most effective ways to protect the environment
from increasing pollution caused by the burgeoning industrial development and recommendations
for environmental-friendly development initiatives in the region.
Rakamcherla IP - EIA Introduction
4
the receiving environment and includes an objective evaluation of the mitigation of the impact.
During the EIA, the impact of the Industrial park Development on the biophysical and social
environments was assessed. From the assessment, it was determined which parts of the two
environments will be more significantly affected as compared to others. It was this assessment that
allowed the EAP to make an informed analysis & opinion of the proposed development.
With a view to evaluate likely impacts due to the proposed projects on various component of the
environment and propose appropriate management and monitoring plan, TSIIC took services of
NABET Accredited Consultant, Hubert Enviro Care System Pvt. Ltd.
1.4 Rationale of the Study
The development of steel rerolling industries within the Rakamcherla Industrial Park should be
done in such a way that the water resources, biodiversity, health of the local people and visitors will
not get affected. However, on the reverse side, these same industries will become an important
source of revenue for the local people. The adverse impacts caused by industrial expansion within
the zone needs to be identified and assessed to protect the biodiversity of the region by promoting
the sustainable development of the surrounding communities in a deliberate and tactful way.
Furthermore, environmental pollution by the emerging industries around the industrial park needs
to be assessed. In order to assess the situation, comprehensive information about the proposed
industries; multi-dimensional impacts expected by the industries; land use planning for the
promotion of livelihoods of the locals using non-carbon emissions sources of income generation;
and preservation of cultural values of the Pudur Mandal need to be integrated into the conservation
and development plan of the region in order to reduce the environmental degradation.
In this regard, as per the Environment protection act 1986 as amended in 1991, and the rules there
under an Environmental Impact Assessment (EIA) is mandatory for the protection, conservation
and sustainable management of the environment.
The scope of the work mentioned includes an assessment study of proposed industries and their
impact on the region. This study puts forward the most effective ways to protect the environment
from increasing pollution caused by the burgeoning industrial development and recommendations
for environmental-friendly development initiatives in the region.
Rakamcherla IP - EIA Introduction
5
1.5 Applicability of Environmental Clearance
The Proposed activity attracts EC under sector 7c (B) of the EIA Notification 14th September, 2006
and its amendments there off.
The application for Environmental Clearance (EC) was submitted to Andhra Pradesh SEIAA
(before bifurcation of Andhra Pradesh and Telangana) on 8th August 2013 and the proposal was
taken up in the SEAC meeting held on 27th August, 2013 and the Terms of Reference (TOR) for the
project was given vide Letter no. SEIAA/AP/RRD/2012-3812 dated 25.09.2013 and the same is
enclosed in Annexure -1. Further due to changes in the area and survey nos., change in the layout
of the Industrial park and for extension of ToR, the project was again taken up in 11th SEAC
Meeting held on 10.12.2015 and the changes in the survey nos., change in the layout were accepted
by SEAC on and the validity of ToR was extended for one more year and the same is enclosed in
Annexure 2. The project was again taken up in 23rd SEAC Meeting held on 30.12.2016, and the
additional ToR Extension was accepted by SEAC and the validity of ToR will be extended for One
more year. The copy of Minutes of meeting is enclosed in Annexure-18. The EIA report is based
on the Terms of Reference issued by SEIAA, Telangana.
The Industrial Park is proposed only for category B & Other non-polluting/low pollution potential
industrial activities. All industries Proposed inside the Industrial Park will obtain EC & other
applicable permissions under application statutes from competent authorities.
Applicable Regulatory Framework
The following are applicable Acts and Rules related to the proposed project:
The Environment Protection Act - 1986
EIA Notification 2006 and its amendments
Water (Prevention and Control of Pollution) Act,1974and its amendments
Air (Prevention and Control of Pollution) Act,1981and its amendments
The National Environment Appellate Authority Act (NEAA) 1997
The Land Acquisition Act 1894 & 1989
The Noise Pollution (Regulation and Control) Act 1990
Central Motor Vehicle Act, 1988
Hazardous Waste (Management and Handling) Rules, 1989 amended 2000 and 2003
Rakamcherla IP - EIA Introduction
5
1.5 Applicability of Environmental Clearance
The Proposed activity attracts EC under sector 7c (B) of the EIA Notification 14th September, 2006
and its amendments there off.
The application for Environmental Clearance (EC) was submitted to Andhra Pradesh SEIAA
(before bifurcation of Andhra Pradesh and Telangana) on 8th August 2013 and the proposal was
taken up in the SEAC meeting held on 27th August, 2013 and the Terms of Reference (TOR) for the
project was given vide Letter no. SEIAA/AP/RRD/2012-3812 dated 25.09.2013 and the same is
enclosed in Annexure -1. Further due to changes in the area and survey nos., change in the layout
of the Industrial park and for extension of ToR, the project was again taken up in 11th SEAC
Meeting held on 10.12.2015 and the changes in the survey nos., change in the layout were accepted
by SEAC on and the validity of ToR was extended for one more year and the same is enclosed in
Annexure 2. The project was again taken up in 23rd SEAC Meeting held on 30.12.2016, and the
additional ToR Extension was accepted by SEAC and the validity of ToR will be extended for One
more year. The copy of Minutes of meeting is enclosed in Annexure-18. The EIA report is based
on the Terms of Reference issued by SEIAA, Telangana.
The Industrial Park is proposed only for category B & Other non-polluting/low pollution potential
industrial activities. All industries Proposed inside the Industrial Park will obtain EC & other
applicable permissions under application statutes from competent authorities.
Applicable Regulatory Framework
The following are applicable Acts and Rules related to the proposed project:
The Environment Protection Act - 1986
EIA Notification 2006 and its amendments
Water (Prevention and Control of Pollution) Act,1974and its amendments
Air (Prevention and Control of Pollution) Act,1981and its amendments
The National Environment Appellate Authority Act (NEAA) 1997
The Land Acquisition Act 1894 & 1989
The Noise Pollution (Regulation and Control) Act 1990
Central Motor Vehicle Act, 1988
Hazardous Waste (Management and Handling) Rules, 1989 amended 2000 and 2003
Rakamcherla IP - EIA Introduction
5
1.5 Applicability of Environmental Clearance
The Proposed activity attracts EC under sector 7c (B) of the EIA Notification 14th September, 2006
and its amendments there off.
The application for Environmental Clearance (EC) was submitted to Andhra Pradesh SEIAA
(before bifurcation of Andhra Pradesh and Telangana) on 8th August 2013 and the proposal was
taken up in the SEAC meeting held on 27th August, 2013 and the Terms of Reference (TOR) for the
project was given vide Letter no. SEIAA/AP/RRD/2012-3812 dated 25.09.2013 and the same is
enclosed in Annexure -1. Further due to changes in the area and survey nos., change in the layout
of the Industrial park and for extension of ToR, the project was again taken up in 11th SEAC
Meeting held on 10.12.2015 and the changes in the survey nos., change in the layout were accepted
by SEAC on and the validity of ToR was extended for one more year and the same is enclosed in
Annexure 2. The project was again taken up in 23rd SEAC Meeting held on 30.12.2016, and the
additional ToR Extension was accepted by SEAC and the validity of ToR will be extended for One
more year. The copy of Minutes of meeting is enclosed in Annexure-18. The EIA report is based
on the Terms of Reference issued by SEIAA, Telangana.
The Industrial Park is proposed only for category B & Other non-polluting/low pollution potential
industrial activities. All industries Proposed inside the Industrial Park will obtain EC & other
applicable permissions under application statutes from competent authorities.
Applicable Regulatory Framework
The following are applicable Acts and Rules related to the proposed project:
The Environment Protection Act - 1986
EIA Notification 2006 and its amendments
Water (Prevention and Control of Pollution) Act,1974and its amendments
Air (Prevention and Control of Pollution) Act,1981and its amendments
The National Environment Appellate Authority Act (NEAA) 1997
The Land Acquisition Act 1894 & 1989
The Noise Pollution (Regulation and Control) Act 1990
Central Motor Vehicle Act, 1988
Hazardous Waste (Management and Handling) Rules, 1989 amended 2000 and 2003
Rakamcherla IP - EIA Introduction
6
Manufacture Storage and Import of Hazardous Chemicals Rules, 1989 amended 2000
Chemical Accidents (Emergency Planning, Preparedness and Response) Rules, 1996
Batteries (Management and Handling) Rules, 2001.
The Public Liability Insurance Act, 1991 amended 1992
The Factories Act, 1948
The Petroleum Act, 1934
The Petroleum Rules, 2002
The Gas Cylinder Rules, 2004
The Static and Mobile Pressure Vessels (Unfired) Rules, 1981
Central Motor Vehicle Act 1988 and Central Motor Vehicle Rules1989
The details of Acts and Rules with applicability for the proposed project are given in Table 1-1.
Rakamcherla IP - EIA Introduction
6
Manufacture Storage and Import of Hazardous Chemicals Rules, 1989 amended 2000
Chemical Accidents (Emergency Planning, Preparedness and Response) Rules, 1996
Batteries (Management and Handling) Rules, 2001.
The Public Liability Insurance Act, 1991 amended 1992
The Factories Act, 1948
The Petroleum Act, 1934
The Petroleum Rules, 2002
The Gas Cylinder Rules, 2004
The Static and Mobile Pressure Vessels (Unfired) Rules, 1981
Central Motor Vehicle Act 1988 and Central Motor Vehicle Rules1989
The details of Acts and Rules with applicability for the proposed project are given in Table 1-1.
Rakamcherla IP - EIA Introduction
6
Manufacture Storage and Import of Hazardous Chemicals Rules, 1989 amended 2000
Chemical Accidents (Emergency Planning, Preparedness and Response) Rules, 1996
Batteries (Management and Handling) Rules, 2001.
The Public Liability Insurance Act, 1991 amended 1992
The Factories Act, 1948
The Petroleum Act, 1934
The Petroleum Rules, 2002
The Gas Cylinder Rules, 2004
The Static and Mobile Pressure Vessels (Unfired) Rules, 1981
Central Motor Vehicle Act 1988 and Central Motor Vehicle Rules1989
The details of Acts and Rules with applicability for the proposed project are given in Table 1-1.
Rakamcherla IP - EIA Introduction
7
Table 1-1 Applicable Acts and Rules for the Proposed Project
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
1. The Environment
Protection Act-1986
To protect and improve
overall environment
Yes All the industries proposed
attract this Act
MoEF & CC. GoI; CPCB;
SPCB
2. Environmental Impact
Assessment
Notification 14th Sep
2006 and subsequent
amendments time to
time
To provide
environmental clearance
to new development
activities following
environmental impact
assessment
Yes The project falls under
Schedule 7 (c) Category B
as per the notification.
MoEF & CC, SEIAA
3. The National
Environment Appellate
Authority Act (NEAA)
1997
Address Grievances
regarding the process of
environmental
clearance.
Yes Grievances if any will be
dealt with, within this act.
NEAA
4. The Air (Prevention
and Control of
Pollution) Act, 1981
Prevention, control and
abatement of air
pollution
Yes During construction of
roads, piling works inside
the industrial park,
During operation -Air
pollutants from Industries in
the Industrial park
CPCB and SPCB
Rakamcherla IP - EIA Introduction
7
Table 1-1 Applicable Acts and Rules for the Proposed Project
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
1. The Environment
Protection Act-1986
To protect and improve
overall environment
Yes All the industries proposed
attract this Act
MoEF & CC. GoI; CPCB;
SPCB
2. Environmental Impact
Assessment
Notification 14th Sep
2006 and subsequent
amendments time to
time
To provide
environmental clearance
to new development
activities following
environmental impact
assessment
Yes The project falls under
Schedule 7 (c) Category B
as per the notification.
MoEF & CC, SEIAA
3. The National
Environment Appellate
Authority Act (NEAA)
1997
Address Grievances
regarding the process of
environmental
clearance.
Yes Grievances if any will be
dealt with, within this act.
NEAA
4. The Air (Prevention
and Control of
Pollution) Act, 1981
Prevention, control and
abatement of air
pollution
Yes During construction of
roads, piling works inside
the industrial park,
During operation -Air
pollutants from Industries in
the Industrial park
CPCB and SPCB
Rakamcherla IP - EIA Introduction
7
Table 1-1 Applicable Acts and Rules for the Proposed Project
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
1. The Environment
Protection Act-1986
To protect and improve
overall environment
Yes All the industries proposed
attract this Act
MoEF & CC. GoI; CPCB;
SPCB
2. Environmental Impact
Assessment
Notification 14th Sep
2006 and subsequent
amendments time to
time
To provide
environmental clearance
to new development
activities following
environmental impact
assessment
Yes The project falls under
Schedule 7 (c) Category B
as per the notification.
MoEF & CC, SEIAA
3. The National
Environment Appellate
Authority Act (NEAA)
1997
Address Grievances
regarding the process of
environmental
clearance.
Yes Grievances if any will be
dealt with, within this act.
NEAA
4. The Air (Prevention
and Control of
Pollution) Act, 1981
Prevention, control and
abatement of air
pollution
Yes During construction of
roads, piling works inside
the industrial park,
During operation -Air
pollutants from Industries in
the Industrial park
CPCB and SPCB
Rakamcherla IP - EIA Introduction
8
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
5. The Water Prevention
and Control of
Pollution) Act 1974
amended 1988
Prevention and control
of water pollution and
also maintaining or
restoring the
wholesomeness of water
Yes Water Pollutants generate
from industries in the
Industrial park has to be
treated to prescribed
standards
CPCB and SPCB
6. The Noise Pollution
(Regulation and
Control) Act 1990
The standards for noise
for day and night have
been promulgated by the
MoEF for various land
uses.
Yes This act will be applicable as
noise generates from industrial
process and vehicular
movement and to assess the
impact for protection measure
needs to be considered in
design.
CPCB and SPCB
7. Environmental
(Protection) Rules,
1986 (Amendments in
1999, 2001, 2002,
2002, 2002, 2003,
2004)
Protection and
Improvement of the
Environment
Yes As all environmental
notifications, rules and
Schedules are issued under
this act.
MoEF, GoI; CPCB and
SPCB
Rakamcherla IP - EIA Introduction
8
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
5. The Water Prevention
and Control of
Pollution) Act 1974
amended 1988
Prevention and control
of water pollution and
also maintaining or
restoring the
wholesomeness of water
Yes Water Pollutants generate
from industries in the
Industrial park has to be
treated to prescribed
standards
CPCB and SPCB
6. The Noise Pollution
(Regulation and
Control) Act 1990
The standards for noise
for day and night have
been promulgated by the
MoEF for various land
uses.
Yes This act will be applicable as
noise generates from industrial
process and vehicular
movement and to assess the
impact for protection measure
needs to be considered in
design.
CPCB and SPCB
7. Environmental
(Protection) Rules,
1986 (Amendments in
1999, 2001, 2002,
2002, 2002, 2003,
2004)
Protection and
Improvement of the
Environment
Yes As all environmental
notifications, rules and
Schedules are issued under
this act.
MoEF, GoI; CPCB and
SPCB
Rakamcherla IP - EIA Introduction
8
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
5. The Water Prevention
and Control of
Pollution) Act 1974
amended 1988
Prevention and control
of water pollution and
also maintaining or
restoring the
wholesomeness of water
Yes Water Pollutants generate
from industries in the
Industrial park has to be
treated to prescribed
standards
CPCB and SPCB
6. The Noise Pollution
(Regulation and
Control) Act 1990
The standards for noise
for day and night have
been promulgated by the
MoEF for various land
uses.
Yes This act will be applicable as
noise generates from industrial
process and vehicular
movement and to assess the
impact for protection measure
needs to be considered in
design.
CPCB and SPCB
7. Environmental
(Protection) Rules,
1986 (Amendments in
1999, 2001, 2002,
2002, 2002, 2003,
2004)
Protection and
Improvement of the
Environment
Yes As all environmental
notifications, rules and
Schedules are issued under
this act.
MoEF, GoI; CPCB and
SPCB
Rakamcherla IP - EIA Introduction
9
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
8. Hazardous Waste
(Management and
Handling) Rules, 1989
amended 2000 and
2003
Management &
Handling of hazardous
wastes in line with the
Basel convention
Yes Industries will generate
hazardous waste which may
be from process, utilities etc
and they have to be
managed as per the Rules
MoEF, CPCB, SPCB,
DGFT, Port Authority
and Customs Authority
9. Manufacture Storage
and Import of
Hazardous Chemicals
Rules, 1989 amended
2000
Regulate the
manufacture, storage
and import of
Hazardous Chemicals
Yes Some Industries will use
Hazardous Chemicals -
Toxic, Explosive,
Flammable, Reactive
Ministry of Environment
& Forests, CPCB, SPCB,
Chief Inspector of
Factories, Chief Inspector
of Mines, AERB, Chief
Controller of Explosives,
District Collector or
District Emergency
Authority, CEES under
DRDO
10. Chemical Accidents
(Emergency Planning,
Preparedness and
Response) Rules, 1996
Emergency Planning
Preparedness and
Response to chemical
accidents
Yes Some Industries will use
Hazardous Chemicals -
Toxic, Explosive,
Flammable, Reactive
CCG, SCG, DCG, LCG
and MAH Units
Rakamcherla IP - EIA Introduction
9
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
8. Hazardous Waste
(Management and
Handling) Rules, 1989
amended 2000 and
2003
Management &
Handling of hazardous
wastes in line with the
Basel convention
Yes Industries will generate
hazardous waste which may
be from process, utilities etc
and they have to be
managed as per the Rules
MoEF, CPCB, SPCB,
DGFT, Port Authority
and Customs Authority
9. Manufacture Storage
and Import of
Hazardous Chemicals
Rules, 1989 amended
2000
Regulate the
manufacture, storage
and import of
Hazardous Chemicals
Yes Some Industries will use
Hazardous Chemicals -
Toxic, Explosive,
Flammable, Reactive
Ministry of Environment
& Forests, CPCB, SPCB,
Chief Inspector of
Factories, Chief Inspector
of Mines, AERB, Chief
Controller of Explosives,
District Collector or
District Emergency
Authority, CEES under
DRDO
10. Chemical Accidents
(Emergency Planning,
Preparedness and
Response) Rules, 1996
Emergency Planning
Preparedness and
Response to chemical
accidents
Yes Some Industries will use
Hazardous Chemicals -
Toxic, Explosive,
Flammable, Reactive
CCG, SCG, DCG, LCG
and MAH Units
Rakamcherla IP - EIA Introduction
9
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
8. Hazardous Waste
(Management and
Handling) Rules, 1989
amended 2000 and
2003
Management &
Handling of hazardous
wastes in line with the
Basel convention
Yes Industries will generate
hazardous waste which may
be from process, utilities etc
and they have to be
managed as per the Rules
MoEF, CPCB, SPCB,
DGFT, Port Authority
and Customs Authority
9. Manufacture Storage
and Import of
Hazardous Chemicals
Rules, 1989 amended
2000
Regulate the
manufacture, storage
and import of
Hazardous Chemicals
Yes Some Industries will use
Hazardous Chemicals -
Toxic, Explosive,
Flammable, Reactive
Ministry of Environment
& Forests, CPCB, SPCB,
Chief Inspector of
Factories, Chief Inspector
of Mines, AERB, Chief
Controller of Explosives,
District Collector or
District Emergency
Authority, CEES under
DRDO
10. Chemical Accidents
(Emergency Planning,
Preparedness and
Response) Rules, 1996
Emergency Planning
Preparedness and
Response to chemical
accidents
Yes Some Industries will use
Hazardous Chemicals -
Toxic, Explosive,
Flammable, Reactive
CCG, SCG, DCG, LCG
and MAH Units
Rakamcherla IP - EIA Introduction
10
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
11. Batteries (Management
and Handling) Rules,
2001.
To control the
hazardous waste
generation (lead waste)
from used lead acid
batteries
Yes Lead Acid Batteries SPCB, CPCB and MoEF
12. The Public Liability
Insurance Act, 1991
amended 1992
To provide immediate
relief to persons
affected by accident
involving hazardous
substances
Yes Protect the staff working in
the Industry due to use of
Hazardous Substances
Ministry of Environment
& Forests, District
Collector
13. The Factories Act, 1948 Control of workplace
environment, and
providing for good
health and safety of
workers
Yes All the industries to be
established attract the Act.
Ministry of Labour,
DGFASLI and
Directorate of Industrial
Safety And
Health/Factories
Inspectorate
14. The Petroleum Act,
1934
Regulate the import,
transport, storage,
production, refining and
blending of petroleum
Yes Some Industries may use
petroleum products for
storage.
Ministry of Petroleum and
Natural Gas
Rakamcherla IP - EIA Introduction
10
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
11. Batteries (Management
and Handling) Rules,
2001.
To control the
hazardous waste
generation (lead waste)
from used lead acid
batteries
Yes Lead Acid Batteries SPCB, CPCB and MoEF
12. The Public Liability
Insurance Act, 1991
amended 1992
To provide immediate
relief to persons
affected by accident
involving hazardous
substances
Yes Protect the staff working in
the Industry due to use of
Hazardous Substances
Ministry of Environment
& Forests, District
Collector
13. The Factories Act, 1948 Control of workplace
environment, and
providing for good
health and safety of
workers
Yes All the industries to be
established attract the Act.
Ministry of Labour,
DGFASLI and
Directorate of Industrial
Safety And
Health/Factories
Inspectorate
14. The Petroleum Act,
1934
Regulate the import,
transport, storage,
production, refining and
blending of petroleum
Yes Some Industries may use
petroleum products for
storage.
Ministry of Petroleum and
Natural Gas
Rakamcherla IP - EIA Introduction
10
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
11. Batteries (Management
and Handling) Rules,
2001.
To control the
hazardous waste
generation (lead waste)
from used lead acid
batteries
Yes Lead Acid Batteries SPCB, CPCB and MoEF
12. The Public Liability
Insurance Act, 1991
amended 1992
To provide immediate
relief to persons
affected by accident
involving hazardous
substances
Yes Protect the staff working in
the Industry due to use of
Hazardous Substances
Ministry of Environment
& Forests, District
Collector
13. The Factories Act, 1948 Control of workplace
environment, and
providing for good
health and safety of
workers
Yes All the industries to be
established attract the Act.
Ministry of Labour,
DGFASLI and
Directorate of Industrial
Safety And
Health/Factories
Inspectorate
14. The Petroleum Act,
1934
Regulate the import,
transport, storage,
production, refining and
blending of petroleum
Yes Some Industries may use
petroleum products for
storage.
Ministry of Petroleum and
Natural Gas
Rakamcherla IP - EIA Introduction
11
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
15. The Petroleum Rules,
2002
Regulate the import,
transport, storage,
production, refining and
blending of petroleum
Yes Some Industries may use
petroleum products for
storage.
Ministry of Petroleum and
Natural Gas, Ministry of
Environment & Forests or
SPCB Chief Controller of
Explosives, district
authority
16. The Gas Cylinder
Rules, 2004
Regulate the import,
storage, handling and
transportation of gas
cylinders with a view to
prevent accidents
Yes Some industries may use
Gases (Toxic, non toxic and
non flammable, non toxic
and flammable, Dissolved
Acetylene Gas, Non toxic
and flammable liquefiable
gas other than LPG,
Ministry of Commerce
and Industry and Chief
Controller of Explosives,
collector, DGCA, DC,
DM, Police (sub inspector
to commissioner)
Rakamcherla IP - EIA Introduction
11
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
15. The Petroleum Rules,
2002
Regulate the import,
transport, storage,
production, refining and
blending of petroleum
Yes Some Industries may use
petroleum products for
storage.
Ministry of Petroleum and
Natural Gas, Ministry of
Environment & Forests or
SPCB Chief Controller of
Explosives, district
authority
16. The Gas Cylinder
Rules, 2004
Regulate the import,
storage, handling and
transportation of gas
cylinders with a view to
prevent accidents
Yes Some industries may use
Gases (Toxic, non toxic and
non flammable, non toxic
and flammable, Dissolved
Acetylene Gas, Non toxic
and flammable liquefiable
gas other than LPG,
Ministry of Commerce
and Industry and Chief
Controller of Explosives,
collector, DGCA, DC,
DM, Police (sub inspector
to commissioner)
Rakamcherla IP - EIA Introduction
11
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
15. The Petroleum Rules,
2002
Regulate the import,
transport, storage,
production, refining and
blending of petroleum
Yes Some Industries may use
petroleum products for
storage.
Ministry of Petroleum and
Natural Gas, Ministry of
Environment & Forests or
SPCB Chief Controller of
Explosives, district
authority
16. The Gas Cylinder
Rules, 2004
Regulate the import,
storage, handling and
transportation of gas
cylinders with a view to
prevent accidents
Yes Some industries may use
Gases (Toxic, non toxic and
non flammable, non toxic
and flammable, Dissolved
Acetylene Gas, Non toxic
and flammable liquefiable
gas other than LPG,
Ministry of Commerce
and Industry and Chief
Controller of Explosives,
collector, DGCA, DC,
DM, Police (sub inspector
to commissioner)
Rakamcherla IP - EIA Introduction
12
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
17. The Static and Mobile
Pressure Vessels
(Unfired) Rules, 1981
Regulate the import,
manufacture, design,
installation,
transportation, handling,
use and testing of
mobile and static
pressure vessels
(unfired) with a view to
prevent accidents
Yes Some of the industries may
use boilers/ Thermic Fluid
Heaters/ Thermo Pack for
process.
Ministry of Commerce
and Industry and Chief
Controller of Explosives,
collector, DGCA, DC,
DM, Police (sub inspector
to commissioner)
18. Central Motor Vehicle
Act 1988 and Central
Motor Vehicle
Rules1989
For transportation of
dangerous goods
Yes Some of the industries may
transport solvents/
petroleum products etc.
Ministry of Road
Transport and Highways
Rakamcherla IP - EIA Introduction
12
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
17. The Static and Mobile
Pressure Vessels
(Unfired) Rules, 1981
Regulate the import,
manufacture, design,
installation,
transportation, handling,
use and testing of
mobile and static
pressure vessels
(unfired) with a view to
prevent accidents
Yes Some of the industries may
use boilers/ Thermic Fluid
Heaters/ Thermo Pack for
process.
Ministry of Commerce
and Industry and Chief
Controller of Explosives,
collector, DGCA, DC,
DM, Police (sub inspector
to commissioner)
18. Central Motor Vehicle
Act 1988 and Central
Motor Vehicle
Rules1989
For transportation of
dangerous goods
Yes Some of the industries may
transport solvents/
petroleum products etc.
Ministry of Road
Transport and Highways
Rakamcherla IP - EIA Introduction
12
S.No Act / Rules PurposeApplicable
Yes/ NoReason for Applicability Authority
17. The Static and Mobile
Pressure Vessels
(Unfired) Rules, 1981
Regulate the import,
manufacture, design,
installation,
transportation, handling,
use and testing of
mobile and static
pressure vessels
(unfired) with a view to
prevent accidents
Yes Some of the industries may
use boilers/ Thermic Fluid
Heaters/ Thermo Pack for
process.
Ministry of Commerce
and Industry and Chief
Controller of Explosives,
collector, DGCA, DC,
DM, Police (sub inspector
to commissioner)
18. Central Motor Vehicle
Act 1988 and Central
Motor Vehicle
Rules1989
For transportation of
dangerous goods
Yes Some of the industries may
transport solvents/
petroleum products etc.
Ministry of Road
Transport and Highways
Rakamcherla IP - EIA Introduction
13
1.6 Objectives and Scope
The scope of the work mentioned includes an assessment study of the proposed
industries and their impact on the region. This study puts forward the most effective
ways to protect the environment from increasing pollution caused by the proposed
industrial development and recommendations for environmental-friendly
development initiatives in the region.
The major objective of this study is to prepare a detailed Environment Impact study
of the Industrial Park at Rakamcherla Village.
1.6.1 Objectives of this EIA Report
Identify and locate the industries in the industrial area.
An assessment of the environments likely to be affected by the proposed
project;
An assessment of the nature, extent, duration, probability and significance of
the identified potential environmental, social and cultural impacts of the
proposed project;
Assess the baseline information of the study area, baseline information
regarding the geographical, socio-economical, cultural and bio-physical
environmental status.
A comparative assessment of the identified land use and development
alternatives and their potential environmental, social and cultural impacts;
The appropriate mitigation measures for each significant impact of the
proposed project;
Develop an environmental plan, monitoring and auditing frameworks.
Details of the engagement process of Interested and Affected Parties (I&AP’s)
followed during the course of the assessment and an indication of how the
issues raised have been addressed;
Identification of knowledge gaps and reporting on the adequacy of predictive
methods, underlying assumptions and uncertainties encountered in compiling
the required information;
To fully recognize the scope and requirements of the TOR and comply with
the same.
Rakamcherla IP - EIA Introduction
13
1.6 Objectives and Scope
The scope of the work mentioned includes an assessment study of the proposed
industries and their impact on the region. This study puts forward the most effective
ways to protect the environment from increasing pollution caused by the proposed
industrial development and recommendations for environmental-friendly
development initiatives in the region.
The major objective of this study is to prepare a detailed Environment Impact study
of the Industrial Park at Rakamcherla Village.
1.6.1 Objectives of this EIA Report
Identify and locate the industries in the industrial area.
An assessment of the environments likely to be affected by the proposed
project;
An assessment of the nature, extent, duration, probability and significance of
the identified potential environmental, social and cultural impacts of the
proposed project;
Assess the baseline information of the study area, baseline information
regarding the geographical, socio-economical, cultural and bio-physical
environmental status.
A comparative assessment of the identified land use and development
alternatives and their potential environmental, social and cultural impacts;
The appropriate mitigation measures for each significant impact of the
proposed project;
Develop an environmental plan, monitoring and auditing frameworks.
Details of the engagement process of Interested and Affected Parties (I&AP’s)
followed during the course of the assessment and an indication of how the
issues raised have been addressed;
Identification of knowledge gaps and reporting on the adequacy of predictive
methods, underlying assumptions and uncertainties encountered in compiling
the required information;
To fully recognize the scope and requirements of the TOR and comply with
the same.
Rakamcherla IP - EIA Introduction
13
1.6 Objectives and Scope
The scope of the work mentioned includes an assessment study of the proposed
industries and their impact on the region. This study puts forward the most effective
ways to protect the environment from increasing pollution caused by the proposed
industrial development and recommendations for environmental-friendly
development initiatives in the region.
The major objective of this study is to prepare a detailed Environment Impact study
of the Industrial Park at Rakamcherla Village.
1.6.1 Objectives of this EIA Report
Identify and locate the industries in the industrial area.
An assessment of the environments likely to be affected by the proposed
project;
An assessment of the nature, extent, duration, probability and significance of
the identified potential environmental, social and cultural impacts of the
proposed project;
Assess the baseline information of the study area, baseline information
regarding the geographical, socio-economical, cultural and bio-physical
environmental status.
A comparative assessment of the identified land use and development
alternatives and their potential environmental, social and cultural impacts;
The appropriate mitigation measures for each significant impact of the
proposed project;
Develop an environmental plan, monitoring and auditing frameworks.
Details of the engagement process of Interested and Affected Parties (I&AP’s)
followed during the course of the assessment and an indication of how the
issues raised have been addressed;
Identification of knowledge gaps and reporting on the adequacy of predictive
methods, underlying assumptions and uncertainties encountered in compiling
the required information;
To fully recognize the scope and requirements of the TOR and comply with
the same.
Rakamcherla IP - EIA Introduction
14
The scope of the study included the following areas of work:
Collection of detailed information on industries proposed within the industrial
area including their location, size, nature of production, capacity, use of raw
materials and use of energy sources in order to establish the baseline condition.
Their emissions, wastage and by-products if any, are accounted for evaluating
their multiple impacts on the prevailing environmental conditions of the area.
Preparation of an environmental management plan, monitoring strategies and
proposals for the most effective mitigation measures, including auditing plans
and matrices for the monitoring of various pollution parameters within the
Industrial Park.
1.7 Methodology Adopted for the Study
An Environmental Impact Assessment (EIA) is an assessment of the possible
impact, whether positive or negative, that a proposed project may have on the
environment, together consisting of the natural, social and economic aspects, i.e.,
aiming at “Sustainable Development” due to the project activities.
1.7.1 EIA Process
The EIA process followed for this EIA report is composed of the following
stages:
Study of project information
Screening & Scoping
Environmental pre-feasibility study & application for approval of ToR
Collection of detailed project management plan/report
Baseline data collection
Impact identification, Prediction & Evaluation
Mitigation measures & delineation of EMP
Risk assessment and safety & disaster management plan
Review & finalization of EIA Report based on the ToR requirements.
Submission of Draft EIA report for Public Hearing.
Incorporation of Issues raised in Public Hearing and measures to solve theissues in the EIA report and Submission of the EIA report forimplementation of mitigation measures & EMP as well as necessaryclearances from relevant Authorities.
Rakamcherla IP - EIA Introduction
14
The scope of the study included the following areas of work:
Collection of detailed information on industries proposed within the industrial
area including their location, size, nature of production, capacity, use of raw
materials and use of energy sources in order to establish the baseline condition.
Their emissions, wastage and by-products if any, are accounted for evaluating
their multiple impacts on the prevailing environmental conditions of the area.
Preparation of an environmental management plan, monitoring strategies and
proposals for the most effective mitigation measures, including auditing plans
and matrices for the monitoring of various pollution parameters within the
Industrial Park.
1.7 Methodology Adopted for the Study
An Environmental Impact Assessment (EIA) is an assessment of the possible
impact, whether positive or negative, that a proposed project may have on the
environment, together consisting of the natural, social and economic aspects, i.e.,
aiming at “Sustainable Development” due to the project activities.
1.7.1 EIA Process
The EIA process followed for this EIA report is composed of the following
stages:
Study of project information
Screening & Scoping
Environmental pre-feasibility study & application for approval of ToR
Collection of detailed project management plan/report
Baseline data collection
Impact identification, Prediction & Evaluation
Mitigation measures & delineation of EMP
Risk assessment and safety & disaster management plan
Review & finalization of EIA Report based on the ToR requirements.
Submission of Draft EIA report for Public Hearing.
Incorporation of Issues raised in Public Hearing and measures to solve theissues in the EIA report and Submission of the EIA report forimplementation of mitigation measures & EMP as well as necessaryclearances from relevant Authorities.
Rakamcherla IP - EIA Introduction
14
The scope of the study included the following areas of work:
Collection of detailed information on industries proposed within the industrial
area including their location, size, nature of production, capacity, use of raw
materials and use of energy sources in order to establish the baseline condition.
Their emissions, wastage and by-products if any, are accounted for evaluating
their multiple impacts on the prevailing environmental conditions of the area.
Preparation of an environmental management plan, monitoring strategies and
proposals for the most effective mitigation measures, including auditing plans
and matrices for the monitoring of various pollution parameters within the
Industrial Park.
1.7 Methodology Adopted for the Study
An Environmental Impact Assessment (EIA) is an assessment of the possible
impact, whether positive or negative, that a proposed project may have on the
environment, together consisting of the natural, social and economic aspects, i.e.,
aiming at “Sustainable Development” due to the project activities.
1.7.1 EIA Process
The EIA process followed for this EIA report is composed of the following
stages:
Study of project information
Screening & Scoping
Environmental pre-feasibility study & application for approval of ToR
Collection of detailed project management plan/report
Baseline data collection
Impact identification, Prediction & Evaluation
Mitigation measures & delineation of EMP
Risk assessment and safety & disaster management plan
Review & finalization of EIA Report based on the ToR requirements.
Submission of Draft EIA report for Public Hearing.
Incorporation of Issues raised in Public Hearing and measures to solve theissues in the EIA report and Submission of the EIA report forimplementation of mitigation measures & EMP as well as necessaryclearances from relevant Authorities.
Rakamcherla IP - EIA Introduction
15
The EIA Cycle based on the above stages has been illustrated in Figure 1.1.
Figure 1.1 EIA Process Cycle
Screening and Reconnaissance Survey
Citation of Necessary Mitigation Measures, Delineation ofEnvironment Monitoring And Management Plan
Feasibility Study and Application of TOR
Scoping and Application of TOR
Identification of Monitoring locations ForMonitoring & Sampling, Analysis Of Samples
And Generation Of Primary Data
Establishment of Baseline Environmental StatusCollection of Detailed Project Plan/Report
Identification of SecondaryData Sources & Collection of Data
Compilation of Verification and Validation of data
Study of Project Details
Consequence Analysis & RiskAssessment
Incorporation of Corrections or suggestions By Public
Preparation of Draft EIA Report for Public Hearing
Identification, Prediction & Evaluation of Impacts
Citation of necessary preventive, control &precautionary Measure and Delineation ofSafety and Disaster Management Plan
Preparation & Issue of Final EIA Report
Submission by/Appraisal by Authorities for necessary clearance
Rakamcherla IP - EIA Introduction
15
The EIA Cycle based on the above stages has been illustrated in Figure 1.1.
Figure 1.1 EIA Process Cycle
Screening and Reconnaissance Survey
Citation of Necessary Mitigation Measures, Delineation ofEnvironment Monitoring And Management Plan
Feasibility Study and Application of TOR
Scoping and Application of TOR
Identification of Monitoring locations ForMonitoring & Sampling, Analysis Of Samples
And Generation Of Primary Data
Establishment of Baseline Environmental StatusCollection of Detailed Project Plan/Report
Identification of SecondaryData Sources & Collection of Data
Compilation of Verification and Validation of data
Study of Project Details
Consequence Analysis & RiskAssessment
Incorporation of Corrections or suggestions By Public
Preparation of Draft EIA Report for Public Hearing
Identification, Prediction & Evaluation of Impacts
Citation of necessary preventive, control &precautionary Measure and Delineation ofSafety and Disaster Management Plan
Preparation & Issue of Final EIA Report
Submission by/Appraisal by Authorities for necessary clearance
Rakamcherla IP - EIA Introduction
15
The EIA Cycle based on the above stages has been illustrated in Figure 1.1.
Figure 1.1 EIA Process Cycle
Screening and Reconnaissance Survey
Citation of Necessary Mitigation Measures, Delineation ofEnvironment Monitoring And Management Plan
Feasibility Study and Application of TOR
Scoping and Application of TOR
Identification of Monitoring locations ForMonitoring & Sampling, Analysis Of Samples
And Generation Of Primary Data
Establishment of Baseline Environmental StatusCollection of Detailed Project Plan/Report
Identification of SecondaryData Sources & Collection of Data
Compilation of Verification and Validation of data
Study of Project Details
Consequence Analysis & RiskAssessment
Incorporation of Corrections or suggestions By Public
Preparation of Draft EIA Report for Public Hearing
Identification, Prediction & Evaluation of Impacts
Citation of necessary preventive, control &precautionary Measure and Delineation ofSafety and Disaster Management Plan
Preparation & Issue of Final EIA Report
Submission by/Appraisal by Authorities for necessary clearance
Rakamcherla IP - EIA Project Description
Chapter 2
Project Description
Rakamcherla IP - EIA Project Description
Chapter 2
Project Description
Rakamcherla IP - EIA Project Description
Chapter 2
Project Description
Rakamcherla IP - EIA Process Description
17
2 Project Description
2.1 Type of the Project
TSIIC proposes the development of an Industrial Park at Rakamcherla &
Pudur village, Pudur mandal, Vikarabad District, Telangana State. The
Industrial Park is proposed to be spread over 112.48 Acres (45.52 Hec) and
caters to the socio-economic development of the region.
Total plotted area for the proposed site 60.66 Acres. There are totally 45 plots
proposed for the site. B category industries are proposed as per the EIA
notification 2006 and its amendments.
2.2 Project Location
The proposed Industrial Park is located at 17°14’40.09”N and 77°57’59.85”E,
Sy.No 5/1 of Rakamcherla village and Sy.Nos 243/1, 244/1, 245/1, 246/1,
247/1 and 248/1 of Pudur Village, Pudur Mandal, Vikarabad District,
Telangana, India. The Development area for the project is 112.48 Acres
(45.52 Ha). The land documents are enclosed as Annexure – 3. The proposed
site is strategically situated adjacent to the SH 4 connecting Manneguda and
Pargi. The site is furthermore situated at 12 kilometer North West of
Vikarabad town. The satellite image showing the site and its surrounding
features within 10Km radius is given in Figure 2-2. Project site location map
is given in Figure 2-3. Google image of the site with coordinates are given in
Figure 2-4. The Google image of the site clearly shows that so far at site there
is no development and the site is a vacant land. The salient features of the site
and surrounding features are given in Table 2-1.
Table 2.1 Project site and surrounding features
S.No Item Details
1. Name of the Project Industrial Park-Rakamcherla
2.Schedule and Category of Project 7(C) , Category B
3.Proposed total area 112.48Acres / 45.52 Hectares
4.Location:
Rakamcherla IP - EIA Process Description
17
2 Project Description
2.1 Type of the Project
TSIIC proposes the development of an Industrial Park at Rakamcherla &
Pudur village, Pudur mandal, Vikarabad District, Telangana State. The
Industrial Park is proposed to be spread over 112.48 Acres (45.52 Hec) and
caters to the socio-economic development of the region.
Total plotted area for the proposed site 60.66 Acres. There are totally 45 plots
proposed for the site. B category industries are proposed as per the EIA
notification 2006 and its amendments.
2.2 Project Location
The proposed Industrial Park is located at 17°14’40.09”N and 77°57’59.85”E,
Sy.No 5/1 of Rakamcherla village and Sy.Nos 243/1, 244/1, 245/1, 246/1,
247/1 and 248/1 of Pudur Village, Pudur Mandal, Vikarabad District,
Telangana, India. The Development area for the project is 112.48 Acres
(45.52 Ha). The land documents are enclosed as Annexure – 3. The proposed
site is strategically situated adjacent to the SH 4 connecting Manneguda and
Pargi. The site is furthermore situated at 12 kilometer North West of
Vikarabad town. The satellite image showing the site and its surrounding
features within 10Km radius is given in Figure 2-2. Project site location map
is given in Figure 2-3. Google image of the site with coordinates are given in
Figure 2-4. The Google image of the site clearly shows that so far at site there
is no development and the site is a vacant land. The salient features of the site
and surrounding features are given in Table 2-1.
Table 2.1 Project site and surrounding features
S.No Item Details
1. Name of the Project Industrial Park-Rakamcherla
2.Schedule and Category of Project 7(C) , Category B
3.Proposed total area 112.48Acres / 45.52 Hectares
4.Location:
Rakamcherla IP - EIA Process Description
17
2 Project Description
2.1 Type of the Project
TSIIC proposes the development of an Industrial Park at Rakamcherla &
Pudur village, Pudur mandal, Vikarabad District, Telangana State. The
Industrial Park is proposed to be spread over 112.48 Acres (45.52 Hec) and
caters to the socio-economic development of the region.
Total plotted area for the proposed site 60.66 Acres. There are totally 45 plots
proposed for the site. B category industries are proposed as per the EIA
notification 2006 and its amendments.
2.2 Project Location
The proposed Industrial Park is located at 17°14’40.09”N and 77°57’59.85”E,
Sy.No 5/1 of Rakamcherla village and Sy.Nos 243/1, 244/1, 245/1, 246/1,
247/1 and 248/1 of Pudur Village, Pudur Mandal, Vikarabad District,
Telangana, India. The Development area for the project is 112.48 Acres
(45.52 Ha). The land documents are enclosed as Annexure – 3. The proposed
site is strategically situated adjacent to the SH 4 connecting Manneguda and
Pargi. The site is furthermore situated at 12 kilometer North West of
Vikarabad town. The satellite image showing the site and its surrounding
features within 10Km radius is given in Figure 2-2. Project site location map
is given in Figure 2-3. Google image of the site with coordinates are given in
Figure 2-4. The Google image of the site clearly shows that so far at site there
is no development and the site is a vacant land. The salient features of the site
and surrounding features are given in Table 2-1.
Table 2.1 Project site and surrounding features
S.No Item Details
1. Name of the Project Industrial Park-Rakamcherla
2.Schedule and Category of Project 7(C) , Category B
3.Proposed total area 112.48Acres / 45.52 Hectares
4.Location:
Rakamcherla IP - EIA Process Description
18
S.No Item Details
Plot/Survey/Khasra No. Sy.No 5/1 – Rakamcherla VillageSy.Nos. 243/1, 244/1, 245/1, 246/1,247/1, 248/1- Pudur village
Village Rakamcherla & Pudur
Mandal Pudur
District Vikarabad
State Telangana
5.Nearest Railway Station/Airport Rangareddy Railway Station - 15 Km,
Hyderabad –Rajiv GandhiInternational Airport -73 Km
6.Nearest Town, City, District Town: Rangareddy -12 Km
City: Hyderabad-70 KmDistrict Hq: Hyderabad-70 Km
7.Nearest habitat Rakamcherla village - 0.5 Km
8.Inland water bodies Shiv Sagar lake - 11 Km NW
Laknapur tank - 14 Km SW
9.Elevation 704m ( 2310 ft)
10.Government Order / Policy relevant/ relating to the site
GO No. 111 dated 8 March, 1996 forrelocation of industries with in 10 kmFTL of Himayatsagar and Osmansagarlake. (Annexure-4)
11.Project Cost 798.50 Lakhs
12.Presence of Eco Sensitive Areas Nil
13.Nearby Industries Shiv Shakthi steel mills - 5 Km
South
Rakamcherla IP - EIA Process Description
18
S.No Item Details
Plot/Survey/Khasra No. Sy.No 5/1 – Rakamcherla VillageSy.Nos. 243/1, 244/1, 245/1, 246/1,247/1, 248/1- Pudur village
Village Rakamcherla & Pudur
Mandal Pudur
District Vikarabad
State Telangana
5.Nearest Railway Station/Airport Rangareddy Railway Station - 15 Km,
Hyderabad –Rajiv GandhiInternational Airport -73 Km
6.Nearest Town, City, District Town: Rangareddy -12 Km
City: Hyderabad-70 KmDistrict Hq: Hyderabad-70 Km
7.Nearest habitat Rakamcherla village - 0.5 Km
8.Inland water bodies Shiv Sagar lake - 11 Km NW
Laknapur tank - 14 Km SW
9.Elevation 704m ( 2310 ft)
10.Government Order / Policy relevant/ relating to the site
GO No. 111 dated 8 March, 1996 forrelocation of industries with in 10 kmFTL of Himayatsagar and Osmansagarlake. (Annexure-4)
11.Project Cost 798.50 Lakhs
12.Presence of Eco Sensitive Areas Nil
13.Nearby Industries Shiv Shakthi steel mills - 5 Km
South
Rakamcherla IP - EIA Process Description
18
S.No Item Details
Plot/Survey/Khasra No. Sy.No 5/1 – Rakamcherla VillageSy.Nos. 243/1, 244/1, 245/1, 246/1,247/1, 248/1- Pudur village
Village Rakamcherla & Pudur
Mandal Pudur
District Vikarabad
State Telangana
5.Nearest Railway Station/Airport Rangareddy Railway Station - 15 Km,
Hyderabad –Rajiv GandhiInternational Airport -73 Km
6.Nearest Town, City, District Town: Rangareddy -12 Km
City: Hyderabad-70 KmDistrict Hq: Hyderabad-70 Km
7.Nearest habitat Rakamcherla village - 0.5 Km
8.Inland water bodies Shiv Sagar lake - 11 Km NW
Laknapur tank - 14 Km SW
9.Elevation 704m ( 2310 ft)
10.Government Order / Policy relevant/ relating to the site
GO No. 111 dated 8 March, 1996 forrelocation of industries with in 10 kmFTL of Himayatsagar and Osmansagarlake. (Annexure-4)
11.Project Cost 798.50 Lakhs
12.Presence of Eco Sensitive Areas Nil
13.Nearby Industries Shiv Shakthi steel mills - 5 Km
South
Rakamcherla IP - EIA Process Description
19
Figure 2.1 Location of the Project site
Proposed Industrial Park -Rakamcherla
Rakamcherla IP - EIA Process Description
19
Figure 2.1 Location of the Project site
Proposed Industrial Park -Rakamcherla
Rakamcherla IP - EIA Process Description
19
Figure 2.1 Location of the Project site
Proposed Industrial Park -Rakamcherla
Rakamcherla IP - EIA Project Description
20
Figure 2.2 Project Site 15 Km Radius Map
Rakamcherla IP - EIA Project Description
20
Figure 2.2 Project Site 15 Km Radius Map
Rakamcherla IP - EIA Project Description
20
Figure 2.2 Project Site 15 Km Radius Map
Rakamcherla IP - EIA Project Description
21
Figure 2.3 Satellite Imagery of the site Showing 10 Km radius
Rakamcherla IP - EIA Project Description
21
Figure 2.3 Satellite Imagery of the site Showing 10 Km radius
Rakamcherla IP - EIA Project Description
21
Figure 2.3 Satellite Imagery of the site Showing 10 Km radius
Rakamcherla IP – EIA Project Description
Figure 2.4 Google Image showing the project site boundary with coordinates
2.3 Need for the Project
The development of industrial park at Rakamcherla village will help the
Government agencies in achieving the objective of relocation of industries
within 10 km FTL (Full Tank Level) of Himayatsagar and Osmansagar lake
(As per the GO copy attached in Annexure 4), since the site is credited to be
suitable for industrial development. The development of industrial park in
the region will help to meet a growing demand in the services sector, and to
enhance future economic growth within the region. The proposed
development is envisaged to provide short-term and long-term employment
opportunities.
Rakamcherla IP – EIA Project Description
Figure 2.4 Google Image showing the project site boundary with coordinates
2.3 Need for the Project
The development of industrial park at Rakamcherla village will help the
Government agencies in achieving the objective of relocation of industries
within 10 km FTL (Full Tank Level) of Himayatsagar and Osmansagar lake
(As per the GO copy attached in Annexure 4), since the site is credited to be
suitable for industrial development. The development of industrial park in
the region will help to meet a growing demand in the services sector, and to
enhance future economic growth within the region. The proposed
development is envisaged to provide short-term and long-term employment
opportunities.
Rakamcherla IP – EIA Project Description
Figure 2.4 Google Image showing the project site boundary with coordinates
2.3 Need for the Project
The development of industrial park at Rakamcherla village will help the
Government agencies in achieving the objective of relocation of industries
within 10 km FTL (Full Tank Level) of Himayatsagar and Osmansagar lake
(As per the GO copy attached in Annexure 4), since the site is credited to be
suitable for industrial development. The development of industrial park in
the region will help to meet a growing demand in the services sector, and to
enhance future economic growth within the region. The proposed
development is envisaged to provide short-term and long-term employment
opportunities.
Rakamcherla IP – EIA Project Description
23
2.4 Project Site
The 45.52 Hectares (112.48 Acres) of land area is predominantly devoid of trees and
has some shrubs with only small herbaceous vegetation. The land is covered with
pebbles and soft weathered rock formations are exposed in some places. The terrain is
flat and having slope at southern side.
2.5 Existing Site Conditions
The site is located at Rakamcherla village and close to Pudur on pudur Maandal. The
elevation at the project site is around 704m. The site photographs are enclosed in
Figure 2-5.
Rakamcherla IP – EIA Project Description
23
2.4 Project Site
The 45.52 Hectares (112.48 Acres) of land area is predominantly devoid of trees and
has some shrubs with only small herbaceous vegetation. The land is covered with
pebbles and soft weathered rock formations are exposed in some places. The terrain is
flat and having slope at southern side.
2.5 Existing Site Conditions
The site is located at Rakamcherla village and close to Pudur on pudur Maandal. The
elevation at the project site is around 704m. The site photographs are enclosed in
Figure 2-5.
Rakamcherla IP – EIA Project Description
23
2.4 Project Site
The 45.52 Hectares (112.48 Acres) of land area is predominantly devoid of trees and
has some shrubs with only small herbaceous vegetation. The land is covered with
pebbles and soft weathered rock formations are exposed in some places. The terrain is
flat and having slope at southern side.
2.5 Existing Site Conditions
The site is located at Rakamcherla village and close to Pudur on pudur Maandal. The
elevation at the project site is around 704m. The site photographs are enclosed in
Figure 2-5.
Rakamcherla IP – EIA Project Description
24
Figure 2.5 Site Photographs
2.6 Approach to the Site
The site is surrounded by Barren land on the north, State highway Manneguda- Pargi
road to the west, agricultural land to the east and south. Rakamcherla village to the
south west at a distance of 0.5 km from the site. The photograph of the approach road
is given in Figure 2-6.
Figure 2.6 Site approach road from SH 4
Rakamcherla IP – EIA Project Description
24
Figure 2.5 Site Photographs
2.6 Approach to the Site
The site is surrounded by Barren land on the north, State highway Manneguda- Pargi
road to the west, agricultural land to the east and south. Rakamcherla village to the
south west at a distance of 0.5 km from the site. The photograph of the approach road
is given in Figure 2-6.
Figure 2.6 Site approach road from SH 4
Rakamcherla IP – EIA Project Description
24
Figure 2.5 Site Photographs
2.6 Approach to the Site
The site is surrounded by Barren land on the north, State highway Manneguda- Pargi
road to the west, agricultural land to the east and south. Rakamcherla village to the
south west at a distance of 0.5 km from the site. The photograph of the approach road
is given in Figure 2-6.
Figure 2.6 Site approach road from SH 4
Rakamcherla IP – EIA Project Description
25
2.7 Proposed Development
The 45.52 Hectares (112.48 acres) land area is planned for development of Industrial
park. The Industrial Park is developed for relocation of industries mainly steel rerolling
mills within 10 km FTL of Himayatsagar and Osmansagar lake. The GO copy is
enclosed in Annexure-4.
The type of industries proposed for this Park are Steel Re-rolling, Foundry,
Polyethene Bag Manufacturing, Tiles, Mangalore tiles, crucible manufacturing
industry, Manufacture of mirror from sheet glass and photo framing, Wire drawing
(cold process) and bailing straps, Electrical and Electronics items assembling General
Engineering, Tyre retreading & Vulcanizing Industry, Glass Industries, bicycles, baby
carriage and other non motorized vehicles Assembling units, Printing press, Footwear
(rubber) Flexible packaging Printing press, Cardboard or corrugated box and paper
products, Polythene, plastic and P.V.C. goods through extrusion Moulding, Biscuit
trays, etc. from rolled PVC Sheet (using automatic vaccum forming machine) Leather
cutting and stitching units, Automobile Fuel Outlet. The allotment of industries will
be in such a way that none of the Industry of Category A as specified in EIA
Notification, 2006 and its amendments will be allotted. Table 2-2 provides the area
breakup of the Industrial Park.
Table 2.2 Land use breakup for the project
Break up of Area Area (Acres) Percentage (%)Plotted Area 60.66 53.94
Road Area 15.83 14.07Open space Area 16.81 14.94
Common Utilities 6.55 5.82
Electrical Substation 10 8.89
Commercial Area/ CFC 2.63 2.34Proposed Layout 112.48 100
Rakamcherla IP – EIA Project Description
25
2.7 Proposed Development
The 45.52 Hectares (112.48 acres) land area is planned for development of Industrial
park. The Industrial Park is developed for relocation of industries mainly steel rerolling
mills within 10 km FTL of Himayatsagar and Osmansagar lake. The GO copy is
enclosed in Annexure-4.
The type of industries proposed for this Park are Steel Re-rolling, Foundry,
Polyethene Bag Manufacturing, Tiles, Mangalore tiles, crucible manufacturing
industry, Manufacture of mirror from sheet glass and photo framing, Wire drawing
(cold process) and bailing straps, Electrical and Electronics items assembling General
Engineering, Tyre retreading & Vulcanizing Industry, Glass Industries, bicycles, baby
carriage and other non motorized vehicles Assembling units, Printing press, Footwear
(rubber) Flexible packaging Printing press, Cardboard or corrugated box and paper
products, Polythene, plastic and P.V.C. goods through extrusion Moulding, Biscuit
trays, etc. from rolled PVC Sheet (using automatic vaccum forming machine) Leather
cutting and stitching units, Automobile Fuel Outlet. The allotment of industries will
be in such a way that none of the Industry of Category A as specified in EIA
Notification, 2006 and its amendments will be allotted. Table 2-2 provides the area
breakup of the Industrial Park.
Table 2.2 Land use breakup for the project
Break up of Area Area (Acres) Percentage (%)Plotted Area 60.66 53.94
Road Area 15.83 14.07Open space Area 16.81 14.94
Common Utilities 6.55 5.82
Electrical Substation 10 8.89
Commercial Area/ CFC 2.63 2.34Proposed Layout 112.48 100
Rakamcherla IP – EIA Project Description
25
2.7 Proposed Development
The 45.52 Hectares (112.48 acres) land area is planned for development of Industrial
park. The Industrial Park is developed for relocation of industries mainly steel rerolling
mills within 10 km FTL of Himayatsagar and Osmansagar lake. The GO copy is
enclosed in Annexure-4.
The type of industries proposed for this Park are Steel Re-rolling, Foundry,
Polyethene Bag Manufacturing, Tiles, Mangalore tiles, crucible manufacturing
industry, Manufacture of mirror from sheet glass and photo framing, Wire drawing
(cold process) and bailing straps, Electrical and Electronics items assembling General
Engineering, Tyre retreading & Vulcanizing Industry, Glass Industries, bicycles, baby
carriage and other non motorized vehicles Assembling units, Printing press, Footwear
(rubber) Flexible packaging Printing press, Cardboard or corrugated box and paper
products, Polythene, plastic and P.V.C. goods through extrusion Moulding, Biscuit
trays, etc. from rolled PVC Sheet (using automatic vaccum forming machine) Leather
cutting and stitching units, Automobile Fuel Outlet. The allotment of industries will
be in such a way that none of the Industry of Category A as specified in EIA
Notification, 2006 and its amendments will be allotted. Table 2-2 provides the area
breakup of the Industrial Park.
Table 2.2 Land use breakup for the project
Break up of Area Area (Acres) Percentage (%)Plotted Area 60.66 53.94
Road Area 15.83 14.07Open space Area 16.81 14.94
Common Utilities 6.55 5.82
Electrical Substation 10 8.89
Commercial Area/ CFC 2.63 2.34Proposed Layout 112.48 100
Rakamcherla IP – EIA Project Description
26
2.7.1 Plotted Area & Bulk Allotments
Out of the total layout area, 53.94% area is earmarked for plotted area i.e., 60.66
Acres and it consists of 45 plots. The site plan is enclosed as Annexure - 5. Table 2-
3 indicates the list of industries allotted.
Table 2.3 List of Industries Allocated
S.No Name Of Industry Type Of Industry ClassificationAs Per EIA
Total Area InAcre
1. Binjusaria Metal BoxCom
Steel Re-RollingIndustry
B 2.50
2. Anil Re-Rolling Mills Steel Re-RollingIndustry
B 1.13
3. Garg Steels Steel Re-RollingIndustry
B 2.5
4. Arun Ispat Udyog Steel Re-RollingIndustry
B 3.14
5. Neha Steels Steel Re-RollingIndustry
B 2.5
6. Gujarat Enviro Protection& Infrastructure Ltd
Alternate FuelResource facilityfrom Hazardouswaste, incinerablehazardous waste andIndustrial Nonhazardous waste
------ 4.88
7. M.N. Industries Copper Productsmanufacturing
------ 1.52
Total allotted area 18.17
(No” A” Category industry will be allotted in the Industrial Park.)
Table 2.4 List of Industries Proposed
S.No Type of Industry Proposed Classification as perCPCB
1 Metallurgical Industry Red2 Steel Mill Red3 Steel mill Red4 Foundry Red5 Polyethene Bag Manufacturing Green6 Production of Tiles, Mangalore tiles, crucible etc., Orange7 Manufacture of mirror from sheet glass and photo framing Orange8 Wire drawing (cold process) and bailing straps Orange9 Electrical and Electronics items assembling Green
Rakamcherla IP – EIA Project Description
26
2.7.1 Plotted Area & Bulk Allotments
Out of the total layout area, 53.94% area is earmarked for plotted area i.e., 60.66
Acres and it consists of 45 plots. The site plan is enclosed as Annexure - 5. Table 2-
3 indicates the list of industries allotted.
Table 2.3 List of Industries Allocated
S.No Name Of Industry Type Of Industry ClassificationAs Per EIA
Total Area InAcre
1. Binjusaria Metal BoxCom
Steel Re-RollingIndustry
B 2.50
2. Anil Re-Rolling Mills Steel Re-RollingIndustry
B 1.13
3. Garg Steels Steel Re-RollingIndustry
B 2.5
4. Arun Ispat Udyog Steel Re-RollingIndustry
B 3.14
5. Neha Steels Steel Re-RollingIndustry
B 2.5
6. Gujarat Enviro Protection& Infrastructure Ltd
Alternate FuelResource facilityfrom Hazardouswaste, incinerablehazardous waste andIndustrial Nonhazardous waste
------ 4.88
7. M.N. Industries Copper Productsmanufacturing
------ 1.52
Total allotted area 18.17
(No” A” Category industry will be allotted in the Industrial Park.)
Table 2.4 List of Industries Proposed
S.No Type of Industry Proposed Classification as perCPCB
1 Metallurgical Industry Red2 Steel Mill Red3 Steel mill Red4 Foundry Red5 Polyethene Bag Manufacturing Green6 Production of Tiles, Mangalore tiles, crucible etc., Orange7 Manufacture of mirror from sheet glass and photo framing Orange8 Wire drawing (cold process) and bailing straps Orange9 Electrical and Electronics items assembling Green
Rakamcherla IP – EIA Project Description
26
2.7.1 Plotted Area & Bulk Allotments
Out of the total layout area, 53.94% area is earmarked for plotted area i.e., 60.66
Acres and it consists of 45 plots. The site plan is enclosed as Annexure - 5. Table 2-
3 indicates the list of industries allotted.
Table 2.3 List of Industries Allocated
S.No Name Of Industry Type Of Industry ClassificationAs Per EIA
Total Area InAcre
1. Binjusaria Metal BoxCom
Steel Re-RollingIndustry
B 2.50
2. Anil Re-Rolling Mills Steel Re-RollingIndustry
B 1.13
3. Garg Steels Steel Re-RollingIndustry
B 2.5
4. Arun Ispat Udyog Steel Re-RollingIndustry
B 3.14
5. Neha Steels Steel Re-RollingIndustry
B 2.5
6. Gujarat Enviro Protection& Infrastructure Ltd
Alternate FuelResource facilityfrom Hazardouswaste, incinerablehazardous waste andIndustrial Nonhazardous waste
------ 4.88
7. M.N. Industries Copper Productsmanufacturing
------ 1.52
Total allotted area 18.17
(No” A” Category industry will be allotted in the Industrial Park.)
Table 2.4 List of Industries Proposed
S.No Type of Industry Proposed Classification as perCPCB
1 Metallurgical Industry Red2 Steel Mill Red3 Steel mill Red4 Foundry Red5 Polyethene Bag Manufacturing Green6 Production of Tiles, Mangalore tiles, crucible etc., Orange7 Manufacture of mirror from sheet glass and photo framing Orange8 Wire drawing (cold process) and bailing straps Orange9 Electrical and Electronics items assembling Green
Rakamcherla IP – EIA Project Description
27
S.No Type of Industry Proposed Classification as perCPCB
10 General Engineering Orange11 Tyre retreading & Vulcanizing Industry Green12 Glass Industries Red13 Flexible Packaging Green14 Assembling of bicycles, baby carriage and other non motorized
vehiclesGreen
15 Printing press Green16 Footwear (rubber) Green17 Flexible packaging Printing press Green18 Cardboard or corrugated box and paper products (Paper or pulp
manufacturing excluded).Green
19 Polythene, plastic and P.V.C. goods through extrusion moulding Green20 Biscuit trays etc. from rolled PVC Sheet(using automatic vacuum
forming machine)Green
21 Leather cutting and stitching Green22 Automobile Fuel Outlet Green
Area available for Allotment 39.59 Acres
2.7.2 Access Road and Internal Roads
A 30 m wide road is proposed for access to the Industrial Park from Manneguda –
Pargi State Highway 4. The photograph of access road to site is given in Figure 2-7.
The proposed internal roads are 18.30 m and 15.2 m wide. The proposed internal
road covers 14.07% % of total area i.e., 15.83 Acres. The access road and internal
roads will be constructed and acceptable for the type of commercial/ industrial
traffic that would be anticipated. Some cut and fill using blasted rock may be
necessary to achieve the desired slopes. The traffic plan of the site is enclosed as
Annexure- 6.
Rakamcherla IP – EIA Project Description
27
S.No Type of Industry Proposed Classification as perCPCB
10 General Engineering Orange11 Tyre retreading & Vulcanizing Industry Green12 Glass Industries Red13 Flexible Packaging Green14 Assembling of bicycles, baby carriage and other non motorized
vehiclesGreen
15 Printing press Green16 Footwear (rubber) Green17 Flexible packaging Printing press Green18 Cardboard or corrugated box and paper products (Paper or pulp
manufacturing excluded).Green
19 Polythene, plastic and P.V.C. goods through extrusion moulding Green20 Biscuit trays etc. from rolled PVC Sheet(using automatic vacuum
forming machine)Green
21 Leather cutting and stitching Green22 Automobile Fuel Outlet Green
Area available for Allotment 39.59 Acres
2.7.2 Access Road and Internal Roads
A 30 m wide road is proposed for access to the Industrial Park from Manneguda –
Pargi State Highway 4. The photograph of access road to site is given in Figure 2-7.
The proposed internal roads are 18.30 m and 15.2 m wide. The proposed internal
road covers 14.07% % of total area i.e., 15.83 Acres. The access road and internal
roads will be constructed and acceptable for the type of commercial/ industrial
traffic that would be anticipated. Some cut and fill using blasted rock may be
necessary to achieve the desired slopes. The traffic plan of the site is enclosed as
Annexure- 6.
Rakamcherla IP – EIA Project Description
27
S.No Type of Industry Proposed Classification as perCPCB
10 General Engineering Orange11 Tyre retreading & Vulcanizing Industry Green12 Glass Industries Red13 Flexible Packaging Green14 Assembling of bicycles, baby carriage and other non motorized
vehiclesGreen
15 Printing press Green16 Footwear (rubber) Green17 Flexible packaging Printing press Green18 Cardboard or corrugated box and paper products (Paper or pulp
manufacturing excluded).Green
19 Polythene, plastic and P.V.C. goods through extrusion moulding Green20 Biscuit trays etc. from rolled PVC Sheet(using automatic vacuum
forming machine)Green
21 Leather cutting and stitching Green22 Automobile Fuel Outlet Green
Area available for Allotment 39.59 Acres
2.7.2 Access Road and Internal Roads
A 30 m wide road is proposed for access to the Industrial Park from Manneguda –
Pargi State Highway 4. The photograph of access road to site is given in Figure 2-7.
The proposed internal roads are 18.30 m and 15.2 m wide. The proposed internal
road covers 14.07% % of total area i.e., 15.83 Acres. The access road and internal
roads will be constructed and acceptable for the type of commercial/ industrial
traffic that would be anticipated. Some cut and fill using blasted rock may be
necessary to achieve the desired slopes. The traffic plan of the site is enclosed as
Annexure- 6.
Rakamcherla IP – EIA Project Description
28
Figure 2.7 Access road to site from SH 4
2.7.3 Green Belt Development
10 m width buffer Zone (Green Belt) will be provided all along the boundary of
Industrial Park. Open space area of 16.81 Acres (14.94%) is earmarked for green
belt development. Apart from this green belt area, the individual industries will
develop greenbelt at their individual unit premises as per the norms. Green belt
will be proposed on the median of roads and avenue plantation also. Adequate
green belt will be provided and maintained by individual industries in their
premises.
2.8 Utilities
The utilities required for the project will be power, water supply. The details are given
in sections below. Total area allotted for common utilities is 6.55 Acres. This will
include Administration Building, common Facilities like water works CETP/ STP,
fire station, water, Police station, bus shelter and social welfare center to facilitate the
Industries within the Industrial Park.
2.8.1 Power Requirement
The total power requirement for the project is estimated to be 70 MVA. Three-
phase electrical power supply will provide through the nearest available Sub-
Station. The power requirement is tentatively calculated by giving numbers for
Rakamcherla IP – EIA Project Description
28
Figure 2.7 Access road to site from SH 4
2.7.3 Green Belt Development
10 m width buffer Zone (Green Belt) will be provided all along the boundary of
Industrial Park. Open space area of 16.81 Acres (14.94%) is earmarked for green
belt development. Apart from this green belt area, the individual industries will
develop greenbelt at their individual unit premises as per the norms. Green belt
will be proposed on the median of roads and avenue plantation also. Adequate
green belt will be provided and maintained by individual industries in their
premises.
2.8 Utilities
The utilities required for the project will be power, water supply. The details are given
in sections below. Total area allotted for common utilities is 6.55 Acres. This will
include Administration Building, common Facilities like water works CETP/ STP,
fire station, water, Police station, bus shelter and social welfare center to facilitate the
Industries within the Industrial Park.
2.8.1 Power Requirement
The total power requirement for the project is estimated to be 70 MVA. Three-
phase electrical power supply will provide through the nearest available Sub-
Station. The power requirement is tentatively calculated by giving numbers for
Rakamcherla IP – EIA Project Description
28
Figure 2.7 Access road to site from SH 4
2.7.3 Green Belt Development
10 m width buffer Zone (Green Belt) will be provided all along the boundary of
Industrial Park. Open space area of 16.81 Acres (14.94%) is earmarked for green
belt development. Apart from this green belt area, the individual industries will
develop greenbelt at their individual unit premises as per the norms. Green belt
will be proposed on the median of roads and avenue plantation also. Adequate
green belt will be provided and maintained by individual industries in their
premises.
2.8 Utilities
The utilities required for the project will be power, water supply. The details are given
in sections below. Total area allotted for common utilities is 6.55 Acres. This will
include Administration Building, common Facilities like water works CETP/ STP,
fire station, water, Police station, bus shelter and social welfare center to facilitate the
Industries within the Industrial Park.
2.8.1 Power Requirement
The total power requirement for the project is estimated to be 70 MVA. Three-
phase electrical power supply will provide through the nearest available Sub-
Station. The power requirement is tentatively calculated by giving numbers for
Rakamcherla IP – EIA Project Description
29
proposed industries. The numbers are tentative only and may vary during
execution.
2.8.1.1 Electrical Substation
To cater the electrical needs of the proposed Industrial Park, TSIIC hasallocated an extent of 10 Acres.
2.8.2 Water Requirement
2.8.2.1 Construction Phase
During the construction phase, the water requirement for the project is
calculated around 200 KLD. The breakup of water requirement is given in
Table 2-5. Only infrastructure development like provision of storm water drain,
laying of roads, water supply line, providing substation, green belt in common
area, common facilities are under the scope of TSIIC.
Table 2.5 Water Requirement during Construction Phase
S.No Activities Water Requirement (KLD)
1 Labors 15
2 Water for Construction activities 135
3 Other activities (including green
belt development)50
Total 200
2.8.2.2 Operation Phase
The Domestic water requirements for the 1000 employees are estimated as
45KLD and for process water requirement as 405KLD. The total of 450 KLD
of water can be sustainably abstracted from ground water sources and can be
allotted to the industries on the First cum first basis.
The Water required for Green Belt will be used from Recycle Water of STP.
Development status of Ground Water in the area along with Hydrogeology
report is enclosed in Annexure-8.
Rakamcherla IP – EIA Project Description
29
proposed industries. The numbers are tentative only and may vary during
execution.
2.8.1.1 Electrical Substation
To cater the electrical needs of the proposed Industrial Park, TSIIC hasallocated an extent of 10 Acres.
2.8.2 Water Requirement
2.8.2.1 Construction Phase
During the construction phase, the water requirement for the project is
calculated around 200 KLD. The breakup of water requirement is given in
Table 2-5. Only infrastructure development like provision of storm water drain,
laying of roads, water supply line, providing substation, green belt in common
area, common facilities are under the scope of TSIIC.
Table 2.5 Water Requirement during Construction Phase
S.No Activities Water Requirement (KLD)
1 Labors 15
2 Water for Construction activities 135
3 Other activities (including green
belt development)50
Total 200
2.8.2.2 Operation Phase
The Domestic water requirements for the 1000 employees are estimated as
45KLD and for process water requirement as 405KLD. The total of 450 KLD
of water can be sustainably abstracted from ground water sources and can be
allotted to the industries on the First cum first basis.
The Water required for Green Belt will be used from Recycle Water of STP.
Development status of Ground Water in the area along with Hydrogeology
report is enclosed in Annexure-8.
Rakamcherla IP – EIA Project Description
29
proposed industries. The numbers are tentative only and may vary during
execution.
2.8.1.1 Electrical Substation
To cater the electrical needs of the proposed Industrial Park, TSIIC hasallocated an extent of 10 Acres.
2.8.2 Water Requirement
2.8.2.1 Construction Phase
During the construction phase, the water requirement for the project is
calculated around 200 KLD. The breakup of water requirement is given in
Table 2-5. Only infrastructure development like provision of storm water drain,
laying of roads, water supply line, providing substation, green belt in common
area, common facilities are under the scope of TSIIC.
Table 2.5 Water Requirement during Construction Phase
S.No Activities Water Requirement (KLD)
1 Labors 15
2 Water for Construction activities 135
3 Other activities (including green
belt development)50
Total 200
2.8.2.2 Operation Phase
The Domestic water requirements for the 1000 employees are estimated as
45KLD and for process water requirement as 405KLD. The total of 450 KLD
of water can be sustainably abstracted from ground water sources and can be
allotted to the industries on the First cum first basis.
The Water required for Green Belt will be used from Recycle Water of STP.
Development status of Ground Water in the area along with Hydrogeology
report is enclosed in Annexure-8.
Rakamcherla IP – EIA Project Description
30
2.8.2.3 Waste Water generation
Water pollution from the process can be divided into process and domestic
water. Individual industry upon establishment will have their own facility for
treating their sewage and effluent water.
Space has been provided within the Industrial Park for the provision of CETP,
once the need for CETP arises, stake holders will form SPV and will take up
CETP.
During the operation phase, the domestic waste water estimated to be about
43KLD and the process Effluent estimated to be about 345KLD which will be
treated in STP/ETP, established by the individual industry.
Table 2.6 Water Requirement for Proposed Industries
S.No PurposeMan
power
Total WaterRequirement
(KLD)
Sewage/Effluentgenerates
(KLD)
Treatment proposed
1 Domestic 1000 45 43 Individual industry upon
establishment will have their own
facility for treating their sewage
and effluent water.
The treated water will be re
utilized for suitable purposes.
2 Industrialprocess
- 405 345
Total 450 388
Rakamcherla IP – EIA Project Description
30
2.8.2.3 Waste Water generation
Water pollution from the process can be divided into process and domestic
water. Individual industry upon establishment will have their own facility for
treating their sewage and effluent water.
Space has been provided within the Industrial Park for the provision of CETP,
once the need for CETP arises, stake holders will form SPV and will take up
CETP.
During the operation phase, the domestic waste water estimated to be about
43KLD and the process Effluent estimated to be about 345KLD which will be
treated in STP/ETP, established by the individual industry.
Table 2.6 Water Requirement for Proposed Industries
S.No PurposeMan
power
Total WaterRequirement
(KLD)
Sewage/Effluentgenerates
(KLD)
Treatment proposed
1 Domestic 1000 45 43 Individual industry upon
establishment will have their own
facility for treating their sewage
and effluent water.
The treated water will be re
utilized for suitable purposes.
2 Industrialprocess
- 405 345
Total 450 388
Rakamcherla IP – EIA Project Description
30
2.8.2.3 Waste Water generation
Water pollution from the process can be divided into process and domestic
water. Individual industry upon establishment will have their own facility for
treating their sewage and effluent water.
Space has been provided within the Industrial Park for the provision of CETP,
once the need for CETP arises, stake holders will form SPV and will take up
CETP.
During the operation phase, the domestic waste water estimated to be about
43KLD and the process Effluent estimated to be about 345KLD which will be
treated in STP/ETP, established by the individual industry.
Table 2.6 Water Requirement for Proposed Industries
S.No PurposeMan
power
Total WaterRequirement
(KLD)
Sewage/Effluentgenerates
(KLD)
Treatment proposed
1 Domestic 1000 45 43 Individual industry upon
establishment will have their own
facility for treating their sewage
and effluent water.
The treated water will be re
utilized for suitable purposes.
2 Industrialprocess
- 405 345
Total 450 388
Rakamcherla IP – EIA Project Description
31
Figure 2.8 Water Balance Chart
2.8.3 Rain Water/Storm Water Drain
The site will have well designed storm water drain to carry runoff; the adequate
rain water harvesting pits will be constructed with in the individual industries
premises and other all possible places with in the I.P. The excess storm water will
be diverted based on the natural slope/stream.
2.8.4 Solid and Hazardous Wastes
During construction phase, around 200 persons will be working. The Municipal
Solid Waste generated during construction phase is given in Table 2-7.
Treated WaterTotal Water Demand: 450 KLD
Domestic water requirement: 45 KLD Water for Process:405 KLD
Sewage Generation: 43KLD
STP in Individual Industry
Process Effluentgenerated: 345 KLD
Treatment in ETP inIndividual Industry
Net Water Requirement: 105KLD
Treated WaterTreated Water
Gardening/ Flushing
Rakamcherla IP – EIA Project Description
31
Figure 2.8 Water Balance Chart
2.8.3 Rain Water/Storm Water Drain
The site will have well designed storm water drain to carry runoff; the adequate
rain water harvesting pits will be constructed with in the individual industries
premises and other all possible places with in the I.P. The excess storm water will
be diverted based on the natural slope/stream.
2.8.4 Solid and Hazardous Wastes
During construction phase, around 200 persons will be working. The Municipal
Solid Waste generated during construction phase is given in Table 2-7.
Treated WaterTotal Water Demand: 450 KLD
Domestic water requirement: 45 KLD Water for Process:405 KLD
Sewage Generation: 43KLD
STP in Individual Industry
Process Effluentgenerated: 345 KLD
Treatment in ETP inIndividual Industry
Net Water Requirement: 105KLD
Treated WaterTreated Water
Gardening/ Flushing
Rakamcherla IP – EIA Project Description
31
Figure 2.8 Water Balance Chart
2.8.3 Rain Water/Storm Water Drain
The site will have well designed storm water drain to carry runoff; the adequate
rain water harvesting pits will be constructed with in the individual industries
premises and other all possible places with in the I.P. The excess storm water will
be diverted based on the natural slope/stream.
2.8.4 Solid and Hazardous Wastes
During construction phase, around 200 persons will be working. The Municipal
Solid Waste generated during construction phase is given in Table 2-7.
Treated WaterTotal Water Demand: 450 KLD
Domestic water requirement: 45 KLD Water for Process:405 KLD
Sewage Generation: 43KLD
STP in Individual Industry
Process Effluentgenerated: 345 KLD
Treatment in ETP inIndividual Industry
Net Water Requirement: 105KLD
Treated WaterTreated Water
Gardening/ Flushing
Rakamcherla IP – EIA Project Description
32
Table 2.7 Municipal waste generated during construction phase
S.No Waste Quantity(Kg/Day)
Treatment/ disposal
1 Organic waste 36 Will be segregatedand disposed to localauthorities
2 Inorganic waste 44 Will be segregatedand sold toauthorized vendors
During the operation phase around 1000 persons will be working at different places
within the Industrial Park. The process waste considered as per the standards of 20
kg/T for the metallurgical industries with a capacity of 1000T/A Plant each of 10
industries. The STP Sludge developed by individual industry is used as manure for
green belt. The Solid Waste generated during operation phase is given in Table 2-8.
Table 2.8 Solid & Hazardous Waste details of Allotted & Proposed Industries
S.No Waste Quantity Treatment/ disposal
1. Organic waste 180 Kg/Day Will be segregated and disposed to localauthorities by individual industries
2. Inorganic waste 220 Kg/Day Will be segregated and sold toauthorized vendors by individualindustries
3. Process Waste for10 steel ReRolling industries
1000 T/A Steel scrap has been recycled or sold toauthorized vendors.
During the operation phase the hazardous waste generated by the industries will be
either recycled or sent to authorized recyclers / TSDF facility for disposal based on the
type of waste. It will be the sole responsibility of the individual industries to manage the
hazardous waste generated from the operations of industries.
Rakamcherla IP – EIA Project Description
32
Table 2.7 Municipal waste generated during construction phase
S.No Waste Quantity(Kg/Day)
Treatment/ disposal
1 Organic waste 36 Will be segregatedand disposed to localauthorities
2 Inorganic waste 44 Will be segregatedand sold toauthorized vendors
During the operation phase around 1000 persons will be working at different places
within the Industrial Park. The process waste considered as per the standards of 20
kg/T for the metallurgical industries with a capacity of 1000T/A Plant each of 10
industries. The STP Sludge developed by individual industry is used as manure for
green belt. The Solid Waste generated during operation phase is given in Table 2-8.
Table 2.8 Solid & Hazardous Waste details of Allotted & Proposed Industries
S.No Waste Quantity Treatment/ disposal
1. Organic waste 180 Kg/Day Will be segregated and disposed to localauthorities by individual industries
2. Inorganic waste 220 Kg/Day Will be segregated and sold toauthorized vendors by individualindustries
3. Process Waste for10 steel ReRolling industries
1000 T/A Steel scrap has been recycled or sold toauthorized vendors.
During the operation phase the hazardous waste generated by the industries will be
either recycled or sent to authorized recyclers / TSDF facility for disposal based on the
type of waste. It will be the sole responsibility of the individual industries to manage the
hazardous waste generated from the operations of industries.
Rakamcherla IP – EIA Project Description
32
Table 2.7 Municipal waste generated during construction phase
S.No Waste Quantity(Kg/Day)
Treatment/ disposal
1 Organic waste 36 Will be segregatedand disposed to localauthorities
2 Inorganic waste 44 Will be segregatedand sold toauthorized vendors
During the operation phase around 1000 persons will be working at different places
within the Industrial Park. The process waste considered as per the standards of 20
kg/T for the metallurgical industries with a capacity of 1000T/A Plant each of 10
industries. The STP Sludge developed by individual industry is used as manure for
green belt. The Solid Waste generated during operation phase is given in Table 2-8.
Table 2.8 Solid & Hazardous Waste details of Allotted & Proposed Industries
S.No Waste Quantity Treatment/ disposal
1. Organic waste 180 Kg/Day Will be segregated and disposed to localauthorities by individual industries
2. Inorganic waste 220 Kg/Day Will be segregated and sold toauthorized vendors by individualindustries
3. Process Waste for10 steel ReRolling industries
1000 T/A Steel scrap has been recycled or sold toauthorized vendors.
During the operation phase the hazardous waste generated by the industries will be
either recycled or sent to authorized recyclers / TSDF facility for disposal based on the
type of waste. It will be the sole responsibility of the individual industries to manage the
hazardous waste generated from the operations of industries.
Rakamcherla IP – EIA Project Description
33
2.9 Project Cost
The estimate cost for development of Industrial Park is estimated at a cost of
Rs.798.50 Lakhs. The detailed break up of project cost is given in Table 2-9.
Table 2.9 Project Cost
S.No Activities Proposed Expenditure
(in Lakhs)
1 Fencing and avenue plantation 22.502 Roads & Strom Water drains 460.00
3 Water supply 166.004 Power supply including substation 150.00
Total 798.50
Rakamcherla IP – EIA Project Description
33
2.9 Project Cost
The estimate cost for development of Industrial Park is estimated at a cost of
Rs.798.50 Lakhs. The detailed break up of project cost is given in Table 2-9.
Table 2.9 Project Cost
S.No Activities Proposed Expenditure
(in Lakhs)
1 Fencing and avenue plantation 22.502 Roads & Strom Water drains 460.00
3 Water supply 166.004 Power supply including substation 150.00
Total 798.50
Rakamcherla IP – EIA Project Description
33
2.9 Project Cost
The estimate cost for development of Industrial Park is estimated at a cost of
Rs.798.50 Lakhs. The detailed break up of project cost is given in Table 2-9.
Table 2.9 Project Cost
S.No Activities Proposed Expenditure
(in Lakhs)
1 Fencing and avenue plantation 22.502 Roads & Strom Water drains 460.00
3 Water supply 166.004 Power supply including substation 150.00
Total 798.50
Rakamcherla IP – EIA Description of Environment
34
Chapter 3
Description of Environment
Rakamcherla IP – EIA Description of Environment
34
Chapter 3
Description of Environment
Rakamcherla IP – EIA Description of Environment
34
Chapter 3
Description of Environment
Rakamcherla IP – EIA Description of Environment
35
3 Description of Environment
3.1 Scope of Study
The objective of the present study is to assess environmental impacts due to proposed
Industrial Park. The area covering 15Km radial distance around the Project site has been
delineated as study area.
The pre-project status of environmental quality is assessed through field surveys
corresponding to different components of environment, viz. air, noise, water, land,
biology/ecology and socio-economics. The current environmental quality status around
the project site becomes the baseline status for proposed Project but at the same time it
does include the environmental impacts from the already existing industrial area,
commercial, infrastructure activities as well as residential zones in the study area. In this
EIA study, the baseline status of all environmental components has been monitored
during March to May 2014.
3.2 Location
The Study Area within 10 km radius zone comprises of parts of Pudur, Pargi, Vikarbad
and Dharur Mandals of Rangareddy District, Telangana State. The study area (15 km
radius from the project boundary) lies between Latitudes 17°10’ and 17.20’ N and
Longitude 77°54’ and 78°03’ E and forms part of the Survey of India Toposheet Nos. 56
G15, G16, 56K 3 and 4, The project site is well connected by Railway and Roads.
Besides these, there is a good network of moterable roads in the study area. The map
showing the project study area is given in Figure 3-1.
Rakamcherla IP – EIA Description of Environment
35
3 Description of Environment
3.1 Scope of Study
The objective of the present study is to assess environmental impacts due to proposed
Industrial Park. The area covering 15Km radial distance around the Project site has been
delineated as study area.
The pre-project status of environmental quality is assessed through field surveys
corresponding to different components of environment, viz. air, noise, water, land,
biology/ecology and socio-economics. The current environmental quality status around
the project site becomes the baseline status for proposed Project but at the same time it
does include the environmental impacts from the already existing industrial area,
commercial, infrastructure activities as well as residential zones in the study area. In this
EIA study, the baseline status of all environmental components has been monitored
during March to May 2014.
3.2 Location
The Study Area within 10 km radius zone comprises of parts of Pudur, Pargi, Vikarbad
and Dharur Mandals of Rangareddy District, Telangana State. The study area (15 km
radius from the project boundary) lies between Latitudes 17°10’ and 17.20’ N and
Longitude 77°54’ and 78°03’ E and forms part of the Survey of India Toposheet Nos. 56
G15, G16, 56K 3 and 4, The project site is well connected by Railway and Roads.
Besides these, there is a good network of moterable roads in the study area. The map
showing the project study area is given in Figure 3-1.
Rakamcherla IP – EIA Description of Environment
35
3 Description of Environment
3.1 Scope of Study
The objective of the present study is to assess environmental impacts due to proposed
Industrial Park. The area covering 15Km radial distance around the Project site has been
delineated as study area.
The pre-project status of environmental quality is assessed through field surveys
corresponding to different components of environment, viz. air, noise, water, land,
biology/ecology and socio-economics. The current environmental quality status around
the project site becomes the baseline status for proposed Project but at the same time it
does include the environmental impacts from the already existing industrial area,
commercial, infrastructure activities as well as residential zones in the study area. In this
EIA study, the baseline status of all environmental components has been monitored
during March to May 2014.
3.2 Location
The Study Area within 10 km radius zone comprises of parts of Pudur, Pargi, Vikarbad
and Dharur Mandals of Rangareddy District, Telangana State. The study area (15 km
radius from the project boundary) lies between Latitudes 17°10’ and 17.20’ N and
Longitude 77°54’ and 78°03’ E and forms part of the Survey of India Toposheet Nos. 56
G15, G16, 56K 3 and 4, The project site is well connected by Railway and Roads.
Besides these, there is a good network of moterable roads in the study area. The map
showing the project study area is given in Figure 3-1.
Rakamcherla IP – EIA Description of Environment
36
Figure 3.1 Project Site Showing the administrative Setup
Rakamcherla IP – EIA Description of Environment
36
Figure 3.1 Project Site Showing the administrative Setup
Rakamcherla IP – EIA Description of Environment
36
Figure 3.1 Project Site Showing the administrative Setup
Rakamcherla IP – EIA Description of Environment
37
Figure 3.2 Topo map showing the project site and its surrounding features
3.3 Climate
The climate is characterized by hot summer and is generally dry except during the
southwest monsoon. The climate is distinguished by four seasons:
Hot Summer (from March to May)
South west monsoon season (from June to September)
Post monsoon season (October and November)
Cold winter (from December to February).
The following sections describe the key elements of the climate, viz., temperature, wind,
rainfall and relative humidity and evaporation.
The annual temperature in the project region ranges between 18C - 43C. May is the
hottest month with a mean max of 43C. With the advance of south west monsoon into
Rakamcherla IP – EIA Description of Environment
37
Figure 3.2 Topo map showing the project site and its surrounding features
3.3 Climate
The climate is characterized by hot summer and is generally dry except during the
southwest monsoon. The climate is distinguished by four seasons:
Hot Summer (from March to May)
South west monsoon season (from June to September)
Post monsoon season (October and November)
Cold winter (from December to February).
The following sections describe the key elements of the climate, viz., temperature, wind,
rainfall and relative humidity and evaporation.
The annual temperature in the project region ranges between 18C - 43C. May is the
hottest month with a mean max of 43C. With the advance of south west monsoon into
Rakamcherla IP – EIA Description of Environment
37
Figure 3.2 Topo map showing the project site and its surrounding features
3.3 Climate
The climate is characterized by hot summer and is generally dry except during the
southwest monsoon. The climate is distinguished by four seasons:
Hot Summer (from March to May)
South west monsoon season (from June to September)
Post monsoon season (October and November)
Cold winter (from December to February).
The following sections describe the key elements of the climate, viz., temperature, wind,
rainfall and relative humidity and evaporation.
The annual temperature in the project region ranges between 18C - 43C. May is the
hottest month with a mean max of 43C. With the advance of south west monsoon into
Rakamcherla IP – EIA Description of Environment
38
the area, by the middle of June, day temperature drop is observed. By about the first week
of October the monsoon, the temperature drops to about 18C. The monthly temperature
range is lowest in August because of overcast conditions and highest in March on the
contrary.
3.4 Rainfall
The actual annual rainfall in the project districts varies from 807.3mm to 913.8mm with
the months of August and September receiving the most. The bulk of the annual rainfall
is received during the southwest monsoon. The Vikarabad district rainfall (mm) is given
in the Table 3-1 below.
Table 3.1 Climatic Condition in Vikarabad district in 2014
Month Rainfall(mm)
Normal
Temperature (0C) RelativeHumidity (%)
Mean windspeed (kmph)
NormalMaximum Minimum
January 5.0 28.6 14.6 57 06February 3.0 31.2 18.7 49 07March 7.0 34.8 21.1 40 08April 15.0 36.9 23.0 42 08May 31.0 38.7 26.7 44 12June 104.0 34.1 24.8 64 14July 183.0 29.8 23.0 73 14August 172.0 29.5 22.0 78 13September 128.0 29.7 22.3 74 10October 98.0 30.3 20.5 66 07November 30.0 28.7 17.5 59 06December 5.0 27.8 14.9 53 06
Table 3.2 Rainfall distribution during the respective seasons
Season Months Normal Rainfall (mm)
Hot weather March – May 53.0 (6.8%)
South west Monsoon June – September 587.0 (75.16 %)
North east Monsoon Oct – December 133.0 (17.03 %)
Winter Jan – February 8.0 (1.01%)
Rakamcherla IP – EIA Description of Environment
38
the area, by the middle of June, day temperature drop is observed. By about the first week
of October the monsoon, the temperature drops to about 18C. The monthly temperature
range is lowest in August because of overcast conditions and highest in March on the
contrary.
3.4 Rainfall
The actual annual rainfall in the project districts varies from 807.3mm to 913.8mm with
the months of August and September receiving the most. The bulk of the annual rainfall
is received during the southwest monsoon. The Vikarabad district rainfall (mm) is given
in the Table 3-1 below.
Table 3.1 Climatic Condition in Vikarabad district in 2014
Month Rainfall(mm)
Normal
Temperature (0C) RelativeHumidity (%)
Mean windspeed (kmph)
NormalMaximum Minimum
January 5.0 28.6 14.6 57 06February 3.0 31.2 18.7 49 07March 7.0 34.8 21.1 40 08April 15.0 36.9 23.0 42 08May 31.0 38.7 26.7 44 12June 104.0 34.1 24.8 64 14July 183.0 29.8 23.0 73 14August 172.0 29.5 22.0 78 13September 128.0 29.7 22.3 74 10October 98.0 30.3 20.5 66 07November 30.0 28.7 17.5 59 06December 5.0 27.8 14.9 53 06
Table 3.2 Rainfall distribution during the respective seasons
Season Months Normal Rainfall (mm)
Hot weather March – May 53.0 (6.8%)
South west Monsoon June – September 587.0 (75.16 %)
North east Monsoon Oct – December 133.0 (17.03 %)
Winter Jan – February 8.0 (1.01%)
Rakamcherla IP – EIA Description of Environment
38
the area, by the middle of June, day temperature drop is observed. By about the first week
of October the monsoon, the temperature drops to about 18C. The monthly temperature
range is lowest in August because of overcast conditions and highest in March on the
contrary.
3.4 Rainfall
The actual annual rainfall in the project districts varies from 807.3mm to 913.8mm with
the months of August and September receiving the most. The bulk of the annual rainfall
is received during the southwest monsoon. The Vikarabad district rainfall (mm) is given
in the Table 3-1 below.
Table 3.1 Climatic Condition in Vikarabad district in 2014
Month Rainfall(mm)
Normal
Temperature (0C) RelativeHumidity (%)
Mean windspeed (kmph)
NormalMaximum Minimum
January 5.0 28.6 14.6 57 06February 3.0 31.2 18.7 49 07March 7.0 34.8 21.1 40 08April 15.0 36.9 23.0 42 08May 31.0 38.7 26.7 44 12June 104.0 34.1 24.8 64 14July 183.0 29.8 23.0 73 14August 172.0 29.5 22.0 78 13September 128.0 29.7 22.3 74 10October 98.0 30.3 20.5 66 07November 30.0 28.7 17.5 59 06December 5.0 27.8 14.9 53 06
Table 3.2 Rainfall distribution during the respective seasons
Season Months Normal Rainfall (mm)
Hot weather March – May 53.0 (6.8%)
South west Monsoon June – September 587.0 (75.16 %)
North east Monsoon Oct – December 133.0 (17.03 %)
Winter Jan – February 8.0 (1.01%)
Rakamcherla IP – EIA Description of Environment
39
Figure 3.3 Monthly and Annual Rainfall of Vikarabad District (Source IMD)
Rakamcherla IP – EIA Description of Environment
39
Figure 3.3 Monthly and Annual Rainfall of Vikarabad District (Source IMD)
Rakamcherla IP – EIA Description of Environment
39
Figure 3.3 Monthly and Annual Rainfall of Vikarabad District (Source IMD)
Rakamcherla IP – EIA Description of Environment
40
Figure 3.4 Rainfall pattern in Vikarabad District
Figure 3.5 Deviation of rainfall from Normal for Vikarabad District
The 10 years monthly rainfall for the Vikarabad district has been collected from the
Indian Meteorological Department (IMD). The normal annual rainfall in the district is
around 781mm. The study area receives fairly good amount of rainfall during Southwest
monsoon. The monthly normal, yearly rainfall and deviation of rainfall from Normal for
the Vikarabad district is presented in the above Graphs.
From the above it is clear that the project area receives fairly a good amount of rainfall.
Around 70 % of the rainfall occurs during South west monsoon and the remaining rainfall
occurs during Northeast and Transitional period.
Rakamcherla IP – EIA Description of Environment
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Figure 3.4 Rainfall pattern in Vikarabad District
Figure 3.5 Deviation of rainfall from Normal for Vikarabad District
The 10 years monthly rainfall for the Vikarabad district has been collected from the
Indian Meteorological Department (IMD). The normal annual rainfall in the district is
around 781mm. The study area receives fairly good amount of rainfall during Southwest
monsoon. The monthly normal, yearly rainfall and deviation of rainfall from Normal for
the Vikarabad district is presented in the above Graphs.
From the above it is clear that the project area receives fairly a good amount of rainfall.
Around 70 % of the rainfall occurs during South west monsoon and the remaining rainfall
occurs during Northeast and Transitional period.
Rakamcherla IP – EIA Description of Environment
40
Figure 3.4 Rainfall pattern in Vikarabad District
Figure 3.5 Deviation of rainfall from Normal for Vikarabad District
The 10 years monthly rainfall for the Vikarabad district has been collected from the
Indian Meteorological Department (IMD). The normal annual rainfall in the district is
around 781mm. The study area receives fairly good amount of rainfall during Southwest
monsoon. The monthly normal, yearly rainfall and deviation of rainfall from Normal for
the Vikarabad district is presented in the above Graphs.
From the above it is clear that the project area receives fairly a good amount of rainfall.
Around 70 % of the rainfall occurs during South west monsoon and the remaining rainfall
occurs during Northeast and Transitional period.
Rakamcherla IP – EIA Description of Environment
41
Out of 10 years, 4 years the study area received more than normal rainfall. Maximum
rainfall received was during 2010 for the past 10 years.
3.5 Micrometeorology
The micro-meteorological conditions in study area during air quality study period are of
importance to understand the variations in ambient air quality status in study region. The
prevailing micrometeorology at project site plays a crucial role in transport and dispersion
of air pollutants released from the plant. The principal variables are horizontal transport
and dispersion (average wind speed and directions), convective transport and vertical
mixing (atmospheric stability) and also topography of the area as local influences. For
determining the prevailing micro-meteorological conditions during the study period, an
automatic continuous digital weather station was installed at project site.
The location is chosen such that there is no obstruction to the flow of wind and sunlight.
The hourly meteorological data of wind speed, wind direction, temperature and solar
radiation were recorded at the project site. These frequencies were computed on 12 hours
basis and the corresponding results are used to draw wind rose for 07hrs to 19hrs
corresponding to study period as shown in subsequent sections. The terrain is flat and
elevation varied from 3-5 m above mean sea level when one travels from coast and
landward. The wind rose for the months of March, April and May 2014 shows the
predominant wind directions. Winds are light & moderate with some strengthening in the
period from May to August. During the post-monsoon and cold season, winds blow
mostly from the east or north-east. By March, south westerlies and westerlies start
blowing and continue during the rest of summer.
The south west monsoon season winds are mostly from directions between south-west
and North-West. The percentage frequency occurrence of calm winds is very high
contributing 54% and 50% of the time in post-monsoon and winter seasons, respectively.
During these seasons the easterly winds become stronger. The general dominant flow
pattern is westerly during monsoon while the flow pattern is easterly in the post-monsoon
and winter seasons. A moderately high percentage frequency of occurrence of calm
conditions was observed during all the seasons. In the month of March to May 2014 the
wind blows towards SE- ESE & NW.
Rakamcherla IP – EIA Description of Environment
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Out of 10 years, 4 years the study area received more than normal rainfall. Maximum
rainfall received was during 2010 for the past 10 years.
3.5 Micrometeorology
The micro-meteorological conditions in study area during air quality study period are of
importance to understand the variations in ambient air quality status in study region. The
prevailing micrometeorology at project site plays a crucial role in transport and dispersion
of air pollutants released from the plant. The principal variables are horizontal transport
and dispersion (average wind speed and directions), convective transport and vertical
mixing (atmospheric stability) and also topography of the area as local influences. For
determining the prevailing micro-meteorological conditions during the study period, an
automatic continuous digital weather station was installed at project site.
The location is chosen such that there is no obstruction to the flow of wind and sunlight.
The hourly meteorological data of wind speed, wind direction, temperature and solar
radiation were recorded at the project site. These frequencies were computed on 12 hours
basis and the corresponding results are used to draw wind rose for 07hrs to 19hrs
corresponding to study period as shown in subsequent sections. The terrain is flat and
elevation varied from 3-5 m above mean sea level when one travels from coast and
landward. The wind rose for the months of March, April and May 2014 shows the
predominant wind directions. Winds are light & moderate with some strengthening in the
period from May to August. During the post-monsoon and cold season, winds blow
mostly from the east or north-east. By March, south westerlies and westerlies start
blowing and continue during the rest of summer.
The south west monsoon season winds are mostly from directions between south-west
and North-West. The percentage frequency occurrence of calm winds is very high
contributing 54% and 50% of the time in post-monsoon and winter seasons, respectively.
During these seasons the easterly winds become stronger. The general dominant flow
pattern is westerly during monsoon while the flow pattern is easterly in the post-monsoon
and winter seasons. A moderately high percentage frequency of occurrence of calm
conditions was observed during all the seasons. In the month of March to May 2014 the
wind blows towards SE- ESE & NW.
Rakamcherla IP – EIA Description of Environment
41
Out of 10 years, 4 years the study area received more than normal rainfall. Maximum
rainfall received was during 2010 for the past 10 years.
3.5 Micrometeorology
The micro-meteorological conditions in study area during air quality study period are of
importance to understand the variations in ambient air quality status in study region. The
prevailing micrometeorology at project site plays a crucial role in transport and dispersion
of air pollutants released from the plant. The principal variables are horizontal transport
and dispersion (average wind speed and directions), convective transport and vertical
mixing (atmospheric stability) and also topography of the area as local influences. For
determining the prevailing micro-meteorological conditions during the study period, an
automatic continuous digital weather station was installed at project site.
The location is chosen such that there is no obstruction to the flow of wind and sunlight.
The hourly meteorological data of wind speed, wind direction, temperature and solar
radiation were recorded at the project site. These frequencies were computed on 12 hours
basis and the corresponding results are used to draw wind rose for 07hrs to 19hrs
corresponding to study period as shown in subsequent sections. The terrain is flat and
elevation varied from 3-5 m above mean sea level when one travels from coast and
landward. The wind rose for the months of March, April and May 2014 shows the
predominant wind directions. Winds are light & moderate with some strengthening in the
period from May to August. During the post-monsoon and cold season, winds blow
mostly from the east or north-east. By March, south westerlies and westerlies start
blowing and continue during the rest of summer.
The south west monsoon season winds are mostly from directions between south-west
and North-West. The percentage frequency occurrence of calm winds is very high
contributing 54% and 50% of the time in post-monsoon and winter seasons, respectively.
During these seasons the easterly winds become stronger. The general dominant flow
pattern is westerly during monsoon while the flow pattern is easterly in the post-monsoon
and winter seasons. A moderately high percentage frequency of occurrence of calm
conditions was observed during all the seasons. In the month of March to May 2014 the
wind blows towards SE- ESE & NW.
Rakamcherla IP – EIA Description of Environment
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Table 3.3 Meteorological Observations (March-May)
S.No Parameter Observation
1 Wind Direction SE-ESE & NW2 Wind Speed Range 4-25 Km/hr3 Average Wind Speed 5.6 Kmph4 Temperature Range 20-360C5 Average Temperature 300C6 Humidity Range 60-95%
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Table 3.3 Meteorological Observations (March-May)
S.No Parameter Observation
1 Wind Direction SE-ESE & NW2 Wind Speed Range 4-25 Km/hr3 Average Wind Speed 5.6 Kmph4 Temperature Range 20-360C5 Average Temperature 300C6 Humidity Range 60-95%
Rakamcherla IP – EIA Description of Environment
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Table 3.3 Meteorological Observations (March-May)
S.No Parameter Observation
1 Wind Direction SE-ESE & NW2 Wind Speed Range 4-25 Km/hr3 Average Wind Speed 5.6 Kmph4 Temperature Range 20-360C5 Average Temperature 300C6 Humidity Range 60-95%
Rakamcherla IP – EIA Description of Environment
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Figure 3.6 Wind Rose Diagrams in the month of March to May 2014
3.6 Air Environment
Assessment of baseline ambient air quality status in the vicinity of industrial site is an
indispensable part of environmental impact assessment studies. The pre-project air
quality status serves as the baseline upon which the predicted air pollution impacts from
the proposed projects could be superimposed to derive the final (post-project) status of air
environment in the project region. The tropical climatic conditions, especially monsoon
winds prevailing over India mainly control the transport and dispersion of air pollutants
during different seasons. According to the climatological conditions in India, the seasons
considered for all practical purposes in air pollution studies are winter, summer and post-
monsoon seasons. Significant changes, in predominant winds and weather conditions are
observed in these seasons apart from the local topographic influences.
The baseline studies for air environment covers identification of specific air pollutants
expected to have significant impacts from the proposed project along with the
conventional/criteria air pollutants and assessing their prevailing levels in ambient air at
optimum representative locations within the impact zone. The environmental impact
Rakamcherla IP – EIA Description of Environment
43
Figure 3.6 Wind Rose Diagrams in the month of March to May 2014
3.6 Air Environment
Assessment of baseline ambient air quality status in the vicinity of industrial site is an
indispensable part of environmental impact assessment studies. The pre-project air
quality status serves as the baseline upon which the predicted air pollution impacts from
the proposed projects could be superimposed to derive the final (post-project) status of air
environment in the project region. The tropical climatic conditions, especially monsoon
winds prevailing over India mainly control the transport and dispersion of air pollutants
during different seasons. According to the climatological conditions in India, the seasons
considered for all practical purposes in air pollution studies are winter, summer and post-
monsoon seasons. Significant changes, in predominant winds and weather conditions are
observed in these seasons apart from the local topographic influences.
The baseline studies for air environment covers identification of specific air pollutants
expected to have significant impacts from the proposed project along with the
conventional/criteria air pollutants and assessing their prevailing levels in ambient air at
optimum representative locations within the impact zone. The environmental impact
Rakamcherla IP – EIA Description of Environment
43
Figure 3.6 Wind Rose Diagrams in the month of March to May 2014
3.6 Air Environment
Assessment of baseline ambient air quality status in the vicinity of industrial site is an
indispensable part of environmental impact assessment studies. The pre-project air
quality status serves as the baseline upon which the predicted air pollution impacts from
the proposed projects could be superimposed to derive the final (post-project) status of air
environment in the project region. The tropical climatic conditions, especially monsoon
winds prevailing over India mainly control the transport and dispersion of air pollutants
during different seasons. According to the climatological conditions in India, the seasons
considered for all practical purposes in air pollution studies are winter, summer and post-
monsoon seasons. Significant changes, in predominant winds and weather conditions are
observed in these seasons apart from the local topographic influences.
The baseline studies for air environment covers identification of specific air pollutants
expected to have significant impacts from the proposed project along with the
conventional/criteria air pollutants and assessing their prevailing levels in ambient air at
optimum representative locations within the impact zone. The environmental impact
Rakamcherla IP – EIA Description of Environment
44
assessment study requires monitoring of baseline status during one season (preferably
non-monsoon season). The baseline status of air environment in the study area is assessed
through a systematic air quality surveillance programme.
10 ambient air quality stations were proposed within a radius of 10 km from the project
site. The air quality stations were selected based on the predominant wind direction, wind
speed and atmospheric stability category in the region which governs the plume rise and
dispersion of air pollutants. Selection of the stations were also based on locations of
existing sources of air pollution and sensitive receptors such as hospitals, schools, thickly
populated residential localities, elderly homes etc.,
3.6.1 Reconnaissance Survey
Reconnaissance survey was conducted up to 10 km radius from the project site. The
study area is situated in an uneven terrain with ground elevation varying from 580 - 725
m above mean sea level. The surrounding impact zone of 5 km radial distance
consisting of the rural and industrial areas is marked. In general the study area
experiences predominant wind from NW and SE direction during the season March –
May 2014. The baseline status of air environment included identification of specific air
pollution parameters expected to have significant impacts and assessing their existing
levels in ambient air within the impact zone. The baseline status of air environment
with respect to the identified air pollutants can be assessed through air quality
monitoring programme using methodically designed air monitoring network.
To establish the baseline monitoring status of air environment in the study area during
the period of March, April & May 2014, 10 AAQM locations were selected using
network design criteria and monitored as per CPCB guidelines (Twice a week sampling
and 24 hr continuous sampling each day). The selected sampling locations are reported
in Table below. All the 12 parameters mentioned as per National Ambient Air Quality
Standards (NAAQ’S) were analyzed. The location of monitoring is given in Table 3-4.
Rakamcherla IP – EIA Description of Environment
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assessment study requires monitoring of baseline status during one season (preferably
non-monsoon season). The baseline status of air environment in the study area is assessed
through a systematic air quality surveillance programme.
10 ambient air quality stations were proposed within a radius of 10 km from the project
site. The air quality stations were selected based on the predominant wind direction, wind
speed and atmospheric stability category in the region which governs the plume rise and
dispersion of air pollutants. Selection of the stations were also based on locations of
existing sources of air pollution and sensitive receptors such as hospitals, schools, thickly
populated residential localities, elderly homes etc.,
3.6.1 Reconnaissance Survey
Reconnaissance survey was conducted up to 10 km radius from the project site. The
study area is situated in an uneven terrain with ground elevation varying from 580 - 725
m above mean sea level. The surrounding impact zone of 5 km radial distance
consisting of the rural and industrial areas is marked. In general the study area
experiences predominant wind from NW and SE direction during the season March –
May 2014. The baseline status of air environment included identification of specific air
pollution parameters expected to have significant impacts and assessing their existing
levels in ambient air within the impact zone. The baseline status of air environment
with respect to the identified air pollutants can be assessed through air quality
monitoring programme using methodically designed air monitoring network.
To establish the baseline monitoring status of air environment in the study area during
the period of March, April & May 2014, 10 AAQM locations were selected using
network design criteria and monitored as per CPCB guidelines (Twice a week sampling
and 24 hr continuous sampling each day). The selected sampling locations are reported
in Table below. All the 12 parameters mentioned as per National Ambient Air Quality
Standards (NAAQ’S) were analyzed. The location of monitoring is given in Table 3-4.
Rakamcherla IP – EIA Description of Environment
44
assessment study requires monitoring of baseline status during one season (preferably
non-monsoon season). The baseline status of air environment in the study area is assessed
through a systematic air quality surveillance programme.
10 ambient air quality stations were proposed within a radius of 10 km from the project
site. The air quality stations were selected based on the predominant wind direction, wind
speed and atmospheric stability category in the region which governs the plume rise and
dispersion of air pollutants. Selection of the stations were also based on locations of
existing sources of air pollution and sensitive receptors such as hospitals, schools, thickly
populated residential localities, elderly homes etc.,
3.6.1 Reconnaissance Survey
Reconnaissance survey was conducted up to 10 km radius from the project site. The
study area is situated in an uneven terrain with ground elevation varying from 580 - 725
m above mean sea level. The surrounding impact zone of 5 km radial distance
consisting of the rural and industrial areas is marked. In general the study area
experiences predominant wind from NW and SE direction during the season March –
May 2014. The baseline status of air environment included identification of specific air
pollution parameters expected to have significant impacts and assessing their existing
levels in ambient air within the impact zone. The baseline status of air environment
with respect to the identified air pollutants can be assessed through air quality
monitoring programme using methodically designed air monitoring network.
To establish the baseline monitoring status of air environment in the study area during
the period of March, April & May 2014, 10 AAQM locations were selected using
network design criteria and monitored as per CPCB guidelines (Twice a week sampling
and 24 hr continuous sampling each day). The selected sampling locations are reported
in Table below. All the 12 parameters mentioned as per National Ambient Air Quality
Standards (NAAQ’S) were analyzed. The location of monitoring is given in Table 3-4.
Rakamcherla IP – EIA Description of Environment
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Table 3.4 Ambient Air Quality Monitoring Locations
S.No Sampling Stations GeographicalCoordinates
Aerial distancefrom the site in
(km)
Directionwith respect
to site
1. AAQ1Site entrance
N-17°14’45.5”E-77°57’48.8”
- Within Site
2. AAQ2Site (south end)
N-17°14’26.21”E-77°57’55.53”
0.5 Within Site
3. AAQ3Rakamcherla village
N-17°14’23.4”E-77°57’24.48”
1.3 WNW
4. AAQ4Nazeerabad
N-17°10’22.6”E-77°54’19.8”
9.8 SW
5. AAQ5Rukumpalle
N-17°12’13.6”E-77°51’45.2”
10.0 W
6. AAQ6Kankal
N-17°12’17.1”E-78°00’24.4”
6.3 SE
7. AAQ7Changomul
N-17°15’27.1”E-78°01’34.0”
6.57 ENE
8. AAQ8Manneguda
N-17°18’03.0”E-77°58’54.7”
6.50 N
9. AAQ9Manchanpally
N-17°10’44.2”E-77°58’08.5”
7.51 S
10. AAQ10Burgupalle
N-17°16’37.88”E-77°53’48.09”
8.4 NW
Rakamcherla IP – EIA Description of Environment
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Table 3.4 Ambient Air Quality Monitoring Locations
S.No Sampling Stations GeographicalCoordinates
Aerial distancefrom the site in
(km)
Directionwith respect
to site
1. AAQ1Site entrance
N-17°14’45.5”E-77°57’48.8”
- Within Site
2. AAQ2Site (south end)
N-17°14’26.21”E-77°57’55.53”
0.5 Within Site
3. AAQ3Rakamcherla village
N-17°14’23.4”E-77°57’24.48”
1.3 WNW
4. AAQ4Nazeerabad
N-17°10’22.6”E-77°54’19.8”
9.8 SW
5. AAQ5Rukumpalle
N-17°12’13.6”E-77°51’45.2”
10.0 W
6. AAQ6Kankal
N-17°12’17.1”E-78°00’24.4”
6.3 SE
7. AAQ7Changomul
N-17°15’27.1”E-78°01’34.0”
6.57 ENE
8. AAQ8Manneguda
N-17°18’03.0”E-77°58’54.7”
6.50 N
9. AAQ9Manchanpally
N-17°10’44.2”E-77°58’08.5”
7.51 S
10. AAQ10Burgupalle
N-17°16’37.88”E-77°53’48.09”
8.4 NW
Rakamcherla IP – EIA Description of Environment
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Table 3.4 Ambient Air Quality Monitoring Locations
S.No Sampling Stations GeographicalCoordinates
Aerial distancefrom the site in
(km)
Directionwith respect
to site
1. AAQ1Site entrance
N-17°14’45.5”E-77°57’48.8”
- Within Site
2. AAQ2Site (south end)
N-17°14’26.21”E-77°57’55.53”
0.5 Within Site
3. AAQ3Rakamcherla village
N-17°14’23.4”E-77°57’24.48”
1.3 WNW
4. AAQ4Nazeerabad
N-17°10’22.6”E-77°54’19.8”
9.8 SW
5. AAQ5Rukumpalle
N-17°12’13.6”E-77°51’45.2”
10.0 W
6. AAQ6Kankal
N-17°12’17.1”E-78°00’24.4”
6.3 SE
7. AAQ7Changomul
N-17°15’27.1”E-78°01’34.0”
6.57 ENE
8. AAQ8Manneguda
N-17°18’03.0”E-77°58’54.7”
6.50 N
9. AAQ9Manchanpally
N-17°10’44.2”E-77°58’08.5”
7.51 S
10. AAQ10Burgupalle
N-17°16’37.88”E-77°53’48.09”
8.4 NW
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Figure 3.7 Air quality monitoring sampling locations map (10Km Radius)
Rakamcherla IP – EIA Description of Environment
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Figure 3.7 Air quality monitoring sampling locations map (10Km Radius)
Rakamcherla IP – EIA Description of Environment
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Figure 3.7 Air quality monitoring sampling locations map (10Km Radius)
Rakamcherla IP – EIA Description of Environment
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Figure 3.8 Photographs (clockwise from top left) of Noise, Water, meteorology, Air and soilmonitoring in the study area
Rakamcherla IP – EIA Description of Environment
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Figure 3.8 Photographs (clockwise from top left) of Noise, Water, meteorology, Air and soilmonitoring in the study area
Rakamcherla IP – EIA Description of Environment
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Figure 3.8 Photographs (clockwise from top left) of Noise, Water, meteorology, Air and soilmonitoring in the study area
Rakamcherla IP – EIA Description of Environment
48
3.6.2 Baseline Status
The mean value of Particulate Matter (PM2.5), Particulate Matter (PM10), Sulphur
Dioxide (SO2), Nitrogen Dioxide (NO2), CO μg/m3, Pb μg/m3, O3, NH3, Benzene,
Benzo (a) pyrene, As and Ni at various monitoring locations during the AAQ
monitoring period were monitored and tabulated. The concentration of SO2 ranged
from 5.2 to 10.4 μg/m3 across the sampling stations. The highest concentration of SO2
μg/m3 was observed at Manchanpally (AAQ9). The concentration of NO2 ranged from
9.3 to 15.3 μg/m3 across the sampling stations. The highest concentration of NO2 15.3
μg/m3 was also observed at Manchanpally (AAQ9). This may be due to the movement
of vehicles at this region. The concentration of SO2 and NO2 are well within the
standards. The concentration of PM2.5 was found to be below the permissible limit of
60μg/m3 at all the sampling stations. The concentrations O3, Pb, NH3, Benzene, Benzo
(a) pyrene, As and Ni were Below Detectable Level (BDL) at all the sampling stations.
All the above parameters were observed to be well below the CPCB prescribed
standards at all the sampling stations. The average result of monitoring is given in
Table 3-5.
Table 3.5 Test Methods for the Analysis of Ambient Air Quality Parameters
S.No Parameters Analytical method NAAQ standards: 2009
1.Sulphur Dioxide (SO2),
μg/m3
IS:5182(Part-2):2001
(Reaff:2006)50 (Annual) 80 (24 Hours)
2.Nitrogen Dioxide
(NO2), μg/m3 IS: 5182 (Part - 6): 2006 40 (Annual) 80 (24 Hours)
3.Particulate Matter
(PM2.5), μg/m3
IS: 5182 (Part - 23):
200640 (Annual) 60 (24 hours)
4.Particulate Matter
(PM10), μg/m3 IS:5182 (Part– 23): 2006 60 (Annual) 100(24 hours)
5. CO μg/m3 IS:5182(Part–10):1999
(Reaff:2006)2 (8 hours) 4 (1hour)
6. Pb μg/m3 IS:5182(Part–22):2004
(Reaff:2006)0.5(Annual) 1 (24 hours)
7. O3, μg/m3 IS: 5182 (Part – 9): 1974 100(8hours) 180 (1hour)
8. NH3, μg/m3 APHA(air) 2nd edition 100(Annual) 400 (24 hours)
Rakamcherla IP – EIA Description of Environment
48
3.6.2 Baseline Status
The mean value of Particulate Matter (PM2.5), Particulate Matter (PM10), Sulphur
Dioxide (SO2), Nitrogen Dioxide (NO2), CO μg/m3, Pb μg/m3, O3, NH3, Benzene,
Benzo (a) pyrene, As and Ni at various monitoring locations during the AAQ
monitoring period were monitored and tabulated. The concentration of SO2 ranged
from 5.2 to 10.4 μg/m3 across the sampling stations. The highest concentration of SO2
μg/m3 was observed at Manchanpally (AAQ9). The concentration of NO2 ranged from
9.3 to 15.3 μg/m3 across the sampling stations. The highest concentration of NO2 15.3
μg/m3 was also observed at Manchanpally (AAQ9). This may be due to the movement
of vehicles at this region. The concentration of SO2 and NO2 are well within the
standards. The concentration of PM2.5 was found to be below the permissible limit of
60μg/m3 at all the sampling stations. The concentrations O3, Pb, NH3, Benzene, Benzo
(a) pyrene, As and Ni were Below Detectable Level (BDL) at all the sampling stations.
All the above parameters were observed to be well below the CPCB prescribed
standards at all the sampling stations. The average result of monitoring is given in
Table 3-5.
Table 3.5 Test Methods for the Analysis of Ambient Air Quality Parameters
S.No Parameters Analytical method NAAQ standards: 2009
1.Sulphur Dioxide (SO2),
μg/m3
IS:5182(Part-2):2001
(Reaff:2006)50 (Annual) 80 (24 Hours)
2.Nitrogen Dioxide
(NO2), μg/m3 IS: 5182 (Part - 6): 2006 40 (Annual) 80 (24 Hours)
3.Particulate Matter
(PM2.5), μg/m3
IS: 5182 (Part - 23):
200640 (Annual) 60 (24 hours)
4.Particulate Matter
(PM10), μg/m3 IS:5182 (Part– 23): 2006 60 (Annual) 100(24 hours)
5. CO μg/m3 IS:5182(Part–10):1999
(Reaff:2006)2 (8 hours) 4 (1hour)
6. Pb μg/m3 IS:5182(Part–22):2004
(Reaff:2006)0.5(Annual) 1 (24 hours)
7. O3, μg/m3 IS: 5182 (Part – 9): 1974 100(8hours) 180 (1hour)
8. NH3, μg/m3 APHA(air) 2nd edition 100(Annual) 400 (24 hours)
Rakamcherla IP – EIA Description of Environment
48
3.6.2 Baseline Status
The mean value of Particulate Matter (PM2.5), Particulate Matter (PM10), Sulphur
Dioxide (SO2), Nitrogen Dioxide (NO2), CO μg/m3, Pb μg/m3, O3, NH3, Benzene,
Benzo (a) pyrene, As and Ni at various monitoring locations during the AAQ
monitoring period were monitored and tabulated. The concentration of SO2 ranged
from 5.2 to 10.4 μg/m3 across the sampling stations. The highest concentration of SO2
μg/m3 was observed at Manchanpally (AAQ9). The concentration of NO2 ranged from
9.3 to 15.3 μg/m3 across the sampling stations. The highest concentration of NO2 15.3
μg/m3 was also observed at Manchanpally (AAQ9). This may be due to the movement
of vehicles at this region. The concentration of SO2 and NO2 are well within the
standards. The concentration of PM2.5 was found to be below the permissible limit of
60μg/m3 at all the sampling stations. The concentrations O3, Pb, NH3, Benzene, Benzo
(a) pyrene, As and Ni were Below Detectable Level (BDL) at all the sampling stations.
All the above parameters were observed to be well below the CPCB prescribed
standards at all the sampling stations. The average result of monitoring is given in
Table 3-5.
Table 3.5 Test Methods for the Analysis of Ambient Air Quality Parameters
S.No Parameters Analytical method NAAQ standards: 2009
1.Sulphur Dioxide (SO2),
μg/m3
IS:5182(Part-2):2001
(Reaff:2006)50 (Annual) 80 (24 Hours)
2.Nitrogen Dioxide
(NO2), μg/m3 IS: 5182 (Part - 6): 2006 40 (Annual) 80 (24 Hours)
3.Particulate Matter
(PM2.5), μg/m3
IS: 5182 (Part - 23):
200640 (Annual) 60 (24 hours)
4.Particulate Matter
(PM10), μg/m3 IS:5182 (Part– 23): 2006 60 (Annual) 100(24 hours)
5. CO μg/m3 IS:5182(Part–10):1999
(Reaff:2006)2 (8 hours) 4 (1hour)
6. Pb μg/m3 IS:5182(Part–22):2004
(Reaff:2006)0.5(Annual) 1 (24 hours)
7. O3, μg/m3 IS: 5182 (Part – 9): 1974 100(8hours) 180 (1hour)
8. NH3, μg/m3 APHA(air) 2nd edition 100(Annual) 400 (24 hours)
Rakamcherla IP – EIA Description of Environment
49
(Indophenol-blue
method)
9. Benzene, μg/m3 IS:5182(Part–11):1999
(RA:2009)5 (Annual) 5 (Annual)
10. Benzo (a) pyrene, ng/m3 IS:5182(Part–12):2004(RA:2009)
1 (Annual) 1 (Annual)
11. Arsenic, ng/ m3 APHA (air) 2nd edition 6 (Annual) 6 (Annual)
12. Nickel, ng/ m3 APHA (air) 2nd edition 20 (Annual) 20 (Annual)
Rakamcherla IP – EIA Description of Environment
49
(Indophenol-blue
method)
9. Benzene, μg/m3 IS:5182(Part–11):1999
(RA:2009)5 (Annual) 5 (Annual)
10. Benzo (a) pyrene, ng/m3 IS:5182(Part–12):2004(RA:2009)
1 (Annual) 1 (Annual)
11. Arsenic, ng/ m3 APHA (air) 2nd edition 6 (Annual) 6 (Annual)
12. Nickel, ng/ m3 APHA (air) 2nd edition 20 (Annual) 20 (Annual)
Rakamcherla IP – EIA Description of Environment
49
(Indophenol-blue
method)
9. Benzene, μg/m3 IS:5182(Part–11):1999
(RA:2009)5 (Annual) 5 (Annual)
10. Benzo (a) pyrene, ng/m3 IS:5182(Part–12):2004(RA:2009)
1 (Annual) 1 (Annual)
11. Arsenic, ng/ m3 APHA (air) 2nd edition 6 (Annual) 6 (Annual)
12. Nickel, ng/ m3 APHA (air) 2nd edition 20 (Annual) 20 (Annual)
Rakamcherla IP – EIA Description of Environment
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Table 3.6 Average Ambient Air Quality Monitoring Data (March to May, 2015)
S.No Samplingstations
Parameters
SO2
μg/m3
NO2
μg/m3
PM2.5
μg/m3
PM10
μg/m3
CO
mg/m3
Pb
μg/m3
O3
μg/m3
NH3
μg/m3
Benz-ene
µg/m3
Benzo (a)pyreneng/m3
As
ng/m3
Ni
ng/m3
1. AAQ1Site entrance
5.4 10.3 12.5 20.5 0.02 BDL BDL BDL BDL BDL BDL BDL
2. AAQ2Site (southend)
6.3 11.2 14.8 26.4 0.03 BDL BDL BDL BDL BDL BDL BDL
3. AAQ3Rakamcherlavillage
6.5 9.3 15.0 28.5 0.04 BDL BDL BDL BDL BDL BDL BDL
4. AAQ4Nazeerabad
7.2 13.8 11.0 20.6 0.05 BDL BDL BDL BDL BDL BDL BDL
5. AAQ5Rukumpalle
4.8 9.7 15.3 25.6 0.04 BDL BDL BDL BDL BDL BDL BDL
6. AAQ6Kankal
8.7 12.5 16.4 26.5 0.04 BDL BDL BDL BDL BDL BDL BDL
7. AAQ7Changomul
6.8 14.7 21.0 32.5 0.025 BDL BDL BDL BDL BDL BDL BDL
Rakamcherla IP – EIA Description of Environment
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Table 3.6 Average Ambient Air Quality Monitoring Data (March to May, 2015)
S.No Samplingstations
Parameters
SO2
μg/m3
NO2
μg/m3
PM2.5
μg/m3
PM10
μg/m3
CO
mg/m3
Pb
μg/m3
O3
μg/m3
NH3
μg/m3
Benz-ene
µg/m3
Benzo (a)pyreneng/m3
As
ng/m3
Ni
ng/m3
1. AAQ1Site entrance
5.4 10.3 12.5 20.5 0.02 BDL BDL BDL BDL BDL BDL BDL
2. AAQ2Site (southend)
6.3 11.2 14.8 26.4 0.03 BDL BDL BDL BDL BDL BDL BDL
3. AAQ3Rakamcherlavillage
6.5 9.3 15.0 28.5 0.04 BDL BDL BDL BDL BDL BDL BDL
4. AAQ4Nazeerabad
7.2 13.8 11.0 20.6 0.05 BDL BDL BDL BDL BDL BDL BDL
5. AAQ5Rukumpalle
4.8 9.7 15.3 25.6 0.04 BDL BDL BDL BDL BDL BDL BDL
6. AAQ6Kankal
8.7 12.5 16.4 26.5 0.04 BDL BDL BDL BDL BDL BDL BDL
7. AAQ7Changomul
6.8 14.7 21.0 32.5 0.025 BDL BDL BDL BDL BDL BDL BDL
Rakamcherla IP – EIA Description of Environment
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Table 3.6 Average Ambient Air Quality Monitoring Data (March to May, 2015)
S.No Samplingstations
Parameters
SO2
μg/m3
NO2
μg/m3
PM2.5
μg/m3
PM10
μg/m3
CO
mg/m3
Pb
μg/m3
O3
μg/m3
NH3
μg/m3
Benz-ene
µg/m3
Benzo (a)pyreneng/m3
As
ng/m3
Ni
ng/m3
1. AAQ1Site entrance
5.4 10.3 12.5 20.5 0.02 BDL BDL BDL BDL BDL BDL BDL
2. AAQ2Site (southend)
6.3 11.2 14.8 26.4 0.03 BDL BDL BDL BDL BDL BDL BDL
3. AAQ3Rakamcherlavillage
6.5 9.3 15.0 28.5 0.04 BDL BDL BDL BDL BDL BDL BDL
4. AAQ4Nazeerabad
7.2 13.8 11.0 20.6 0.05 BDL BDL BDL BDL BDL BDL BDL
5. AAQ5Rukumpalle
4.8 9.7 15.3 25.6 0.04 BDL BDL BDL BDL BDL BDL BDL
6. AAQ6Kankal
8.7 12.5 16.4 26.5 0.04 BDL BDL BDL BDL BDL BDL BDL
7. AAQ7Changomul
6.8 14.7 21.0 32.5 0.025 BDL BDL BDL BDL BDL BDL BDL
Rakamcherla IP – EIA Description of Environment
51
S.No Samplingstations
Parameters
SO2
μg/m3
NO2
μg/m3
PM2.5
μg/m3
PM10
μg/m3
CO
mg/m3
Pb
μg/m3
O3
μg/m3
NH3
μg/m3
Benz-ene
µg/m3
Benzo (a)pyreneng/m3
As
ng/m3
Ni
ng/m3
8. AAQ8Manneguda
8.3 12.1 18.5 28.6 0.016 BDL BDL BDL BDL BDL BDL BDL
9. AAQ9Manchanpally
10.4 15.3 14.6 26.3 0.320 BDL BDL BDL BDL BDL BDL BDL
10. AAQ10Burgupalle
5.2 10.3 15.7 27.7 0.040 BDL BDL BDL BDL BDL BDL BDL
NAAQ Standards(for 24 hrs)
80 80 60 100 4.0 1.0 180 400 5.0 1.0 6.0 20.0
(DL for CO = 0.01 mg/m3; O3 = 10 μg/m3 ; Pb = 0.05 μg/m3 ; Benzene = 0.05 μg/m3 ; Benzo (a) pyrene = 0.01 ng/m3 ; As = 0.01 ng/m3 ; Ni = 0.01 ng/m3), (BDL - BelowDetection Limit, DL - Detection Limit)
Rakamcherla IP – EIA Description of Environment
51
S.No Samplingstations
Parameters
SO2
μg/m3
NO2
μg/m3
PM2.5
μg/m3
PM10
μg/m3
CO
mg/m3
Pb
μg/m3
O3
μg/m3
NH3
μg/m3
Benz-ene
µg/m3
Benzo (a)pyreneng/m3
As
ng/m3
Ni
ng/m3
8. AAQ8Manneguda
8.3 12.1 18.5 28.6 0.016 BDL BDL BDL BDL BDL BDL BDL
9. AAQ9Manchanpally
10.4 15.3 14.6 26.3 0.320 BDL BDL BDL BDL BDL BDL BDL
10. AAQ10Burgupalle
5.2 10.3 15.7 27.7 0.040 BDL BDL BDL BDL BDL BDL BDL
NAAQ Standards(for 24 hrs)
80 80 60 100 4.0 1.0 180 400 5.0 1.0 6.0 20.0
(DL for CO = 0.01 mg/m3; O3 = 10 μg/m3 ; Pb = 0.05 μg/m3 ; Benzene = 0.05 μg/m3 ; Benzo (a) pyrene = 0.01 ng/m3 ; As = 0.01 ng/m3 ; Ni = 0.01 ng/m3), (BDL - BelowDetection Limit, DL - Detection Limit)
Rakamcherla IP – EIA Description of Environment
51
S.No Samplingstations
Parameters
SO2
μg/m3
NO2
μg/m3
PM2.5
μg/m3
PM10
μg/m3
CO
mg/m3
Pb
μg/m3
O3
μg/m3
NH3
μg/m3
Benz-ene
µg/m3
Benzo (a)pyreneng/m3
As
ng/m3
Ni
ng/m3
8. AAQ8Manneguda
8.3 12.1 18.5 28.6 0.016 BDL BDL BDL BDL BDL BDL BDL
9. AAQ9Manchanpally
10.4 15.3 14.6 26.3 0.320 BDL BDL BDL BDL BDL BDL BDL
10. AAQ10Burgupalle
5.2 10.3 15.7 27.7 0.040 BDL BDL BDL BDL BDL BDL BDL
NAAQ Standards(for 24 hrs)
80 80 60 100 4.0 1.0 180 400 5.0 1.0 6.0 20.0
(DL for CO = 0.01 mg/m3; O3 = 10 μg/m3 ; Pb = 0.05 μg/m3 ; Benzene = 0.05 μg/m3 ; Benzo (a) pyrene = 0.01 ng/m3 ; As = 0.01 ng/m3 ; Ni = 0.01 ng/m3), (BDL - BelowDetection Limit, DL - Detection Limit)
Rakamcherla IP – EIA Description of Environment
52
3.7 Noise Environment
The noise generated due to operation of individual process units at an industrial project
site cause significant impacts on the surrounding environment including nearby human
habitats. Such operations fall in the category of continuous point sources of noise
generation. There are also some secondary noise sources associated with almost all types
of large scale industrial projects, which are mainly vehicles used for transportation of
materials as well as employees and material handling equipment at the project site.
However, such sources could be categorized as intermittent/continuous noise sources
depending on frequency/intensity.
The prevailing ambient noise level at a particular location is nothing but the resultant
(total) of all kinds of noise sources existing at various distances around that location. The
ambient noise level at a location varies continuously depending on the type of surrounding
activities. The ambient noise levels generally does not reflect any seasonal variation,
however, the weather conditions of wind direction, rain, snow, fog etc., physical
conditions like barrier or any other natural ground variations (topography) as well as
direction of source play significant role in regulating the noise propagation and ultimately
the intensity of its impact.
The status of noise environment within 10 km radius of the project site was assessed
through identification of major noise sources, monitoring of baseline noise levels in the
study area and measurement of resultant noise levels due to existing vehicular movement
on major roads, according to existing land use pattern.
3.7.1 Reconnaissance Survey
Reconnaissance survey was conducted to locate the existing noise generating sources
and identify suitable locations to evaluate background noise levels. The surrounding
impact zone of 10 km radial distance consisting of the rural, urban and industrial areas
is marked. State Highway SH 4 is the access road to the site.
Since the project site is located in rural area there are many small villages which
contribute to baseline noise levels. The vehicular traffic on state highway SH 4
contributes significantly to the noise levels in study area. The commercial activities in
the individual villages also influence the background noise levels. The noise levels in
Rakamcherla IP – EIA Description of Environment
52
3.7 Noise Environment
The noise generated due to operation of individual process units at an industrial project
site cause significant impacts on the surrounding environment including nearby human
habitats. Such operations fall in the category of continuous point sources of noise
generation. There are also some secondary noise sources associated with almost all types
of large scale industrial projects, which are mainly vehicles used for transportation of
materials as well as employees and material handling equipment at the project site.
However, such sources could be categorized as intermittent/continuous noise sources
depending on frequency/intensity.
The prevailing ambient noise level at a particular location is nothing but the resultant
(total) of all kinds of noise sources existing at various distances around that location. The
ambient noise level at a location varies continuously depending on the type of surrounding
activities. The ambient noise levels generally does not reflect any seasonal variation,
however, the weather conditions of wind direction, rain, snow, fog etc., physical
conditions like barrier or any other natural ground variations (topography) as well as
direction of source play significant role in regulating the noise propagation and ultimately
the intensity of its impact.
The status of noise environment within 10 km radius of the project site was assessed
through identification of major noise sources, monitoring of baseline noise levels in the
study area and measurement of resultant noise levels due to existing vehicular movement
on major roads, according to existing land use pattern.
3.7.1 Reconnaissance Survey
Reconnaissance survey was conducted to locate the existing noise generating sources
and identify suitable locations to evaluate background noise levels. The surrounding
impact zone of 10 km radial distance consisting of the rural, urban and industrial areas
is marked. State Highway SH 4 is the access road to the site.
Since the project site is located in rural area there are many small villages which
contribute to baseline noise levels. The vehicular traffic on state highway SH 4
contributes significantly to the noise levels in study area. The commercial activities in
the individual villages also influence the background noise levels. The noise levels in
Rakamcherla IP – EIA Description of Environment
52
3.7 Noise Environment
The noise generated due to operation of individual process units at an industrial project
site cause significant impacts on the surrounding environment including nearby human
habitats. Such operations fall in the category of continuous point sources of noise
generation. There are also some secondary noise sources associated with almost all types
of large scale industrial projects, which are mainly vehicles used for transportation of
materials as well as employees and material handling equipment at the project site.
However, such sources could be categorized as intermittent/continuous noise sources
depending on frequency/intensity.
The prevailing ambient noise level at a particular location is nothing but the resultant
(total) of all kinds of noise sources existing at various distances around that location. The
ambient noise level at a location varies continuously depending on the type of surrounding
activities. The ambient noise levels generally does not reflect any seasonal variation,
however, the weather conditions of wind direction, rain, snow, fog etc., physical
conditions like barrier or any other natural ground variations (topography) as well as
direction of source play significant role in regulating the noise propagation and ultimately
the intensity of its impact.
The status of noise environment within 10 km radius of the project site was assessed
through identification of major noise sources, monitoring of baseline noise levels in the
study area and measurement of resultant noise levels due to existing vehicular movement
on major roads, according to existing land use pattern.
3.7.1 Reconnaissance Survey
Reconnaissance survey was conducted to locate the existing noise generating sources
and identify suitable locations to evaluate background noise levels. The surrounding
impact zone of 10 km radial distance consisting of the rural, urban and industrial areas
is marked. State Highway SH 4 is the access road to the site.
Since the project site is located in rural area there are many small villages which
contribute to baseline noise levels. The vehicular traffic on state highway SH 4
contributes significantly to the noise levels in study area. The commercial activities in
the individual villages also influence the background noise levels. The noise levels in
Rakamcherla IP – EIA Description of Environment
53
surrounding selected villages and junction of the state highways were monitored using
a precision noise level meter.
The community noise is determined by recording the day-night noise level (Ldn). Ldn
is defined as the 24 hours equivalent sound level derived with a penalty of 10 dB(A) is
added to the measured instantaneous noise level measured during night time. i.e., from
22:00 hrs to 06:00 hrs. This is because the same level of noise during night time is more
annoying than day time. Ldn for a given location is calculated from hourly equivalent
sound levels (Leq) using the following equation:
Ldn = 10 log [1/24{16(10(Ld/10)) + 8(10(Ln+10)/10))}]
Where, Ld – equivalent noise level during day time (06:00 to 22:00 hrs)
Ln – equivalent noise level during night time (22:00 to 06:00 hrs)
Table 3.7 Noise level Sampling Monitoring Locations
S.No Sampling
station
Sampling
Code
Geographical
coordinates
Aerial
distance
from the
site in (km)
Direction
with
respect to
site
1. Site entrance N1 N-17°14’45.5”E-77°57’48.8”
- Within Site
2. Site (south end) N2 N-17°14’26.21”E-77°57’55.53”
0.5 Within Site
3. Rakamcherlavillage
N3 N-17°14’23.4”E-77°57’24.48”
1.3 SW
4. Nazeerabad N4 N-17°10’22.6”E-77°54’19.8”
9.8 S
5. Rukumpalle N5 N-17°12’13.6”E-77°51’45.2”
10.0 SW
6. Kankal N6 N-17°12’17.1”E-78°00’24.4”
6.3 SE
7. Changomul N7 N-17°15’27.1”E-78°01’34.0”
6.57 E
8. Manneguda N8 N-17°18’03.0”E-77°58’54.7”
6.50 N
Rakamcherla IP – EIA Description of Environment
53
surrounding selected villages and junction of the state highways were monitored using
a precision noise level meter.
The community noise is determined by recording the day-night noise level (Ldn). Ldn
is defined as the 24 hours equivalent sound level derived with a penalty of 10 dB(A) is
added to the measured instantaneous noise level measured during night time. i.e., from
22:00 hrs to 06:00 hrs. This is because the same level of noise during night time is more
annoying than day time. Ldn for a given location is calculated from hourly equivalent
sound levels (Leq) using the following equation:
Ldn = 10 log [1/24{16(10(Ld/10)) + 8(10(Ln+10)/10))}]
Where, Ld – equivalent noise level during day time (06:00 to 22:00 hrs)
Ln – equivalent noise level during night time (22:00 to 06:00 hrs)
Table 3.7 Noise level Sampling Monitoring Locations
S.No Sampling
station
Sampling
Code
Geographical
coordinates
Aerial
distance
from the
site in (km)
Direction
with
respect to
site
1. Site entrance N1 N-17°14’45.5”E-77°57’48.8”
- Within Site
2. Site (south end) N2 N-17°14’26.21”E-77°57’55.53”
0.5 Within Site
3. Rakamcherlavillage
N3 N-17°14’23.4”E-77°57’24.48”
1.3 SW
4. Nazeerabad N4 N-17°10’22.6”E-77°54’19.8”
9.8 S
5. Rukumpalle N5 N-17°12’13.6”E-77°51’45.2”
10.0 SW
6. Kankal N6 N-17°12’17.1”E-78°00’24.4”
6.3 SE
7. Changomul N7 N-17°15’27.1”E-78°01’34.0”
6.57 E
8. Manneguda N8 N-17°18’03.0”E-77°58’54.7”
6.50 N
Rakamcherla IP – EIA Description of Environment
53
surrounding selected villages and junction of the state highways were monitored using
a precision noise level meter.
The community noise is determined by recording the day-night noise level (Ldn). Ldn
is defined as the 24 hours equivalent sound level derived with a penalty of 10 dB(A) is
added to the measured instantaneous noise level measured during night time. i.e., from
22:00 hrs to 06:00 hrs. This is because the same level of noise during night time is more
annoying than day time. Ldn for a given location is calculated from hourly equivalent
sound levels (Leq) using the following equation:
Ldn = 10 log [1/24{16(10(Ld/10)) + 8(10(Ln+10)/10))}]
Where, Ld – equivalent noise level during day time (06:00 to 22:00 hrs)
Ln – equivalent noise level during night time (22:00 to 06:00 hrs)
Table 3.7 Noise level Sampling Monitoring Locations
S.No Sampling
station
Sampling
Code
Geographical
coordinates
Aerial
distance
from the
site in (km)
Direction
with
respect to
site
1. Site entrance N1 N-17°14’45.5”E-77°57’48.8”
- Within Site
2. Site (south end) N2 N-17°14’26.21”E-77°57’55.53”
0.5 Within Site
3. Rakamcherlavillage
N3 N-17°14’23.4”E-77°57’24.48”
1.3 SW
4. Nazeerabad N4 N-17°10’22.6”E-77°54’19.8”
9.8 S
5. Rukumpalle N5 N-17°12’13.6”E-77°51’45.2”
10.0 SW
6. Kankal N6 N-17°12’17.1”E-78°00’24.4”
6.3 SE
7. Changomul N7 N-17°15’27.1”E-78°01’34.0”
6.57 E
8. Manneguda N8 N-17°18’03.0”E-77°58’54.7”
6.50 N
Rakamcherla IP – EIA Description of Environment
54
Figure 3.9 Noise Level Monitoring Locations Map (10 Km radius)
3.7.2 Baseline Status
Noise levels in the villages and along Highways within the study area were measured
using a precision microprocessor based digital noise level meter. Taking into
consideration the quieter hour, the minimum equivalent noise level at a particular
place is called the background noise level.
During the study period day time noise levels varied from 40 to 53 dB (A) across the
sampling stations and night time noise levels varied from 30 to 46 dB (A) across the
9. Manchanpally N9 N-17°10’44.2”E-77°58’08.5”
7.51 S
10. Burgupalle N10 N-17°16’37.88”E-77°53’48.09”
8.4 NW
Rakamcherla IP – EIA Description of Environment
54
Figure 3.9 Noise Level Monitoring Locations Map (10 Km radius)
3.7.2 Baseline Status
Noise levels in the villages and along Highways within the study area were measured
using a precision microprocessor based digital noise level meter. Taking into
consideration the quieter hour, the minimum equivalent noise level at a particular
place is called the background noise level.
During the study period day time noise levels varied from 40 to 53 dB (A) across the
sampling stations and night time noise levels varied from 30 to 46 dB (A) across the
9. Manchanpally N9 N-17°10’44.2”E-77°58’08.5”
7.51 S
10. Burgupalle N10 N-17°16’37.88”E-77°53’48.09”
8.4 NW
Rakamcherla IP – EIA Description of Environment
54
Figure 3.9 Noise Level Monitoring Locations Map (10 Km radius)
3.7.2 Baseline Status
Noise levels in the villages and along Highways within the study area were measured
using a precision microprocessor based digital noise level meter. Taking into
consideration the quieter hour, the minimum equivalent noise level at a particular
place is called the background noise level.
During the study period day time noise levels varied from 40 to 53 dB (A) across the
sampling stations and night time noise levels varied from 30 to 46 dB (A) across the
9. Manchanpally N9 N-17°10’44.2”E-77°58’08.5”
7.51 S
10. Burgupalle N10 N-17°16’37.88”E-77°53’48.09”
8.4 NW
Rakamcherla IP – EIA Description of Environment
55
sampling stations. The field observations during the study period indicate that the
ambient noise levels in the study area were well within the prescribed standards at all
the different noise zones prescribed by CPCB. The result details of the monitoring
stations are presented in Table 3.8.
3.7.3 Limits Set by CPCB
Industrial Area : Day Time - 75 dB (A); Night Time - 70 dB (A)
Commercial Area : Day Time - 65 dB (A); Night Time - 55 dB (A)
Residential Area : Day Time - 55 dB (A); Night Time - 45 dB (A)
Silence Zone : Day Time - 50 dB (A); Night Time - 40 dB (A)
Table 3.8 Summary of Noise monitoring in the study area
S.No Location Geographicalcoordinates
Noise level in dB (A)Day Night
1. Site entrance – N1 N-17°14’45.5”E-77°57’48.8”
40 32
2. Site (south end) – N2 N-17°14’26.21”E-77°57’55.53”
45 30
3. Rakamcherla village– N3
N-17°14’23.4”E-77°57’24.48”
41 35
4. Nazeerabad – N4 N-17°10’22.6”E-77°54’19.8”
46 33
5. Rukumpalle – N5 N-17°12’13.6”E-77°51’45.2”
53 46
6. Kankal – N6 N-17°12’17.1”E-78°00’24.4”
49 39
7. Changomul – N7 N-17°15’27.1”E-78°01’34.0”
42 36
8. Manneguda – N8 N-17°18’03.0”E-77°58’54.7”
48 34
9. Manchanpally – N9 N-17°10’44.2”E-77°58’08.5”
50 39
10. Burgupalle – N10 N-17°16’37.88”E-77°53’48.09”
53 46
Rakamcherla IP – EIA Description of Environment
55
sampling stations. The field observations during the study period indicate that the
ambient noise levels in the study area were well within the prescribed standards at all
the different noise zones prescribed by CPCB. The result details of the monitoring
stations are presented in Table 3.8.
3.7.3 Limits Set by CPCB
Industrial Area : Day Time - 75 dB (A); Night Time - 70 dB (A)
Commercial Area : Day Time - 65 dB (A); Night Time - 55 dB (A)
Residential Area : Day Time - 55 dB (A); Night Time - 45 dB (A)
Silence Zone : Day Time - 50 dB (A); Night Time - 40 dB (A)
Table 3.8 Summary of Noise monitoring in the study area
S.No Location Geographicalcoordinates
Noise level in dB (A)Day Night
1. Site entrance – N1 N-17°14’45.5”E-77°57’48.8”
40 32
2. Site (south end) – N2 N-17°14’26.21”E-77°57’55.53”
45 30
3. Rakamcherla village– N3
N-17°14’23.4”E-77°57’24.48”
41 35
4. Nazeerabad – N4 N-17°10’22.6”E-77°54’19.8”
46 33
5. Rukumpalle – N5 N-17°12’13.6”E-77°51’45.2”
53 46
6. Kankal – N6 N-17°12’17.1”E-78°00’24.4”
49 39
7. Changomul – N7 N-17°15’27.1”E-78°01’34.0”
42 36
8. Manneguda – N8 N-17°18’03.0”E-77°58’54.7”
48 34
9. Manchanpally – N9 N-17°10’44.2”E-77°58’08.5”
50 39
10. Burgupalle – N10 N-17°16’37.88”E-77°53’48.09”
53 46
Rakamcherla IP – EIA Description of Environment
55
sampling stations. The field observations during the study period indicate that the
ambient noise levels in the study area were well within the prescribed standards at all
the different noise zones prescribed by CPCB. The result details of the monitoring
stations are presented in Table 3.8.
3.7.3 Limits Set by CPCB
Industrial Area : Day Time - 75 dB (A); Night Time - 70 dB (A)
Commercial Area : Day Time - 65 dB (A); Night Time - 55 dB (A)
Residential Area : Day Time - 55 dB (A); Night Time - 45 dB (A)
Silence Zone : Day Time - 50 dB (A); Night Time - 40 dB (A)
Table 3.8 Summary of Noise monitoring in the study area
S.No Location Geographicalcoordinates
Noise level in dB (A)Day Night
1. Site entrance – N1 N-17°14’45.5”E-77°57’48.8”
40 32
2. Site (south end) – N2 N-17°14’26.21”E-77°57’55.53”
45 30
3. Rakamcherla village– N3
N-17°14’23.4”E-77°57’24.48”
41 35
4. Nazeerabad – N4 N-17°10’22.6”E-77°54’19.8”
46 33
5. Rukumpalle – N5 N-17°12’13.6”E-77°51’45.2”
53 46
6. Kankal – N6 N-17°12’17.1”E-78°00’24.4”
49 39
7. Changomul – N7 N-17°15’27.1”E-78°01’34.0”
42 36
8. Manneguda – N8 N-17°18’03.0”E-77°58’54.7”
48 34
9. Manchanpally – N9 N-17°10’44.2”E-77°58’08.5”
50 39
10. Burgupalle – N10 N-17°16’37.88”E-77°53’48.09”
53 46
Rakamcherla IP – EIA Description of Environment
56
The field observations during the study period indicate that the ambient noise levels in the
study area were well within the prescribed standards at all the different noise zones
prescribed by CPCB.
3.8 Water Environment
The impacts on water environment are inherent part of any major developmental projects
in two ways: one is stress on water resources (continuous withdrawal of large quantities of
water) and the other is pollution impacts through discharge of effluents. These impacts
may be on either or both surface and groundwater resources in the project area depending
on the specific situation. To address these issues it is necessary to take a stock of available
water resources in project area with respect to their existing quality as well as their
supportive capacity to represent the baseline status of water environment.
The existing water resources, both surface and ground water with the corresponding
significance are identified within the study area around proposed Project of TSIIC. The
representative sampling locations for surface water and groundwater are selected through
reconnaissance of project area to assess the existing (pre-project) status of water quality in
the study area. Physico-chemical, nutrient, Oxygen demand, bacteriological and biological
parameters having relevance to public health and aesthetic significance are selected to
assess the water quality status with special attention to raw water resources and the
receiving body of the treated effluent discharge from proposed project. The standard
methods prescribed for surface, groundwater sampling as well as the analytical procedures
for individual parameters is followed in this study.
3.8.1 Reconnaissance Survey
The Reconnaissance survey was undertaken to ascertain the location of water bodies
viz streams, rivers, lakes, etc. The sampling stations were chosen based on the existing
pollution sources near these water bodies and threat of pollution in the future. The
agriculture practices in study area are predominantly rain fed. The surface water is used
for irrigation purposes wherever available. Ground water is used for irrigation in many
parts of the study area during dry season. Groundwater is the principal source for
domestic and drinking purposes in almost all villages in the study area. The water
Rakamcherla IP – EIA Description of Environment
56
The field observations during the study period indicate that the ambient noise levels in the
study area were well within the prescribed standards at all the different noise zones
prescribed by CPCB.
3.8 Water Environment
The impacts on water environment are inherent part of any major developmental projects
in two ways: one is stress on water resources (continuous withdrawal of large quantities of
water) and the other is pollution impacts through discharge of effluents. These impacts
may be on either or both surface and groundwater resources in the project area depending
on the specific situation. To address these issues it is necessary to take a stock of available
water resources in project area with respect to their existing quality as well as their
supportive capacity to represent the baseline status of water environment.
The existing water resources, both surface and ground water with the corresponding
significance are identified within the study area around proposed Project of TSIIC. The
representative sampling locations for surface water and groundwater are selected through
reconnaissance of project area to assess the existing (pre-project) status of water quality in
the study area. Physico-chemical, nutrient, Oxygen demand, bacteriological and biological
parameters having relevance to public health and aesthetic significance are selected to
assess the water quality status with special attention to raw water resources and the
receiving body of the treated effluent discharge from proposed project. The standard
methods prescribed for surface, groundwater sampling as well as the analytical procedures
for individual parameters is followed in this study.
3.8.1 Reconnaissance Survey
The Reconnaissance survey was undertaken to ascertain the location of water bodies
viz streams, rivers, lakes, etc. The sampling stations were chosen based on the existing
pollution sources near these water bodies and threat of pollution in the future. The
agriculture practices in study area are predominantly rain fed. The surface water is used
for irrigation purposes wherever available. Ground water is used for irrigation in many
parts of the study area during dry season. Groundwater is the principal source for
domestic and drinking purposes in almost all villages in the study area. The water
Rakamcherla IP – EIA Description of Environment
56
The field observations during the study period indicate that the ambient noise levels in the
study area were well within the prescribed standards at all the different noise zones
prescribed by CPCB.
3.8 Water Environment
The impacts on water environment are inherent part of any major developmental projects
in two ways: one is stress on water resources (continuous withdrawal of large quantities of
water) and the other is pollution impacts through discharge of effluents. These impacts
may be on either or both surface and groundwater resources in the project area depending
on the specific situation. To address these issues it is necessary to take a stock of available
water resources in project area with respect to their existing quality as well as their
supportive capacity to represent the baseline status of water environment.
The existing water resources, both surface and ground water with the corresponding
significance are identified within the study area around proposed Project of TSIIC. The
representative sampling locations for surface water and groundwater are selected through
reconnaissance of project area to assess the existing (pre-project) status of water quality in
the study area. Physico-chemical, nutrient, Oxygen demand, bacteriological and biological
parameters having relevance to public health and aesthetic significance are selected to
assess the water quality status with special attention to raw water resources and the
receiving body of the treated effluent discharge from proposed project. The standard
methods prescribed for surface, groundwater sampling as well as the analytical procedures
for individual parameters is followed in this study.
3.8.1 Reconnaissance Survey
The Reconnaissance survey was undertaken to ascertain the location of water bodies
viz streams, rivers, lakes, etc. The sampling stations were chosen based on the existing
pollution sources near these water bodies and threat of pollution in the future. The
agriculture practices in study area are predominantly rain fed. The surface water is used
for irrigation purposes wherever available. Ground water is used for irrigation in many
parts of the study area during dry season. Groundwater is the principal source for
domestic and drinking purposes in almost all villages in the study area. The water
Rakamcherla IP – EIA Description of Environment
57
samples were collected and analyzed by standard test methods which are given in table:
The prevailing status of water quality has been assessed during March, April & May
2014. 10 sampling stations for ground water and 2 sampling stations for surface water
were selected for the study the details are given in table and the findings of the water
quality monitoring study is summarized. The locations of water quality monitoring are
given in Table 3-9.
Table 3.9 Water sampling location details
S.No Samplingstation
Samplinglocation
GPSCoordinates
Aerialdistancefrom the sitein (km)
Direction withrespect to site
1.Ground Water(Bore well)(GWS1)
Mannegudavillage
N-17°18’03.0”E-77°58’54.7”
6.5 N
2.Ground Water(Bore well)(GWS2)
Changomulvillage
N-17°15’27.1”E-78°01’34.0”
6.57 ENE
3.Ground Water(Bore well),(GWS3)
Kankal village N-17°12’17.1”E-78°00’24.4”
6.3 SE
4.Ground Water(Bore well),(GWS4)
NearRakamcherlaIndustrial Park
N-17°14’45.5”E-77°57’48.8”Elev 2290 ft
0.4 N
5.Ground Water(well water),(GWS5)
Rakamcherlavillage
N-17°14’16.4”E-77°57’17.1”
1.4 SW
6.Ground Water(Bore well),(GWS6)
Somangurthyvillage
N-17°13’34.6”E-77°56’08.7”
3.75 SW
7.Ground Water(Bore well),(GWS7)
Manchanpallyvillage
N-17°10’44.2”E-77°58’08.5”
7.17 S
8.Ground Water(Bore well),(GWS8)
Nazeerabadvillage
N-17°10’22.6”E-77°54’19.8”
9.8 SW
9.Ground Water(Bore well),
Rukumpallevillage
N-17°12’13.6”E-77°51’45.2”
10.0 W
Rakamcherla IP – EIA Description of Environment
57
samples were collected and analyzed by standard test methods which are given in table:
The prevailing status of water quality has been assessed during March, April & May
2014. 10 sampling stations for ground water and 2 sampling stations for surface water
were selected for the study the details are given in table and the findings of the water
quality monitoring study is summarized. The locations of water quality monitoring are
given in Table 3-9.
Table 3.9 Water sampling location details
S.No Samplingstation
Samplinglocation
GPSCoordinates
Aerialdistancefrom the sitein (km)
Direction withrespect to site
1.Ground Water(Bore well)(GWS1)
Mannegudavillage
N-17°18’03.0”E-77°58’54.7”
6.5 N
2.Ground Water(Bore well)(GWS2)
Changomulvillage
N-17°15’27.1”E-78°01’34.0”
6.57 ENE
3.Ground Water(Bore well),(GWS3)
Kankal village N-17°12’17.1”E-78°00’24.4”
6.3 SE
4.Ground Water(Bore well),(GWS4)
NearRakamcherlaIndustrial Park
N-17°14’45.5”E-77°57’48.8”Elev 2290 ft
0.4 N
5.Ground Water(well water),(GWS5)
Rakamcherlavillage
N-17°14’16.4”E-77°57’17.1”
1.4 SW
6.Ground Water(Bore well),(GWS6)
Somangurthyvillage
N-17°13’34.6”E-77°56’08.7”
3.75 SW
7.Ground Water(Bore well),(GWS7)
Manchanpallyvillage
N-17°10’44.2”E-77°58’08.5”
7.17 S
8.Ground Water(Bore well),(GWS8)
Nazeerabadvillage
N-17°10’22.6”E-77°54’19.8”
9.8 SW
9.Ground Water(Bore well),
Rukumpallevillage
N-17°12’13.6”E-77°51’45.2”
10.0 W
Rakamcherla IP – EIA Description of Environment
57
samples were collected and analyzed by standard test methods which are given in table:
The prevailing status of water quality has been assessed during March, April & May
2014. 10 sampling stations for ground water and 2 sampling stations for surface water
were selected for the study the details are given in table and the findings of the water
quality monitoring study is summarized. The locations of water quality monitoring are
given in Table 3-9.
Table 3.9 Water sampling location details
S.No Samplingstation
Samplinglocation
GPSCoordinates
Aerialdistancefrom the sitein (km)
Direction withrespect to site
1.Ground Water(Bore well)(GWS1)
Mannegudavillage
N-17°18’03.0”E-77°58’54.7”
6.5 N
2.Ground Water(Bore well)(GWS2)
Changomulvillage
N-17°15’27.1”E-78°01’34.0”
6.57 ENE
3.Ground Water(Bore well),(GWS3)
Kankal village N-17°12’17.1”E-78°00’24.4”
6.3 SE
4.Ground Water(Bore well),(GWS4)
NearRakamcherlaIndustrial Park
N-17°14’45.5”E-77°57’48.8”Elev 2290 ft
0.4 N
5.Ground Water(well water),(GWS5)
Rakamcherlavillage
N-17°14’16.4”E-77°57’17.1”
1.4 SW
6.Ground Water(Bore well),(GWS6)
Somangurthyvillage
N-17°13’34.6”E-77°56’08.7”
3.75 SW
7.Ground Water(Bore well),(GWS7)
Manchanpallyvillage
N-17°10’44.2”E-77°58’08.5”
7.17 S
8.Ground Water(Bore well),(GWS8)
Nazeerabadvillage
N-17°10’22.6”E-77°54’19.8”
9.8 SW
9.Ground Water(Bore well),
Rukumpallevillage
N-17°12’13.6”E-77°51’45.2”
10.0 W
Rakamcherla IP – EIA Description of Environment
58
S.No Samplingstation
Samplinglocation
GPSCoordinates
Aerialdistancefrom the sitein (km)
Direction withrespect to site
(GWS9)
10.Ground Water(Bore well),(GWS10)
Near Burgupallevillage
N-17°16’37.88”E-77°53’48.09”
8.3 NW
11.Surface Water(stream),(SW1),
Near Changomulvillage
N-17°16’15.00”E-78°00’47.10”
5.9 ENE
12.Stream Water,(SW2)
Near Kankalvillage
N-17°13’33.40”E-77°59’12.45”
2.86 SE
Figure 3.10 Water Sampling locations Map (10Km Radius)
Rakamcherla IP – EIA Description of Environment
58
S.No Samplingstation
Samplinglocation
GPSCoordinates
Aerialdistancefrom the sitein (km)
Direction withrespect to site
(GWS9)
10.Ground Water(Bore well),(GWS10)
Near Burgupallevillage
N-17°16’37.88”E-77°53’48.09”
8.3 NW
11.Surface Water(stream),(SW1),
Near Changomulvillage
N-17°16’15.00”E-78°00’47.10”
5.9 ENE
12.Stream Water,(SW2)
Near Kankalvillage
N-17°13’33.40”E-77°59’12.45”
2.86 SE
Figure 3.10 Water Sampling locations Map (10Km Radius)
Rakamcherla IP – EIA Description of Environment
58
S.No Samplingstation
Samplinglocation
GPSCoordinates
Aerialdistancefrom the sitein (km)
Direction withrespect to site
(GWS9)
10.Ground Water(Bore well),(GWS10)
Near Burgupallevillage
N-17°16’37.88”E-77°53’48.09”
8.3 NW
11.Surface Water(stream),(SW1),
Near Changomulvillage
N-17°16’15.00”E-78°00’47.10”
5.9 ENE
12.Stream Water,(SW2)
Near Kankalvillage
N-17°13’33.40”E-77°59’12.45”
2.86 SE
Figure 3.10 Water Sampling locations Map (10Km Radius)
Rakamcherla IP – EIA Description of Environment
59
Table 3.10 Test methods used for the analysis of water quality parameters
3.8.2 Baseline Status
The prevailing (pre-project) status of water quality has been assessed through
identification of water resources and appropriate sampling locations for both surface
and groundwater quality in study area depending on topography, surface runoff as well
as natural drainage systems during Post-monsoon season. Total 12 sampling locations
S.No Parameter Measured Test Method
1. pH (at 25°C) IS:3025 (Part - 11): 1983 (Reaff: 2006)
2. Electrical Conductivity IS:3025 (Part - 14): 1983 (Reaff: 2006)
3. Color IS:3025 (Part- 4) 1983 (Reaff 2006)
4. Total Hardness as CaCO3 IS:3025 (Part - 21) 1983 (Reaff 2006)
5. Total Alkalinity as
CaCO3IS:3025,1 (Part - 23) 1986 (Reaff 2009)
6. Cadmium IS:3025 (Part 41) 1991
7. Chloride as Cl IS:3025 (Part - 32) 1988(Reaff 2009)
8. Total Dissolved Solids IS:3025:1(Part - 16) 1984 (Reaff 2006)
9. Aluminium as Al IS:3025 (Part - 55) 2003 (Reaff 2009)
10. Chromium as Cr IS:3025 (Part - 52) 2003 (Reaff 2009)
11. Lead as Pb IS:3025 (Part - 47) 1994 (Reaff 2009)
12. Zinc as Zn IS:3025 (Part - 49) 1994 (Reaff 2009)
13. Sodium as Na IS:3025,5(Part - 45) 1993 (Reaff 2006)
14. Temperature IS:3025 (Part - 9) 1983 (Reaff 2006)
15. Chemical oxygen
demand as O2IS:3025 (Part-58)-2006
16. Dissolved Oxygen (mg/l) IS:3025 (Part - 38)1989 (Reaff 2009)
17. Salinity -
18. Copper as Cu IS:3025 (Part - 42)1992 (Reaff: 2009)
19. BOD,5 days @200C as
O25210B APHA 22nd Edn 2012
20. Total coliform bacteria
(MPN/100ml)IS:1622 1981 (Reaff: 2009)
21. F-Coli IS:1622, 1981 (Reaff: 2009)
Rakamcherla IP – EIA Description of Environment
59
Table 3.10 Test methods used for the analysis of water quality parameters
3.8.2 Baseline Status
The prevailing (pre-project) status of water quality has been assessed through
identification of water resources and appropriate sampling locations for both surface
and groundwater quality in study area depending on topography, surface runoff as well
as natural drainage systems during Post-monsoon season. Total 12 sampling locations
S.No Parameter Measured Test Method
1. pH (at 25°C) IS:3025 (Part - 11): 1983 (Reaff: 2006)
2. Electrical Conductivity IS:3025 (Part - 14): 1983 (Reaff: 2006)
3. Color IS:3025 (Part- 4) 1983 (Reaff 2006)
4. Total Hardness as CaCO3 IS:3025 (Part - 21) 1983 (Reaff 2006)
5. Total Alkalinity as
CaCO3IS:3025,1 (Part - 23) 1986 (Reaff 2009)
6. Cadmium IS:3025 (Part 41) 1991
7. Chloride as Cl IS:3025 (Part - 32) 1988(Reaff 2009)
8. Total Dissolved Solids IS:3025:1(Part - 16) 1984 (Reaff 2006)
9. Aluminium as Al IS:3025 (Part - 55) 2003 (Reaff 2009)
10. Chromium as Cr IS:3025 (Part - 52) 2003 (Reaff 2009)
11. Lead as Pb IS:3025 (Part - 47) 1994 (Reaff 2009)
12. Zinc as Zn IS:3025 (Part - 49) 1994 (Reaff 2009)
13. Sodium as Na IS:3025,5(Part - 45) 1993 (Reaff 2006)
14. Temperature IS:3025 (Part - 9) 1983 (Reaff 2006)
15. Chemical oxygen
demand as O2IS:3025 (Part-58)-2006
16. Dissolved Oxygen (mg/l) IS:3025 (Part - 38)1989 (Reaff 2009)
17. Salinity -
18. Copper as Cu IS:3025 (Part - 42)1992 (Reaff: 2009)
19. BOD,5 days @200C as
O25210B APHA 22nd Edn 2012
20. Total coliform bacteria
(MPN/100ml)IS:1622 1981 (Reaff: 2009)
21. F-Coli IS:1622, 1981 (Reaff: 2009)
Rakamcherla IP – EIA Description of Environment
59
Table 3.10 Test methods used for the analysis of water quality parameters
3.8.2 Baseline Status
The prevailing (pre-project) status of water quality has been assessed through
identification of water resources and appropriate sampling locations for both surface
and groundwater quality in study area depending on topography, surface runoff as well
as natural drainage systems during Post-monsoon season. Total 12 sampling locations
S.No Parameter Measured Test Method
1. pH (at 25°C) IS:3025 (Part - 11): 1983 (Reaff: 2006)
2. Electrical Conductivity IS:3025 (Part - 14): 1983 (Reaff: 2006)
3. Color IS:3025 (Part- 4) 1983 (Reaff 2006)
4. Total Hardness as CaCO3 IS:3025 (Part - 21) 1983 (Reaff 2006)
5. Total Alkalinity as
CaCO3IS:3025,1 (Part - 23) 1986 (Reaff 2009)
6. Cadmium IS:3025 (Part 41) 1991
7. Chloride as Cl IS:3025 (Part - 32) 1988(Reaff 2009)
8. Total Dissolved Solids IS:3025:1(Part - 16) 1984 (Reaff 2006)
9. Aluminium as Al IS:3025 (Part - 55) 2003 (Reaff 2009)
10. Chromium as Cr IS:3025 (Part - 52) 2003 (Reaff 2009)
11. Lead as Pb IS:3025 (Part - 47) 1994 (Reaff 2009)
12. Zinc as Zn IS:3025 (Part - 49) 1994 (Reaff 2009)
13. Sodium as Na IS:3025,5(Part - 45) 1993 (Reaff 2006)
14. Temperature IS:3025 (Part - 9) 1983 (Reaff 2006)
15. Chemical oxygen
demand as O2IS:3025 (Part-58)-2006
16. Dissolved Oxygen (mg/l) IS:3025 (Part - 38)1989 (Reaff 2009)
17. Salinity -
18. Copper as Cu IS:3025 (Part - 42)1992 (Reaff: 2009)
19. BOD,5 days @200C as
O25210B APHA 22nd Edn 2012
20. Total coliform bacteria
(MPN/100ml)IS:1622 1981 (Reaff: 2009)
21. F-Coli IS:1622, 1981 (Reaff: 2009)
Rakamcherla IP – EIA Description of Environment
60
are identified among that 10 ground water and 2 surface water samples collected at
around 10 Km radius distance.
3.8.2.1 Physico-Chemical Characteristics
The results obtained for Physico-chemical characteristics of surface water
collected during summer season are presented in Table 3-11. The pH of the
surface water was alkaline and ranged from 7.83 to 7.96 across the sampling
stations. The Electrical conductivity of the sample ranged from 820 to 1030 µS/cm
across the sampling stations. The concentration of Total dissolved solids (TDS)
ranged from 540 to 660 mg/l across the sampling stations. The concentration of
chlorides varied from 14.5 to 22.5 mg/l across the sampling stations. The
concentration of sulphate varied from 34.1 to 35.4 mg/l. Other parameters like
Iron, Chromium, and Lead were below the surface water quality standards.
Table 3.11 Results of Surface Water Samples
S. No. Parameters Unit SW1 SW2
1 Colour Hazen BDL (DL1) BDL (DL1)
2 Odour - U/O U/O
3 Turbidity NTU 1 BDL (DL0.1)
4 pH -- 7.83 7.96
5 Conductivity µS/cm 1030 820
6 Total Dissolve Solids mg/l 660 540
7 Alkalinity as CaCO3 mg/l 75 64
8 Total Hardness as CaCo3 mg/l 338 239
9 Calcium as Ca mg/l 76 52
10 Magnesium as Mg mg/l 34 25
11 Chloride as Cl mg/l 14.5 22.5
12 Sulphate as SO4 mg/l 34.1 35.4
13 Nitrate as NO3 mg/l 1.2 2.5
14 Fluorides as F mg/l 0.34 0.41
15 Cadmium mg/l BDL BDL
16 Total Chromium mg/l BDL (DL 0.01) BDL (DL 0.01)
17 Iron mg/l 0.17 0.22
18 Copper mg/l 0.16 0.6
Rakamcherla IP – EIA Description of Environment
60
are identified among that 10 ground water and 2 surface water samples collected at
around 10 Km radius distance.
3.8.2.1 Physico-Chemical Characteristics
The results obtained for Physico-chemical characteristics of surface water
collected during summer season are presented in Table 3-11. The pH of the
surface water was alkaline and ranged from 7.83 to 7.96 across the sampling
stations. The Electrical conductivity of the sample ranged from 820 to 1030 µS/cm
across the sampling stations. The concentration of Total dissolved solids (TDS)
ranged from 540 to 660 mg/l across the sampling stations. The concentration of
chlorides varied from 14.5 to 22.5 mg/l across the sampling stations. The
concentration of sulphate varied from 34.1 to 35.4 mg/l. Other parameters like
Iron, Chromium, and Lead were below the surface water quality standards.
Table 3.11 Results of Surface Water Samples
S. No. Parameters Unit SW1 SW2
1 Colour Hazen BDL (DL1) BDL (DL1)
2 Odour - U/O U/O
3 Turbidity NTU 1 BDL (DL0.1)
4 pH -- 7.83 7.96
5 Conductivity µS/cm 1030 820
6 Total Dissolve Solids mg/l 660 540
7 Alkalinity as CaCO3 mg/l 75 64
8 Total Hardness as CaCo3 mg/l 338 239
9 Calcium as Ca mg/l 76 52
10 Magnesium as Mg mg/l 34 25
11 Chloride as Cl mg/l 14.5 22.5
12 Sulphate as SO4 mg/l 34.1 35.4
13 Nitrate as NO3 mg/l 1.2 2.5
14 Fluorides as F mg/l 0.34 0.41
15 Cadmium mg/l BDL BDL
16 Total Chromium mg/l BDL (DL 0.01) BDL (DL 0.01)
17 Iron mg/l 0.17 0.22
18 Copper mg/l 0.16 0.6
Rakamcherla IP – EIA Description of Environment
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are identified among that 10 ground water and 2 surface water samples collected at
around 10 Km radius distance.
3.8.2.1 Physico-Chemical Characteristics
The results obtained for Physico-chemical characteristics of surface water
collected during summer season are presented in Table 3-11. The pH of the
surface water was alkaline and ranged from 7.83 to 7.96 across the sampling
stations. The Electrical conductivity of the sample ranged from 820 to 1030 µS/cm
across the sampling stations. The concentration of Total dissolved solids (TDS)
ranged from 540 to 660 mg/l across the sampling stations. The concentration of
chlorides varied from 14.5 to 22.5 mg/l across the sampling stations. The
concentration of sulphate varied from 34.1 to 35.4 mg/l. Other parameters like
Iron, Chromium, and Lead were below the surface water quality standards.
Table 3.11 Results of Surface Water Samples
S. No. Parameters Unit SW1 SW2
1 Colour Hazen BDL (DL1) BDL (DL1)
2 Odour - U/O U/O
3 Turbidity NTU 1 BDL (DL0.1)
4 pH -- 7.83 7.96
5 Conductivity µS/cm 1030 820
6 Total Dissolve Solids mg/l 660 540
7 Alkalinity as CaCO3 mg/l 75 64
8 Total Hardness as CaCo3 mg/l 338 239
9 Calcium as Ca mg/l 76 52
10 Magnesium as Mg mg/l 34 25
11 Chloride as Cl mg/l 14.5 22.5
12 Sulphate as SO4 mg/l 34.1 35.4
13 Nitrate as NO3 mg/l 1.2 2.5
14 Fluorides as F mg/l 0.34 0.41
15 Cadmium mg/l BDL BDL
16 Total Chromium mg/l BDL (DL 0.01) BDL (DL 0.01)
17 Iron mg/l 0.17 0.22
18 Copper mg/l 0.16 0.6
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S. No. Parameters Unit SW1 SW2
19 Lead mg/l BDL (DL 0.01) BDL (DL 0.01)
20 Zinc mg/l 0.34 BDL (DL 0.01)
21 Dissolved Oxygen mg/l 4 4.6
22 COD mg/l 4 4
23 Total Coliform /100 ml 24 256
24 Feacal Coliform /100 ml 10 160
The pH of the ground water ranged from 6.38 to 7.91 across the sampling
stations. The Electrical conductivity of the sample ranged from 625 to 2650
µS/cm across the sampling stations. The highest E.C value observed at GW3
sampling station. The concentration of Total dissolved solids (TDS) ranged
between 408 to 1776 mg/l across the sampling stations. The highest TDS value of
1776 mg/l was observed at GW3 sampling station. The concentration of chlorides
varied from 52 - 318 mg/l across the sampling stations. High concentration of
chlorides was observed at GW3 sampling station. The concentration of sulphate
varied from 24 to 124 mg/l. The highest concentration of sulphate was recorded at
GW10 sampling station. The concentration of Iron varied from 0.12 – 0.34 mg/l
across the sampling stations. High concentration of Iron was observed at GW10
sampling station. The concentration of other parameters like Chromium (mg/l),
Lead (mg/l) and Total suspended Solids (mg/l) were below the detection limit.
The results of ground water quality monitoring are given in Table 3-12.
Table 3.12 Analytical results on Ground water samples
Sl. No. Parameters UnitGW
S1
GW
S2
GW
S3
GW
S4
GW
S5
GW
S6
GW
S7
GW
S8
GW
S9
GW
S10
1 ColourHaze
n1 1 1 2 1 1 1 1 1 1
2 Odour - U/O U/O U/O U/O U/O U/O U/O U/O U/O U/O
3 Turbidity NTU 1 2 2 2 2 1 1 1 2 1
4 pH - 7.4 7.28 7.78 7.64 6.38 7.91 7.24 7.85 7.04 7.12
5 Conductivity 1110 1580 2650 885 650 625 1976 794 1991 2160
6Total Dissolve
Solidsmg/l 768 1096 1776 676 528 408 1325 543 1452 1404
7 Alkalinity as mg/l 226 325 585 154 152 146 439 168 486 335
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S. No. Parameters Unit SW1 SW2
19 Lead mg/l BDL (DL 0.01) BDL (DL 0.01)
20 Zinc mg/l 0.34 BDL (DL 0.01)
21 Dissolved Oxygen mg/l 4 4.6
22 COD mg/l 4 4
23 Total Coliform /100 ml 24 256
24 Feacal Coliform /100 ml 10 160
The pH of the ground water ranged from 6.38 to 7.91 across the sampling
stations. The Electrical conductivity of the sample ranged from 625 to 2650
µS/cm across the sampling stations. The highest E.C value observed at GW3
sampling station. The concentration of Total dissolved solids (TDS) ranged
between 408 to 1776 mg/l across the sampling stations. The highest TDS value of
1776 mg/l was observed at GW3 sampling station. The concentration of chlorides
varied from 52 - 318 mg/l across the sampling stations. High concentration of
chlorides was observed at GW3 sampling station. The concentration of sulphate
varied from 24 to 124 mg/l. The highest concentration of sulphate was recorded at
GW10 sampling station. The concentration of Iron varied from 0.12 – 0.34 mg/l
across the sampling stations. High concentration of Iron was observed at GW10
sampling station. The concentration of other parameters like Chromium (mg/l),
Lead (mg/l) and Total suspended Solids (mg/l) were below the detection limit.
The results of ground water quality monitoring are given in Table 3-12.
Table 3.12 Analytical results on Ground water samples
Sl. No. Parameters UnitGW
S1
GW
S2
GW
S3
GW
S4
GW
S5
GW
S6
GW
S7
GW
S8
GW
S9
GW
S10
1 ColourHaze
n1 1 1 2 1 1 1 1 1 1
2 Odour - U/O U/O U/O U/O U/O U/O U/O U/O U/O U/O
3 Turbidity NTU 1 2 2 2 2 1 1 1 2 1
4 pH - 7.4 7.28 7.78 7.64 6.38 7.91 7.24 7.85 7.04 7.12
5 Conductivity 1110 1580 2650 885 650 625 1976 794 1991 2160
6Total Dissolve
Solidsmg/l 768 1096 1776 676 528 408 1325 543 1452 1404
7 Alkalinity as mg/l 226 325 585 154 152 146 439 168 486 335
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S. No. Parameters Unit SW1 SW2
19 Lead mg/l BDL (DL 0.01) BDL (DL 0.01)
20 Zinc mg/l 0.34 BDL (DL 0.01)
21 Dissolved Oxygen mg/l 4 4.6
22 COD mg/l 4 4
23 Total Coliform /100 ml 24 256
24 Feacal Coliform /100 ml 10 160
The pH of the ground water ranged from 6.38 to 7.91 across the sampling
stations. The Electrical conductivity of the sample ranged from 625 to 2650
µS/cm across the sampling stations. The highest E.C value observed at GW3
sampling station. The concentration of Total dissolved solids (TDS) ranged
between 408 to 1776 mg/l across the sampling stations. The highest TDS value of
1776 mg/l was observed at GW3 sampling station. The concentration of chlorides
varied from 52 - 318 mg/l across the sampling stations. High concentration of
chlorides was observed at GW3 sampling station. The concentration of sulphate
varied from 24 to 124 mg/l. The highest concentration of sulphate was recorded at
GW10 sampling station. The concentration of Iron varied from 0.12 – 0.34 mg/l
across the sampling stations. High concentration of Iron was observed at GW10
sampling station. The concentration of other parameters like Chromium (mg/l),
Lead (mg/l) and Total suspended Solids (mg/l) were below the detection limit.
The results of ground water quality monitoring are given in Table 3-12.
Table 3.12 Analytical results on Ground water samples
Sl. No. Parameters UnitGW
S1
GW
S2
GW
S3
GW
S4
GW
S5
GW
S6
GW
S7
GW
S8
GW
S9
GW
S10
1 ColourHaze
n1 1 1 2 1 1 1 1 1 1
2 Odour - U/O U/O U/O U/O U/O U/O U/O U/O U/O U/O
3 Turbidity NTU 1 2 2 2 2 1 1 1 2 1
4 pH - 7.4 7.28 7.78 7.64 6.38 7.91 7.24 7.85 7.04 7.12
5 Conductivity 1110 1580 2650 885 650 625 1976 794 1991 2160
6Total Dissolve
Solidsmg/l 768 1096 1776 676 528 408 1325 543 1452 1404
7 Alkalinity as mg/l 226 325 585 154 152 146 439 168 486 335
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3.8.3 Hydrogeology
Central Ground Water Board has covered entire District through systematic hydro
geological surveys by 1990, 2003 and reappraisal survey done by 2012. Under
Canadian assisted project during 1971-75, an area of 4764 sq.km was covered by
constructing 40 exploratory bore wells. In all 32 exploratory wells are in granitic and 8
are in basaltic terrain. A study of litho logical logs of these wells reveals that the
thickness of Deccan traps range between about 30 and 77m. Weathered vesicular
fractured and massive traps are normally encountered successively. The thickness of
the weathered zone ranges between a few centimeters to about 18m. In granitic terrain
the exploratory wells drilled down to 164 m has revealed that in general the weathered
zone is followed by massive granite with occasional fractured zones of limited
thickness.
Ground water is the main source of irrigation in the district. Since the urban
agglomeration of the twin cities of Hyderabad and Secunderabad has extended by leaps
CaCO3
8Total Hardness
as CaCo3mg/l 219 300 562 199 88 113 405 161 589 456
9 Calcium as Ca mg/l 53 74 136 35 23 27 116 38 135 92
10Magnesium as
Mgmg/l 21 28 54 27 7.5 11 28 16 61 55
11 Sodium mg/l 186 224 310 158 115 105 235 113 315 295
12 Potassium mg/l 23 18 22 26 16 14 18 15 24 27
13SAR (sodium
absorption ratio)5.47 5.63 5.69 4.88 5.32 4.30 5.08 3.88 5.65 6.01
14 Chloride as Cl mg/l 119 156 318 115 74 52 190 63 242 276
15 Sulphate as SO4 mg/l 25.5 98 102 65 54 24 98 35 83 124
16 Bicarbonate mg/l 276 397 714 188 185 178 536 205 593 409
17 Nitrate as NO3 mg/l 4.1 3.4 0.43 3.9 3.6 2.4 3.5 4.6 2.3 4.8
18 Fluorides as F mg/l 0.06 0.65 0.78 0.32 0.54 0.53 0.34 0.32 0.36 0.54
19 Total Chromium mg/l BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
20 Iron mg/l 0.21 0.12 0.17 0.16 0.42 0.31 0.32 0.41 0.56 0.34
21 Lead mg/l BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
22 Zinc mg/l 2.5 1.2 2.6 3.5 2.5 3 1.4 2.3 1.5 2.2
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3.8.3 Hydrogeology
Central Ground Water Board has covered entire District through systematic hydro
geological surveys by 1990, 2003 and reappraisal survey done by 2012. Under
Canadian assisted project during 1971-75, an area of 4764 sq.km was covered by
constructing 40 exploratory bore wells. In all 32 exploratory wells are in granitic and 8
are in basaltic terrain. A study of litho logical logs of these wells reveals that the
thickness of Deccan traps range between about 30 and 77m. Weathered vesicular
fractured and massive traps are normally encountered successively. The thickness of
the weathered zone ranges between a few centimeters to about 18m. In granitic terrain
the exploratory wells drilled down to 164 m has revealed that in general the weathered
zone is followed by massive granite with occasional fractured zones of limited
thickness.
Ground water is the main source of irrigation in the district. Since the urban
agglomeration of the twin cities of Hyderabad and Secunderabad has extended by leaps
CaCO3
8Total Hardness
as CaCo3mg/l 219 300 562 199 88 113 405 161 589 456
9 Calcium as Ca mg/l 53 74 136 35 23 27 116 38 135 92
10Magnesium as
Mgmg/l 21 28 54 27 7.5 11 28 16 61 55
11 Sodium mg/l 186 224 310 158 115 105 235 113 315 295
12 Potassium mg/l 23 18 22 26 16 14 18 15 24 27
13SAR (sodium
absorption ratio)5.47 5.63 5.69 4.88 5.32 4.30 5.08 3.88 5.65 6.01
14 Chloride as Cl mg/l 119 156 318 115 74 52 190 63 242 276
15 Sulphate as SO4 mg/l 25.5 98 102 65 54 24 98 35 83 124
16 Bicarbonate mg/l 276 397 714 188 185 178 536 205 593 409
17 Nitrate as NO3 mg/l 4.1 3.4 0.43 3.9 3.6 2.4 3.5 4.6 2.3 4.8
18 Fluorides as F mg/l 0.06 0.65 0.78 0.32 0.54 0.53 0.34 0.32 0.36 0.54
19 Total Chromium mg/l BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
20 Iron mg/l 0.21 0.12 0.17 0.16 0.42 0.31 0.32 0.41 0.56 0.34
21 Lead mg/l BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
22 Zinc mg/l 2.5 1.2 2.6 3.5 2.5 3 1.4 2.3 1.5 2.2
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3.8.3 Hydrogeology
Central Ground Water Board has covered entire District through systematic hydro
geological surveys by 1990, 2003 and reappraisal survey done by 2012. Under
Canadian assisted project during 1971-75, an area of 4764 sq.km was covered by
constructing 40 exploratory bore wells. In all 32 exploratory wells are in granitic and 8
are in basaltic terrain. A study of litho logical logs of these wells reveals that the
thickness of Deccan traps range between about 30 and 77m. Weathered vesicular
fractured and massive traps are normally encountered successively. The thickness of
the weathered zone ranges between a few centimeters to about 18m. In granitic terrain
the exploratory wells drilled down to 164 m has revealed that in general the weathered
zone is followed by massive granite with occasional fractured zones of limited
thickness.
Ground water is the main source of irrigation in the district. Since the urban
agglomeration of the twin cities of Hyderabad and Secunderabad has extended by leaps
CaCO3
8Total Hardness
as CaCo3mg/l 219 300 562 199 88 113 405 161 589 456
9 Calcium as Ca mg/l 53 74 136 35 23 27 116 38 135 92
10Magnesium as
Mgmg/l 21 28 54 27 7.5 11 28 16 61 55
11 Sodium mg/l 186 224 310 158 115 105 235 113 315 295
12 Potassium mg/l 23 18 22 26 16 14 18 15 24 27
13SAR (sodium
absorption ratio)5.47 5.63 5.69 4.88 5.32 4.30 5.08 3.88 5.65 6.01
14 Chloride as Cl mg/l 119 156 318 115 74 52 190 63 242 276
15 Sulphate as SO4 mg/l 25.5 98 102 65 54 24 98 35 83 124
16 Bicarbonate mg/l 276 397 714 188 185 178 536 205 593 409
17 Nitrate as NO3 mg/l 4.1 3.4 0.43 3.9 3.6 2.4 3.5 4.6 2.3 4.8
18 Fluorides as F mg/l 0.06 0.65 0.78 0.32 0.54 0.53 0.34 0.32 0.36 0.54
19 Total Chromium mg/l BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
20 Iron mg/l 0.21 0.12 0.17 0.16 0.42 0.31 0.32 0.41 0.56 0.34
21 Lead mg/l BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
22 Zinc mg/l 2.5 1.2 2.6 3.5 2.5 3 1.4 2.3 1.5 2.2
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of bonds into Vikarabad district also, stress on ground water has increased
tremendously to cater to the needs of industrial and domestic sectors.
Ground water level data for a monitoring well collected from CGWB located in Pudur
which is located at a distance of 2 km north of the project site indicates that the deepest
water level is 14.85 m bgl during May 2012 and shallowest water level is 4.36 m bgl
November 2013. The season wise ground water level data collected for Pudur
monitoring well is given below. It clearly indicates that the natural recharge is good in
and around the project site. Figure 3-11 gives the details on ground water quality at
Pudur.
Figure 3.11 Ground Water Quality of Pudur Area
Rakamcherla IP – EIA Description of Environment
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of bonds into Vikarabad district also, stress on ground water has increased
tremendously to cater to the needs of industrial and domestic sectors.
Ground water level data for a monitoring well collected from CGWB located in Pudur
which is located at a distance of 2 km north of the project site indicates that the deepest
water level is 14.85 m bgl during May 2012 and shallowest water level is 4.36 m bgl
November 2013. The season wise ground water level data collected for Pudur
monitoring well is given below. It clearly indicates that the natural recharge is good in
and around the project site. Figure 3-11 gives the details on ground water quality at
Pudur.
Figure 3.11 Ground Water Quality of Pudur Area
Rakamcherla IP – EIA Description of Environment
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of bonds into Vikarabad district also, stress on ground water has increased
tremendously to cater to the needs of industrial and domestic sectors.
Ground water level data for a monitoring well collected from CGWB located in Pudur
which is located at a distance of 2 km north of the project site indicates that the deepest
water level is 14.85 m bgl during May 2012 and shallowest water level is 4.36 m bgl
November 2013. The season wise ground water level data collected for Pudur
monitoring well is given below. It clearly indicates that the natural recharge is good in
and around the project site. Figure 3-11 gives the details on ground water quality at
Pudur.
Figure 3.11 Ground Water Quality of Pudur Area
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3.8.4 Drainage and water Bodies of the Study Area
Surface water plays major role in irrigation when compared to the ground water source.
There is no major river within 10 km of the project site. However, Musa Nadi (River)
flows from South west to North East at a distance of 6 km from the Project site. There
is no major dam/reservoir within the 10 km from the project boundary.
The drainage of the study area is mostly controlled by the structural features. Among
the different drainage pattern the noteworthy are sub-parallel. Streams flowing in the
low lying tracts have been bounded on one side and serve as storage tanks for
collection of rain water. The map showing the water bodies with the project influence
area is given in Figure 3-12.
3.8.5 Irrigation Practices
Though, two good rivers traverse in the District there are no irrigation projects. Musi
flows through the district untapped for irrigation since it feeds the Himayath sagar and
Osman sagar reservoirs mainly for drinking water purpose in Hyderabad district.
However, the water of Kagna have been utilized by a medium project known as
Kotepally project which has an ayacut of 3,723 ha in Vikarabad, Marpally and Dharur
mandals. The Navandgi irrigation scheme also on the river Kagna (Tandur area)
irrigated about 2023 hectares. Inderched and Gangavarm lift irrigation schemes also
irrigate some area in this part. Though there are other medium projects like Juntupally
(Tandur area) Kotepally (Marpally, Vikarabad and Tandur) which has an ayacut of
2080 ha and Laknapur (Pargi and Dhjarur mandals) which has an ayacut of 2649 ha
they irrigate only a limited area and as such, wells form the principal source of
irrigation in the district. The source wise area irrigated is given in the Table 3-13.
Rakamcherla IP – EIA Description of Environment
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3.8.4 Drainage and water Bodies of the Study Area
Surface water plays major role in irrigation when compared to the ground water source.
There is no major river within 10 km of the project site. However, Musa Nadi (River)
flows from South west to North East at a distance of 6 km from the Project site. There
is no major dam/reservoir within the 10 km from the project boundary.
The drainage of the study area is mostly controlled by the structural features. Among
the different drainage pattern the noteworthy are sub-parallel. Streams flowing in the
low lying tracts have been bounded on one side and serve as storage tanks for
collection of rain water. The map showing the water bodies with the project influence
area is given in Figure 3-12.
3.8.5 Irrigation Practices
Though, two good rivers traverse in the District there are no irrigation projects. Musi
flows through the district untapped for irrigation since it feeds the Himayath sagar and
Osman sagar reservoirs mainly for drinking water purpose in Hyderabad district.
However, the water of Kagna have been utilized by a medium project known as
Kotepally project which has an ayacut of 3,723 ha in Vikarabad, Marpally and Dharur
mandals. The Navandgi irrigation scheme also on the river Kagna (Tandur area)
irrigated about 2023 hectares. Inderched and Gangavarm lift irrigation schemes also
irrigate some area in this part. Though there are other medium projects like Juntupally
(Tandur area) Kotepally (Marpally, Vikarabad and Tandur) which has an ayacut of
2080 ha and Laknapur (Pargi and Dhjarur mandals) which has an ayacut of 2649 ha
they irrigate only a limited area and as such, wells form the principal source of
irrigation in the district. The source wise area irrigated is given in the Table 3-13.
Rakamcherla IP – EIA Description of Environment
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3.8.4 Drainage and water Bodies of the Study Area
Surface water plays major role in irrigation when compared to the ground water source.
There is no major river within 10 km of the project site. However, Musa Nadi (River)
flows from South west to North East at a distance of 6 km from the Project site. There
is no major dam/reservoir within the 10 km from the project boundary.
The drainage of the study area is mostly controlled by the structural features. Among
the different drainage pattern the noteworthy are sub-parallel. Streams flowing in the
low lying tracts have been bounded on one side and serve as storage tanks for
collection of rain water. The map showing the water bodies with the project influence
area is given in Figure 3-12.
3.8.5 Irrigation Practices
Though, two good rivers traverse in the District there are no irrigation projects. Musi
flows through the district untapped for irrigation since it feeds the Himayath sagar and
Osman sagar reservoirs mainly for drinking water purpose in Hyderabad district.
However, the water of Kagna have been utilized by a medium project known as
Kotepally project which has an ayacut of 3,723 ha in Vikarabad, Marpally and Dharur
mandals. The Navandgi irrigation scheme also on the river Kagna (Tandur area)
irrigated about 2023 hectares. Inderched and Gangavarm lift irrigation schemes also
irrigate some area in this part. Though there are other medium projects like Juntupally
(Tandur area) Kotepally (Marpally, Vikarabad and Tandur) which has an ayacut of
2080 ha and Laknapur (Pargi and Dhjarur mandals) which has an ayacut of 2649 ha
they irrigate only a limited area and as such, wells form the principal source of
irrigation in the district. The source wise area irrigated is given in the Table 3-13.
Rakamcherla IP – EIA Description of Environment
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Table 3.13 Area irrigated different source (in Ha)
S.No Source of irrigation 1994-95 2005-06 2010-11 2013-141. Canals 1030 1000 1334 465
2. Tanks 2120 1000 6088 2139
3. Tube wells and filter points 35413 47000 87863 67732
4. Other wells / Dug wells 20100 10000 8663 2587
5. Other sources 1580 1000 1573 913
6. Net area irrigated 45307 60000 74730 101968
Table 3.14 Area Irrigated under food & Nonfood crops of Vikarabad district
(2013 – 2014)
S.No Food Crops (Cereals &Millets)
Area in (Ha) Food Crops (Pulses) Area in (H)
1 Rice 45040 Horse gram -2 Wheat 568 Green gram -3 Jowar 1097 Black gram -4 Bajra - Red gram -5 Maize 1669 Bengal gram -6 Ragi 327 Other Pulses 236
S.No Food Crops (Condiments,Spices and Others)
Area in (Ha) Non Food Crops(OilSeeds)
Area in (H)
1 Turmeric 3740 Groundnut 106352 Chillies 587 Seasamum -3 Ginger 50 Cocounut 24 Others 257 Castor -5 Sugarcane 1780 Others 2766 Onions 24247 Others 27612(Source: Directorate of Economics & Statistics, Telangana)
(Source: Directorate of Economics & Statistics, Chief planning office: Govt. of Andhra Pradesh & Telangana)
Rakamcherla IP – EIA Description of Environment
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Table 3.13 Area irrigated different source (in Ha)
S.No Source of irrigation 1994-95 2005-06 2010-11 2013-141. Canals 1030 1000 1334 465
2. Tanks 2120 1000 6088 2139
3. Tube wells and filter points 35413 47000 87863 67732
4. Other wells / Dug wells 20100 10000 8663 2587
5. Other sources 1580 1000 1573 913
6. Net area irrigated 45307 60000 74730 101968
Table 3.14 Area Irrigated under food & Nonfood crops of Vikarabad district
(2013 – 2014)
S.No Food Crops (Cereals &Millets)
Area in (Ha) Food Crops (Pulses) Area in (H)
1 Rice 45040 Horse gram -2 Wheat 568 Green gram -3 Jowar 1097 Black gram -4 Bajra - Red gram -5 Maize 1669 Bengal gram -6 Ragi 327 Other Pulses 236
S.No Food Crops (Condiments,Spices and Others)
Area in (Ha) Non Food Crops(OilSeeds)
Area in (H)
1 Turmeric 3740 Groundnut 106352 Chillies 587 Seasamum -3 Ginger 50 Cocounut 24 Others 257 Castor -5 Sugarcane 1780 Others 2766 Onions 24247 Others 27612(Source: Directorate of Economics & Statistics, Telangana)
(Source: Directorate of Economics & Statistics, Chief planning office: Govt. of Andhra Pradesh & Telangana)
Rakamcherla IP – EIA Description of Environment
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Table 3.13 Area irrigated different source (in Ha)
S.No Source of irrigation 1994-95 2005-06 2010-11 2013-141. Canals 1030 1000 1334 465
2. Tanks 2120 1000 6088 2139
3. Tube wells and filter points 35413 47000 87863 67732
4. Other wells / Dug wells 20100 10000 8663 2587
5. Other sources 1580 1000 1573 913
6. Net area irrigated 45307 60000 74730 101968
Table 3.14 Area Irrigated under food & Nonfood crops of Vikarabad district
(2013 – 2014)
S.No Food Crops (Cereals &Millets)
Area in (Ha) Food Crops (Pulses) Area in (H)
1 Rice 45040 Horse gram -2 Wheat 568 Green gram -3 Jowar 1097 Black gram -4 Bajra - Red gram -5 Maize 1669 Bengal gram -6 Ragi 327 Other Pulses 236
S.No Food Crops (Condiments,Spices and Others)
Area in (Ha) Non Food Crops(OilSeeds)
Area in (H)
1 Turmeric 3740 Groundnut 106352 Chillies 587 Seasamum -3 Ginger 50 Cocounut 24 Others 257 Castor -5 Sugarcane 1780 Others 2766 Onions 24247 Others 27612(Source: Directorate of Economics & Statistics, Telangana)
(Source: Directorate of Economics & Statistics, Chief planning office: Govt. of Andhra Pradesh & Telangana)
Rakamcherla IP – EIA Description of Environment
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Figure 3.12 Drainage Map of the Study area
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Figure 3.12 Drainage Map of the Study area
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Figure 3.12 Drainage Map of the Study area
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3.9 Land Environment
In general any major developmental projects related to industrial sector are expected to
cause direct and indirect impacts on land environment, which could be attributed to
mainly change in land use pattern (direct and indirect) as well as pollution impacts due
to disposal of solid/hazardous wastes on the land and discharge of wastewater either
on to land (direct impacts) or in to surface water resources. Moreover, impacts on
agriculture land/vegetation are also expected due to fallout of air pollutants in case of
excessive emissions beyond certain limit (indirect impacts). Accordingly, for impact
assessment on land component, it is pertinent to study the existing landuse pattern in
project area, soil characteristics and details of estimated waste generation from
proposed new activities including the impacts on soil with respect to land
application/disposal of solid/hazardous wastes and the consequential impacts on the
surrounding terrestrial and aquatic environment.
3.9.1 Reconnaissance Survey
The proposed project is located at Rakamcherla Village, Pudur Mandal and Vikarabad
District. The site is located near to SH Road.
Location : Latitude 17°14'50.25"N, and
Longitude 77°57'46.57"E
Site elevation within 5
Km radius
: Ground elevations varying from 690 m to 705
m above MSL
Highway Connectivity : SH-4 at a distance of 0.5Km
Nearest Railway
Station/distance
: Vikarabad- 15 Km
Nearest Town, City,
District
: Town: Vikarabad -14 KmCity: Hyderabad-70 KmDistrict Hq: Hyderabad-70 Km
3.9.2 Geology
Geology the study area (10 km radius) comprises of the following rock types such as
Laterite, Basalt with intertrappians and Granites. The project site is located in Laterite
formation. The geology map of the study area is presented in Figure 3-13.
Rakamcherla IP – EIA Description of Environment
67
3.9 Land Environment
In general any major developmental projects related to industrial sector are expected to
cause direct and indirect impacts on land environment, which could be attributed to
mainly change in land use pattern (direct and indirect) as well as pollution impacts due
to disposal of solid/hazardous wastes on the land and discharge of wastewater either
on to land (direct impacts) or in to surface water resources. Moreover, impacts on
agriculture land/vegetation are also expected due to fallout of air pollutants in case of
excessive emissions beyond certain limit (indirect impacts). Accordingly, for impact
assessment on land component, it is pertinent to study the existing landuse pattern in
project area, soil characteristics and details of estimated waste generation from
proposed new activities including the impacts on soil with respect to land
application/disposal of solid/hazardous wastes and the consequential impacts on the
surrounding terrestrial and aquatic environment.
3.9.1 Reconnaissance Survey
The proposed project is located at Rakamcherla Village, Pudur Mandal and Vikarabad
District. The site is located near to SH Road.
Location : Latitude 17°14'50.25"N, and
Longitude 77°57'46.57"E
Site elevation within 5
Km radius
: Ground elevations varying from 690 m to 705
m above MSL
Highway Connectivity : SH-4 at a distance of 0.5Km
Nearest Railway
Station/distance
: Vikarabad- 15 Km
Nearest Town, City,
District
: Town: Vikarabad -14 KmCity: Hyderabad-70 KmDistrict Hq: Hyderabad-70 Km
3.9.2 Geology
Geology the study area (10 km radius) comprises of the following rock types such as
Laterite, Basalt with intertrappians and Granites. The project site is located in Laterite
formation. The geology map of the study area is presented in Figure 3-13.
Rakamcherla IP – EIA Description of Environment
67
3.9 Land Environment
In general any major developmental projects related to industrial sector are expected to
cause direct and indirect impacts on land environment, which could be attributed to
mainly change in land use pattern (direct and indirect) as well as pollution impacts due
to disposal of solid/hazardous wastes on the land and discharge of wastewater either
on to land (direct impacts) or in to surface water resources. Moreover, impacts on
agriculture land/vegetation are also expected due to fallout of air pollutants in case of
excessive emissions beyond certain limit (indirect impacts). Accordingly, for impact
assessment on land component, it is pertinent to study the existing landuse pattern in
project area, soil characteristics and details of estimated waste generation from
proposed new activities including the impacts on soil with respect to land
application/disposal of solid/hazardous wastes and the consequential impacts on the
surrounding terrestrial and aquatic environment.
3.9.1 Reconnaissance Survey
The proposed project is located at Rakamcherla Village, Pudur Mandal and Vikarabad
District. The site is located near to SH Road.
Location : Latitude 17°14'50.25"N, and
Longitude 77°57'46.57"E
Site elevation within 5
Km radius
: Ground elevations varying from 690 m to 705
m above MSL
Highway Connectivity : SH-4 at a distance of 0.5Km
Nearest Railway
Station/distance
: Vikarabad- 15 Km
Nearest Town, City,
District
: Town: Vikarabad -14 KmCity: Hyderabad-70 KmDistrict Hq: Hyderabad-70 Km
3.9.2 Geology
Geology the study area (10 km radius) comprises of the following rock types such as
Laterite, Basalt with intertrappians and Granites. The project site is located in Laterite
formation. The geology map of the study area is presented in Figure 3-13.
Rakamcherla IP – EIA Description of Environment
68
Figure 3.13 Geology Map of the Project Site
3.9.3 Geomorphology
The landforms in the district are the products of different geomorphic processes such
as erosion, deposition, crustal movements coupled with climatic changes operating on
the surface. The specific geomorphic groups are (i) Residual hills (ii) Plateau (Deccan
traps) (iii) Pediment Inselberg complex (iv) Pediplain and (v) Flood plain.
i) Residual Hills: These geomorphic forms occur as massive hills comprising of
forest areas in Kulakacherla, Manchal and in Yacharam mandals with a maximum
elevation of 704 m above msl. The residual hills occurring around Ghatkesar,
Shamirpet and Rajendernagar mandals , the soil cover is thin and devoid of
Rakamcherla IP – EIA Description of Environment
68
Figure 3.13 Geology Map of the Project Site
3.9.3 Geomorphology
The landforms in the district are the products of different geomorphic processes such
as erosion, deposition, crustal movements coupled with climatic changes operating on
the surface. The specific geomorphic groups are (i) Residual hills (ii) Plateau (Deccan
traps) (iii) Pediment Inselberg complex (iv) Pediplain and (v) Flood plain.
i) Residual Hills: These geomorphic forms occur as massive hills comprising of
forest areas in Kulakacherla, Manchal and in Yacharam mandals with a maximum
elevation of 704 m above msl. The residual hills occurring around Ghatkesar,
Shamirpet and Rajendernagar mandals , the soil cover is thin and devoid of
Rakamcherla IP – EIA Description of Environment
68
Figure 3.13 Geology Map of the Project Site
3.9.3 Geomorphology
The landforms in the district are the products of different geomorphic processes such
as erosion, deposition, crustal movements coupled with climatic changes operating on
the surface. The specific geomorphic groups are (i) Residual hills (ii) Plateau (Deccan
traps) (iii) Pediment Inselberg complex (iv) Pediplain and (v) Flood plain.
i) Residual Hills: These geomorphic forms occur as massive hills comprising of
forest areas in Kulakacherla, Manchal and in Yacharam mandals with a maximum
elevation of 704 m above msl. The residual hills occurring around Ghatkesar,
Shamirpet and Rajendernagar mandals , the soil cover is thin and devoid of
Rakamcherla IP – EIA Description of Environment
69
vegetation except with low trees, thorny bushes and shrubs. Other forms in the
area include Mesa/Butt, having flat topped hills comprising of laterite and basalts.
ii) Plateau (Deccan traps): This geomorphic unit is characterized by elevated
uplands with steep slope and dissected by deep and narrow valleys occupied by
different flows.
iii) Pediment Inselberg Complex: Pediment inselberg complex is a gently undulating
plain abounding with a number of small hills, mounds, tors etc.
iv) Pediplain: Pediplains are characterized by flat or gentle sloping surface which is
the end product of coalescence of several pediments at the foot of hill slopes.
Pediplains are characterized by the vast area of low lying flat terrain with gentle
slopes covered by red brown and black clayey soils ranging in thickness from 20
cm to 60 cm.
v) Flood plain: Alluvial deposits occur along major river courses mostly derived
from catchments, transported and deposited.
3.9.4 Physiography
It is a subfield of geography which helps to study physical patterns and processes of
the study area. The general elevation of the study area ranges from 565 m to 725 m
above MSL. The elevation contour indicates the area is sloping towards east.
Relatively higher elevation is observed in the eastern side of the project site. No hill
ranges noticed within 10 km of the project site. The project site is located in the 690-
705 m above MSL. Features and attributes of earth's land surface of the site are shown
in Figure 3-14.
Rakamcherla IP – EIA Description of Environment
69
vegetation except with low trees, thorny bushes and shrubs. Other forms in the
area include Mesa/Butt, having flat topped hills comprising of laterite and basalts.
ii) Plateau (Deccan traps): This geomorphic unit is characterized by elevated
uplands with steep slope and dissected by deep and narrow valleys occupied by
different flows.
iii) Pediment Inselberg Complex: Pediment inselberg complex is a gently undulating
plain abounding with a number of small hills, mounds, tors etc.
iv) Pediplain: Pediplains are characterized by flat or gentle sloping surface which is
the end product of coalescence of several pediments at the foot of hill slopes.
Pediplains are characterized by the vast area of low lying flat terrain with gentle
slopes covered by red brown and black clayey soils ranging in thickness from 20
cm to 60 cm.
v) Flood plain: Alluvial deposits occur along major river courses mostly derived
from catchments, transported and deposited.
3.9.4 Physiography
It is a subfield of geography which helps to study physical patterns and processes of
the study area. The general elevation of the study area ranges from 565 m to 725 m
above MSL. The elevation contour indicates the area is sloping towards east.
Relatively higher elevation is observed in the eastern side of the project site. No hill
ranges noticed within 10 km of the project site. The project site is located in the 690-
705 m above MSL. Features and attributes of earth's land surface of the site are shown
in Figure 3-14.
Rakamcherla IP – EIA Description of Environment
69
vegetation except with low trees, thorny bushes and shrubs. Other forms in the
area include Mesa/Butt, having flat topped hills comprising of laterite and basalts.
ii) Plateau (Deccan traps): This geomorphic unit is characterized by elevated
uplands with steep slope and dissected by deep and narrow valleys occupied by
different flows.
iii) Pediment Inselberg Complex: Pediment inselberg complex is a gently undulating
plain abounding with a number of small hills, mounds, tors etc.
iv) Pediplain: Pediplains are characterized by flat or gentle sloping surface which is
the end product of coalescence of several pediments at the foot of hill slopes.
Pediplains are characterized by the vast area of low lying flat terrain with gentle
slopes covered by red brown and black clayey soils ranging in thickness from 20
cm to 60 cm.
v) Flood plain: Alluvial deposits occur along major river courses mostly derived
from catchments, transported and deposited.
3.9.4 Physiography
It is a subfield of geography which helps to study physical patterns and processes of
the study area. The general elevation of the study area ranges from 565 m to 725 m
above MSL. The elevation contour indicates the area is sloping towards east.
Relatively higher elevation is observed in the eastern side of the project site. No hill
ranges noticed within 10 km of the project site. The project site is located in the 690-
705 m above MSL. Features and attributes of earth's land surface of the site are shown
in Figure 3-14.
Rakamcherla IP – EIA Description of Environment
70
Figure 3.14 Physiography of the Study area
3.9.5 Land Use/ Land Cover Classification
Land use information of an area in the form of map and statistical data are very vital for
spatial analysis, planning, management and utilization of land for agriculture, forestry,
urban and industrial planning. The level of spatial classification is classed under 4
categories. They are Level 1 with 1:1 million scale, Level 2 with 1:250,000 scale, Level
3 with 1:50,000 scale and level 4 with 1:25,000 or larger scale. The cost and
availability of data and purpose for which the land use classification is to be taken up is
important for taking up the level of classification. In the present study Level 3
classification is made which is fairly a good classification of urban and industrial
planning. However level 4 classifications is the ultimate for all kind of planning and
management. Owing to the exorbitant cost and time of obtaining the Satellite Data
Rakamcherla IP – EIA Description of Environment
70
Figure 3.14 Physiography of the Study area
3.9.5 Land Use/ Land Cover Classification
Land use information of an area in the form of map and statistical data are very vital for
spatial analysis, planning, management and utilization of land for agriculture, forestry,
urban and industrial planning. The level of spatial classification is classed under 4
categories. They are Level 1 with 1:1 million scale, Level 2 with 1:250,000 scale, Level
3 with 1:50,000 scale and level 4 with 1:25,000 or larger scale. The cost and
availability of data and purpose for which the land use classification is to be taken up is
important for taking up the level of classification. In the present study Level 3
classification is made which is fairly a good classification of urban and industrial
planning. However level 4 classifications is the ultimate for all kind of planning and
management. Owing to the exorbitant cost and time of obtaining the Satellite Data
Rakamcherla IP – EIA Description of Environment
70
Figure 3.14 Physiography of the Study area
3.9.5 Land Use/ Land Cover Classification
Land use information of an area in the form of map and statistical data are very vital for
spatial analysis, planning, management and utilization of land for agriculture, forestry,
urban and industrial planning. The level of spatial classification is classed under 4
categories. They are Level 1 with 1:1 million scale, Level 2 with 1:250,000 scale, Level
3 with 1:50,000 scale and level 4 with 1:25,000 or larger scale. The cost and
availability of data and purpose for which the land use classification is to be taken up is
important for taking up the level of classification. In the present study Level 3
classification is made which is fairly a good classification of urban and industrial
planning. However level 4 classifications is the ultimate for all kind of planning and
management. Owing to the exorbitant cost and time of obtaining the Satellite Data
Rakamcherla IP – EIA Description of Environment
71
from the concerned agencies, the present land use classification has been restricted to
level 2.
For the preparation of land use map IRS P6 LISS-III Satellite data has been procured
from NRSC, Hyderabad. At most care has been taken to select the cloud free satellite
data. The recent digital data dated March-2014 has been taken for the preparation of
land use mapping. Visual interpretation technique has been adopted for land use
classification based on the interpretation keys suggested in the guidelines of NNRMS,
Bangalore.
The land use of the study area reflects the socio-economic conditions of the people in
addition to the natural environmental factors. The factors controlling the land use
pattern of the area are land forms, slope, shape of the land, soil, natural resources and
natural and manmade hazards. In the hills of the study area there is no dense vegetation.
Vegetation consists of thorny bushes and shrubs. The uncultivable area includes barren
and non-cultivable waste.
The crop land occupies 169.01 Sq.Km (52.76 %) of the study area followed by
Plantation 63.44 Sq.Km (19.80 %), Barren land occupies 36.58 Sq.Km (11.42 %) and
Fallow land occupies 25.67 Sq.Km (8.01 %). The land use classification details of the
study area denoted in Table 3-15 and Figure 3-15.
Table 3.15 Land use classification
Land use Area(Sq.Km)
Area(percentage)
Crop Land 169.01 52.76
Plantation 63.44 19.80
Fallow Land 25.67 8.01
Land with Scrub 7.34 2.29
Land without Scrub 10.99 3.43
Scrub Land 5.22 1.63
Barren Land 36.58 11.42
Built-up Land 1.01 0.32
Water body 1.10 0.34
Total 320.36 100.00
Rakamcherla IP – EIA Description of Environment
71
from the concerned agencies, the present land use classification has been restricted to
level 2.
For the preparation of land use map IRS P6 LISS-III Satellite data has been procured
from NRSC, Hyderabad. At most care has been taken to select the cloud free satellite
data. The recent digital data dated March-2014 has been taken for the preparation of
land use mapping. Visual interpretation technique has been adopted for land use
classification based on the interpretation keys suggested in the guidelines of NNRMS,
Bangalore.
The land use of the study area reflects the socio-economic conditions of the people in
addition to the natural environmental factors. The factors controlling the land use
pattern of the area are land forms, slope, shape of the land, soil, natural resources and
natural and manmade hazards. In the hills of the study area there is no dense vegetation.
Vegetation consists of thorny bushes and shrubs. The uncultivable area includes barren
and non-cultivable waste.
The crop land occupies 169.01 Sq.Km (52.76 %) of the study area followed by
Plantation 63.44 Sq.Km (19.80 %), Barren land occupies 36.58 Sq.Km (11.42 %) and
Fallow land occupies 25.67 Sq.Km (8.01 %). The land use classification details of the
study area denoted in Table 3-15 and Figure 3-15.
Table 3.15 Land use classification
Land use Area(Sq.Km)
Area(percentage)
Crop Land 169.01 52.76
Plantation 63.44 19.80
Fallow Land 25.67 8.01
Land with Scrub 7.34 2.29
Land without Scrub 10.99 3.43
Scrub Land 5.22 1.63
Barren Land 36.58 11.42
Built-up Land 1.01 0.32
Water body 1.10 0.34
Total 320.36 100.00
Rakamcherla IP – EIA Description of Environment
71
from the concerned agencies, the present land use classification has been restricted to
level 2.
For the preparation of land use map IRS P6 LISS-III Satellite data has been procured
from NRSC, Hyderabad. At most care has been taken to select the cloud free satellite
data. The recent digital data dated March-2014 has been taken for the preparation of
land use mapping. Visual interpretation technique has been adopted for land use
classification based on the interpretation keys suggested in the guidelines of NNRMS,
Bangalore.
The land use of the study area reflects the socio-economic conditions of the people in
addition to the natural environmental factors. The factors controlling the land use
pattern of the area are land forms, slope, shape of the land, soil, natural resources and
natural and manmade hazards. In the hills of the study area there is no dense vegetation.
Vegetation consists of thorny bushes and shrubs. The uncultivable area includes barren
and non-cultivable waste.
The crop land occupies 169.01 Sq.Km (52.76 %) of the study area followed by
Plantation 63.44 Sq.Km (19.80 %), Barren land occupies 36.58 Sq.Km (11.42 %) and
Fallow land occupies 25.67 Sq.Km (8.01 %). The land use classification details of the
study area denoted in Table 3-15 and Figure 3-15.
Table 3.15 Land use classification
Land use Area(Sq.Km)
Area(percentage)
Crop Land 169.01 52.76
Plantation 63.44 19.80
Fallow Land 25.67 8.01
Land with Scrub 7.34 2.29
Land without Scrub 10.99 3.43
Scrub Land 5.22 1.63
Barren Land 36.58 11.42
Built-up Land 1.01 0.32
Water body 1.10 0.34
Total 320.36 100.00
Rakamcherla IP – EIA Description of Environment
72
Figure 3.15 Land Use and Land cover Classification of Study area
Figure 3.16 Land Use / Land Cover Map of the Study area
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72
Figure 3.15 Land Use and Land cover Classification of Study area
Figure 3.16 Land Use / Land Cover Map of the Study area
Rakamcherla IP – EIA Description of Environment
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Figure 3.15 Land Use and Land cover Classification of Study area
Figure 3.16 Land Use / Land Cover Map of the Study area
Rakamcherla IP – EIA Description of Environment
73
3.10 Soil Environment
Assessment of soil characteristics is of paramount importance since the vegetation
growth, agricultural practices and production is directly related to the soil fertility and
quality. The predominant soil type is black cotton soil followed by red soils. In Pargi
mandal more than 50% of the villages have Red-Chelka soils. The mandals with black
soils are Vikarabad, Pudur. Red soils are neutral whereas black soils are slightly
alkaline, pH ranges from 6.5 to 8.5. The soils are highly deficient in nitrogen, low to
medium in available P and high in available K. Zinc deficiency is common in all the
mandals (deficiency ranges from 16 per cent to 90 per cent).
3.10.1 Soil Type
The soils in the study area are classified into 3 type’s namely deep calcareous black
soil, Lateritic gravelly clay soil and shallow black soil. The soil map of the study area is
prepared based on the National Bureau of Soil Survey and Land use Planning, Nagpur
is presented in Figure 3-17. Deep calcareous block soil occupies 65 % of the study
area. The Project site lies in the lateritic gravelly clay soil.
Figure 3.17 Geological formation of the Study Area
Rakamcherla IP – EIA Description of Environment
73
3.10 Soil Environment
Assessment of soil characteristics is of paramount importance since the vegetation
growth, agricultural practices and production is directly related to the soil fertility and
quality. The predominant soil type is black cotton soil followed by red soils. In Pargi
mandal more than 50% of the villages have Red-Chelka soils. The mandals with black
soils are Vikarabad, Pudur. Red soils are neutral whereas black soils are slightly
alkaline, pH ranges from 6.5 to 8.5. The soils are highly deficient in nitrogen, low to
medium in available P and high in available K. Zinc deficiency is common in all the
mandals (deficiency ranges from 16 per cent to 90 per cent).
3.10.1 Soil Type
The soils in the study area are classified into 3 type’s namely deep calcareous black
soil, Lateritic gravelly clay soil and shallow black soil. The soil map of the study area is
prepared based on the National Bureau of Soil Survey and Land use Planning, Nagpur
is presented in Figure 3-17. Deep calcareous block soil occupies 65 % of the study
area. The Project site lies in the lateritic gravelly clay soil.
Figure 3.17 Geological formation of the Study Area
Rakamcherla IP – EIA Description of Environment
73
3.10 Soil Environment
Assessment of soil characteristics is of paramount importance since the vegetation
growth, agricultural practices and production is directly related to the soil fertility and
quality. The predominant soil type is black cotton soil followed by red soils. In Pargi
mandal more than 50% of the villages have Red-Chelka soils. The mandals with black
soils are Vikarabad, Pudur. Red soils are neutral whereas black soils are slightly
alkaline, pH ranges from 6.5 to 8.5. The soils are highly deficient in nitrogen, low to
medium in available P and high in available K. Zinc deficiency is common in all the
mandals (deficiency ranges from 16 per cent to 90 per cent).
3.10.1 Soil Type
The soils in the study area are classified into 3 type’s namely deep calcareous black
soil, Lateritic gravelly clay soil and shallow black soil. The soil map of the study area is
prepared based on the National Bureau of Soil Survey and Land use Planning, Nagpur
is presented in Figure 3-17. Deep calcareous block soil occupies 65 % of the study
area. The Project site lies in the lateritic gravelly clay soil.
Figure 3.17 Geological formation of the Study Area
Rakamcherla IP – EIA Description of Environment
74
Figure 3.18 Soil Classification of the Study Area
3.10.2 Soil Monitoring
For monitoring the soil quality within 10 Km radius, 10 sampling locations were
identified and the details of locations are given in Table 3-16.
Table -3.16 Soil Sampling Locations in the study area
S.No Sample
ID
Location Geographical
coordinates
Aerial
distance
(Km)
Direction with
respect to site
1. S1 Manneguda village N-17°18’03.0”E-77°58’54.7”
6.5 N
2. S2 Changomul village N-17°15’27.1”E-78°01’34.0”
6.57 ENE
3. S3 Kankal village N-17°12’17.1”E-78°00’24.4”
6.3 SE
4. S4 Near RakamcherlaIndustrial Park
N-17°14’45.5”E-77°57’48.8”
0.4 N
Rakamcherla IP – EIA Description of Environment
74
Figure 3.18 Soil Classification of the Study Area
3.10.2 Soil Monitoring
For monitoring the soil quality within 10 Km radius, 10 sampling locations were
identified and the details of locations are given in Table 3-16.
Table -3.16 Soil Sampling Locations in the study area
S.No Sample
ID
Location Geographical
coordinates
Aerial
distance
(Km)
Direction with
respect to site
1. S1 Manneguda village N-17°18’03.0”E-77°58’54.7”
6.5 N
2. S2 Changomul village N-17°15’27.1”E-78°01’34.0”
6.57 ENE
3. S3 Kankal village N-17°12’17.1”E-78°00’24.4”
6.3 SE
4. S4 Near RakamcherlaIndustrial Park
N-17°14’45.5”E-77°57’48.8”
0.4 N
Rakamcherla IP – EIA Description of Environment
74
Figure 3.18 Soil Classification of the Study Area
3.10.2 Soil Monitoring
For monitoring the soil quality within 10 Km radius, 10 sampling locations were
identified and the details of locations are given in Table 3-16.
Table -3.16 Soil Sampling Locations in the study area
S.No Sample
ID
Location Geographical
coordinates
Aerial
distance
(Km)
Direction with
respect to site
1. S1 Manneguda village N-17°18’03.0”E-77°58’54.7”
6.5 N
2. S2 Changomul village N-17°15’27.1”E-78°01’34.0”
6.57 ENE
3. S3 Kankal village N-17°12’17.1”E-78°00’24.4”
6.3 SE
4. S4 Near RakamcherlaIndustrial Park
N-17°14’45.5”E-77°57’48.8”
0.4 N
Rakamcherla IP – EIA Description of Environment
75
S.No Sample
ID
Location Geographical
coordinates
Aerial
distance
(Km)
Direction with
respect to site
5. S5 Rakamcherlavillage
N-17°14’16.4”E-77°57’17.1”
1.4 SW
6. S6 Somangurthyvillage
N-17°13’34.6”E-77°56’08.7”
3.75 SW
7. S7 Manchanpallyvillage
N-17°10’44.2”E-77°58’08.5”
7.17 S
8. S8 Nazeerabad village N-17°10’22.6”E-77°54’19.8”
9.8 SW
9. S9 Rukumpallevillage
N-17°12’13.6”E-77°51’45.2”
10.0 W
10. S10 Near Burgupallevillage
N-17°16’37.88”E-77°53’48.09”
8.3 NW
Figure 3.19 Types of soil in the study area
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75
S.No Sample
ID
Location Geographical
coordinates
Aerial
distance
(Km)
Direction with
respect to site
5. S5 Rakamcherlavillage
N-17°14’16.4”E-77°57’17.1”
1.4 SW
6. S6 Somangurthyvillage
N-17°13’34.6”E-77°56’08.7”
3.75 SW
7. S7 Manchanpallyvillage
N-17°10’44.2”E-77°58’08.5”
7.17 S
8. S8 Nazeerabad village N-17°10’22.6”E-77°54’19.8”
9.8 SW
9. S9 Rukumpallevillage
N-17°12’13.6”E-77°51’45.2”
10.0 W
10. S10 Near Burgupallevillage
N-17°16’37.88”E-77°53’48.09”
8.3 NW
Figure 3.19 Types of soil in the study area
Rakamcherla IP – EIA Description of Environment
75
S.No Sample
ID
Location Geographical
coordinates
Aerial
distance
(Km)
Direction with
respect to site
5. S5 Rakamcherlavillage
N-17°14’16.4”E-77°57’17.1”
1.4 SW
6. S6 Somangurthyvillage
N-17°13’34.6”E-77°56’08.7”
3.75 SW
7. S7 Manchanpallyvillage
N-17°10’44.2”E-77°58’08.5”
7.17 S
8. S8 Nazeerabad village N-17°10’22.6”E-77°54’19.8”
9.8 SW
9. S9 Rukumpallevillage
N-17°12’13.6”E-77°51’45.2”
10.0 W
10. S10 Near Burgupallevillage
N-17°16’37.88”E-77°53’48.09”
8.3 NW
Figure 3.19 Types of soil in the study area
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Figure 3.20 Soil Sampling Locations of the study area
3.10.3 Soil Quality
The pH of the soil samples ranged from 7.13 to 8 across the sampling stations. The
Electrical conductivity of the soil samples ranged from to 42-239 µs/cm across the
sampling stations. The water holding capacity of the soil samples varied from 14.65 to
42.38 (%W/W). Other parameters like Mercury, Total Chromium (mg/l), were below
the detection limit. The results of analysis are given in Table 3-17.
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Figure 3.20 Soil Sampling Locations of the study area
3.10.3 Soil Quality
The pH of the soil samples ranged from 7.13 to 8 across the sampling stations. The
Electrical conductivity of the soil samples ranged from to 42-239 µs/cm across the
sampling stations. The water holding capacity of the soil samples varied from 14.65 to
42.38 (%W/W). Other parameters like Mercury, Total Chromium (mg/l), were below
the detection limit. The results of analysis are given in Table 3-17.
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Figure 3.20 Soil Sampling Locations of the study area
3.10.3 Soil Quality
The pH of the soil samples ranged from 7.13 to 8 across the sampling stations. The
Electrical conductivity of the soil samples ranged from to 42-239 µs/cm across the
sampling stations. The water holding capacity of the soil samples varied from 14.65 to
42.38 (%W/W). Other parameters like Mercury, Total Chromium (mg/l), were below
the detection limit. The results of analysis are given in Table 3-17.
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Table 3.17 Analytical results of soil samples collected at different sampling stations
S.No Parameter Unit
S1-Manneg
udavillage
S2-Chango
mulvillage
S3-Kankalvillage
S4-NearRakamcherla I P
S5-Rakamcherla village
S6-Somangurthy village
S7-Manchan
pallyvillage
S8-Nazeerabad village
S9-Rukumpalle village
S10-NearBurgupalle village
1 Colour ReddishBrown
ReddishBrown
Brown ReddishBrown
ReddishBrown
Brown Brown ReddishBrown
Brown Brown
2 Soil Texture SandyClayLoam
SandyClayLoam
ClayLoam
SandyLoam
SandyLoam
Sandy Clay Clay loam Clay loam Clay loam Clay loam
3 Sand % 64 68 39 72 63 60 41 43 35 36
4 Silt % 24 12 34 18 26 24 26 25 35 33
5 Clay % 12 20 27 10 11 16 33 32 30 31
6 pH ( 1:2.) 7.99 7.84 7.58 7.53 7.13 7.63 8.1 7.89 7.58 7.94
7 Cconductivity( 1:2.)
umhos/cm
84 129 167 72 95 94 184 174 168 165
8 InfiltrationRate
cm/hr 1.35 1.47 1.08 1.51 1.31 1.17 1.09 1.04 1.07 1.04
9 Bulk Density gm/cc 1.41 1.39 1.21 1.15 1.43 1.42 1.48 1.51 1.46 1.37
10 CationExchangeCapacity
meq/100 gm
6.62 11.1 13.4 4.9 5.3 8.8 16.8 15.9 15.1 13.9
11 Moisturecontent
% 9.14 13.84 15.146 7.403 5.89 8.27 15.367 15.879 15.013 15.073
12 WaterHoldingCapacity
% 19.7 34.8 42.4 24.06 35.4 23.2 14.7 16.4 24.4 29.3
13 OrganicCarbon
% 0.321 0.645 0.793 0.436 0.423 0.416 0.683 0.564 0.441 0.488
14 Organicmatter
% 0.55 1.11 1.37 0.75 0.73 0.72 1.18 0.97 0.76 0.84
15 Nitrogen as N % 0.017 0.033 0.039 0.023 0.022 0.024 0.030 0.032 0.025 0.022
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Table 3.17 Analytical results of soil samples collected at different sampling stations
S.No Parameter Unit
S1-Manneg
udavillage
S2-Chango
mulvillage
S3-Kankalvillage
S4-NearRakamcherla I P
S5-Rakamcherla village
S6-Somangurthy village
S7-Manchan
pallyvillage
S8-Nazeerabad village
S9-Rukumpalle village
S10-NearBurgupalle village
1 Colour ReddishBrown
ReddishBrown
Brown ReddishBrown
ReddishBrown
Brown Brown ReddishBrown
Brown Brown
2 Soil Texture SandyClayLoam
SandyClayLoam
ClayLoam
SandyLoam
SandyLoam
Sandy Clay Clay loam Clay loam Clay loam Clay loam
3 Sand % 64 68 39 72 63 60 41 43 35 36
4 Silt % 24 12 34 18 26 24 26 25 35 33
5 Clay % 12 20 27 10 11 16 33 32 30 31
6 pH ( 1:2.) 7.99 7.84 7.58 7.53 7.13 7.63 8.1 7.89 7.58 7.94
7 Cconductivity( 1:2.)
umhos/cm
84 129 167 72 95 94 184 174 168 165
8 InfiltrationRate
cm/hr 1.35 1.47 1.08 1.51 1.31 1.17 1.09 1.04 1.07 1.04
9 Bulk Density gm/cc 1.41 1.39 1.21 1.15 1.43 1.42 1.48 1.51 1.46 1.37
10 CationExchangeCapacity
meq/100 gm
6.62 11.1 13.4 4.9 5.3 8.8 16.8 15.9 15.1 13.9
11 Moisturecontent
% 9.14 13.84 15.146 7.403 5.89 8.27 15.367 15.879 15.013 15.073
12 WaterHoldingCapacity
% 19.7 34.8 42.4 24.06 35.4 23.2 14.7 16.4 24.4 29.3
13 OrganicCarbon
% 0.321 0.645 0.793 0.436 0.423 0.416 0.683 0.564 0.441 0.488
14 Organicmatter
% 0.55 1.11 1.37 0.75 0.73 0.72 1.18 0.97 0.76 0.84
15 Nitrogen as N % 0.017 0.033 0.039 0.023 0.022 0.024 0.030 0.032 0.025 0.022
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Table 3.17 Analytical results of soil samples collected at different sampling stations
S.No Parameter Unit
S1-Manneg
udavillage
S2-Chango
mulvillage
S3-Kankalvillage
S4-NearRakamcherla I P
S5-Rakamcherla village
S6-Somangurthy village
S7-Manchan
pallyvillage
S8-Nazeerabad village
S9-Rukumpalle village
S10-NearBurgupalle village
1 Colour ReddishBrown
ReddishBrown
Brown ReddishBrown
ReddishBrown
Brown Brown ReddishBrown
Brown Brown
2 Soil Texture SandyClayLoam
SandyClayLoam
ClayLoam
SandyLoam
SandyLoam
Sandy Clay Clay loam Clay loam Clay loam Clay loam
3 Sand % 64 68 39 72 63 60 41 43 35 36
4 Silt % 24 12 34 18 26 24 26 25 35 33
5 Clay % 12 20 27 10 11 16 33 32 30 31
6 pH ( 1:2.) 7.99 7.84 7.58 7.53 7.13 7.63 8.1 7.89 7.58 7.94
7 Cconductivity( 1:2.)
umhos/cm
84 129 167 72 95 94 184 174 168 165
8 InfiltrationRate
cm/hr 1.35 1.47 1.08 1.51 1.31 1.17 1.09 1.04 1.07 1.04
9 Bulk Density gm/cc 1.41 1.39 1.21 1.15 1.43 1.42 1.48 1.51 1.46 1.37
10 CationExchangeCapacity
meq/100 gm
6.62 11.1 13.4 4.9 5.3 8.8 16.8 15.9 15.1 13.9
11 Moisturecontent
% 9.14 13.84 15.146 7.403 5.89 8.27 15.367 15.879 15.013 15.073
12 WaterHoldingCapacity
% 19.7 34.8 42.4 24.06 35.4 23.2 14.7 16.4 24.4 29.3
13 OrganicCarbon
% 0.321 0.645 0.793 0.436 0.423 0.416 0.683 0.564 0.441 0.488
14 Organicmatter
% 0.55 1.11 1.37 0.75 0.73 0.72 1.18 0.97 0.76 0.84
15 Nitrogen as N % 0.017 0.033 0.039 0.023 0.022 0.024 0.030 0.032 0.025 0.022
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16 Phosphorus % 0.39 0.38 0.20 0.37 0.27 0.26 0.25 0.24 0.19 0.13
17 Potassium % 1.55 1.53 0.79 1.47 1.07 1.05 1.00 0.97 0.76 0.50
18 C/N Ratio 19.1 19.8 20.6 18.9 18.9 17.5 23.0 17.9 17.5 22.2
18 Calcium % 0.39 0.38 0.21 0.33 0.14 0.11 0.17 0.16 0.2 0.089
25 Magnesium % 0.210 0.195 0.14 0.145 0.12 0.14 0.15 0.145 0.11 0.06
19 Boron mg/kg 1.17 1.28 1.14 0.07 1.09 1.32 1.04 0.09 0.08 0.41
20 Cadmium mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL21 Chromium
(Total )mg/kg
BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL22 Copper mg/kg 12.6 26.4 23.1 24.3 11.5 20.4 17.4 31.7 19.2 11.5
23 Iron mg/kg 34685 34729 34906 34609 34931 34413 37539 29108 30477 27558
24 Lead mg/kg 41.39 38.36 36.9 38.88 40.47 29.37 38.48 25.93 24.93 30.49
28 Manganese mg/kg 11.9 13.4 7.8 13.1 15.7 17.3 15.7 12.8 13.5 12.3
26 mercury mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL27 Zinc mg/kg 18.7 21.3 15.3 18.8 21.5 24.2 22.3 19.1 9.5 18.7
28 Arsenic mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
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16 Phosphorus % 0.39 0.38 0.20 0.37 0.27 0.26 0.25 0.24 0.19 0.13
17 Potassium % 1.55 1.53 0.79 1.47 1.07 1.05 1.00 0.97 0.76 0.50
18 C/N Ratio 19.1 19.8 20.6 18.9 18.9 17.5 23.0 17.9 17.5 22.2
18 Calcium % 0.39 0.38 0.21 0.33 0.14 0.11 0.17 0.16 0.2 0.089
25 Magnesium % 0.210 0.195 0.14 0.145 0.12 0.14 0.15 0.145 0.11 0.06
19 Boron mg/kg 1.17 1.28 1.14 0.07 1.09 1.32 1.04 0.09 0.08 0.41
20 Cadmium mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL21 Chromium
(Total )mg/kg
BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL22 Copper mg/kg 12.6 26.4 23.1 24.3 11.5 20.4 17.4 31.7 19.2 11.5
23 Iron mg/kg 34685 34729 34906 34609 34931 34413 37539 29108 30477 27558
24 Lead mg/kg 41.39 38.36 36.9 38.88 40.47 29.37 38.48 25.93 24.93 30.49
28 Manganese mg/kg 11.9 13.4 7.8 13.1 15.7 17.3 15.7 12.8 13.5 12.3
26 mercury mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL27 Zinc mg/kg 18.7 21.3 15.3 18.8 21.5 24.2 22.3 19.1 9.5 18.7
28 Arsenic mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
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16 Phosphorus % 0.39 0.38 0.20 0.37 0.27 0.26 0.25 0.24 0.19 0.13
17 Potassium % 1.55 1.53 0.79 1.47 1.07 1.05 1.00 0.97 0.76 0.50
18 C/N Ratio 19.1 19.8 20.6 18.9 18.9 17.5 23.0 17.9 17.5 22.2
18 Calcium % 0.39 0.38 0.21 0.33 0.14 0.11 0.17 0.16 0.2 0.089
25 Magnesium % 0.210 0.195 0.14 0.145 0.12 0.14 0.15 0.145 0.11 0.06
19 Boron mg/kg 1.17 1.28 1.14 0.07 1.09 1.32 1.04 0.09 0.08 0.41
20 Cadmium mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL21 Chromium
(Total )mg/kg
BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL22 Copper mg/kg 12.6 26.4 23.1 24.3 11.5 20.4 17.4 31.7 19.2 11.5
23 Iron mg/kg 34685 34729 34906 34609 34931 34413 37539 29108 30477 27558
24 Lead mg/kg 41.39 38.36 36.9 38.88 40.47 29.37 38.48 25.93 24.93 30.49
28 Manganese mg/kg 11.9 13.4 7.8 13.1 15.7 17.3 15.7 12.8 13.5 12.3
26 mercury mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL27 Zinc mg/kg 18.7 21.3 15.3 18.8 21.5 24.2 22.3 19.1 9.5 18.7
28 Arsenic mg/kg BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL
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3.11 Terrestrial Ecology
The study of terrestrial ecology within the study area of 10 km radius has been carried out
through field investigation and satellite imagery data as discussed earlier. The area can be
classified into the following ecological zone.
3.11.1 Flora in the Study Area
The study experiences hot climate during summer and cooler winter due to absence of
thick forest cover in the region. Large tracts of land in the region are under cotton
cultivation. Forest types found in the study area predominantly open forest type, scrub
forest are found distributed in the few patches in the SW of the site. Social forestry
development induced Eucalyptus plantations can be seen in Northern and eastern
region to the site. Two plant species. Banjan (Ficus benghalensis) Butea frondosa are
predominantly distributed in the study area. The biodiversity study was conducted to
provide information on flora present in the study area. The study was conducted from
05.03.2014 to 07.03.2014 in places situated within a radius of 10 km from the site. The
list of places covered in the floral biodiversity and faunal biodiversity survey are
Rakamcherla, Rukumpalle, Nazeerabad, Kankal, Changomul, Manneguda,
Manchanpally, Gudpalle, Madgul Chittempalle, Thirumalapur tanda, Somangurthy,
Pudur and Burgupalle. The various species of flora and fauna recorded in the study
are tabulated. Discussions were held with local people to gather related information on
the richness of plant and animal resources.
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3.11 Terrestrial Ecology
The study of terrestrial ecology within the study area of 10 km radius has been carried out
through field investigation and satellite imagery data as discussed earlier. The area can be
classified into the following ecological zone.
3.11.1 Flora in the Study Area
The study experiences hot climate during summer and cooler winter due to absence of
thick forest cover in the region. Large tracts of land in the region are under cotton
cultivation. Forest types found in the study area predominantly open forest type, scrub
forest are found distributed in the few patches in the SW of the site. Social forestry
development induced Eucalyptus plantations can be seen in Northern and eastern
region to the site. Two plant species. Banjan (Ficus benghalensis) Butea frondosa are
predominantly distributed in the study area. The biodiversity study was conducted to
provide information on flora present in the study area. The study was conducted from
05.03.2014 to 07.03.2014 in places situated within a radius of 10 km from the site. The
list of places covered in the floral biodiversity and faunal biodiversity survey are
Rakamcherla, Rukumpalle, Nazeerabad, Kankal, Changomul, Manneguda,
Manchanpally, Gudpalle, Madgul Chittempalle, Thirumalapur tanda, Somangurthy,
Pudur and Burgupalle. The various species of flora and fauna recorded in the study
are tabulated. Discussions were held with local people to gather related information on
the richness of plant and animal resources.
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3.11 Terrestrial Ecology
The study of terrestrial ecology within the study area of 10 km radius has been carried out
through field investigation and satellite imagery data as discussed earlier. The area can be
classified into the following ecological zone.
3.11.1 Flora in the Study Area
The study experiences hot climate during summer and cooler winter due to absence of
thick forest cover in the region. Large tracts of land in the region are under cotton
cultivation. Forest types found in the study area predominantly open forest type, scrub
forest are found distributed in the few patches in the SW of the site. Social forestry
development induced Eucalyptus plantations can be seen in Northern and eastern
region to the site. Two plant species. Banjan (Ficus benghalensis) Butea frondosa are
predominantly distributed in the study area. The biodiversity study was conducted to
provide information on flora present in the study area. The study was conducted from
05.03.2014 to 07.03.2014 in places situated within a radius of 10 km from the site. The
list of places covered in the floral biodiversity and faunal biodiversity survey are
Rakamcherla, Rukumpalle, Nazeerabad, Kankal, Changomul, Manneguda,
Manchanpally, Gudpalle, Madgul Chittempalle, Thirumalapur tanda, Somangurthy,
Pudur and Burgupalle. The various species of flora and fauna recorded in the study
are tabulated. Discussions were held with local people to gather related information on
the richness of plant and animal resources.
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Figure 3.21 Floral biodiversity in the study area
3.11.1.1 Trees
A number of tree species was observed in the study area which is given in the
below table.
Table 3.18 List of Trees in the Study Area
S.No Botanical name English name Local name (Telugu )
1.Magnifera indica Mango Mamidi
2.Ficus benghalensis Banyan Marri
3.Butea frondosa Flame of the forest Moduga
4.Techtona grandis Teak Teku
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Figure 3.21 Floral biodiversity in the study area
3.11.1.1 Trees
A number of tree species was observed in the study area which is given in the
below table.
Table 3.18 List of Trees in the Study Area
S.No Botanical name English name Local name (Telugu )
1.Magnifera indica Mango Mamidi
2.Ficus benghalensis Banyan Marri
3.Butea frondosa Flame of the forest Moduga
4.Techtona grandis Teak Teku
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Figure 3.21 Floral biodiversity in the study area
3.11.1.1 Trees
A number of tree species was observed in the study area which is given in the
below table.
Table 3.18 List of Trees in the Study Area
S.No Botanical name English name Local name (Telugu )
1.Magnifera indica Mango Mamidi
2.Ficus benghalensis Banyan Marri
3.Butea frondosa Flame of the forest Moduga
4.Techtona grandis Teak Teku
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S.No Botanical name English name Local name (Telugu )
5.Phoenix sylvestris Wild date palm Itha
6.Bambusa bambo Bamboo Bongu veduru
7.Acacia arabica Gum arabic tree Natu tuma
8.Acacia melanoxylon Sally Wattle Kondakorinda
9.Ficus religiosa Pee pal Raavi
10.Prosopis spicigera Indian mesquit. Jammi
11.Pongamia pinnata Indian beech Kanuga
12.Peltophorum africanum Weeping wattle Pacha sunkesula
13.Acacia mearnsii black wattle Tumma
14.Acacia farnesiana Cassie flower Kasturitumma
15.Enterolobium saman Rain tree Nidra ganneru
16.Eucalyptus globules Eucalyptus Jamayul
17.Sesbania grandiflora Hummingbird tree Avisi
18.Balanites aegyptiaca Desert date Gara
19.Barringtonia acutangula Indian putat Kadimi
20.Bauhinia malabarica Mountain ebony Puli chinta
21.Bauhinia racemosa Burmese Silk Orchid Tella Are chettu
22.Acacia ferruginea Rusty Acacia Anisandra
23.Acacia leucophloea White barked Acacia Tella tumma
24.Acacia nilotica Babool Nalla tumma
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S.No Botanical name English name Local name (Telugu )
5.Phoenix sylvestris Wild date palm Itha
6.Bambusa bambo Bamboo Bongu veduru
7.Acacia arabica Gum arabic tree Natu tuma
8.Acacia melanoxylon Sally Wattle Kondakorinda
9.Ficus religiosa Pee pal Raavi
10.Prosopis spicigera Indian mesquit. Jammi
11.Pongamia pinnata Indian beech Kanuga
12.Peltophorum africanum Weeping wattle Pacha sunkesula
13.Acacia mearnsii black wattle Tumma
14.Acacia farnesiana Cassie flower Kasturitumma
15.Enterolobium saman Rain tree Nidra ganneru
16.Eucalyptus globules Eucalyptus Jamayul
17.Sesbania grandiflora Hummingbird tree Avisi
18.Balanites aegyptiaca Desert date Gara
19.Barringtonia acutangula Indian putat Kadimi
20.Bauhinia malabarica Mountain ebony Puli chinta
21.Bauhinia racemosa Burmese Silk Orchid Tella Are chettu
22.Acacia ferruginea Rusty Acacia Anisandra
23.Acacia leucophloea White barked Acacia Tella tumma
24.Acacia nilotica Babool Nalla tumma
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S.No Botanical name English name Local name (Telugu )
5.Phoenix sylvestris Wild date palm Itha
6.Bambusa bambo Bamboo Bongu veduru
7.Acacia arabica Gum arabic tree Natu tuma
8.Acacia melanoxylon Sally Wattle Kondakorinda
9.Ficus religiosa Pee pal Raavi
10.Prosopis spicigera Indian mesquit. Jammi
11.Pongamia pinnata Indian beech Kanuga
12.Peltophorum africanum Weeping wattle Pacha sunkesula
13.Acacia mearnsii black wattle Tumma
14.Acacia farnesiana Cassie flower Kasturitumma
15.Enterolobium saman Rain tree Nidra ganneru
16.Eucalyptus globules Eucalyptus Jamayul
17.Sesbania grandiflora Hummingbird tree Avisi
18.Balanites aegyptiaca Desert date Gara
19.Barringtonia acutangula Indian putat Kadimi
20.Bauhinia malabarica Mountain ebony Puli chinta
21.Bauhinia racemosa Burmese Silk Orchid Tella Are chettu
22.Acacia ferruginea Rusty Acacia Anisandra
23.Acacia leucophloea White barked Acacia Tella tumma
24.Acacia nilotica Babool Nalla tumma
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S.No Botanical name English name Local name (Telugu )
25.Albizia lebbeck Flea tree Dirisena
26.Albizia odoratissima Black siris Cinduga
27.Albizia procera White siris Tella cinduga
3.11.1.2 Shrubs
The study area has patches of shrub forest in many places therefore number of
shrubs where recorded during the study. Shrubs encountered during the survey are
given in the table.
Table 3.19 Shrubs Recorded in the Study Area
S.No Scientific name English name Vernacular name
1. Senna auriculata Tanner's Cassia Tangedu
2.Abutilon indicum Indian Mallow Tutura benda
3.Acacia latronum Buffalo thorn Tella tumma
4.Ageratum conyzoides Goat weed Pumpillu
5.Allophylus cobbe Indian Allophylus Erra avalu
6.Anisomeles malabarica Malabar Catmint Mahaveera
7.Breynia vitis-ideaea Phyllanthaceae Erra-balli
8.Bridelia Montana --- Pantangi, Panchavoni
9.Carissa carandas Karanda Kalivi
10.Calycopteris floribunda Paper flower climber Bonta teega, Adavi jama, Pottengi
11.Calotropis gigantean Crown Flower Jilledu
12.Carissa spinarum Wild Karanda Vaka
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S.No Botanical name English name Local name (Telugu )
25.Albizia lebbeck Flea tree Dirisena
26.Albizia odoratissima Black siris Cinduga
27.Albizia procera White siris Tella cinduga
3.11.1.2 Shrubs
The study area has patches of shrub forest in many places therefore number of
shrubs where recorded during the study. Shrubs encountered during the survey are
given in the table.
Table 3.19 Shrubs Recorded in the Study Area
S.No Scientific name English name Vernacular name
1. Senna auriculata Tanner's Cassia Tangedu
2.Abutilon indicum Indian Mallow Tutura benda
3.Acacia latronum Buffalo thorn Tella tumma
4.Ageratum conyzoides Goat weed Pumpillu
5.Allophylus cobbe Indian Allophylus Erra avalu
6.Anisomeles malabarica Malabar Catmint Mahaveera
7.Breynia vitis-ideaea Phyllanthaceae Erra-balli
8.Bridelia Montana --- Pantangi, Panchavoni
9.Carissa carandas Karanda Kalivi
10.Calycopteris floribunda Paper flower climber Bonta teega, Adavi jama, Pottengi
11.Calotropis gigantean Crown Flower Jilledu
12.Carissa spinarum Wild Karanda Vaka
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S.No Botanical name English name Local name (Telugu )
25.Albizia lebbeck Flea tree Dirisena
26.Albizia odoratissima Black siris Cinduga
27.Albizia procera White siris Tella cinduga
3.11.1.2 Shrubs
The study area has patches of shrub forest in many places therefore number of
shrubs where recorded during the study. Shrubs encountered during the survey are
given in the table.
Table 3.19 Shrubs Recorded in the Study Area
S.No Scientific name English name Vernacular name
1. Senna auriculata Tanner's Cassia Tangedu
2.Abutilon indicum Indian Mallow Tutura benda
3.Acacia latronum Buffalo thorn Tella tumma
4.Ageratum conyzoides Goat weed Pumpillu
5.Allophylus cobbe Indian Allophylus Erra avalu
6.Anisomeles malabarica Malabar Catmint Mahaveera
7.Breynia vitis-ideaea Phyllanthaceae Erra-balli
8.Bridelia Montana --- Pantangi, Panchavoni
9.Carissa carandas Karanda Kalivi
10.Calycopteris floribunda Paper flower climber Bonta teega, Adavi jama, Pottengi
11.Calotropis gigantean Crown Flower Jilledu
12.Carissa spinarum Wild Karanda Vaka
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S.No Scientific name English name Vernacular name
13.Cassia surattensis Scrambled Egg Tree Metta tangedu
14.Cipadessa baccifera Ranabili Chedu Bira
15.Cleistanthus collinus Garari Kodisha
16.Cissus quadrangularis Devil's Backbone Gudametige
17.Clerodendron phlomidis Arni Tekkali, Nelli
18.Dichrostachys cinerea Sickle Bush Velthuru
19.Dodonaea viscose Hop Bush Puli-vailu, Bandam, Golla pulleda
20.Drypetes sepiaria Wild Caper Bush Bira
21.Erythroxylummonogynum
Red Cedar Deva Dharu, Pagadamu chettu
22.Euphorbia antiquorum Square Milk Hedge Bomma Jemmudu
23.Euphorbia nivulia Leafy Milk Hedge Jemmudu
24.Euphorbia tirucalli Round Milk Hedge Manchi Jemmudu
25.Gardenia gummifera Cambi gum tree, Bikki
26.Gymnosporia spinosa Bharati Danti
27.Holarrhena pubescens Indrajao Tedla pala
28.Hugonia mystax Tomentose Pisangi, Kakibira,
29.Jatropha curcas Physic Nut Nepalamu
30.Lawsonia inermis Henna Gorintaku
31.Maytenus emarginatus Notched Leaf Soapnut Kukudu-kayalu
32.Mimosa intsia Twisted Acacia Konda-korinta
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S.No Scientific name English name Vernacular name
13.Cassia surattensis Scrambled Egg Tree Metta tangedu
14.Cipadessa baccifera Ranabili Chedu Bira
15.Cleistanthus collinus Garari Kodisha
16.Cissus quadrangularis Devil's Backbone Gudametige
17.Clerodendron phlomidis Arni Tekkali, Nelli
18.Dichrostachys cinerea Sickle Bush Velthuru
19.Dodonaea viscose Hop Bush Puli-vailu, Bandam, Golla pulleda
20.Drypetes sepiaria Wild Caper Bush Bira
21.Erythroxylummonogynum
Red Cedar Deva Dharu, Pagadamu chettu
22.Euphorbia antiquorum Square Milk Hedge Bomma Jemmudu
23.Euphorbia nivulia Leafy Milk Hedge Jemmudu
24.Euphorbia tirucalli Round Milk Hedge Manchi Jemmudu
25.Gardenia gummifera Cambi gum tree, Bikki
26.Gymnosporia spinosa Bharati Danti
27.Holarrhena pubescens Indrajao Tedla pala
28.Hugonia mystax Tomentose Pisangi, Kakibira,
29.Jatropha curcas Physic Nut Nepalamu
30.Lawsonia inermis Henna Gorintaku
31.Maytenus emarginatus Notched Leaf Soapnut Kukudu-kayalu
32.Mimosa intsia Twisted Acacia Konda-korinta
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S.No Scientific name English name Vernacular name
13.Cassia surattensis Scrambled Egg Tree Metta tangedu
14.Cipadessa baccifera Ranabili Chedu Bira
15.Cleistanthus collinus Garari Kodisha
16.Cissus quadrangularis Devil's Backbone Gudametige
17.Clerodendron phlomidis Arni Tekkali, Nelli
18.Dichrostachys cinerea Sickle Bush Velthuru
19.Dodonaea viscose Hop Bush Puli-vailu, Bandam, Golla pulleda
20.Drypetes sepiaria Wild Caper Bush Bira
21.Erythroxylummonogynum
Red Cedar Deva Dharu, Pagadamu chettu
22.Euphorbia antiquorum Square Milk Hedge Bomma Jemmudu
23.Euphorbia nivulia Leafy Milk Hedge Jemmudu
24.Euphorbia tirucalli Round Milk Hedge Manchi Jemmudu
25.Gardenia gummifera Cambi gum tree, Bikki
26.Gymnosporia spinosa Bharati Danti
27.Holarrhena pubescens Indrajao Tedla pala
28.Hugonia mystax Tomentose Pisangi, Kakibira,
29.Jatropha curcas Physic Nut Nepalamu
30.Lawsonia inermis Henna Gorintaku
31.Maytenus emarginatus Notched Leaf Soapnut Kukudu-kayalu
32.Mimosa intsia Twisted Acacia Konda-korinta
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S.No Scientific name English name Vernacular name
33.Phyllanthus reticulates Black honey shrub Pulsare
34.Randia dumetorum Mountain Pomegranate Manga chettu
35.Rhus mysorensis Mysore sumac Sith-sundari
36.Scutia myrtina Cat thorn Pariki
37.Woodfordia fruticosa Red Bell Bush Jargi, Seringi, Jaji
3.11.1.3 Climbers
Climbers encountered during the survey are given in the below table.
Table 3.20 Climbers present in the study area
S.No Scientific name English name Vernacular name
1.Ipomoea pes-carpae Goat's foot creeper Chevulapilli theege
2.Rivea hypocrateriformis Midnapore creeper Nirubodi
3.Ichnocarpus frutescens Black creeper Karampala
4.Tinospora cordifolia Giloy Tippatiga, Somida
5.Bauhinia vahlii Maloo creeper Madapu
6.Argyreia nervosa Elephant creeper Samudrapala
7.Cucumis melo Melon Mulam pandu
8.Toddalia asiatica varfloribunda
Wild orange tree Kondakasinda
9.Ipomoea sepiaria Purple heart glory Mettatuti
10.Trichosanthes cuspidat Snake gourd Avaduta
11.Merremia hederacea Ivy woodrose Kalasa
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S.No Scientific name English name Vernacular name
33.Phyllanthus reticulates Black honey shrub Pulsare
34.Randia dumetorum Mountain Pomegranate Manga chettu
35.Rhus mysorensis Mysore sumac Sith-sundari
36.Scutia myrtina Cat thorn Pariki
37.Woodfordia fruticosa Red Bell Bush Jargi, Seringi, Jaji
3.11.1.3 Climbers
Climbers encountered during the survey are given in the below table.
Table 3.20 Climbers present in the study area
S.No Scientific name English name Vernacular name
1.Ipomoea pes-carpae Goat's foot creeper Chevulapilli theege
2.Rivea hypocrateriformis Midnapore creeper Nirubodi
3.Ichnocarpus frutescens Black creeper Karampala
4.Tinospora cordifolia Giloy Tippatiga, Somida
5.Bauhinia vahlii Maloo creeper Madapu
6.Argyreia nervosa Elephant creeper Samudrapala
7.Cucumis melo Melon Mulam pandu
8.Toddalia asiatica varfloribunda
Wild orange tree Kondakasinda
9.Ipomoea sepiaria Purple heart glory Mettatuti
10.Trichosanthes cuspidat Snake gourd Avaduta
11.Merremia hederacea Ivy woodrose Kalasa
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S.No Scientific name English name Vernacular name
33.Phyllanthus reticulates Black honey shrub Pulsare
34.Randia dumetorum Mountain Pomegranate Manga chettu
35.Rhus mysorensis Mysore sumac Sith-sundari
36.Scutia myrtina Cat thorn Pariki
37.Woodfordia fruticosa Red Bell Bush Jargi, Seringi, Jaji
3.11.1.3 Climbers
Climbers encountered during the survey are given in the below table.
Table 3.20 Climbers present in the study area
S.No Scientific name English name Vernacular name
1.Ipomoea pes-carpae Goat's foot creeper Chevulapilli theege
2.Rivea hypocrateriformis Midnapore creeper Nirubodi
3.Ichnocarpus frutescens Black creeper Karampala
4.Tinospora cordifolia Giloy Tippatiga, Somida
5.Bauhinia vahlii Maloo creeper Madapu
6.Argyreia nervosa Elephant creeper Samudrapala
7.Cucumis melo Melon Mulam pandu
8.Toddalia asiatica varfloribunda
Wild orange tree Kondakasinda
9.Ipomoea sepiaria Purple heart glory Mettatuti
10.Trichosanthes cuspidat Snake gourd Avaduta
11.Merremia hederacea Ivy woodrose Kalasa
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S.No Scientific name English name Vernacular name
12.Ampelocissus latifolia Wild grape Bedasatiga, Bedalatiga
13.Cissus quadrangularis Veldt grape Gudametige
14.Pentatropis capensis Ambarvel Chekurtitiwa
15.Pergularia daemia Pergularia Jittupaku, Dushtupatige
16.Pentatropis capensis Ambarvel Chetaurtitiwa
3.11.1.4 Herbs
The herbaceous vegetation observed in the study area are given below
Table 3.21 Herbs recorded in the study area
S.No Scientific name English name Vernacular name
1.Argemone Mexicana Mexican Prickly Poppy Brahmadandi
2.Parthenium hysterophorus, Carrot Grass Chandani
3.Acalypha alnifolia Alder Leaved Cat Tail Chiru kuppinta
4.Adenostemma lavenia Sticky Daisy Jangli-jira
5.Aerva lanata Mountain knot grass Pindi konda
6.Alternanthera sessilis Sessile Joyweed Ponna Ganti kura
7.Barleria cristata Striped Philippine Violet Tellanilambari
8.Bidens pilosa Beggar tick Phutium
9.Cassia tora Stinking cassia Tantepu
10.Cleome viscose Asian spider flower Kukka-vaminta
11.Corchorus aestuans East Indian mallow Nela Bera
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S.No Scientific name English name Vernacular name
12.Ampelocissus latifolia Wild grape Bedasatiga, Bedalatiga
13.Cissus quadrangularis Veldt grape Gudametige
14.Pentatropis capensis Ambarvel Chekurtitiwa
15.Pergularia daemia Pergularia Jittupaku, Dushtupatige
16.Pentatropis capensis Ambarvel Chetaurtitiwa
3.11.1.4 Herbs
The herbaceous vegetation observed in the study area are given below
Table 3.21 Herbs recorded in the study area
S.No Scientific name English name Vernacular name
1.Argemone Mexicana Mexican Prickly Poppy Brahmadandi
2.Parthenium hysterophorus, Carrot Grass Chandani
3.Acalypha alnifolia Alder Leaved Cat Tail Chiru kuppinta
4.Adenostemma lavenia Sticky Daisy Jangli-jira
5.Aerva lanata Mountain knot grass Pindi konda
6.Alternanthera sessilis Sessile Joyweed Ponna Ganti kura
7.Barleria cristata Striped Philippine Violet Tellanilambari
8.Bidens pilosa Beggar tick Phutium
9.Cassia tora Stinking cassia Tantepu
10.Cleome viscose Asian spider flower Kukka-vaminta
11.Corchorus aestuans East Indian mallow Nela Bera
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S.No Scientific name English name Vernacular name
12.Ampelocissus latifolia Wild grape Bedasatiga, Bedalatiga
13.Cissus quadrangularis Veldt grape Gudametige
14.Pentatropis capensis Ambarvel Chekurtitiwa
15.Pergularia daemia Pergularia Jittupaku, Dushtupatige
16.Pentatropis capensis Ambarvel Chetaurtitiwa
3.11.1.4 Herbs
The herbaceous vegetation observed in the study area are given below
Table 3.21 Herbs recorded in the study area
S.No Scientific name English name Vernacular name
1.Argemone Mexicana Mexican Prickly Poppy Brahmadandi
2.Parthenium hysterophorus, Carrot Grass Chandani
3.Acalypha alnifolia Alder Leaved Cat Tail Chiru kuppinta
4.Adenostemma lavenia Sticky Daisy Jangli-jira
5.Aerva lanata Mountain knot grass Pindi konda
6.Alternanthera sessilis Sessile Joyweed Ponna Ganti kura
7.Barleria cristata Striped Philippine Violet Tellanilambari
8.Bidens pilosa Beggar tick Phutium
9.Cassia tora Stinking cassia Tantepu
10.Cleome viscose Asian spider flower Kukka-vaminta
11.Corchorus aestuans East Indian mallow Nela Bera
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12.Emilla sonchifolia Purple Sow Thistle mayarcevi
13.Euphorbia prostrate Prostrate Sandmat Rongoalathi
14.Grangea maderaspatana Madras Carpet Mastaru
15.Gynura crepidioides Thickhead Tera paibi
16.Heliotropium indicum Indian Heliotrope Nagadanthi
17.Hybanthus enneaspermus Spade flower Ratna Purusha
18.Sida cordifolia Heart leaf sida Chiru Benda
19.Triumfetta rhomboidea Burr bush Dekki,
20.Vernonia cinerea Little iron weed Sahadevi
21.Waltheria indica Sleepy morning Nalla Benda
3.11.1.5 Aquatic Plants
The aquatic plants observed in the study area are given below
Table 3.22 Aquatic plants recorded in the study area
S.No Scientific name English name Vernacular name
1. Eichornia crassipes Water hyacinth Budaga tamara
2.Pistia stratiotes Water lettuce Neeru veniki
3.Hydrilla verticillata Water thyme valakada
4.Nymphaea pubescens Pink water lily Thamara
5.Nymphaea nouchali Blue water lily Neelambal
3.11.2 Fauna
i.Domestic - The domestic animals are mainly mammals like cow, goat, cat, dog, etc.
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12.Emilla sonchifolia Purple Sow Thistle mayarcevi
13.Euphorbia prostrate Prostrate Sandmat Rongoalathi
14.Grangea maderaspatana Madras Carpet Mastaru
15.Gynura crepidioides Thickhead Tera paibi
16.Heliotropium indicum Indian Heliotrope Nagadanthi
17.Hybanthus enneaspermus Spade flower Ratna Purusha
18.Sida cordifolia Heart leaf sida Chiru Benda
19.Triumfetta rhomboidea Burr bush Dekki,
20.Vernonia cinerea Little iron weed Sahadevi
21.Waltheria indica Sleepy morning Nalla Benda
3.11.1.5 Aquatic Plants
The aquatic plants observed in the study area are given below
Table 3.22 Aquatic plants recorded in the study area
S.No Scientific name English name Vernacular name
1. Eichornia crassipes Water hyacinth Budaga tamara
2.Pistia stratiotes Water lettuce Neeru veniki
3.Hydrilla verticillata Water thyme valakada
4.Nymphaea pubescens Pink water lily Thamara
5.Nymphaea nouchali Blue water lily Neelambal
3.11.2 Fauna
i.Domestic - The domestic animals are mainly mammals like cow, goat, cat, dog, etc.
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12.Emilla sonchifolia Purple Sow Thistle mayarcevi
13.Euphorbia prostrate Prostrate Sandmat Rongoalathi
14.Grangea maderaspatana Madras Carpet Mastaru
15.Gynura crepidioides Thickhead Tera paibi
16.Heliotropium indicum Indian Heliotrope Nagadanthi
17.Hybanthus enneaspermus Spade flower Ratna Purusha
18.Sida cordifolia Heart leaf sida Chiru Benda
19.Triumfetta rhomboidea Burr bush Dekki,
20.Vernonia cinerea Little iron weed Sahadevi
21.Waltheria indica Sleepy morning Nalla Benda
3.11.1.5 Aquatic Plants
The aquatic plants observed in the study area are given below
Table 3.22 Aquatic plants recorded in the study area
S.No Scientific name English name Vernacular name
1. Eichornia crassipes Water hyacinth Budaga tamara
2.Pistia stratiotes Water lettuce Neeru veniki
3.Hydrilla verticillata Water thyme valakada
4.Nymphaea pubescens Pink water lily Thamara
5.Nymphaea nouchali Blue water lily Neelambal
3.11.2 Fauna
i.Domestic - The domestic animals are mainly mammals like cow, goat, cat, dog, etc.
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ii.Wild Animals -Since the natural forests constitute small amount of the forest area
and since they are in isolated pockets, the wild life does not offer a wide spectrum of
species. Wild animals are rarely seen due to absence of natural dense forest and land
occupied by human being. Other than these, some reptiles and amphibians can also be
seen with a number of bird species.
3.11.2.1 Mammals
The various wild mammalian species observed in the study area are given below;
Table 3.23 List of Mammals recorded in the study area
S.No Zoological name English name Vernacular name
1.Felis chaus Jungle cat Adavi pilli
2.Herpestes javanicus Asian Small Mongoose Mungisa
3.Funambulus palmarum Three-striped palm squirrel Uduta
4.Lepus nigricollis Black-naped Hare Kundelu
5.Manis crassicaudata Indian Pangolin Nela Chepa
6.Vulpes bengalensis Indian Fox Nakka
7.Hystrix indica Indian Porcupine Mullapandi
8.Rattus rattus Common rat Eluka
3.11.2.2 Birds
The various species of birds observed in the study area are given below
Table 3.24 Birds recorded in the study area
S.No Scientific Name English name Vernacular name
1. Phalacrocoraxfuscicollis
Indian Cormorant Neeti kaki
2.Egretta garzetta Little Egret Chinna tella konga
3.Bubulcus ibis Cattle Egret Egret
4. Ardeola grayii Indian Pond Heron Guddi konga
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ii.Wild Animals -Since the natural forests constitute small amount of the forest area
and since they are in isolated pockets, the wild life does not offer a wide spectrum of
species. Wild animals are rarely seen due to absence of natural dense forest and land
occupied by human being. Other than these, some reptiles and amphibians can also be
seen with a number of bird species.
3.11.2.1 Mammals
The various wild mammalian species observed in the study area are given below;
Table 3.23 List of Mammals recorded in the study area
S.No Zoological name English name Vernacular name
1.Felis chaus Jungle cat Adavi pilli
2.Herpestes javanicus Asian Small Mongoose Mungisa
3.Funambulus palmarum Three-striped palm squirrel Uduta
4.Lepus nigricollis Black-naped Hare Kundelu
5.Manis crassicaudata Indian Pangolin Nela Chepa
6.Vulpes bengalensis Indian Fox Nakka
7.Hystrix indica Indian Porcupine Mullapandi
8.Rattus rattus Common rat Eluka
3.11.2.2 Birds
The various species of birds observed in the study area are given below
Table 3.24 Birds recorded in the study area
S.No Scientific Name English name Vernacular name
1. Phalacrocoraxfuscicollis
Indian Cormorant Neeti kaki
2.Egretta garzetta Little Egret Chinna tella konga
3.Bubulcus ibis Cattle Egret Egret
4. Ardeola grayii Indian Pond Heron Guddi konga
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ii.Wild Animals -Since the natural forests constitute small amount of the forest area
and since they are in isolated pockets, the wild life does not offer a wide spectrum of
species. Wild animals are rarely seen due to absence of natural dense forest and land
occupied by human being. Other than these, some reptiles and amphibians can also be
seen with a number of bird species.
3.11.2.1 Mammals
The various wild mammalian species observed in the study area are given below;
Table 3.23 List of Mammals recorded in the study area
S.No Zoological name English name Vernacular name
1.Felis chaus Jungle cat Adavi pilli
2.Herpestes javanicus Asian Small Mongoose Mungisa
3.Funambulus palmarum Three-striped palm squirrel Uduta
4.Lepus nigricollis Black-naped Hare Kundelu
5.Manis crassicaudata Indian Pangolin Nela Chepa
6.Vulpes bengalensis Indian Fox Nakka
7.Hystrix indica Indian Porcupine Mullapandi
8.Rattus rattus Common rat Eluka
3.11.2.2 Birds
The various species of birds observed in the study area are given below
Table 3.24 Birds recorded in the study area
S.No Scientific Name English name Vernacular name
1. Phalacrocoraxfuscicollis
Indian Cormorant Neeti kaki
2.Egretta garzetta Little Egret Chinna tella konga
3.Bubulcus ibis Cattle Egret Egret
4. Ardeola grayii Indian Pond Heron Guddi konga
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S.No Scientific Name English name Vernacular name5. Coturnix coturnix Common Quail Gogari yellichi
6.Columba livia Blue Rock Pigeon Nalla Pavuram
7.Psittacula eupatria Alexandrine Parakeet Pedda chiluka
8.Psittacula krameri Rose-ringed Parakeet Ramachiluka
9.Cuculus micropterus Indian Cuckoo Koyila
10.Bubo nipalensis Forest Eagle-Owl Gudlaguva
11.Alcedo coerulescens Small Blue Kingfisher Lakumuki
12.Merops orientalis Green Bee-eater Chinna passeriki
13.Dinopium benghalense Golden-backed Woodpecker Vadrangi pitta
14.Pycnonotus jocosus Red-whiskered Bulbul Turaka-pigli-pitta
15.Pycnonotus cafer Red-vented Bulbul Pigli-pitta
16.Corvus splendens House Crow Kaki
3.11.2.3 Reptiles
The various species of reptiles observed in the study area are given below.
Table 3.25 Reptiles recorded in the study area
S.No Scientific name Common Name Vernacular name
1.Calotes versicolor Common garden lizard Tonda
2.Ptyas mucosus Common rat snake Jerripothu
3.Varanus bengalensis Common Indian monitor Udumu
4.Hemidactylus flaviviridis House Gecko Balli
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S.No Scientific Name English name Vernacular name5. Coturnix coturnix Common Quail Gogari yellichi
6.Columba livia Blue Rock Pigeon Nalla Pavuram
7.Psittacula eupatria Alexandrine Parakeet Pedda chiluka
8.Psittacula krameri Rose-ringed Parakeet Ramachiluka
9.Cuculus micropterus Indian Cuckoo Koyila
10.Bubo nipalensis Forest Eagle-Owl Gudlaguva
11.Alcedo coerulescens Small Blue Kingfisher Lakumuki
12.Merops orientalis Green Bee-eater Chinna passeriki
13.Dinopium benghalense Golden-backed Woodpecker Vadrangi pitta
14.Pycnonotus jocosus Red-whiskered Bulbul Turaka-pigli-pitta
15.Pycnonotus cafer Red-vented Bulbul Pigli-pitta
16.Corvus splendens House Crow Kaki
3.11.2.3 Reptiles
The various species of reptiles observed in the study area are given below.
Table 3.25 Reptiles recorded in the study area
S.No Scientific name Common Name Vernacular name
1.Calotes versicolor Common garden lizard Tonda
2.Ptyas mucosus Common rat snake Jerripothu
3.Varanus bengalensis Common Indian monitor Udumu
4.Hemidactylus flaviviridis House Gecko Balli
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S.No Scientific Name English name Vernacular name5. Coturnix coturnix Common Quail Gogari yellichi
6.Columba livia Blue Rock Pigeon Nalla Pavuram
7.Psittacula eupatria Alexandrine Parakeet Pedda chiluka
8.Psittacula krameri Rose-ringed Parakeet Ramachiluka
9.Cuculus micropterus Indian Cuckoo Koyila
10.Bubo nipalensis Forest Eagle-Owl Gudlaguva
11.Alcedo coerulescens Small Blue Kingfisher Lakumuki
12.Merops orientalis Green Bee-eater Chinna passeriki
13.Dinopium benghalense Golden-backed Woodpecker Vadrangi pitta
14.Pycnonotus jocosus Red-whiskered Bulbul Turaka-pigli-pitta
15.Pycnonotus cafer Red-vented Bulbul Pigli-pitta
16.Corvus splendens House Crow Kaki
3.11.2.3 Reptiles
The various species of reptiles observed in the study area are given below.
Table 3.25 Reptiles recorded in the study area
S.No Scientific name Common Name Vernacular name
1.Calotes versicolor Common garden lizard Tonda
2.Ptyas mucosus Common rat snake Jerripothu
3.Varanus bengalensis Common Indian monitor Udumu
4.Hemidactylus flaviviridis House Gecko Balli
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S.No Scientific name Common Name Vernacular name
5.Hemidactylus brookii Spotted Indian House Gecko Nallikeechu
6.Ahaetulla mycterizans Common Green Whip Snake Pasirika
7.Chamaeleo zeylanicus Indian Chameleon Usaravilli
8.Calotes versicolor Oriental Garden Lizard Tonda
9.Bungarus caeruleus Common Indian Krait Katla pamu
3.11.2.4 Amphibians
The various species of amphibians observed in the study area are given below
Table 3.26 List of Amphibians
S.No Scientific Name English name Vernacular name
1.Rana temporaria Common frog Kappa
2.Euphlyctis hexadactylus Indian green frog Godrukappa
3.Fejervarya kudremukhensis Cricket frog Kappa
4.Sphaerotheca breviceps Indian burrowing frog Kappa
5.Euphlyctis cyanophlyctis Skipper frog Chettukappa
6.Hoplobatrachus crassus Jerdon's bullfrog Kappa
3.11.2.5 Insects
The various species of insects observed in the study area are given below
Table 3.27 List of Insects recorded in the study area
S.No Scientific Name English name Vernacular name
1.Oecophylla smaragdina Weaver ant Neta cimala
2.Paratrechina longicornis Longhorn crazy ant Gandru chima
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S.No Scientific name Common Name Vernacular name
5.Hemidactylus brookii Spotted Indian House Gecko Nallikeechu
6.Ahaetulla mycterizans Common Green Whip Snake Pasirika
7.Chamaeleo zeylanicus Indian Chameleon Usaravilli
8.Calotes versicolor Oriental Garden Lizard Tonda
9.Bungarus caeruleus Common Indian Krait Katla pamu
3.11.2.4 Amphibians
The various species of amphibians observed in the study area are given below
Table 3.26 List of Amphibians
S.No Scientific Name English name Vernacular name
1.Rana temporaria Common frog Kappa
2.Euphlyctis hexadactylus Indian green frog Godrukappa
3.Fejervarya kudremukhensis Cricket frog Kappa
4.Sphaerotheca breviceps Indian burrowing frog Kappa
5.Euphlyctis cyanophlyctis Skipper frog Chettukappa
6.Hoplobatrachus crassus Jerdon's bullfrog Kappa
3.11.2.5 Insects
The various species of insects observed in the study area are given below
Table 3.27 List of Insects recorded in the study area
S.No Scientific Name English name Vernacular name
1.Oecophylla smaragdina Weaver ant Neta cimala
2.Paratrechina longicornis Longhorn crazy ant Gandru chima
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S.No Scientific name Common Name Vernacular name
5.Hemidactylus brookii Spotted Indian House Gecko Nallikeechu
6.Ahaetulla mycterizans Common Green Whip Snake Pasirika
7.Chamaeleo zeylanicus Indian Chameleon Usaravilli
8.Calotes versicolor Oriental Garden Lizard Tonda
9.Bungarus caeruleus Common Indian Krait Katla pamu
3.11.2.4 Amphibians
The various species of amphibians observed in the study area are given below
Table 3.26 List of Amphibians
S.No Scientific Name English name Vernacular name
1.Rana temporaria Common frog Kappa
2.Euphlyctis hexadactylus Indian green frog Godrukappa
3.Fejervarya kudremukhensis Cricket frog Kappa
4.Sphaerotheca breviceps Indian burrowing frog Kappa
5.Euphlyctis cyanophlyctis Skipper frog Chettukappa
6.Hoplobatrachus crassus Jerdon's bullfrog Kappa
3.11.2.5 Insects
The various species of insects observed in the study area are given below
Table 3.27 List of Insects recorded in the study area
S.No Scientific Name English name Vernacular name
1.Oecophylla smaragdina Weaver ant Neta cimala
2.Paratrechina longicornis Longhorn crazy ant Gandru chima
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3.Monomorium floricula Flower ant Puspam chima
4.Solenopis invicta Fire ant
Chima
5.Tetra morium guineense Guinea ant Giniya cimala
6.Pieris rapae Cabbage Butterfly Cabbage seethakokachilaka
7.Euploea core Common indian crow Kaki
8.Phalanta phalanta Common leopard Chirutha chiluka
9.Danaus chrysippus Plain tiger Pulli chiluka
10.Papilio demoleus Lime butterfly Akuchilaka
11.Coccinella magnifica Ladybird beetle Arudra purugu
12.Panagaeus cruxmajor Ground beetle Pedapurugu
13.Ceratogomphus pictus Dragon fly Tuniga
14.Eurythyrea austriaca Jewel beetle Boddenka
3.12 Socio Economic Environment
3.12.1 Social Indicators
Vikarabad district was formed in the year 1978 by carving out of erstwhile
Hyderabad district. The district is bounded on the North by Medak district, east by
Nalgonda district, South by Mahbubnagar district, west by Gulbarga district and
North west by Bidar district of Karnataka state. The area of the district is 7564.88
Sq.kms. The agro climatic zone of the district is Southern Telangana Zone (AP-5).
Now the district is part of Telangana state.
3.12.1.1 Demography
As per Census 2011, RR district has the population of 52,96,741 comprises of
27,01,008 of male and 25,95,733 female population as per census 2011. The
rural population of the district is only 30% as its proximity to Hyderabad city.
Majority of population belongs to the general category (83.56%), 12.31% of
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3.Monomorium floricula Flower ant Puspam chima
4.Solenopis invicta Fire ant
Chima
5.Tetra morium guineense Guinea ant Giniya cimala
6.Pieris rapae Cabbage Butterfly Cabbage seethakokachilaka
7.Euploea core Common indian crow Kaki
8.Phalanta phalanta Common leopard Chirutha chiluka
9.Danaus chrysippus Plain tiger Pulli chiluka
10.Papilio demoleus Lime butterfly Akuchilaka
11.Coccinella magnifica Ladybird beetle Arudra purugu
12.Panagaeus cruxmajor Ground beetle Pedapurugu
13.Ceratogomphus pictus Dragon fly Tuniga
14.Eurythyrea austriaca Jewel beetle Boddenka
3.12 Socio Economic Environment
3.12.1 Social Indicators
Vikarabad district was formed in the year 1978 by carving out of erstwhile
Hyderabad district. The district is bounded on the North by Medak district, east by
Nalgonda district, South by Mahbubnagar district, west by Gulbarga district and
North west by Bidar district of Karnataka state. The area of the district is 7564.88
Sq.kms. The agro climatic zone of the district is Southern Telangana Zone (AP-5).
Now the district is part of Telangana state.
3.12.1.1 Demography
As per Census 2011, RR district has the population of 52,96,741 comprises of
27,01,008 of male and 25,95,733 female population as per census 2011. The
rural population of the district is only 30% as its proximity to Hyderabad city.
Majority of population belongs to the general category (83.56%), 12.31% of
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3.Monomorium floricula Flower ant Puspam chima
4.Solenopis invicta Fire ant
Chima
5.Tetra morium guineense Guinea ant Giniya cimala
6.Pieris rapae Cabbage Butterfly Cabbage seethakokachilaka
7.Euploea core Common indian crow Kaki
8.Phalanta phalanta Common leopard Chirutha chiluka
9.Danaus chrysippus Plain tiger Pulli chiluka
10.Papilio demoleus Lime butterfly Akuchilaka
11.Coccinella magnifica Ladybird beetle Arudra purugu
12.Panagaeus cruxmajor Ground beetle Pedapurugu
13.Ceratogomphus pictus Dragon fly Tuniga
14.Eurythyrea austriaca Jewel beetle Boddenka
3.12 Socio Economic Environment
3.12.1 Social Indicators
Vikarabad district was formed in the year 1978 by carving out of erstwhile
Hyderabad district. The district is bounded on the North by Medak district, east by
Nalgonda district, South by Mahbubnagar district, west by Gulbarga district and
North west by Bidar district of Karnataka state. The area of the district is 7564.88
Sq.kms. The agro climatic zone of the district is Southern Telangana Zone (AP-5).
Now the district is part of Telangana state.
3.12.1.1 Demography
As per Census 2011, RR district has the population of 52,96,741 comprises of
27,01,008 of male and 25,95,733 female population as per census 2011. The
rural population of the district is only 30% as its proximity to Hyderabad city.
Majority of population belongs to the general category (83.56%), 12.31% of
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population is Schedule Castes and remaining 4.13% population belongs to
Schedule tribes. The tribe Lambadi is in good numbers in the district.
(Source: Census 2011 – Vikarabad District)
Figure 3.22 District-Social Groups in Rangareddy district
3.12.1.2 Sex Ratio
The sex ratio for the district is 955, but for the state are 990. Though the district is
more urbanized, the sex ratio is abysmally low. Social intervention is required to
normalize the sex ratio. The child sex ratio is decreasing as 933 for 2011 against 959 in
2001.
Source: Statistical year book 2011Figure 3.4 Sex-Ratio District vs State
11.66% 2.72%
994
948953 958
880
900
920
940
960
980
1000
1901
1911
Sex
Ratio
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population is Schedule Castes and remaining 4.13% population belongs to
Schedule tribes. The tribe Lambadi is in good numbers in the district.
(Source: Census 2011 – Vikarabad District)
Figure 3.22 District-Social Groups in Rangareddy district
3.12.1.2 Sex Ratio
The sex ratio for the district is 955, but for the state are 990. Though the district is
more urbanized, the sex ratio is abysmally low. Social intervention is required to
normalize the sex ratio. The child sex ratio is decreasing as 933 for 2011 against 959 in
2001.
Source: Statistical year book 2011Figure 3.4 Sex-Ratio District vs State
84.18%
2.72%0.15%
0.04%0.07%
0.03%
1.15%
District Social Group
Hindu
Muslims
Christian
Sikh
Buddhist
Jain
Others
Not Stated
994
948956
925
944
990 986
963 956941 944
955953 958 964955 959
983 976 969 972 969 974990
1921
1931
1941
1951
1961
1971
1981
1991
2001
2011
Sex Ratio District Vs State
RR District
Telangana
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population is Schedule Castes and remaining 4.13% population belongs to
Schedule tribes. The tribe Lambadi is in good numbers in the district.
(Source: Census 2011 – Vikarabad District)
Figure 3.22 District-Social Groups in Rangareddy district
3.12.1.2 Sex Ratio
The sex ratio for the district is 955, but for the state are 990. Though the district is
more urbanized, the sex ratio is abysmally low. Social intervention is required to
normalize the sex ratio. The child sex ratio is decreasing as 933 for 2011 against 959 in
2001.
Source: Statistical year book 2011Figure 3.4 Sex-Ratio District vs State
Hindu
Muslims
Christian
Sikh
Buddhist
Jain
Others
Not Stated
RR District
Telangana
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3.12.1.3 Child Population
In census enumeration, data regarding child under 0-6 age were also collected for
all districts including Vikarabad District. In 2011, Children under 0-6 formed 6.1
percent of Vikarabad District compared to 2001. There was net change of -2.6
percent in this compared to previous census of India.
Table 3.28 Child Population in the District
Description 2011 2001
Total Child Population (0-6 Age) 633,172 500,024
Male Population (0-6 Age) 327,563 255,216
Female Population (0-6 Age) 305,609 244,808
Child Sex Ratio (0-6 Age) 933 959
Source: Census of India 2011
3.12.1.4 Population Density
The density of the population of the district is 707 whereas same of the state is
312. Percentage of Urban population to the total population of the district is
70.22%, but for the state is 38.88%. It is second in Hyderabad district.
3.12.1.5 Decadal Growth
The decadal growth of population of the district is 48.15%, but that of the state is
13.58 % as per 2011 Census. It is highest in the state due to the fast urbanization
of the district and migration of the workers from different part of the state.
Figure 3.5 Population of Vikarabad District
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3.12.1.3 Child Population
In census enumeration, data regarding child under 0-6 age were also collected for
all districts including Vikarabad District. In 2011, Children under 0-6 formed 6.1
percent of Vikarabad District compared to 2001. There was net change of -2.6
percent in this compared to previous census of India.
Table 3.28 Child Population in the District
Description 2011 2001
Total Child Population (0-6 Age) 633,172 500,024
Male Population (0-6 Age) 327,563 255,216
Female Population (0-6 Age) 305,609 244,808
Child Sex Ratio (0-6 Age) 933 959
Source: Census of India 2011
3.12.1.4 Population Density
The density of the population of the district is 707 whereas same of the state is
312. Percentage of Urban population to the total population of the district is
70.22%, but for the state is 38.88%. It is second in Hyderabad district.
3.12.1.5 Decadal Growth
The decadal growth of population of the district is 48.15%, but that of the state is
13.58 % as per 2011 Census. It is highest in the state due to the fast urbanization
of the district and migration of the workers from different part of the state.
Figure 3.5 Population of Vikarabad District
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3.12.1.3 Child Population
In census enumeration, data regarding child under 0-6 age were also collected for
all districts including Vikarabad District. In 2011, Children under 0-6 formed 6.1
percent of Vikarabad District compared to 2001. There was net change of -2.6
percent in this compared to previous census of India.
Table 3.28 Child Population in the District
Description 2011 2001
Total Child Population (0-6 Age) 633,172 500,024
Male Population (0-6 Age) 327,563 255,216
Female Population (0-6 Age) 305,609 244,808
Child Sex Ratio (0-6 Age) 933 959
Source: Census of India 2011
3.12.1.4 Population Density
The density of the population of the district is 707 whereas same of the state is
312. Percentage of Urban population to the total population of the district is
70.22%, but for the state is 38.88%. It is second in Hyderabad district.
3.12.1.5 Decadal Growth
The decadal growth of population of the district is 48.15%, but that of the state is
13.58 % as per 2011 Census. It is highest in the state due to the fast urbanization
of the district and migration of the workers from different part of the state.
Figure 3.5 Population of Vikarabad District
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Table 3.29 Comparison of Demographic profile 2011 and 2001
Description 2011 2001
Actual Population 5,296,741 3,575,064
Male 2,701,008 1,839,227
Female 2,595,733 1,735,837
Population Growth 48.16% 40.09%
Area Sq. Km 7,493 7,493
Density/km2 707 477
Proportion 6.26% 4.69%
Sex Ratio (Per 1000) 961 944
Child Sex Ratio (0-6 Age) 933 959
Average Literacy 75.87 66.16
Male Literacy 82.11 75.26
Female Literacy 69.40 56.49
Total Child Population (0-6 Age) 633,172 500,024
Male Population (0-6 Age) 327,563 255,216
Female Population (0-6 Age) 305,609 244,808
Literates 3,538,028 2,034,381
Male Literates 1,948,784 1,192,100
Female Literates 1,589,244 842,281
Child Proportion (0-6 Age) 11.95% 13.99%
Boys Proportion (0-6 Age) 12.13% 13.88%
Girls Proportion (0-6 Age) 11.77% 14.10%
(Source: Census 2011 – Vikarabad District)
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Table 3.29 Comparison of Demographic profile 2011 and 2001
Description 2011 2001
Actual Population 5,296,741 3,575,064
Male 2,701,008 1,839,227
Female 2,595,733 1,735,837
Population Growth 48.16% 40.09%
Area Sq. Km 7,493 7,493
Density/km2 707 477
Proportion 6.26% 4.69%
Sex Ratio (Per 1000) 961 944
Child Sex Ratio (0-6 Age) 933 959
Average Literacy 75.87 66.16
Male Literacy 82.11 75.26
Female Literacy 69.40 56.49
Total Child Population (0-6 Age) 633,172 500,024
Male Population (0-6 Age) 327,563 255,216
Female Population (0-6 Age) 305,609 244,808
Literates 3,538,028 2,034,381
Male Literates 1,948,784 1,192,100
Female Literates 1,589,244 842,281
Child Proportion (0-6 Age) 11.95% 13.99%
Boys Proportion (0-6 Age) 12.13% 13.88%
Girls Proportion (0-6 Age) 11.77% 14.10%
(Source: Census 2011 – Vikarabad District)
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Table 3.29 Comparison of Demographic profile 2011 and 2001
Description 2011 2001
Actual Population 5,296,741 3,575,064
Male 2,701,008 1,839,227
Female 2,595,733 1,735,837
Population Growth 48.16% 40.09%
Area Sq. Km 7,493 7,493
Density/km2 707 477
Proportion 6.26% 4.69%
Sex Ratio (Per 1000) 961 944
Child Sex Ratio (0-6 Age) 933 959
Average Literacy 75.87 66.16
Male Literacy 82.11 75.26
Female Literacy 69.40 56.49
Total Child Population (0-6 Age) 633,172 500,024
Male Population (0-6 Age) 327,563 255,216
Female Population (0-6 Age) 305,609 244,808
Literates 3,538,028 2,034,381
Male Literates 1,948,784 1,192,100
Female Literates 1,589,244 842,281
Child Proportion (0-6 Age) 11.95% 13.99%
Boys Proportion (0-6 Age) 12.13% 13.88%
Girls Proportion (0-6 Age) 11.77% 14.10%
(Source: Census 2011 – Vikarabad District)
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Table 3.4 Comparison of Demographic profile between Rural and Urban
Description Rural Urban
Population (%) 29.78 % 70.22 %
Total Population 1,577,569 3,719,172
Male Population 801,013 1,899,995
Female Population 776,556 1,819,177
Sex Ratio 969 957
Child Sex Ratio (0-6) 938 931
Child Population (0-6) 192,848 440,324
Male Child(0-6) 99,495 228,068
Female Child(0-6) 93,353 212,256
Child Percentage (0-6) 12.42 % 12.0 %
Literates 839,187 2,698,841
Male Literates 493,493 1,455,291
Female Literates 345,694 1,243,550
Average Literacy 60.60 % 82.31 %
Male Literacy 70.35 % 87.04 %
Female Literacy 50.60 % 77.39 %
(Source: Census 2011 – Vikarabad District)
3.12.1.6 Occupation and Income
The district is very unique in its character since it has both urban and rural colors.
The economy of the district depends both on agricultural and non-agricultural
activities.
The per capita income of the RR district is Rs.1,17,752/- in the year of 2013-2014
and Rs.1,80,039/- in the year of 2014-2015 based on current price, which is
higher than the state. The following graph shows the consistent growth of the per
capita income.
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Table 3.4 Comparison of Demographic profile between Rural and Urban
Description Rural Urban
Population (%) 29.78 % 70.22 %
Total Population 1,577,569 3,719,172
Male Population 801,013 1,899,995
Female Population 776,556 1,819,177
Sex Ratio 969 957
Child Sex Ratio (0-6) 938 931
Child Population (0-6) 192,848 440,324
Male Child(0-6) 99,495 228,068
Female Child(0-6) 93,353 212,256
Child Percentage (0-6) 12.42 % 12.0 %
Literates 839,187 2,698,841
Male Literates 493,493 1,455,291
Female Literates 345,694 1,243,550
Average Literacy 60.60 % 82.31 %
Male Literacy 70.35 % 87.04 %
Female Literacy 50.60 % 77.39 %
(Source: Census 2011 – Vikarabad District)
3.12.1.6 Occupation and Income
The district is very unique in its character since it has both urban and rural colors.
The economy of the district depends both on agricultural and non-agricultural
activities.
The per capita income of the RR district is Rs.1,17,752/- in the year of 2013-2014
and Rs.1,80,039/- in the year of 2014-2015 based on current price, which is
higher than the state. The following graph shows the consistent growth of the per
capita income.
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Table 3.4 Comparison of Demographic profile between Rural and Urban
Description Rural Urban
Population (%) 29.78 % 70.22 %
Total Population 1,577,569 3,719,172
Male Population 801,013 1,899,995
Female Population 776,556 1,819,177
Sex Ratio 969 957
Child Sex Ratio (0-6) 938 931
Child Population (0-6) 192,848 440,324
Male Child(0-6) 99,495 228,068
Female Child(0-6) 93,353 212,256
Child Percentage (0-6) 12.42 % 12.0 %
Literates 839,187 2,698,841
Male Literates 493,493 1,455,291
Female Literates 345,694 1,243,550
Average Literacy 60.60 % 82.31 %
Male Literacy 70.35 % 87.04 %
Female Literacy 50.60 % 77.39 %
(Source: Census 2011 – Vikarabad District)
3.12.1.6 Occupation and Income
The district is very unique in its character since it has both urban and rural colors.
The economy of the district depends both on agricultural and non-agricultural
activities.
The per capita income of the RR district is Rs.1,17,752/- in the year of 2013-2014
and Rs.1,80,039/- in the year of 2014-2015 based on current price, which is
higher than the state. The following graph shows the consistent growth of the per
capita income.
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Figure 3-6 Types of workers in the district
Figure 3-7 Percapita income of the district
Only 28% of workers involved in agriculture related activities, major workers are
in the Others category (68.43%) .ie. they are all government servants, municipal
employees, teachers, factory workers, plantation workers, those engaged in trade,
commerce, business, transport, banking, mining, construction, political or social
work, priests, entertainment artists, etc. Except other category workers, women
participation in occupation is more than their counterpart.
13.89
01020304050607080
Cultivators
Wor
kers
per
cent
age
2916
6
3677
6
4297
6
2440
9
2898
7
0
20000
40000
60000
80000
100000
120000
140000
Per Capita Income by Districts at Current Prices (in Crores)
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Figure 3-6 Types of workers in the district
Figure 3-7 Percapita income of the district
Only 28% of workers involved in agriculture related activities, major workers are
in the Others category (68.43%) .ie. they are all government servants, municipal
employees, teachers, factory workers, plantation workers, those engaged in trade,
commerce, business, transport, banking, mining, construction, political or social
work, priests, entertainment artists, etc. Except other category workers, women
participation in occupation is more than their counterpart.
14.113.57
68.43
Cultivators Agri.labour Household Workers Other workers
Type of workers
Occupational Details
4297
6
4993
1
6332
8
6686
7 9372
6
1003
08
1105
26
1177
52
3338
1
3965
2
4911
4
5195
5
6695
1
7512
4
8516
9
9536
1
Per Capita Income by Districts at Current Prices (in Crores)
District
State
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Figure 3-6 Types of workers in the district
Figure 3-7 Percapita income of the district
Only 28% of workers involved in agriculture related activities, major workers are
in the Others category (68.43%) .ie. they are all government servants, municipal
employees, teachers, factory workers, plantation workers, those engaged in trade,
commerce, business, transport, banking, mining, construction, political or social
work, priests, entertainment artists, etc. Except other category workers, women
participation in occupation is more than their counterpart.
68.43
Other workers
District
State
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98
The overwhelming majority of farmers are small farmers, and agricultural
labourers. Small and marginal farmers, whose land holdings are below 2 hectares,
constitute almost 84.02% of all farmers, and more than 90% of them are
dependent on rain for their crops. The competition, erratic output price are
compelled them to abandon their farming and take refuge in other places in search
of employment.
The number of marginal/small farmers has increased over the last 10 years shows
the fragmentation of the landholding.
(Source: Ministry of agriculture and welfare)
Figure 3.8 Operational Land Holding
3.12.1.7 Agriculture
The agriculture is the main occupation of the district. The variation in the fertility
of the soils is the main cause for the difference in cropping pattern of the eastern
and western regions in the district. Black cotton soils dominate the western
region (Chevella, Pargi, Vikarabad, Marpally and Tandur). Food crops account
for (85%) and the non-food crops (15%) to the gross area shown in the district.
Grape cultivation makes the district occupy the distinct place in the state.
Paddy is the main cereal crop being cultivated in the district. The District is
predominately dependent on rainfall with limited irrigation potential. The total
77.65
18.08
4.280
10
20
30
40
50
60
70
80
90
2000-01
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The overwhelming majority of farmers are small farmers, and agricultural
labourers. Small and marginal farmers, whose land holdings are below 2 hectares,
constitute almost 84.02% of all farmers, and more than 90% of them are
dependent on rain for their crops. The competition, erratic output price are
compelled them to abandon their farming and take refuge in other places in search
of employment.
The number of marginal/small farmers has increased over the last 10 years shows
the fragmentation of the landholding.
(Source: Ministry of agriculture and welfare)
Figure 3.8 Operational Land Holding
3.12.1.7 Agriculture
The agriculture is the main occupation of the district. The variation in the fertility
of the soils is the main cause for the difference in cropping pattern of the eastern
and western regions in the district. Black cotton soils dominate the western
region (Chevella, Pargi, Vikarabad, Marpally and Tandur). Food crops account
for (85%) and the non-food crops (15%) to the gross area shown in the district.
Grape cultivation makes the district occupy the distinct place in the state.
Paddy is the main cereal crop being cultivated in the district. The District is
predominately dependent on rainfall with limited irrigation potential. The total
77.65 78.4684.02
18.08 17.6813.68
4.28 3.86 2.29
2005-06 2010-11
Operation Landholding Pattern
Small
Medium
Large
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The overwhelming majority of farmers are small farmers, and agricultural
labourers. Small and marginal farmers, whose land holdings are below 2 hectares,
constitute almost 84.02% of all farmers, and more than 90% of them are
dependent on rain for their crops. The competition, erratic output price are
compelled them to abandon their farming and take refuge in other places in search
of employment.
The number of marginal/small farmers has increased over the last 10 years shows
the fragmentation of the landholding.
(Source: Ministry of agriculture and welfare)
Figure 3.8 Operational Land Holding
3.12.1.7 Agriculture
The agriculture is the main occupation of the district. The variation in the fertility
of the soils is the main cause for the difference in cropping pattern of the eastern
and western regions in the district. Black cotton soils dominate the western
region (Chevella, Pargi, Vikarabad, Marpally and Tandur). Food crops account
for (85%) and the non-food crops (15%) to the gross area shown in the district.
Grape cultivation makes the district occupy the distinct place in the state.
Paddy is the main cereal crop being cultivated in the district. The District is
predominately dependent on rainfall with limited irrigation potential. The total
Small
Medium
Large
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99
geographical area of the district is 7.49 Lakhs hectares The net area sown is
33.39%, 80% is rain fed and about 20% is under irrigated conditions. The current
fallows constitute 17.5% of the geographical area.
Further, the potential of medium irrigation projects is not fully exploited. The
major irrigation source is wells (65%) followed by tanks (17%), tubewells (10%)
and others (8%).
Marginal and small farmers constitute 73% of the total land holdings possessing
35% of the total area. While semi-medium to medium farmers constitute 25% of
total holdings occupying 50% of the area. Large holdings constitute only 2% with
only 15 percent area.
Due to spurt in urbanization, development of commercial establishments and
satellite towns in around the Hyderabad, Vikarabad district is influencing farmers
to switch over to other opportunities other than agriculture.
Figure 3.5 Land use pattern 2013-2014
(Source: Directorate of Economics and Statistics, Government of Telangana)
3.12.1.8 Education
Average literacy rate is 66.16% in 2001, 78.05% in 2011. It is second highest
literacy of the state, next to Hyderabad (80.96%). But the literacy rate of united
AP state is 67.66%. Female literacy for the district is 71.82%. The district has
050000
100000150000200000250000300000
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99
geographical area of the district is 7.49 Lakhs hectares The net area sown is
33.39%, 80% is rain fed and about 20% is under irrigated conditions. The current
fallows constitute 17.5% of the geographical area.
Further, the potential of medium irrigation projects is not fully exploited. The
major irrigation source is wells (65%) followed by tanks (17%), tubewells (10%)
and others (8%).
Marginal and small farmers constitute 73% of the total land holdings possessing
35% of the total area. While semi-medium to medium farmers constitute 25% of
total holdings occupying 50% of the area. Large holdings constitute only 2% with
only 15 percent area.
Due to spurt in urbanization, development of commercial establishments and
satellite towns in around the Hyderabad, Vikarabad district is influencing farmers
to switch over to other opportunities other than agriculture.
Figure 3.5 Land use pattern 2013-2014
(Source: Directorate of Economics and Statistics, Government of Telangana)
3.12.1.8 Education
Average literacy rate is 66.16% in 2001, 78.05% in 2011. It is second highest
literacy of the state, next to Hyderabad (80.96%). But the literacy rate of united
AP state is 67.66%. Female literacy for the district is 71.82%. The district has
Rakamcherla IP - EIA Description of Environment
99
geographical area of the district is 7.49 Lakhs hectares The net area sown is
33.39%, 80% is rain fed and about 20% is under irrigated conditions. The current
fallows constitute 17.5% of the geographical area.
Further, the potential of medium irrigation projects is not fully exploited. The
major irrigation source is wells (65%) followed by tanks (17%), tubewells (10%)
and others (8%).
Marginal and small farmers constitute 73% of the total land holdings possessing
35% of the total area. While semi-medium to medium farmers constitute 25% of
total holdings occupying 50% of the area. Large holdings constitute only 2% with
only 15 percent area.
Due to spurt in urbanization, development of commercial establishments and
satellite towns in around the Hyderabad, Vikarabad district is influencing farmers
to switch over to other opportunities other than agriculture.
Figure 3.5 Land use pattern 2013-2014
(Source: Directorate of Economics and Statistics, Government of Telangana)
3.12.1.8 Education
Average literacy rate is 66.16% in 2001, 78.05% in 2011. It is second highest
literacy of the state, next to Hyderabad (80.96%). But the literacy rate of united
AP state is 67.66%. Female literacy for the district is 71.82%. The district has
Rakamcherla IP - EIA Description of Environment
100
good number of primary education facilities and they are all accessible. The
dropout rate of the district for primary classes is at par with the dropout rate of the
state. The dropout rate of girls are lower when compare to the boys. The
following table shows the dropout figure of RR district and the state.
There are 567 Junior colleges in the district. The No. of degree colleges are 171
(Commissioner of Collegiate Education), No. of Engineering colleges are 155 (as
per State council of higher education 2013-14) and Poly technical colleges are 46
(Commissioner of technical education 2013-14) available in the district.
Table 3.6 Schools in the District (2013-20104)
Typ
e of
Sch
ools
Pri
mar
y
Upp
er P
rim
ary
Pri
mar
y W
ith
Upp
er P
rim
ary,
Seco
ndar
y an
dH
ighe
r
Seco
ndar
ySc
hool
s(I
-XII
)U
pper
Pri
mar
yW
ith
Seco
ndar
yA
nd H
ighe
rSe
cond
ary
Scho
ols
(VI-
XII
)P
rim
ary
Wit
hU
pper
Pri
mar
yA
nd S
econ
dary
Scho
ols
( I-
X )
,
Upp
er P
rim
ary
Wit
h Se
cond
ary
Scho
ols
(VI-
X )
CentralGovernment
1 0 6 3 6 2
StateGovernment
40 9 7 16 11 41
MandalParishad
1665 236 0 0 0 423
Aided 17 13 1 0 1 17
Unaided 1068 523 5 5 127 973
Total 2791 781 19 24 145 1456
(Source: Directorate of Economics and Statistics, Govt. of Telangana)
Table 3.7 Dropout rate of Girls and Boys for the district and the State. (2013-14)
Description(Year 2010-11)
Classes I-XBoys Girls Total
District 26.22 28.5 26.02State (united) 39.05 37.33 38.21
Source: Directorate of Economics and Statistics
Rakamcherla IP - EIA Description of Environment
100
good number of primary education facilities and they are all accessible. The
dropout rate of the district for primary classes is at par with the dropout rate of the
state. The dropout rate of girls are lower when compare to the boys. The
following table shows the dropout figure of RR district and the state.
There are 567 Junior colleges in the district. The No. of degree colleges are 171
(Commissioner of Collegiate Education), No. of Engineering colleges are 155 (as
per State council of higher education 2013-14) and Poly technical colleges are 46
(Commissioner of technical education 2013-14) available in the district.
Table 3.6 Schools in the District (2013-20104)
Typ
e of
Sch
ools
Pri
mar
y
Upp
er P
rim
ary
Pri
mar
y W
ith
Upp
er P
rim
ary,
Seco
ndar
y an
dH
ighe
r
Seco
ndar
ySc
hool
s(I
-XII
)U
pper
Pri
mar
yW
ith
Seco
ndar
yA
nd H
ighe
rSe
cond
ary
Scho
ols
(VI-
XII
)P
rim
ary
Wit
hU
pper
Pri
mar
yA
nd S
econ
dary
Scho
ols
( I-
X )
,
Upp
er P
rim
ary
Wit
h Se
cond
ary
Scho
ols
(VI-
X )
CentralGovernment
1 0 6 3 6 2
StateGovernment
40 9 7 16 11 41
MandalParishad
1665 236 0 0 0 423
Aided 17 13 1 0 1 17
Unaided 1068 523 5 5 127 973
Total 2791 781 19 24 145 1456
(Source: Directorate of Economics and Statistics, Govt. of Telangana)
Table 3.7 Dropout rate of Girls and Boys for the district and the State. (2013-14)
Description(Year 2010-11)
Classes I-XBoys Girls Total
District 26.22 28.5 26.02State (united) 39.05 37.33 38.21
Source: Directorate of Economics and Statistics
Rakamcherla IP - EIA Description of Environment
100
good number of primary education facilities and they are all accessible. The
dropout rate of the district for primary classes is at par with the dropout rate of the
state. The dropout rate of girls are lower when compare to the boys. The
following table shows the dropout figure of RR district and the state.
There are 567 Junior colleges in the district. The No. of degree colleges are 171
(Commissioner of Collegiate Education), No. of Engineering colleges are 155 (as
per State council of higher education 2013-14) and Poly technical colleges are 46
(Commissioner of technical education 2013-14) available in the district.
Table 3.6 Schools in the District (2013-20104)
Typ
e of
Sch
ools
Pri
mar
y
Upp
er P
rim
ary
Pri
mar
y W
ith
Upp
er P
rim
ary,
Seco
ndar
y an
dH
ighe
r
Seco
ndar
ySc
hool
s(I
-XII
)U
pper
Pri
mar
yW
ith
Seco
ndar
yA
nd H
ighe
rSe
cond
ary
Scho
ols
(VI-
XII
)P
rim
ary
Wit
hU
pper
Pri
mar
yA
nd S
econ
dary
Scho
ols
( I-
X )
,
Upp
er P
rim
ary
Wit
h Se
cond
ary
Scho
ols
(VI-
X )
CentralGovernment
1 0 6 3 6 2
StateGovernment
40 9 7 16 11 41
MandalParishad
1665 236 0 0 0 423
Aided 17 13 1 0 1 17
Unaided 1068 523 5 5 127 973
Total 2791 781 19 24 145 1456
(Source: Directorate of Economics and Statistics, Govt. of Telangana)
Table 3.7 Dropout rate of Girls and Boys for the district and the State. (2013-14)
Description(Year 2010-11)
Classes I-XBoys Girls Total
District 26.22 28.5 26.02State (united) 39.05 37.33 38.21
Source: Directorate of Economics and Statistics
Rakamcherla IP - EIA Description of Environment
101
3.12.1.9 Health
There are no serious/contagious diseases found in the district. Polio and Leprosy
have been completely eradicated. The district has good health facilities. They
avail good health facilities as Hyderabad is close to the district.
Some of the health indicators of the district are as follows:
The Crude birth rate (year 2013) is 17.9,
Crude death rate is 7,
The infant Mortality rate (IMR-2013) is 33,
Maternal Mortality rate is 78 (2013 per 100000 live births)
Table 3.8 Health facilities in the district
S.No Health facility Nos.
1 No. of P.H.C.s (Rural) 52
2 No. of Sub-Centers 399
3 No of Area hospitals 4
4 No of CHC’s 9
3 No of district hospitals 1(Source: National Health Mission)
3.12.1.10 Animal Husbandry
The district has good livestock resources. The Livestock play a vital role in
sustaining Socio-economic life of people providing additional livelihood means to
a large number of small and marginal farmers. Many women and old people have
involved in rearing and maintaining of cattle and ruminants. Back yard poultry is
commonly prevalent in the rural areas. The buffaloes, sheep and the poultry
population have increased. Meat, milk products, egg, skin are main supplementary
income in the rural economy. Apart from the production of Milk and Meat, the
Cattle in the District are used as drought power in Agriculture and it is an allied
activity to Agriculture.
Rakamcherla IP - EIA Description of Environment
101
3.12.1.9 Health
There are no serious/contagious diseases found in the district. Polio and Leprosy
have been completely eradicated. The district has good health facilities. They
avail good health facilities as Hyderabad is close to the district.
Some of the health indicators of the district are as follows:
The Crude birth rate (year 2013) is 17.9,
Crude death rate is 7,
The infant Mortality rate (IMR-2013) is 33,
Maternal Mortality rate is 78 (2013 per 100000 live births)
Table 3.8 Health facilities in the district
S.No Health facility Nos.
1 No. of P.H.C.s (Rural) 52
2 No. of Sub-Centers 399
3 No of Area hospitals 4
4 No of CHC’s 9
3 No of district hospitals 1(Source: National Health Mission)
3.12.1.10 Animal Husbandry
The district has good livestock resources. The Livestock play a vital role in
sustaining Socio-economic life of people providing additional livelihood means to
a large number of small and marginal farmers. Many women and old people have
involved in rearing and maintaining of cattle and ruminants. Back yard poultry is
commonly prevalent in the rural areas. The buffaloes, sheep and the poultry
population have increased. Meat, milk products, egg, skin are main supplementary
income in the rural economy. Apart from the production of Milk and Meat, the
Cattle in the District are used as drought power in Agriculture and it is an allied
activity to Agriculture.
Rakamcherla IP - EIA Description of Environment
101
3.12.1.9 Health
There are no serious/contagious diseases found in the district. Polio and Leprosy
have been completely eradicated. The district has good health facilities. They
avail good health facilities as Hyderabad is close to the district.
Some of the health indicators of the district are as follows:
The Crude birth rate (year 2013) is 17.9,
Crude death rate is 7,
The infant Mortality rate (IMR-2013) is 33,
Maternal Mortality rate is 78 (2013 per 100000 live births)
Table 3.8 Health facilities in the district
S.No Health facility Nos.
1 No. of P.H.C.s (Rural) 52
2 No. of Sub-Centers 399
3 No of Area hospitals 4
4 No of CHC’s 9
3 No of district hospitals 1(Source: National Health Mission)
3.12.1.10 Animal Husbandry
The district has good livestock resources. The Livestock play a vital role in
sustaining Socio-economic life of people providing additional livelihood means to
a large number of small and marginal farmers. Many women and old people have
involved in rearing and maintaining of cattle and ruminants. Back yard poultry is
commonly prevalent in the rural areas. The buffaloes, sheep and the poultry
population have increased. Meat, milk products, egg, skin are main supplementary
income in the rural economy. Apart from the production of Milk and Meat, the
Cattle in the District are used as drought power in Agriculture and it is an allied
activity to Agriculture.
Rakamcherla IP - EIA Description of Environment
102
Table 3.9 Livestock population in the district
Sl.No Item 1999 2003 2007 2012
1 Cattle 3,16,915 3,04,592 3,03,053 3,20,253
2 Buffaloes 3,16,915 2,72,342 2,67,591 2,71,364
3 Goats 2,42,501 3,18,646 3,86,874 4,29,391
4 Sheep 2,41,471 6,46,920 6,03,512 6,62,217
5 Others 92,143 74656 1,07,659 1,18,992
6 TotalLivestock (allcategories)
10,94,552 16,17,156 16,68,689 16,83,290
7 Poultry 95,27,246 1,18,76,380 1,40,99,276 1,51,14,027
(Source: District Hand Book, Vikarabad District and Livestock Census 2012)
3.12.2 Economy of the District
The District is bounded on the North by Medak District, East by Nalgonda
District, South by Mahaboobnagar District, West by Gulbarga District & North
West of Bidar District of Karnataka State. It covers an area of 7564.88 Sq. Kms.
The district has three Revenue divisions, 12 Agricultural Sub-divisions, with 37
Mandals and 1055 villages.
3.12.3 Industries
The Vikarabad District is playing an important role in the development of
industries in the State because of its proximity to Hyderabad City. The District is
in more advantageous position for setting up of industries as the location is nearer
to the market and also the easy availability of required technical man-power. This
District has a strong industrial base with public sector undertakings like BHEL
(R&D), ECIL, IDPL, HCL, HAL, HMT Bearings and NFC etc.
3.12.3.1 Major Industries in Rangareddy District
Amoda Publication Pvt Ltd
Kl-hitch Secure Print Ltd
Bharathi Brahma Seeds
ICI India Limited
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102
Table 3.9 Livestock population in the district
Sl.No Item 1999 2003 2007 2012
1 Cattle 3,16,915 3,04,592 3,03,053 3,20,253
2 Buffaloes 3,16,915 2,72,342 2,67,591 2,71,364
3 Goats 2,42,501 3,18,646 3,86,874 4,29,391
4 Sheep 2,41,471 6,46,920 6,03,512 6,62,217
5 Others 92,143 74656 1,07,659 1,18,992
6 TotalLivestock (allcategories)
10,94,552 16,17,156 16,68,689 16,83,290
7 Poultry 95,27,246 1,18,76,380 1,40,99,276 1,51,14,027
(Source: District Hand Book, Vikarabad District and Livestock Census 2012)
3.12.2 Economy of the District
The District is bounded on the North by Medak District, East by Nalgonda
District, South by Mahaboobnagar District, West by Gulbarga District & North
West of Bidar District of Karnataka State. It covers an area of 7564.88 Sq. Kms.
The district has three Revenue divisions, 12 Agricultural Sub-divisions, with 37
Mandals and 1055 villages.
3.12.3 Industries
The Vikarabad District is playing an important role in the development of
industries in the State because of its proximity to Hyderabad City. The District is
in more advantageous position for setting up of industries as the location is nearer
to the market and also the easy availability of required technical man-power. This
District has a strong industrial base with public sector undertakings like BHEL
(R&D), ECIL, IDPL, HCL, HAL, HMT Bearings and NFC etc.
3.12.3.1 Major Industries in Rangareddy District
Amoda Publication Pvt Ltd
Kl-hitch Secure Print Ltd
Bharathi Brahma Seeds
ICI India Limited
Rakamcherla IP - EIA Description of Environment
102
Table 3.9 Livestock population in the district
Sl.No Item 1999 2003 2007 2012
1 Cattle 3,16,915 3,04,592 3,03,053 3,20,253
2 Buffaloes 3,16,915 2,72,342 2,67,591 2,71,364
3 Goats 2,42,501 3,18,646 3,86,874 4,29,391
4 Sheep 2,41,471 6,46,920 6,03,512 6,62,217
5 Others 92,143 74656 1,07,659 1,18,992
6 TotalLivestock (allcategories)
10,94,552 16,17,156 16,68,689 16,83,290
7 Poultry 95,27,246 1,18,76,380 1,40,99,276 1,51,14,027
(Source: District Hand Book, Vikarabad District and Livestock Census 2012)
3.12.2 Economy of the District
The District is bounded on the North by Medak District, East by Nalgonda
District, South by Mahaboobnagar District, West by Gulbarga District & North
West of Bidar District of Karnataka State. It covers an area of 7564.88 Sq. Kms.
The district has three Revenue divisions, 12 Agricultural Sub-divisions, with 37
Mandals and 1055 villages.
3.12.3 Industries
The Vikarabad District is playing an important role in the development of
industries in the State because of its proximity to Hyderabad City. The District is
in more advantageous position for setting up of industries as the location is nearer
to the market and also the easy availability of required technical man-power. This
District has a strong industrial base with public sector undertakings like BHEL
(R&D), ECIL, IDPL, HCL, HAL, HMT Bearings and NFC etc.
3.12.3.1 Major Industries in Rangareddy District
Amoda Publication Pvt Ltd
Kl-hitch Secure Print Ltd
Bharathi Brahma Seeds
ICI India Limited
Rakamcherla IP - EIA Description of Environment
103
Shrinath Roto Pack Pvt Ltd
Bhagyanagar India Limited
Ramcharan Oil Industries
Shathi Metadooe Ltd
Surana Telecome
Rana Eng Value
3.12.3.2 Small Scale Industries in the Pudur mandal
Cement Hollow Bricks & other products
Flour Mill
Turmeric & Chillies grinding
Clay Bricks
Cattle & Poultry Feed
3.12.4 Social Survey – Interaction with People
During the process of analyzing the socio-economic environment across the
project area, interactions were done with the common men and key person in and
around the area to know better about the development and societal standards of
the district. Some of them are given below:
3.12.4.1 Manneguda
Interacted with Mrs. Maramma, Housewife & labor;
Outcome:
Primary Schools are available.
Urdu and Telugu medium schools.
For higher classes to go to Vikarabad.
No problem for drinking water.
Girls students pursuing higher education.
Women involved in many income generation jobs.
Rakamcherla IP - EIA Description of Environment
103
Shrinath Roto Pack Pvt Ltd
Bhagyanagar India Limited
Ramcharan Oil Industries
Shathi Metadooe Ltd
Surana Telecome
Rana Eng Value
3.12.3.2 Small Scale Industries in the Pudur mandal
Cement Hollow Bricks & other products
Flour Mill
Turmeric & Chillies grinding
Clay Bricks
Cattle & Poultry Feed
3.12.4 Social Survey – Interaction with People
During the process of analyzing the socio-economic environment across the
project area, interactions were done with the common men and key person in and
around the area to know better about the development and societal standards of
the district. Some of them are given below:
3.12.4.1 Manneguda
Interacted with Mrs. Maramma, Housewife & labor;
Outcome:
Primary Schools are available.
Urdu and Telugu medium schools.
For higher classes to go to Vikarabad.
No problem for drinking water.
Girls students pursuing higher education.
Women involved in many income generation jobs.
Rakamcherla IP - EIA Description of Environment
103
Shrinath Roto Pack Pvt Ltd
Bhagyanagar India Limited
Ramcharan Oil Industries
Shathi Metadooe Ltd
Surana Telecome
Rana Eng Value
3.12.3.2 Small Scale Industries in the Pudur mandal
Cement Hollow Bricks & other products
Flour Mill
Turmeric & Chillies grinding
Clay Bricks
Cattle & Poultry Feed
3.12.4 Social Survey – Interaction with People
During the process of analyzing the socio-economic environment across the
project area, interactions were done with the common men and key person in and
around the area to know better about the development and societal standards of
the district. Some of them are given below:
3.12.4.1 Manneguda
Interacted with Mrs. Maramma, Housewife & labor;
Outcome:
Primary Schools are available.
Urdu and Telugu medium schools.
For higher classes to go to Vikarabad.
No problem for drinking water.
Girls students pursuing higher education.
Women involved in many income generation jobs.
Rakamcherla IP - EIA Description of Environment
104
3.12.4.2 Enkepalle
Interacted with Mr.Chotta Khan, labour;
Outcome:
Agriculture is main income.
Transport facility is available.
Employed in local match box industry. It has hundreds of local employees.
The non- agricultural labour salary is 200/- for male and 150/- for female.
3.12.4.3 Kottapalli
Interacted with Mr. Mohamad Faid;
Outcome:
Shivasagar lake situated in the area.
It provides drinking water for Vikarabad town.
The tank will overflow during rainy season.
Fishing activity in the lake by locals and neighboring villages. Fishing is open
to all not tendered by the municipal body.
Scope for aggressive fishing by intervention of authorities, it fetch income to
municipalities and locals.
3.12.4.4 Vikarabad
Interacted with Students in Technical training & Development Centre;
Outcome:
There are about 250 students are studying in the institute.
This co-education institution has Civil and EEE courses.
Being a Govt. Polytechnic, the fees are very meager and it is very beneficial to
the rural deprived communities.
No hostel and in-house facility is available. New building is being constructed
for the same in the nearby area.
Faculty and play services are available
Rakamcherla IP - EIA Description of Environment
104
3.12.4.2 Enkepalle
Interacted with Mr.Chotta Khan, labour;
Outcome:
Agriculture is main income.
Transport facility is available.
Employed in local match box industry. It has hundreds of local employees.
The non- agricultural labour salary is 200/- for male and 150/- for female.
3.12.4.3 Kottapalli
Interacted with Mr. Mohamad Faid;
Outcome:
Shivasagar lake situated in the area.
It provides drinking water for Vikarabad town.
The tank will overflow during rainy season.
Fishing activity in the lake by locals and neighboring villages. Fishing is open
to all not tendered by the municipal body.
Scope for aggressive fishing by intervention of authorities, it fetch income to
municipalities and locals.
3.12.4.4 Vikarabad
Interacted with Students in Technical training & Development Centre;
Outcome:
There are about 250 students are studying in the institute.
This co-education institution has Civil and EEE courses.
Being a Govt. Polytechnic, the fees are very meager and it is very beneficial to
the rural deprived communities.
No hostel and in-house facility is available. New building is being constructed
for the same in the nearby area.
Faculty and play services are available
Rakamcherla IP - EIA Description of Environment
104
3.12.4.2 Enkepalle
Interacted with Mr.Chotta Khan, labour;
Outcome:
Agriculture is main income.
Transport facility is available.
Employed in local match box industry. It has hundreds of local employees.
The non- agricultural labour salary is 200/- for male and 150/- for female.
3.12.4.3 Kottapalli
Interacted with Mr. Mohamad Faid;
Outcome:
Shivasagar lake situated in the area.
It provides drinking water for Vikarabad town.
The tank will overflow during rainy season.
Fishing activity in the lake by locals and neighboring villages. Fishing is open
to all not tendered by the municipal body.
Scope for aggressive fishing by intervention of authorities, it fetch income to
municipalities and locals.
3.12.4.4 Vikarabad
Interacted with Students in Technical training & Development Centre;
Outcome:
There are about 250 students are studying in the institute.
This co-education institution has Civil and EEE courses.
Being a Govt. Polytechnic, the fees are very meager and it is very beneficial to
the rural deprived communities.
No hostel and in-house facility is available. New building is being constructed
for the same in the nearby area.
Faculty and play services are available
Rakamcherla IP - EIA Description of Environment
105
Students are very hopeful of getting jobs after completion of the course. Very
few option for higher education.
No college bus for the rural students, they have to depend on local facilities.
3.12.4.5 Rukumpalli
Interacted with Ms. Vijiamma, School teacher;
Outcome:
Primary schools consist of 2 teachers with 80 students. Anganwadi is attached
Toilet facilities are not available.
The road for the village to the main road (Vikarabad to Pargi) is in good
condition.
The water facilities are available through the bore well.
The village peoples depend on agriculture only.
3.12.4.6 Rakamcherla
Interacted with Mr. Raju, Sarpanch, Gram Panchayat;
Outcome:
Village mainly consists of Hindus and Muslims.
The main occupation of the village is agriculture. Cotton, Maize, Vegetables,
Mango are main crops. Bore well is the main source of irrigation. The area is
rain fed. The modern agriculture implements are widely used. There are 5
tractors available for agriculture and transport purposes.
There is a primary school in the village. For high schools, they need to go
Somangurthy (3km) or Pudur (3km). Girls are being sent to schools
compulsorily and their drop-out rate is very low.
The village lies on the Manneguda-Pargi main road. Buses and Share autos
are main transport facilities.
There are no huts visible. The roofs of the houses are made of stone slab
which is called Tandur Stone. Tandur is a town, which 45 km from the area
where the stones are mined.
Rakamcherla IP - EIA Description of Environment
105
Students are very hopeful of getting jobs after completion of the course. Very
few option for higher education.
No college bus for the rural students, they have to depend on local facilities.
3.12.4.5 Rukumpalli
Interacted with Ms. Vijiamma, School teacher;
Outcome:
Primary schools consist of 2 teachers with 80 students. Anganwadi is attached
Toilet facilities are not available.
The road for the village to the main road (Vikarabad to Pargi) is in good
condition.
The water facilities are available through the bore well.
The village peoples depend on agriculture only.
3.12.4.6 Rakamcherla
Interacted with Mr. Raju, Sarpanch, Gram Panchayat;
Outcome:
Village mainly consists of Hindus and Muslims.
The main occupation of the village is agriculture. Cotton, Maize, Vegetables,
Mango are main crops. Bore well is the main source of irrigation. The area is
rain fed. The modern agriculture implements are widely used. There are 5
tractors available for agriculture and transport purposes.
There is a primary school in the village. For high schools, they need to go
Somangurthy (3km) or Pudur (3km). Girls are being sent to schools
compulsorily and their drop-out rate is very low.
The village lies on the Manneguda-Pargi main road. Buses and Share autos
are main transport facilities.
There are no huts visible. The roofs of the houses are made of stone slab
which is called Tandur Stone. Tandur is a town, which 45 km from the area
where the stones are mined.
Rakamcherla IP - EIA Description of Environment
105
Students are very hopeful of getting jobs after completion of the course. Very
few option for higher education.
No college bus for the rural students, they have to depend on local facilities.
3.12.4.5 Rukumpalli
Interacted with Ms. Vijiamma, School teacher;
Outcome:
Primary schools consist of 2 teachers with 80 students. Anganwadi is attached
Toilet facilities are not available.
The road for the village to the main road (Vikarabad to Pargi) is in good
condition.
The water facilities are available through the bore well.
The village peoples depend on agriculture only.
3.12.4.6 Rakamcherla
Interacted with Mr. Raju, Sarpanch, Gram Panchayat;
Outcome:
Village mainly consists of Hindus and Muslims.
The main occupation of the village is agriculture. Cotton, Maize, Vegetables,
Mango are main crops. Bore well is the main source of irrigation. The area is
rain fed. The modern agriculture implements are widely used. There are 5
tractors available for agriculture and transport purposes.
There is a primary school in the village. For high schools, they need to go
Somangurthy (3km) or Pudur (3km). Girls are being sent to schools
compulsorily and their drop-out rate is very low.
The village lies on the Manneguda-Pargi main road. Buses and Share autos
are main transport facilities.
There are no huts visible. The roofs of the houses are made of stone slab
which is called Tandur Stone. Tandur is a town, which 45 km from the area
where the stones are mined.
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Both pipeline and bore pumps are the source of drinking water. The water is
neither treated nor chlorinated.
Firewood (Chula) is the main fuel for their cooking and other commercial
purposes.
Cows and Buffalos rearing for their livelihood. The grazing land is available
for their feed.
The Laxmi Narasihma Temple of this village attracts hundreds of devotees
from the surrounding villages. The five days Jatra is being celebrated with
pomp and shows for the Lord’s gracious blessing. All kind of festivals like
Deepawali, Dasara and Sankaranthi, etc., are celebrated across all
communities.
The MGNREGA (Mahatma Gandhi National Rural Employment Guarantee
Act) is being implemented with development tasks. The labors for agriculture
is easily available locally, some harvesting season, they brought from the
neighboring villages.
They get health facilities from nearby towns like Pargi (10 km), Pudur (5km),
Vikarabad (12km).
There is no dreaded or communicable disease in the village. Vaccination is
being done regularly. The eye care and dental care camps are being held every
Thursday at Pudur. The people aware of the ambulance service and 104. The
health check up for infants and pregnant women’s are regularly conducted at
Anganwadi centre.
There is no bank facility in the village. The nearby Bank is State Bank of
Hyderabad at Pudur (3km).
The schedule tribe Lambadi is predominant in this area. They have a separate
settlement (Thanda) in the nearby village Tirumalapur.
There are 4 grocery shops and 2 eateries. There is no medical shop in the
village.
There are 36 Self Help Groups operating in the village. The financial
opportunity due to the SHG is being used for petty business, agriculture
purpose etc.
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Both pipeline and bore pumps are the source of drinking water. The water is
neither treated nor chlorinated.
Firewood (Chula) is the main fuel for their cooking and other commercial
purposes.
Cows and Buffalos rearing for their livelihood. The grazing land is available
for their feed.
The Laxmi Narasihma Temple of this village attracts hundreds of devotees
from the surrounding villages. The five days Jatra is being celebrated with
pomp and shows for the Lord’s gracious blessing. All kind of festivals like
Deepawali, Dasara and Sankaranthi, etc., are celebrated across all
communities.
The MGNREGA (Mahatma Gandhi National Rural Employment Guarantee
Act) is being implemented with development tasks. The labors for agriculture
is easily available locally, some harvesting season, they brought from the
neighboring villages.
They get health facilities from nearby towns like Pargi (10 km), Pudur (5km),
Vikarabad (12km).
There is no dreaded or communicable disease in the village. Vaccination is
being done regularly. The eye care and dental care camps are being held every
Thursday at Pudur. The people aware of the ambulance service and 104. The
health check up for infants and pregnant women’s are regularly conducted at
Anganwadi centre.
There is no bank facility in the village. The nearby Bank is State Bank of
Hyderabad at Pudur (3km).
The schedule tribe Lambadi is predominant in this area. They have a separate
settlement (Thanda) in the nearby village Tirumalapur.
There are 4 grocery shops and 2 eateries. There is no medical shop in the
village.
There are 36 Self Help Groups operating in the village. The financial
opportunity due to the SHG is being used for petty business, agriculture
purpose etc.
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Both pipeline and bore pumps are the source of drinking water. The water is
neither treated nor chlorinated.
Firewood (Chula) is the main fuel for their cooking and other commercial
purposes.
Cows and Buffalos rearing for their livelihood. The grazing land is available
for their feed.
The Laxmi Narasihma Temple of this village attracts hundreds of devotees
from the surrounding villages. The five days Jatra is being celebrated with
pomp and shows for the Lord’s gracious blessing. All kind of festivals like
Deepawali, Dasara and Sankaranthi, etc., are celebrated across all
communities.
The MGNREGA (Mahatma Gandhi National Rural Employment Guarantee
Act) is being implemented with development tasks. The labors for agriculture
is easily available locally, some harvesting season, they brought from the
neighboring villages.
They get health facilities from nearby towns like Pargi (10 km), Pudur (5km),
Vikarabad (12km).
There is no dreaded or communicable disease in the village. Vaccination is
being done regularly. The eye care and dental care camps are being held every
Thursday at Pudur. The people aware of the ambulance service and 104. The
health check up for infants and pregnant women’s are regularly conducted at
Anganwadi centre.
There is no bank facility in the village. The nearby Bank is State Bank of
Hyderabad at Pudur (3km).
The schedule tribe Lambadi is predominant in this area. They have a separate
settlement (Thanda) in the nearby village Tirumalapur.
There are 4 grocery shops and 2 eateries. There is no medical shop in the
village.
There are 36 Self Help Groups operating in the village. The financial
opportunity due to the SHG is being used for petty business, agriculture
purpose etc.
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3.12.4.7 Kangal Village
Interacted with Mr.Anwar, Sarpanch;
Outcome:
The village has population of 7000 people and 700 households.
The main livelihood is dependent on agriculture and allied activities. The
agriculture labors easily available and mechanization of agriculture is
balancing the labour demand. There are about 30 tractors in the village.
Bullock carts are being used in large number for local transportation.
There is a High School in the village.
The main transportation is buses and share autos.
The nearest hospital is at Pargi at 12 km.
The average earning of the people is Rs.3000/-
Maize, Cotton, vegetables are main crops of the area. The agriculture produce
is being sent to Pargi and Vikarabad market. Cotton sold through the local
agent and sent to the wholesaler.
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3.12.4.7 Kangal Village
Interacted with Mr.Anwar, Sarpanch;
Outcome:
The village has population of 7000 people and 700 households.
The main livelihood is dependent on agriculture and allied activities. The
agriculture labors easily available and mechanization of agriculture is
balancing the labour demand. There are about 30 tractors in the village.
Bullock carts are being used in large number for local transportation.
There is a High School in the village.
The main transportation is buses and share autos.
The nearest hospital is at Pargi at 12 km.
The average earning of the people is Rs.3000/-
Maize, Cotton, vegetables are main crops of the area. The agriculture produce
is being sent to Pargi and Vikarabad market. Cotton sold through the local
agent and sent to the wholesaler.
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3.12.4.7 Kangal Village
Interacted with Mr.Anwar, Sarpanch;
Outcome:
The village has population of 7000 people and 700 households.
The main livelihood is dependent on agriculture and allied activities. The
agriculture labors easily available and mechanization of agriculture is
balancing the labour demand. There are about 30 tractors in the village.
Bullock carts are being used in large number for local transportation.
There is a High School in the village.
The main transportation is buses and share autos.
The nearest hospital is at Pargi at 12 km.
The average earning of the people is Rs.3000/-
Maize, Cotton, vegetables are main crops of the area. The agriculture produce
is being sent to Pargi and Vikarabad market. Cotton sold through the local
agent and sent to the wholesaler.
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Figure 3. 10 Amenities available in study area
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Figure 3. 10 Amenities available in study area
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Figure 3. 10 Amenities available in study area
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Figure 3. 11 Living Culture of People in the study area
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Figure 3. 11 Living Culture of People in the study area
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Figure 3. 11 Living Culture of People in the study area
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Figure 3.9 Interaction with people on Socio - economic aspects
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Figure 3.9 Interaction with people on Socio - economic aspects
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Figure 3.9 Interaction with people on Socio - economic aspects
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3.12.5 Outcome of Socio Economic Survey
Most of workers depend on agriculture and agriculture related
activities. Agriculture is the principal occupation of the overwhelming
majority of villages. Most of the land is concentrated in the hands of
small, marginal farmers. These are the poor and marginal farmers with
land holdings around one acres (2.5 Acres), who often have fragmented
land holdings. The fragmentation is due to inheritance.
They expressed their inabilities in farming due to the less extent of
land. Their major hurdles are borrowing, selection of crops, marketing,
input cost, smaller return on farming, up gradation of technology,
electricity grid, scarcity of water sources etc.
Women participation in income generation is visible. In general,
women are involved in multiple tasks that include household chores
apart from income generating activities whereas men were exclusively
involved in income generating activities. Traditionally, rural women
have worked alongside their husbands in fields, household activities,
collection of firewood, cattle rearing and management, collection of
fodder and other tradable products.
Skill development programme is required as there are more educated
youth and upcoming industries in the area.
Both the landless poor as well as small and marginal farmers take
livelihood to local labour opportunities.
Local people may be engaged in the industries after developing the
required skills, through skill development programmes. Thus, the
migration of locals will be minimized.
People need more agro based industries in this area.
The transportation facilities in the rural areas are not well developed.
The upcoming industries should contribute to the development of this
area in the field of education, health, infrastructure, training
programmes etc., The industries should undertake more Corporate
Social Responsibility (CSR) activities.
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3.12.5 Outcome of Socio Economic Survey
Most of workers depend on agriculture and agriculture related
activities. Agriculture is the principal occupation of the overwhelming
majority of villages. Most of the land is concentrated in the hands of
small, marginal farmers. These are the poor and marginal farmers with
land holdings around one acres (2.5 Acres), who often have fragmented
land holdings. The fragmentation is due to inheritance.
They expressed their inabilities in farming due to the less extent of
land. Their major hurdles are borrowing, selection of crops, marketing,
input cost, smaller return on farming, up gradation of technology,
electricity grid, scarcity of water sources etc.
Women participation in income generation is visible. In general,
women are involved in multiple tasks that include household chores
apart from income generating activities whereas men were exclusively
involved in income generating activities. Traditionally, rural women
have worked alongside their husbands in fields, household activities,
collection of firewood, cattle rearing and management, collection of
fodder and other tradable products.
Skill development programme is required as there are more educated
youth and upcoming industries in the area.
Both the landless poor as well as small and marginal farmers take
livelihood to local labour opportunities.
Local people may be engaged in the industries after developing the
required skills, through skill development programmes. Thus, the
migration of locals will be minimized.
People need more agro based industries in this area.
The transportation facilities in the rural areas are not well developed.
The upcoming industries should contribute to the development of this
area in the field of education, health, infrastructure, training
programmes etc., The industries should undertake more Corporate
Social Responsibility (CSR) activities.
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3.12.5 Outcome of Socio Economic Survey
Most of workers depend on agriculture and agriculture related
activities. Agriculture is the principal occupation of the overwhelming
majority of villages. Most of the land is concentrated in the hands of
small, marginal farmers. These are the poor and marginal farmers with
land holdings around one acres (2.5 Acres), who often have fragmented
land holdings. The fragmentation is due to inheritance.
They expressed their inabilities in farming due to the less extent of
land. Their major hurdles are borrowing, selection of crops, marketing,
input cost, smaller return on farming, up gradation of technology,
electricity grid, scarcity of water sources etc.
Women participation in income generation is visible. In general,
women are involved in multiple tasks that include household chores
apart from income generating activities whereas men were exclusively
involved in income generating activities. Traditionally, rural women
have worked alongside their husbands in fields, household activities,
collection of firewood, cattle rearing and management, collection of
fodder and other tradable products.
Skill development programme is required as there are more educated
youth and upcoming industries in the area.
Both the landless poor as well as small and marginal farmers take
livelihood to local labour opportunities.
Local people may be engaged in the industries after developing the
required skills, through skill development programmes. Thus, the
migration of locals will be minimized.
People need more agro based industries in this area.
The transportation facilities in the rural areas are not well developed.
The upcoming industries should contribute to the development of this
area in the field of education, health, infrastructure, training
programmes etc., The industries should undertake more Corporate
Social Responsibility (CSR) activities.
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There is a remarkable development in women’s education.
Livestock has an important role in the livelihood of rural households.
The types of livestock include dairy animals (cows and buffaloes),
draught animals (bullocks), other cattle for meat, small ruminants
(sheep and goats) and chicken. The crop-livestock interactions are
complementary in nature.
Common property resources are considered as a form of natural and
social capital. These act as a source of fuel and fodder for the rural poor
in many cases.
Even though agriculture was an important occupation, the majority of
farmers were supplementing their livelihoods through other activities.
They also hired labor. A larger percentage of household members
combined on-farm activities with one or more income generating
activities to sustain the household needs and to overcome the drought
conditions of the previous cropping season.
Horticulture over the years has emerged as an indispensable part of
agriculture, providing financial opportunities for rural farmers.
The cattle farmers prefer rearing buffaloes to cows. This is because
buffaloes adapt better to climate changes, they are more disease
resistant and buffalo milk has more market value due to its higher fat
content.
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There is a remarkable development in women’s education.
Livestock has an important role in the livelihood of rural households.
The types of livestock include dairy animals (cows and buffaloes),
draught animals (bullocks), other cattle for meat, small ruminants
(sheep and goats) and chicken. The crop-livestock interactions are
complementary in nature.
Common property resources are considered as a form of natural and
social capital. These act as a source of fuel and fodder for the rural poor
in many cases.
Even though agriculture was an important occupation, the majority of
farmers were supplementing their livelihoods through other activities.
They also hired labor. A larger percentage of household members
combined on-farm activities with one or more income generating
activities to sustain the household needs and to overcome the drought
conditions of the previous cropping season.
Horticulture over the years has emerged as an indispensable part of
agriculture, providing financial opportunities for rural farmers.
The cattle farmers prefer rearing buffaloes to cows. This is because
buffaloes adapt better to climate changes, they are more disease
resistant and buffalo milk has more market value due to its higher fat
content.
Rakamcherla IP - EIA Description of Environment
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There is a remarkable development in women’s education.
Livestock has an important role in the livelihood of rural households.
The types of livestock include dairy animals (cows and buffaloes),
draught animals (bullocks), other cattle for meat, small ruminants
(sheep and goats) and chicken. The crop-livestock interactions are
complementary in nature.
Common property resources are considered as a form of natural and
social capital. These act as a source of fuel and fodder for the rural poor
in many cases.
Even though agriculture was an important occupation, the majority of
farmers were supplementing their livelihoods through other activities.
They also hired labor. A larger percentage of household members
combined on-farm activities with one or more income generating
activities to sustain the household needs and to overcome the drought
conditions of the previous cropping season.
Horticulture over the years has emerged as an indispensable part of
agriculture, providing financial opportunities for rural farmers.
The cattle farmers prefer rearing buffaloes to cows. This is because
buffaloes adapt better to climate changes, they are more disease
resistant and buffalo milk has more market value due to its higher fat
content.
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Chapter 4
Anticipated Environmental Impacts
& Mitigation Measures
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
113
Chapter 4
Anticipated Environmental Impacts
& Mitigation Measures
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113
Chapter 4
Anticipated Environmental Impacts
& Mitigation Measures
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114
4 Anticipated Environmental Impacts & Mitigation
Measures
4.1 Impact Identification and Evaluation
Once identified, anticipated impacts are analyzed and evaluated based on available
information. The method used for evaluating the overall importance of impacts is based
on four fundamental criteria:
a. Nature (positive or negative, and direct or indirect);
b. Duration (temporary or permanent);
c. Area extent (regional, local, or isolated); and
d. Intensity (low, moderate, or high).
These criteria enable the determination of the overall importance or significance (low,
moderate, or strong negative/positive) of each impact identified. Even if a particular
evaluation is merely based on a value judgment rather than quantitative data that is not
available, the methodology enables the establishment of acceptable levels and defines
necessary mitigation and monitoring measures to minimize or eliminate impacts.
4.1.1 Nature of Impact
The nature of the impact can be described as positive or negative. Positive impacts
enhance the quality or facilitate access to baseline socioeconomic and environmental
elements as described in the above chapter, while negative impacts degrade their
quality or limit access. Impacts are also described as direct or indirect. A direct
impact appears as an immediate result of a project activity, such as the damage to
vegetation caused by the development of project land. An indirect impact arises from
a project activity at the secondary level, such as the enhanced opportunities for
economic development enabled by the project.
4.1.2 Duration of Impact
The duration of an impact can be temporary or permanent. Careful attention has been
made to distinguish between the duration and the source of the impact. For example,
a source of impact of short duration (such as turbidity of river water caused by storm
runoff from the construction site during construction) can exert an impact of
permanent duration on the downstream environment (sedimentation of the riverbed).
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4 Anticipated Environmental Impacts & Mitigation
Measures
4.1 Impact Identification and Evaluation
Once identified, anticipated impacts are analyzed and evaluated based on available
information. The method used for evaluating the overall importance of impacts is based
on four fundamental criteria:
a. Nature (positive or negative, and direct or indirect);
b. Duration (temporary or permanent);
c. Area extent (regional, local, or isolated); and
d. Intensity (low, moderate, or high).
These criteria enable the determination of the overall importance or significance (low,
moderate, or strong negative/positive) of each impact identified. Even if a particular
evaluation is merely based on a value judgment rather than quantitative data that is not
available, the methodology enables the establishment of acceptable levels and defines
necessary mitigation and monitoring measures to minimize or eliminate impacts.
4.1.1 Nature of Impact
The nature of the impact can be described as positive or negative. Positive impacts
enhance the quality or facilitate access to baseline socioeconomic and environmental
elements as described in the above chapter, while negative impacts degrade their
quality or limit access. Impacts are also described as direct or indirect. A direct
impact appears as an immediate result of a project activity, such as the damage to
vegetation caused by the development of project land. An indirect impact arises from
a project activity at the secondary level, such as the enhanced opportunities for
economic development enabled by the project.
4.1.2 Duration of Impact
The duration of an impact can be temporary or permanent. Careful attention has been
made to distinguish between the duration and the source of the impact. For example,
a source of impact of short duration (such as turbidity of river water caused by storm
runoff from the construction site during construction) can exert an impact of
permanent duration on the downstream environment (sedimentation of the riverbed).
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114
4 Anticipated Environmental Impacts & Mitigation
Measures
4.1 Impact Identification and Evaluation
Once identified, anticipated impacts are analyzed and evaluated based on available
information. The method used for evaluating the overall importance of impacts is based
on four fundamental criteria:
a. Nature (positive or negative, and direct or indirect);
b. Duration (temporary or permanent);
c. Area extent (regional, local, or isolated); and
d. Intensity (low, moderate, or high).
These criteria enable the determination of the overall importance or significance (low,
moderate, or strong negative/positive) of each impact identified. Even if a particular
evaluation is merely based on a value judgment rather than quantitative data that is not
available, the methodology enables the establishment of acceptable levels and defines
necessary mitigation and monitoring measures to minimize or eliminate impacts.
4.1.1 Nature of Impact
The nature of the impact can be described as positive or negative. Positive impacts
enhance the quality or facilitate access to baseline socioeconomic and environmental
elements as described in the above chapter, while negative impacts degrade their
quality or limit access. Impacts are also described as direct or indirect. A direct
impact appears as an immediate result of a project activity, such as the damage to
vegetation caused by the development of project land. An indirect impact arises from
a project activity at the secondary level, such as the enhanced opportunities for
economic development enabled by the project.
4.1.2 Duration of Impact
The duration of an impact can be temporary or permanent. Careful attention has been
made to distinguish between the duration and the source of the impact. For example,
a source of impact of short duration (such as turbidity of river water caused by storm
runoff from the construction site during construction) can exert an impact of
permanent duration on the downstream environment (sedimentation of the riverbed).
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The presence and operation of the infrastructure works generally impose impacts of
permanent duration.
The duration of impact can be classified as below:
Construction Phase: 2 – 3 years
The immediate community for the radius of 5 km will be affected. However theimpact will be mainly as below:
a. Traffic Impacts:
Caused by vehicular movements of men, materials and machineries.
b. Air quality impacts:
Due to construction activities viz. dust and particulates
c. Water Quality impacts:
Due to runoff during rainy time of construction materials.
Sewage generation and its disposal in septic tank.
d. Noise Quality impacts:
Caused by vehicular movements of men, materials and machineries.
4.1.3 Aerial Extent of Impact
The aerial extent of an impact refers to its area of influence and can be regional,
local, or isolated to a particularly small and well defined area. An impact of regional
extent exerts an influence far beyond the surroundings of the project area. The local
area of influence refers to the communities of the North and South west affected by
the project. And lastly, an isolated impact is limited in extent to a small, readily
defined area or experienced by a small number of individuals.
4.1.4 Intensity of Impact
The intensity of an impact concerns the scale or size of the impact on socioeconomic
and environmental elements such as the productivity of natural habitat, a community,
or the utilization of resources. Intensity is evaluated as low, moderate or high.
Impacts are evaluated as a function of how they affect the overall integrity of
elements and their vulnerability to degradation or loss in value.
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The presence and operation of the infrastructure works generally impose impacts of
permanent duration.
The duration of impact can be classified as below:
Construction Phase: 2 – 3 years
The immediate community for the radius of 5 km will be affected. However theimpact will be mainly as below:
a. Traffic Impacts:
Caused by vehicular movements of men, materials and machineries.
b. Air quality impacts:
Due to construction activities viz. dust and particulates
c. Water Quality impacts:
Due to runoff during rainy time of construction materials.
Sewage generation and its disposal in septic tank.
d. Noise Quality impacts:
Caused by vehicular movements of men, materials and machineries.
4.1.3 Aerial Extent of Impact
The aerial extent of an impact refers to its area of influence and can be regional,
local, or isolated to a particularly small and well defined area. An impact of regional
extent exerts an influence far beyond the surroundings of the project area. The local
area of influence refers to the communities of the North and South west affected by
the project. And lastly, an isolated impact is limited in extent to a small, readily
defined area or experienced by a small number of individuals.
4.1.4 Intensity of Impact
The intensity of an impact concerns the scale or size of the impact on socioeconomic
and environmental elements such as the productivity of natural habitat, a community,
or the utilization of resources. Intensity is evaluated as low, moderate or high.
Impacts are evaluated as a function of how they affect the overall integrity of
elements and their vulnerability to degradation or loss in value.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
115
The presence and operation of the infrastructure works generally impose impacts of
permanent duration.
The duration of impact can be classified as below:
Construction Phase: 2 – 3 years
The immediate community for the radius of 5 km will be affected. However theimpact will be mainly as below:
a. Traffic Impacts:
Caused by vehicular movements of men, materials and machineries.
b. Air quality impacts:
Due to construction activities viz. dust and particulates
c. Water Quality impacts:
Due to runoff during rainy time of construction materials.
Sewage generation and its disposal in septic tank.
d. Noise Quality impacts:
Caused by vehicular movements of men, materials and machineries.
4.1.3 Aerial Extent of Impact
The aerial extent of an impact refers to its area of influence and can be regional,
local, or isolated to a particularly small and well defined area. An impact of regional
extent exerts an influence far beyond the surroundings of the project area. The local
area of influence refers to the communities of the North and South west affected by
the project. And lastly, an isolated impact is limited in extent to a small, readily
defined area or experienced by a small number of individuals.
4.1.4 Intensity of Impact
The intensity of an impact concerns the scale or size of the impact on socioeconomic
and environmental elements such as the productivity of natural habitat, a community,
or the utilization of resources. Intensity is evaluated as low, moderate or high.
Impacts are evaluated as a function of how they affect the overall integrity of
elements and their vulnerability to degradation or loss in value.
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4.2 Impacts due to Development of Industrial Park
4.2.1 Construction Phase
The potential impacts from the activities are considered for planning of mitigation
measures to reduce the impacts to negligible extend of significance.
4.2.1.1 Land Acquisition and Site Preparation
The site preparation and construction will not generate any major negative
impacts on the regional environmental conditions. In addition, the impacts on
the regional aspects like population affected, land and allied abiotic & biotic
factors of environment would be negligible. The impacts can be further
minimized through effective selection and designing of environment
management plans, proper resource allocation in order to minimize negative
land use change and to use infrastructural sites of least value in current use. As
mentioned earlier, the site acquired is to be used for industrial zone, therefore
issues of land use / land cover change mitigation is not foreseen. Also,
proponent has proposed to develop sufficient greenbelt area to add value to the
improvement of land cover of the area thus, major mitigation measures are not
required.
4.2.1.2 Predicted Impacts during Construction Phase
The major activities considered in the construction phase are civil works,
mechanical works, machinery works, transportation works and other related
activities. As mentioned earlier, majority of impacts would be washed off as the
project is situated in better geographical plain having capacity of natural
mitigation of air pollutants due to efficient dispersion in natural condition. As
the main impacts of the construction phase are envisaged in terms of air
pollution only, this natural mitigation would be significantly helpful in
elimination of predicted impacts of the phase. However the following principal
major impacts to the environment are considered for further planning of
mitigation measures:
Release of construction materials and dust into the environment from the
construction site/materials can spoil the surrounding air quality.
Improper disposal of construction wastes can damage air, water and land
quality.
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4.2 Impacts due to Development of Industrial Park
4.2.1 Construction Phase
The potential impacts from the activities are considered for planning of mitigation
measures to reduce the impacts to negligible extend of significance.
4.2.1.1 Land Acquisition and Site Preparation
The site preparation and construction will not generate any major negative
impacts on the regional environmental conditions. In addition, the impacts on
the regional aspects like population affected, land and allied abiotic & biotic
factors of environment would be negligible. The impacts can be further
minimized through effective selection and designing of environment
management plans, proper resource allocation in order to minimize negative
land use change and to use infrastructural sites of least value in current use. As
mentioned earlier, the site acquired is to be used for industrial zone, therefore
issues of land use / land cover change mitigation is not foreseen. Also,
proponent has proposed to develop sufficient greenbelt area to add value to the
improvement of land cover of the area thus, major mitigation measures are not
required.
4.2.1.2 Predicted Impacts during Construction Phase
The major activities considered in the construction phase are civil works,
mechanical works, machinery works, transportation works and other related
activities. As mentioned earlier, majority of impacts would be washed off as the
project is situated in better geographical plain having capacity of natural
mitigation of air pollutants due to efficient dispersion in natural condition. As
the main impacts of the construction phase are envisaged in terms of air
pollution only, this natural mitigation would be significantly helpful in
elimination of predicted impacts of the phase. However the following principal
major impacts to the environment are considered for further planning of
mitigation measures:
Release of construction materials and dust into the environment from the
construction site/materials can spoil the surrounding air quality.
Improper disposal of construction wastes can damage air, water and land
quality.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
116
4.2 Impacts due to Development of Industrial Park
4.2.1 Construction Phase
The potential impacts from the activities are considered for planning of mitigation
measures to reduce the impacts to negligible extend of significance.
4.2.1.1 Land Acquisition and Site Preparation
The site preparation and construction will not generate any major negative
impacts on the regional environmental conditions. In addition, the impacts on
the regional aspects like population affected, land and allied abiotic & biotic
factors of environment would be negligible. The impacts can be further
minimized through effective selection and designing of environment
management plans, proper resource allocation in order to minimize negative
land use change and to use infrastructural sites of least value in current use. As
mentioned earlier, the site acquired is to be used for industrial zone, therefore
issues of land use / land cover change mitigation is not foreseen. Also,
proponent has proposed to develop sufficient greenbelt area to add value to the
improvement of land cover of the area thus, major mitigation measures are not
required.
4.2.1.2 Predicted Impacts during Construction Phase
The major activities considered in the construction phase are civil works,
mechanical works, machinery works, transportation works and other related
activities. As mentioned earlier, majority of impacts would be washed off as the
project is situated in better geographical plain having capacity of natural
mitigation of air pollutants due to efficient dispersion in natural condition. As
the main impacts of the construction phase are envisaged in terms of air
pollution only, this natural mitigation would be significantly helpful in
elimination of predicted impacts of the phase. However the following principal
major impacts to the environment are considered for further planning of
mitigation measures:
Release of construction materials and dust into the environment from the
construction site/materials can spoil the surrounding air quality.
Improper disposal of construction wastes can damage air, water and land
quality.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
117
The use of automobiles and machinery during construction can deteriorate
the air quality and generate temporary emission.
The use of automobiles and machinery generates Noise pollution from
construction activities.
The irregular working hours, & traffic, night-working, flood-lighting and
transportation damage the socioeconomic balance of surrounding region.
Short term changes or exploitation of environment is expected during
construction which could affect life style of nearby habitants, health of the
human, birds, other terrestrial animals.
Short term heavy construction might cause increase in noise level
Effects on work place condition & human health due to the accidents during
the construction works.
Impacts to avifauna or other carnivores which may prey upon other
organisms affected by the contamination.
Effects on the socio-economic activity due to direct impacts or indirect
impacts on socio-economic activities.
The above mentioned points express that the heavy construction can contaminate
Air, Land, Water and Socioeconomic balance of surrounding region but they can
substantially be minimised or reduced to significant extent by practising suitable
and probable mitigation methods. A slight negligence in the studying, selecting and
implementing process can prove hazardous to abiotic, biotic, social, and economical
or other related attributes of the environment. Hence, the areas of major focus shall
be concentrated mainly on operational and maintenance activity of construction
phase, deciding proper manner and route of working of the vehicles in order to
avoid accidents and hefty traffic, providing suitable facilities and effective
conditions to avoid occupational hazards and proper medical aid in case of
occurrence of any accident so as to avoid any loss of life.
These are only the negative impacts but some of the major beneficial impacts to be
focused are:-
Employment opportunities: recruitment of local labourers
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
117
The use of automobiles and machinery during construction can deteriorate
the air quality and generate temporary emission.
The use of automobiles and machinery generates Noise pollution from
construction activities.
The irregular working hours, & traffic, night-working, flood-lighting and
transportation damage the socioeconomic balance of surrounding region.
Short term changes or exploitation of environment is expected during
construction which could affect life style of nearby habitants, health of the
human, birds, other terrestrial animals.
Short term heavy construction might cause increase in noise level
Effects on work place condition & human health due to the accidents during
the construction works.
Impacts to avifauna or other carnivores which may prey upon other
organisms affected by the contamination.
Effects on the socio-economic activity due to direct impacts or indirect
impacts on socio-economic activities.
The above mentioned points express that the heavy construction can contaminate
Air, Land, Water and Socioeconomic balance of surrounding region but they can
substantially be minimised or reduced to significant extent by practising suitable
and probable mitigation methods. A slight negligence in the studying, selecting and
implementing process can prove hazardous to abiotic, biotic, social, and economical
or other related attributes of the environment. Hence, the areas of major focus shall
be concentrated mainly on operational and maintenance activity of construction
phase, deciding proper manner and route of working of the vehicles in order to
avoid accidents and hefty traffic, providing suitable facilities and effective
conditions to avoid occupational hazards and proper medical aid in case of
occurrence of any accident so as to avoid any loss of life.
These are only the negative impacts but some of the major beneficial impacts to be
focused are:-
Employment opportunities: recruitment of local labourers
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
117
The use of automobiles and machinery during construction can deteriorate
the air quality and generate temporary emission.
The use of automobiles and machinery generates Noise pollution from
construction activities.
The irregular working hours, & traffic, night-working, flood-lighting and
transportation damage the socioeconomic balance of surrounding region.
Short term changes or exploitation of environment is expected during
construction which could affect life style of nearby habitants, health of the
human, birds, other terrestrial animals.
Short term heavy construction might cause increase in noise level
Effects on work place condition & human health due to the accidents during
the construction works.
Impacts to avifauna or other carnivores which may prey upon other
organisms affected by the contamination.
Effects on the socio-economic activity due to direct impacts or indirect
impacts on socio-economic activities.
The above mentioned points express that the heavy construction can contaminate
Air, Land, Water and Socioeconomic balance of surrounding region but they can
substantially be minimised or reduced to significant extent by practising suitable
and probable mitigation methods. A slight negligence in the studying, selecting and
implementing process can prove hazardous to abiotic, biotic, social, and economical
or other related attributes of the environment. Hence, the areas of major focus shall
be concentrated mainly on operational and maintenance activity of construction
phase, deciding proper manner and route of working of the vehicles in order to
avoid accidents and hefty traffic, providing suitable facilities and effective
conditions to avoid occupational hazards and proper medical aid in case of
occurrence of any accident so as to avoid any loss of life.
These are only the negative impacts but some of the major beneficial impacts to be
focused are:-
Employment opportunities: recruitment of local labourers
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
118
Trading opportunities: procurement of construction materials locally
Clean up operations, landscaping and plantations
Hence, the construction activities can have some moderate temporary and
permanent impacts on site. The short-term impact will be mostly effective during
construction phase. The land use and operational amenities might create permanent
changes (open industrial land to built-up industrial land & vegetation) on site which
will be foreseen for long term. The construction phase activities could have some
impacts on on-site noise and air quality, land use and ecology. It might also develop
minor impacts on on-site soils, water quantity & quality. The other impacts of
construction phase will be small in magnitude as well as temporary in nature and are
expected to wear out gradually once the construction activity is completed. Further,
the major and long term impacts can also be reduced and minimized by proper and
substantial implementation of mitigation measures. In brief during the construction
phase following mitigation measures shall be taken in consideration and
implemented to prevent or minimize the respective impacts.
4.2.1.3 Mitigation Measures for Land Environment
The unused construction materials shall be stored in proper area to utilise
further in construction activities and surplus excavated material shall be
disposed of in suitable pre-identified areas.
It is suggested that the construction waste containing sand, brick, gravel,
cement, etc. shall be used for filling or PCC for construction of internal road
or project structures.
Storage & handling of construction materials shall be done properly to avoid
spillage or leakage which may cause release of the material in environment
causing adverse impacts.
Appropriate designed closed & properly lined storage area shall be provided
for storage of construction materials to prevent land/soil contamination.
Designated fuel storage & Refuelling area shall be provided with impervious
lining to prevent land contamination due spill/leak of fuel during storage &
refuelling.
Excavated earth shall be used for filling of low-lying area or construction
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
118
Trading opportunities: procurement of construction materials locally
Clean up operations, landscaping and plantations
Hence, the construction activities can have some moderate temporary and
permanent impacts on site. The short-term impact will be mostly effective during
construction phase. The land use and operational amenities might create permanent
changes (open industrial land to built-up industrial land & vegetation) on site which
will be foreseen for long term. The construction phase activities could have some
impacts on on-site noise and air quality, land use and ecology. It might also develop
minor impacts on on-site soils, water quantity & quality. The other impacts of
construction phase will be small in magnitude as well as temporary in nature and are
expected to wear out gradually once the construction activity is completed. Further,
the major and long term impacts can also be reduced and minimized by proper and
substantial implementation of mitigation measures. In brief during the construction
phase following mitigation measures shall be taken in consideration and
implemented to prevent or minimize the respective impacts.
4.2.1.3 Mitigation Measures for Land Environment
The unused construction materials shall be stored in proper area to utilise
further in construction activities and surplus excavated material shall be
disposed of in suitable pre-identified areas.
It is suggested that the construction waste containing sand, brick, gravel,
cement, etc. shall be used for filling or PCC for construction of internal road
or project structures.
Storage & handling of construction materials shall be done properly to avoid
spillage or leakage which may cause release of the material in environment
causing adverse impacts.
Appropriate designed closed & properly lined storage area shall be provided
for storage of construction materials to prevent land/soil contamination.
Designated fuel storage & Refuelling area shall be provided with impervious
lining to prevent land contamination due spill/leak of fuel during storage &
refuelling.
Excavated earth shall be used for filling of low-lying area or construction
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
118
Trading opportunities: procurement of construction materials locally
Clean up operations, landscaping and plantations
Hence, the construction activities can have some moderate temporary and
permanent impacts on site. The short-term impact will be mostly effective during
construction phase. The land use and operational amenities might create permanent
changes (open industrial land to built-up industrial land & vegetation) on site which
will be foreseen for long term. The construction phase activities could have some
impacts on on-site noise and air quality, land use and ecology. It might also develop
minor impacts on on-site soils, water quantity & quality. The other impacts of
construction phase will be small in magnitude as well as temporary in nature and are
expected to wear out gradually once the construction activity is completed. Further,
the major and long term impacts can also be reduced and minimized by proper and
substantial implementation of mitigation measures. In brief during the construction
phase following mitigation measures shall be taken in consideration and
implemented to prevent or minimize the respective impacts.
4.2.1.3 Mitigation Measures for Land Environment
The unused construction materials shall be stored in proper area to utilise
further in construction activities and surplus excavated material shall be
disposed of in suitable pre-identified areas.
It is suggested that the construction waste containing sand, brick, gravel,
cement, etc. shall be used for filling or PCC for construction of internal road
or project structures.
Storage & handling of construction materials shall be done properly to avoid
spillage or leakage which may cause release of the material in environment
causing adverse impacts.
Appropriate designed closed & properly lined storage area shall be provided
for storage of construction materials to prevent land/soil contamination.
Designated fuel storage & Refuelling area shall be provided with impervious
lining to prevent land contamination due spill/leak of fuel during storage &
refuelling.
Excavated earth shall be used for filling of low-lying area or construction
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
119
works as well as landscaping.
Proper sanitation facilities shall be provided for construction labourers, to
avoid contamination of land due to dumping of domestic waste as well as
disposal of untreated sewage.
4.2.1.4 Mitigation Measures for Water Environment
Construction material shall be stored at adequate distance from the water
storage in order to prevent any chances of accidental leakage or spillage
which could pollute the water storage.
Wherever required impervious lining shall be provided to storage premises
to avoid accidental mixing or mixing due to fugitive losses.
For runoff water guidance runoff routes shall be provided and managed
properly. So the runoff could be collected and treated before release if
serious contamination is observed.
Spillage or leakage of construction material can lead to groundwater
contamination and hence care shall be taken to minimise the chances of the
Spillage or leakage of construction material.
4.2.1.5 Mitigation Measures for Air Environment
To reduce the dust generation on site wherever & whenever required water
shall be sprinkled on ground or stock pile of excavated soil.
Equipments / machineries shall be used efficiently and shall be kept shut in
order to reduce air emission, noise pollution and consumption of energy
resource.
Emission from the equipments / machineries shall be monitored on regular
basis and possible implementation shall be provided on site.
Transport vehicles shall be monitored & maintain regularly to control the
emission quality and fuel consumption.
Construction materials would be stored in covered stores or enclosed spaces
to prevent chance of airborne construction materials which can lead to air
pollution of local area.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
119
works as well as landscaping.
Proper sanitation facilities shall be provided for construction labourers, to
avoid contamination of land due to dumping of domestic waste as well as
disposal of untreated sewage.
4.2.1.4 Mitigation Measures for Water Environment
Construction material shall be stored at adequate distance from the water
storage in order to prevent any chances of accidental leakage or spillage
which could pollute the water storage.
Wherever required impervious lining shall be provided to storage premises
to avoid accidental mixing or mixing due to fugitive losses.
For runoff water guidance runoff routes shall be provided and managed
properly. So the runoff could be collected and treated before release if
serious contamination is observed.
Spillage or leakage of construction material can lead to groundwater
contamination and hence care shall be taken to minimise the chances of the
Spillage or leakage of construction material.
4.2.1.5 Mitigation Measures for Air Environment
To reduce the dust generation on site wherever & whenever required water
shall be sprinkled on ground or stock pile of excavated soil.
Equipments / machineries shall be used efficiently and shall be kept shut in
order to reduce air emission, noise pollution and consumption of energy
resource.
Emission from the equipments / machineries shall be monitored on regular
basis and possible implementation shall be provided on site.
Transport vehicles shall be monitored & maintain regularly to control the
emission quality and fuel consumption.
Construction materials would be stored in covered stores or enclosed spaces
to prevent chance of airborne construction materials which can lead to air
pollution of local area.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
119
works as well as landscaping.
Proper sanitation facilities shall be provided for construction labourers, to
avoid contamination of land due to dumping of domestic waste as well as
disposal of untreated sewage.
4.2.1.4 Mitigation Measures for Water Environment
Construction material shall be stored at adequate distance from the water
storage in order to prevent any chances of accidental leakage or spillage
which could pollute the water storage.
Wherever required impervious lining shall be provided to storage premises
to avoid accidental mixing or mixing due to fugitive losses.
For runoff water guidance runoff routes shall be provided and managed
properly. So the runoff could be collected and treated before release if
serious contamination is observed.
Spillage or leakage of construction material can lead to groundwater
contamination and hence care shall be taken to minimise the chances of the
Spillage or leakage of construction material.
4.2.1.5 Mitigation Measures for Air Environment
To reduce the dust generation on site wherever & whenever required water
shall be sprinkled on ground or stock pile of excavated soil.
Equipments / machineries shall be used efficiently and shall be kept shut in
order to reduce air emission, noise pollution and consumption of energy
resource.
Emission from the equipments / machineries shall be monitored on regular
basis and possible implementation shall be provided on site.
Transport vehicles shall be monitored & maintain regularly to control the
emission quality and fuel consumption.
Construction materials would be stored in covered stores or enclosed spaces
to prevent chance of airborne construction materials which can lead to air
pollution of local area.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
120
Regular inspection of construction site shall be carried out to ensure regular
and timely removal of construction debris to the dumping sites or for
recycle/reuse.
Vehicles needs to be used for construction work shall be kept maintained
and highly efficient to keep emissions within the permissible limits.
All necessary equipments/machineries shall be in good condition for proper
operation and minimal exhaust/emission.
Provision of necessary PPEs like face mask & eye-glasses are provided to
the employees /labourers engaged in construction activities.
4.2.1.6 Mitigation Measures for Noise Generation
The machineries/equipment used on site shall be of highly maintained so
they do work with optimum efficiency generating less noise pollution.
Operation of machineries/equipment causing high noise level shall be
stopped during the night time and all such operations shall be planned for
day time only.
Transportation activities shall not be conducted during the night to avoid
high noise level in nearby villages/locality. Only in case of emergency the
transportation activities shall be allowed in night time.
The vehicles engaged in construction activities & transportation of materials
shall be equipped with the horn of low noise level as recommended by
RTO/concern authority to avoid impacts on noise level. Further, adequate
silencers must be attached with all vehicles to reduce the noise.
Construction equipments & machinery shall be turned off when not in use.
Proponent shall ensure that the labours engaged in construction site of high
noise area are provided with necessary PPEs.
4.2.1.7 Mitigation Measures for Biological Environment
Regular monitoring shall be done to avoid and/or locate any hazards to
natural habitats.
Minimize contamination of each parameter such as air, water etc in order to
maintain the biological balance of the site and adjoining region.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
120
Regular inspection of construction site shall be carried out to ensure regular
and timely removal of construction debris to the dumping sites or for
recycle/reuse.
Vehicles needs to be used for construction work shall be kept maintained
and highly efficient to keep emissions within the permissible limits.
All necessary equipments/machineries shall be in good condition for proper
operation and minimal exhaust/emission.
Provision of necessary PPEs like face mask & eye-glasses are provided to
the employees /labourers engaged in construction activities.
4.2.1.6 Mitigation Measures for Noise Generation
The machineries/equipment used on site shall be of highly maintained so
they do work with optimum efficiency generating less noise pollution.
Operation of machineries/equipment causing high noise level shall be
stopped during the night time and all such operations shall be planned for
day time only.
Transportation activities shall not be conducted during the night to avoid
high noise level in nearby villages/locality. Only in case of emergency the
transportation activities shall be allowed in night time.
The vehicles engaged in construction activities & transportation of materials
shall be equipped with the horn of low noise level as recommended by
RTO/concern authority to avoid impacts on noise level. Further, adequate
silencers must be attached with all vehicles to reduce the noise.
Construction equipments & machinery shall be turned off when not in use.
Proponent shall ensure that the labours engaged in construction site of high
noise area are provided with necessary PPEs.
4.2.1.7 Mitigation Measures for Biological Environment
Regular monitoring shall be done to avoid and/or locate any hazards to
natural habitats.
Minimize contamination of each parameter such as air, water etc in order to
maintain the biological balance of the site and adjoining region.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
120
Regular inspection of construction site shall be carried out to ensure regular
and timely removal of construction debris to the dumping sites or for
recycle/reuse.
Vehicles needs to be used for construction work shall be kept maintained
and highly efficient to keep emissions within the permissible limits.
All necessary equipments/machineries shall be in good condition for proper
operation and minimal exhaust/emission.
Provision of necessary PPEs like face mask & eye-glasses are provided to
the employees /labourers engaged in construction activities.
4.2.1.6 Mitigation Measures for Noise Generation
The machineries/equipment used on site shall be of highly maintained so
they do work with optimum efficiency generating less noise pollution.
Operation of machineries/equipment causing high noise level shall be
stopped during the night time and all such operations shall be planned for
day time only.
Transportation activities shall not be conducted during the night to avoid
high noise level in nearby villages/locality. Only in case of emergency the
transportation activities shall be allowed in night time.
The vehicles engaged in construction activities & transportation of materials
shall be equipped with the horn of low noise level as recommended by
RTO/concern authority to avoid impacts on noise level. Further, adequate
silencers must be attached with all vehicles to reduce the noise.
Construction equipments & machinery shall be turned off when not in use.
Proponent shall ensure that the labours engaged in construction site of high
noise area are provided with necessary PPEs.
4.2.1.7 Mitigation Measures for Biological Environment
Regular monitoring shall be done to avoid and/or locate any hazards to
natural habitats.
Minimize contamination of each parameter such as air, water etc in order to
maintain the biological balance of the site and adjoining region.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
121
Ecological protection plan like greenbelt development shall be formulated
and implemented in the very inception of the construction activity.
The proponent shall prepare a plan for plantation within & near the site and
in the suitable areas in and around the project site. The proponent shall start
the plantation during the construction stage itself.
4.2.1.8 Mitigation Measures for Social Environment
Construction activities shall be regulated by adequate safety codes and tools.
The employees shall be provided with adequate safety equipment.
Training must be given for the operational method, problem solving and
safety.
Employees/ contractors/ person associated with construction activities shall
be provided with proper training before starting their works.
During the construction phase proper traffic management shall be
maintained to avoid problems due to the construction activities.
Employment for the construction work shall be conducted with priority to
local village peoples.
Any emission generation shall be monitored and possible mitigation
measures shall be provided to avoid disturbance in surrounding region.
4.2.1.9 Miscellaneous Measures
All activities must be conducted as per the guidelines and methodology /
procedure provided by the project authority.
All activities shall be done within the area confined by the project authority.
In addition to the above, TSIIC Environment Management and Planning of
TSIIC Cell shall update the mitigation measure depending on the details of
identified impacts as mentioned in EIA Study as well as defined in
environmental management record during the construction phase and
operational phase.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
121
Ecological protection plan like greenbelt development shall be formulated
and implemented in the very inception of the construction activity.
The proponent shall prepare a plan for plantation within & near the site and
in the suitable areas in and around the project site. The proponent shall start
the plantation during the construction stage itself.
4.2.1.8 Mitigation Measures for Social Environment
Construction activities shall be regulated by adequate safety codes and tools.
The employees shall be provided with adequate safety equipment.
Training must be given for the operational method, problem solving and
safety.
Employees/ contractors/ person associated with construction activities shall
be provided with proper training before starting their works.
During the construction phase proper traffic management shall be
maintained to avoid problems due to the construction activities.
Employment for the construction work shall be conducted with priority to
local village peoples.
Any emission generation shall be monitored and possible mitigation
measures shall be provided to avoid disturbance in surrounding region.
4.2.1.9 Miscellaneous Measures
All activities must be conducted as per the guidelines and methodology /
procedure provided by the project authority.
All activities shall be done within the area confined by the project authority.
In addition to the above, TSIIC Environment Management and Planning of
TSIIC Cell shall update the mitigation measure depending on the details of
identified impacts as mentioned in EIA Study as well as defined in
environmental management record during the construction phase and
operational phase.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
121
Ecological protection plan like greenbelt development shall be formulated
and implemented in the very inception of the construction activity.
The proponent shall prepare a plan for plantation within & near the site and
in the suitable areas in and around the project site. The proponent shall start
the plantation during the construction stage itself.
4.2.1.8 Mitigation Measures for Social Environment
Construction activities shall be regulated by adequate safety codes and tools.
The employees shall be provided with adequate safety equipment.
Training must be given for the operational method, problem solving and
safety.
Employees/ contractors/ person associated with construction activities shall
be provided with proper training before starting their works.
During the construction phase proper traffic management shall be
maintained to avoid problems due to the construction activities.
Employment for the construction work shall be conducted with priority to
local village peoples.
Any emission generation shall be monitored and possible mitigation
measures shall be provided to avoid disturbance in surrounding region.
4.2.1.9 Miscellaneous Measures
All activities must be conducted as per the guidelines and methodology /
procedure provided by the project authority.
All activities shall be done within the area confined by the project authority.
In addition to the above, TSIIC Environment Management and Planning of
TSIIC Cell shall update the mitigation measure depending on the details of
identified impacts as mentioned in EIA Study as well as defined in
environmental management record during the construction phase and
operational phase.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
122
4.2.2 Operation Phase Impacts and Mitigation Measures
4.2.2.1 Air Dispersion Modeling of Pollutants
The objective of the study was to determine the locations for maximum ground
level concentrations (GLC) for various air pollutants through air dispersion
modeling technique. The maximum GLC’s would then be utilized to assess the
extent and magnitude of potential air quality impacts resulting from the
emissions of Industrial Park. The AERMOD Modelling system requires stack
emission data such as gas exit temperature, diameter flow rate etc., and
meteorological data as its primary input.
For the 3 phase AERMET processing of the meteorological data, specifications
of the land use in the area are required to determine the terrain roughness for
modelling. The land use was characterized for in and around the site. The
surface characteristics for the site and surroundings were selected and used to
calculate the albedo, Bowen ratio, and surface roughness parameter. The
meteorological data were processed in the AERMET software to generate wind
flow pattern & to generate surface meteorological data and profile meteorological
data in a prescribed format that can be fed to AERMOD for modeling.
4.2.2.2 AERMOD Process
Base line data reveals that ambient air quality in the study area for the Parameters
PM, SO2 and NO2 are well within the permissible Limits as prescribed by the
National Ambient Air Quality Standards (NAAQ) for Industrial Area,
Residential, Rural & Other area. Emission of PM, SOx & NOx from stacks
attached to Boiler, DG’s and Furnace are the only source of air pollution.
AERMOD Software Version 7.5.0 was used for air dispersion modelling and is
applicable to a wide range of buoyant or neutrally buoyant emissions up to a
range of 50km. In addition to more straight forward cases, AERMOD is also
suitable for complex terrain and urban dispersion scenarios.
AERMOD is a steady-state plume model. In the stable boundary layer (SBL), it
assumes the concentration distribution to be Gaussian in both the vertical and
horizontal. In the convective boundary layer (CBL), the horizontal distribution is
also assumed to be Gaussian, but the vertical distribution is described with a bi-
Gaussian probability density function (pdf). This behaviour of the concentration
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
122
4.2.2 Operation Phase Impacts and Mitigation Measures
4.2.2.1 Air Dispersion Modeling of Pollutants
The objective of the study was to determine the locations for maximum ground
level concentrations (GLC) for various air pollutants through air dispersion
modeling technique. The maximum GLC’s would then be utilized to assess the
extent and magnitude of potential air quality impacts resulting from the
emissions of Industrial Park. The AERMOD Modelling system requires stack
emission data such as gas exit temperature, diameter flow rate etc., and
meteorological data as its primary input.
For the 3 phase AERMET processing of the meteorological data, specifications
of the land use in the area are required to determine the terrain roughness for
modelling. The land use was characterized for in and around the site. The
surface characteristics for the site and surroundings were selected and used to
calculate the albedo, Bowen ratio, and surface roughness parameter. The
meteorological data were processed in the AERMET software to generate wind
flow pattern & to generate surface meteorological data and profile meteorological
data in a prescribed format that can be fed to AERMOD for modeling.
4.2.2.2 AERMOD Process
Base line data reveals that ambient air quality in the study area for the Parameters
PM, SO2 and NO2 are well within the permissible Limits as prescribed by the
National Ambient Air Quality Standards (NAAQ) for Industrial Area,
Residential, Rural & Other area. Emission of PM, SOx & NOx from stacks
attached to Boiler, DG’s and Furnace are the only source of air pollution.
AERMOD Software Version 7.5.0 was used for air dispersion modelling and is
applicable to a wide range of buoyant or neutrally buoyant emissions up to a
range of 50km. In addition to more straight forward cases, AERMOD is also
suitable for complex terrain and urban dispersion scenarios.
AERMOD is a steady-state plume model. In the stable boundary layer (SBL), it
assumes the concentration distribution to be Gaussian in both the vertical and
horizontal. In the convective boundary layer (CBL), the horizontal distribution is
also assumed to be Gaussian, but the vertical distribution is described with a bi-
Gaussian probability density function (pdf). This behaviour of the concentration
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
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4.2.2 Operation Phase Impacts and Mitigation Measures
4.2.2.1 Air Dispersion Modeling of Pollutants
The objective of the study was to determine the locations for maximum ground
level concentrations (GLC) for various air pollutants through air dispersion
modeling technique. The maximum GLC’s would then be utilized to assess the
extent and magnitude of potential air quality impacts resulting from the
emissions of Industrial Park. The AERMOD Modelling system requires stack
emission data such as gas exit temperature, diameter flow rate etc., and
meteorological data as its primary input.
For the 3 phase AERMET processing of the meteorological data, specifications
of the land use in the area are required to determine the terrain roughness for
modelling. The land use was characterized for in and around the site. The
surface characteristics for the site and surroundings were selected and used to
calculate the albedo, Bowen ratio, and surface roughness parameter. The
meteorological data were processed in the AERMET software to generate wind
flow pattern & to generate surface meteorological data and profile meteorological
data in a prescribed format that can be fed to AERMOD for modeling.
4.2.2.2 AERMOD Process
Base line data reveals that ambient air quality in the study area for the Parameters
PM, SO2 and NO2 are well within the permissible Limits as prescribed by the
National Ambient Air Quality Standards (NAAQ) for Industrial Area,
Residential, Rural & Other area. Emission of PM, SOx & NOx from stacks
attached to Boiler, DG’s and Furnace are the only source of air pollution.
AERMOD Software Version 7.5.0 was used for air dispersion modelling and is
applicable to a wide range of buoyant or neutrally buoyant emissions up to a
range of 50km. In addition to more straight forward cases, AERMOD is also
suitable for complex terrain and urban dispersion scenarios.
AERMOD is a steady-state plume model. In the stable boundary layer (SBL), it
assumes the concentration distribution to be Gaussian in both the vertical and
horizontal. In the convective boundary layer (CBL), the horizontal distribution is
also assumed to be Gaussian, but the vertical distribution is described with a bi-
Gaussian probability density function (pdf). This behaviour of the concentration
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
123
distributions in the CBL was demonstrated by Willis and Deardorff (1981) and
Briggs (1993). Additionally, in the CBL, AERMOD treats “plume lofting,”
whereby a portion of plume mass, released from a buoyant source, rises to and
remains near the top of the boundary layer before becoming mixed into the CBL.
AERMOD also tracks any plume mass that penetrates into the elevated stable
layer, and then allows it to re-enter the boundary layer when and if appropriate.
For sources in both the CBL and the SBL AERMOD treats the enhancement of
lateral dispersion resulting from plume meander.
Site specific meteorological data for one season (March to May, 2014) were
obtained from on site metrological monitoring station. Data included in the data
set were hourly wind speed, wind direction, temperature, relative humidity, air
pressure, precipitation etc., the emission rates of stacks are predicted and it has
been taken as basis for modeling are shown below:
Table 4.1 Stack emission details for modeling
S.No Industries list FuelType
Maximum
discharge(Nm3/hr)
StackHeight (m)
Temp (0c)
Dia(m)
Gas Exitvelocity(m/sec)
1. Steel RerollingIndustry 2T Boiler
Coal 9717 33 83 0.75 7.5
Steel RerollingIndustry DG of250KVA
Diesel 1847 30 105 0.51 0.95
2. Steel & steelproducts withfurnaces
Coal 3707 42 154 0.65 1.49
Steel & steelproducts DG of250KVA
Diesel 1971 30 102 0.53 0.95
3. Commercial AreaDG of 250KVA
Diesel 1521 19 98 0.45 0.94
4. Common Utilities,facilitiesDG of 100KVA
Diesel 984 24 136 0.64 0.64
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
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distributions in the CBL was demonstrated by Willis and Deardorff (1981) and
Briggs (1993). Additionally, in the CBL, AERMOD treats “plume lofting,”
whereby a portion of plume mass, released from a buoyant source, rises to and
remains near the top of the boundary layer before becoming mixed into the CBL.
AERMOD also tracks any plume mass that penetrates into the elevated stable
layer, and then allows it to re-enter the boundary layer when and if appropriate.
For sources in both the CBL and the SBL AERMOD treats the enhancement of
lateral dispersion resulting from plume meander.
Site specific meteorological data for one season (March to May, 2014) were
obtained from on site metrological monitoring station. Data included in the data
set were hourly wind speed, wind direction, temperature, relative humidity, air
pressure, precipitation etc., the emission rates of stacks are predicted and it has
been taken as basis for modeling are shown below:
Table 4.1 Stack emission details for modeling
S.No Industries list FuelType
Maximum
discharge(Nm3/hr)
StackHeight (m)
Temp (0c)
Dia(m)
Gas Exitvelocity(m/sec)
1. Steel RerollingIndustry 2T Boiler
Coal 9717 33 83 0.75 7.5
Steel RerollingIndustry DG of250KVA
Diesel 1847 30 105 0.51 0.95
2. Steel & steelproducts withfurnaces
Coal 3707 42 154 0.65 1.49
Steel & steelproducts DG of250KVA
Diesel 1971 30 102 0.53 0.95
3. Commercial AreaDG of 250KVA
Diesel 1521 19 98 0.45 0.94
4. Common Utilities,facilitiesDG of 100KVA
Diesel 984 24 136 0.64 0.64
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
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distributions in the CBL was demonstrated by Willis and Deardorff (1981) and
Briggs (1993). Additionally, in the CBL, AERMOD treats “plume lofting,”
whereby a portion of plume mass, released from a buoyant source, rises to and
remains near the top of the boundary layer before becoming mixed into the CBL.
AERMOD also tracks any plume mass that penetrates into the elevated stable
layer, and then allows it to re-enter the boundary layer when and if appropriate.
For sources in both the CBL and the SBL AERMOD treats the enhancement of
lateral dispersion resulting from plume meander.
Site specific meteorological data for one season (March to May, 2014) were
obtained from on site metrological monitoring station. Data included in the data
set were hourly wind speed, wind direction, temperature, relative humidity, air
pressure, precipitation etc., the emission rates of stacks are predicted and it has
been taken as basis for modeling are shown below:
Table 4.1 Stack emission details for modeling
S.No Industries list FuelType
Maximum
discharge(Nm3/hr)
StackHeight (m)
Temp (0c)
Dia(m)
Gas Exitvelocity(m/sec)
1. Steel RerollingIndustry 2T Boiler
Coal 9717 33 83 0.75 7.5
Steel RerollingIndustry DG of250KVA
Diesel 1847 30 105 0.51 0.95
2. Steel & steelproducts withfurnaces
Coal 3707 42 154 0.65 1.49
Steel & steelproducts DG of250KVA
Diesel 1971 30 102 0.53 0.95
3. Commercial AreaDG of 250KVA
Diesel 1521 19 98 0.45 0.94
4. Common Utilities,facilitiesDG of 100KVA
Diesel 984 24 136 0.64 0.64
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
124
Figure 4.1Terrain map of the site
4.2.2.3 Results of Dispersion Modelling
Dispersion modeling was conducted as described in this report to determine the
extent and Magnitude of potential air quality impacts are resulting from proposed
activities. Uniform Cartesian Grid Receptors were used in this model, and the
grid size for model run was 1000mx1000m. The modeling was done for 10 Km
radial distance from the reference point of the site. The GLC contour of SOX,
NOX & PM for both the scenarios have been predicted using AERMOD & the
results are super exported to the Google earth. The results are presented in the
following section.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
124
Figure 4.1Terrain map of the site
4.2.2.3 Results of Dispersion Modelling
Dispersion modeling was conducted as described in this report to determine the
extent and Magnitude of potential air quality impacts are resulting from proposed
activities. Uniform Cartesian Grid Receptors were used in this model, and the
grid size for model run was 1000mx1000m. The modeling was done for 10 Km
radial distance from the reference point of the site. The GLC contour of SOX,
NOX & PM for both the scenarios have been predicted using AERMOD & the
results are super exported to the Google earth. The results are presented in the
following section.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
124
Figure 4.1Terrain map of the site
4.2.2.3 Results of Dispersion Modelling
Dispersion modeling was conducted as described in this report to determine the
extent and Magnitude of potential air quality impacts are resulting from proposed
activities. Uniform Cartesian Grid Receptors were used in this model, and the
grid size for model run was 1000mx1000m. The modeling was done for 10 Km
radial distance from the reference point of the site. The GLC contour of SOX,
NOX & PM for both the scenarios have been predicted using AERMOD & the
results are super exported to the Google earth. The results are presented in the
following section.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
125
Figure 4.2 Ground Level Concentration of SOx
Figure 4.3 Ground Level Concentration of Nox
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
125
Figure 4.2 Ground Level Concentration of SOx
Figure 4.3 Ground Level Concentration of Nox
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
125
Figure 4.2 Ground Level Concentration of SOx
Figure 4.3 Ground Level Concentration of Nox
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
126
Figure 4.4 GLC of PM
Table 4.2 Predicted GLC for Proposed Stack
Parameters Baseline
data
(µg/m3)
Estimated
Maximum
Incremental
Concentration
(µg/m3)
Predicted
Maximum
GLC
(µg/m3)
NAAQ
Standards
Direction Distance
from
center of
the
site(m)
SOX 5.4 16.389 21.789 80 SE 200
NOX 10.3 21.965 32.265 80 SE 150
PM 20.5 27.485 47.985 100 SE 133
Due to the Proposed Industrial park consisting of steel re-rolling units, automobile,
leather cutting industries of small scale there is No Major Impact. As seen from the
above table the concentration levels arising from the proposed Industries are well
within the NAAQ permissible limits.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
126
Figure 4.4 GLC of PM
Table 4.2 Predicted GLC for Proposed Stack
Parameters Baseline
data
(µg/m3)
Estimated
Maximum
Incremental
Concentration
(µg/m3)
Predicted
Maximum
GLC
(µg/m3)
NAAQ
Standards
Direction Distance
from
center of
the
site(m)
SOX 5.4 16.389 21.789 80 SE 200
NOX 10.3 21.965 32.265 80 SE 150
PM 20.5 27.485 47.985 100 SE 133
Due to the Proposed Industrial park consisting of steel re-rolling units, automobile,
leather cutting industries of small scale there is No Major Impact. As seen from the
above table the concentration levels arising from the proposed Industries are well
within the NAAQ permissible limits.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
126
Figure 4.4 GLC of PM
Table 4.2 Predicted GLC for Proposed Stack
Parameters Baseline
data
(µg/m3)
Estimated
Maximum
Incremental
Concentration
(µg/m3)
Predicted
Maximum
GLC
(µg/m3)
NAAQ
Standards
Direction Distance
from
center of
the
site(m)
SOX 5.4 16.389 21.789 80 SE 200
NOX 10.3 21.965 32.265 80 SE 150
PM 20.5 27.485 47.985 100 SE 133
Due to the Proposed Industrial park consisting of steel re-rolling units, automobile,
leather cutting industries of small scale there is No Major Impact. As seen from the
above table the concentration levels arising from the proposed Industries are well
within the NAAQ permissible limits.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
127
4.2.2.4 Mitigation Measures
Therefore the DG sets to be installed at the industrial park should meet the
necessary emission limits as per Environment (Protection) Amendment
Rules, 2003 made under the, Environment Protection Rules, 1986.
Proper stack and scrubbing system will be proposed for the Industries
using boilers.
The details of emission limits for new diesel engines upto 800 kWA for
DG applications shall be as given in the Table below;
Table 4.3 Emission details of diesel Engines
Capacity
Test Cycle
of diesel
engines
Emission Limits (g/kwhr) for Smoke Limit (light
Absorption
coefficient, m-1)
(at full load)
Test Cycle
NOx HC CO PMTorque
%
Weighting
Factors
Upto 19
kWA
9.2 1.3 3.85 0.3 0.7 100 0.05
75 0.25
> 19 kWA
upto 176
kWA
9.2 1.3 3.5 0.3 0.7 25 0.30
> 176 kWA
upto 800
kWA
9.2 1.3 3.5 0.3 0.7 10 0.10
4.2.3 Impacts on Quality of Life
The population of the Pudur Mandal expects that industrial park development will
lead to improvements in infrastructure and public services (health, education, security,
drinking water and power) in the commune, which would be a significant positive
impact on the quality of life of local residents. If the project is not realized, the local
population will not be benefitted from these improvements. This development will
create employment for local people and leads to improvement in infrastructure.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
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4.2.2.4 Mitigation Measures
Therefore the DG sets to be installed at the industrial park should meet the
necessary emission limits as per Environment (Protection) Amendment
Rules, 2003 made under the, Environment Protection Rules, 1986.
Proper stack and scrubbing system will be proposed for the Industries
using boilers.
The details of emission limits for new diesel engines upto 800 kWA for
DG applications shall be as given in the Table below;
Table 4.3 Emission details of diesel Engines
Capacity
Test Cycle
of diesel
engines
Emission Limits (g/kwhr) for Smoke Limit (light
Absorption
coefficient, m-1)
(at full load)
Test Cycle
NOx HC CO PMTorque
%
Weighting
Factors
Upto 19
kWA
9.2 1.3 3.85 0.3 0.7 100 0.05
75 0.25
> 19 kWA
upto 176
kWA
9.2 1.3 3.5 0.3 0.7 25 0.30
> 176 kWA
upto 800
kWA
9.2 1.3 3.5 0.3 0.7 10 0.10
4.2.3 Impacts on Quality of Life
The population of the Pudur Mandal expects that industrial park development will
lead to improvements in infrastructure and public services (health, education, security,
drinking water and power) in the commune, which would be a significant positive
impact on the quality of life of local residents. If the project is not realized, the local
population will not be benefitted from these improvements. This development will
create employment for local people and leads to improvement in infrastructure.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
127
4.2.2.4 Mitigation Measures
Therefore the DG sets to be installed at the industrial park should meet the
necessary emission limits as per Environment (Protection) Amendment
Rules, 2003 made under the, Environment Protection Rules, 1986.
Proper stack and scrubbing system will be proposed for the Industries
using boilers.
The details of emission limits for new diesel engines upto 800 kWA for
DG applications shall be as given in the Table below;
Table 4.3 Emission details of diesel Engines
Capacity
Test Cycle
of diesel
engines
Emission Limits (g/kwhr) for Smoke Limit (light
Absorption
coefficient, m-1)
(at full load)
Test Cycle
NOx HC CO PMTorque
%
Weighting
Factors
Upto 19
kWA
9.2 1.3 3.85 0.3 0.7 100 0.05
75 0.25
> 19 kWA
upto 176
kWA
9.2 1.3 3.5 0.3 0.7 25 0.30
> 176 kWA
upto 800
kWA
9.2 1.3 3.5 0.3 0.7 10 0.10
4.2.3 Impacts on Quality of Life
The population of the Pudur Mandal expects that industrial park development will
lead to improvements in infrastructure and public services (health, education, security,
drinking water and power) in the commune, which would be a significant positive
impact on the quality of life of local residents. If the project is not realized, the local
population will not be benefitted from these improvements. This development will
create employment for local people and leads to improvement in infrastructure.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
128
4.2.4 Impacts on Land Use
The Proposed Industrial Park will have positive impacts as most of the site is barren
land.
4.2.5 Impacts on Standard of Living and Economic Opportunities
Employment will be created by the Industrial Park in Rakamcherla, of which less than
10% of the population has regular salary based jobs. Without the project, these
opportunities will not be realized. In the case that the Industrial Park project is not
realized, the expected economic development will not occur and the local population
will feel discouraged and disappointed in subsistence.
In this environmental impact assessment, the impact of the Industrial Park
development on the biophysical and social environments was assessed. From the
assessment, it was determined which parts of the two environments will be more
significantly affected as compared to others. Below is a summary of the main findings
of the EIA.
Table 4.4 Summary of Findings
S.No. Impact
DescriptionSummary of findings
1 Biophysical Environment
a Geology No significant change in the geology on site will occur; the
proposed development would be of minimal impact as all
disturbances on site will be limited to the construction areas.
b Topography Changes in the topography will occur; appropriate mitigation
measures will be implemented to minimize the impact.
c Soil, Land Use
and Capability
Due to the poor soil for irrigation the land is classified as Barren
land it is used for Industrial Purpose.
d Vegetation The vegetation identified near the site will be accordingly integrated
into the planning of the development. Appropriate mitigation
measures will be implemented to minimize the impacts of
construction activities. There are no specific trees available at site.
Only shrubs and bushes are seen.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
128
4.2.4 Impacts on Land Use
The Proposed Industrial Park will have positive impacts as most of the site is barren
land.
4.2.5 Impacts on Standard of Living and Economic Opportunities
Employment will be created by the Industrial Park in Rakamcherla, of which less than
10% of the population has regular salary based jobs. Without the project, these
opportunities will not be realized. In the case that the Industrial Park project is not
realized, the expected economic development will not occur and the local population
will feel discouraged and disappointed in subsistence.
In this environmental impact assessment, the impact of the Industrial Park
development on the biophysical and social environments was assessed. From the
assessment, it was determined which parts of the two environments will be more
significantly affected as compared to others. Below is a summary of the main findings
of the EIA.
Table 4.4 Summary of Findings
S.No. Impact
DescriptionSummary of findings
1 Biophysical Environment
a Geology No significant change in the geology on site will occur; the
proposed development would be of minimal impact as all
disturbances on site will be limited to the construction areas.
b Topography Changes in the topography will occur; appropriate mitigation
measures will be implemented to minimize the impact.
c Soil, Land Use
and Capability
Due to the poor soil for irrigation the land is classified as Barren
land it is used for Industrial Purpose.
d Vegetation The vegetation identified near the site will be accordingly integrated
into the planning of the development. Appropriate mitigation
measures will be implemented to minimize the impacts of
construction activities. There are no specific trees available at site.
Only shrubs and bushes are seen.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
128
4.2.4 Impacts on Land Use
The Proposed Industrial Park will have positive impacts as most of the site is barren
land.
4.2.5 Impacts on Standard of Living and Economic Opportunities
Employment will be created by the Industrial Park in Rakamcherla, of which less than
10% of the population has regular salary based jobs. Without the project, these
opportunities will not be realized. In the case that the Industrial Park project is not
realized, the expected economic development will not occur and the local population
will feel discouraged and disappointed in subsistence.
In this environmental impact assessment, the impact of the Industrial Park
development on the biophysical and social environments was assessed. From the
assessment, it was determined which parts of the two environments will be more
significantly affected as compared to others. Below is a summary of the main findings
of the EIA.
Table 4.4 Summary of Findings
S.No. Impact
DescriptionSummary of findings
1 Biophysical Environment
a Geology No significant change in the geology on site will occur; the
proposed development would be of minimal impact as all
disturbances on site will be limited to the construction areas.
b Topography Changes in the topography will occur; appropriate mitigation
measures will be implemented to minimize the impact.
c Soil, Land Use
and Capability
Due to the poor soil for irrigation the land is classified as Barren
land it is used for Industrial Purpose.
d Vegetation The vegetation identified near the site will be accordingly integrated
into the planning of the development. Appropriate mitigation
measures will be implemented to minimize the impacts of
construction activities. There are no specific trees available at site.
Only shrubs and bushes are seen.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
129
S.No. Impact
DescriptionSummary of findings
e River The implementation of a comprehensive and effective storm water
management plan with particular focus on erosion and silt
management is a necessity in order to protect the water bodies.
There is no river near the vicinity of the site.
f Surface Water
and Ground
water
The source of fresh water is Bore well. The establishment of a storm
water management system will ensure that all surface water runoff
from the site is appropriately directed to the natural wetland on site.
Rainwater harvesting pits will be constructed to improve the
Existing aquifers. In terms of water consumption limited
consumption by installing water saving taps and dual flushing toilet
systems.
g Air Quality and
Noise
The release of dust into the atmosphere during construction
activities will be monitored and proper mitigation measures will be
implemented. During construction activities, noise will be generated
by vehicles, equipment and building activities, but will be
mitigated.
h Visual Aspects The surrounding areas could experience potential visual impacts;
however from the public meetings residents in these areas support
the development. The design of the development will be in line with
the aesthetics of the surrounding environment. Urban Design and
building guidelines will be provided for new commercial and
industrial development.
i Waste The potential wastes from the project are identified as domestic
waste, construction waste, sewage and process waste. The impact of
the wastes would be minimized by implementing the rigorous
mitigation measures and disposed through proper facility.
j Odour Odour from toilets on site for construction staff will be minimized
by ensuring that the toilets are cleaned and maintained on a regular
time basis.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
129
S.No. Impact
DescriptionSummary of findings
e River The implementation of a comprehensive and effective storm water
management plan with particular focus on erosion and silt
management is a necessity in order to protect the water bodies.
There is no river near the vicinity of the site.
f Surface Water
and Ground
water
The source of fresh water is Bore well. The establishment of a storm
water management system will ensure that all surface water runoff
from the site is appropriately directed to the natural wetland on site.
Rainwater harvesting pits will be constructed to improve the
Existing aquifers. In terms of water consumption limited
consumption by installing water saving taps and dual flushing toilet
systems.
g Air Quality and
Noise
The release of dust into the atmosphere during construction
activities will be monitored and proper mitigation measures will be
implemented. During construction activities, noise will be generated
by vehicles, equipment and building activities, but will be
mitigated.
h Visual Aspects The surrounding areas could experience potential visual impacts;
however from the public meetings residents in these areas support
the development. The design of the development will be in line with
the aesthetics of the surrounding environment. Urban Design and
building guidelines will be provided for new commercial and
industrial development.
i Waste The potential wastes from the project are identified as domestic
waste, construction waste, sewage and process waste. The impact of
the wastes would be minimized by implementing the rigorous
mitigation measures and disposed through proper facility.
j Odour Odour from toilets on site for construction staff will be minimized
by ensuring that the toilets are cleaned and maintained on a regular
time basis.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
129
S.No. Impact
DescriptionSummary of findings
e River The implementation of a comprehensive and effective storm water
management plan with particular focus on erosion and silt
management is a necessity in order to protect the water bodies.
There is no river near the vicinity of the site.
f Surface Water
and Ground
water
The source of fresh water is Bore well. The establishment of a storm
water management system will ensure that all surface water runoff
from the site is appropriately directed to the natural wetland on site.
Rainwater harvesting pits will be constructed to improve the
Existing aquifers. In terms of water consumption limited
consumption by installing water saving taps and dual flushing toilet
systems.
g Air Quality and
Noise
The release of dust into the atmosphere during construction
activities will be monitored and proper mitigation measures will be
implemented. During construction activities, noise will be generated
by vehicles, equipment and building activities, but will be
mitigated.
h Visual Aspects The surrounding areas could experience potential visual impacts;
however from the public meetings residents in these areas support
the development. The design of the development will be in line with
the aesthetics of the surrounding environment. Urban Design and
building guidelines will be provided for new commercial and
industrial development.
i Waste The potential wastes from the project are identified as domestic
waste, construction waste, sewage and process waste. The impact of
the wastes would be minimized by implementing the rigorous
mitigation measures and disposed through proper facility.
j Odour Odour from toilets on site for construction staff will be minimized
by ensuring that the toilets are cleaned and maintained on a regular
time basis.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
130
S.No. Impact
DescriptionSummary of findings
k Spillage and
incidents
There is the potential for spillages, incidents, fires and explosions
during construction and operation activities. Procedures and specific
mitigation measures will be implemented to minimize the risk.
2 Socio-Economic Environment
a Employment The project has the potential to provide employment for local
people. During the construction phase 200 to 400 persons will be
employed and during the operation phase, the direct employment of
1000 person and indirect employment of 2500 person.
b Population
Changes
There should be minimum changes to the population dynamics of
the area as it is recommended that all labour for the project is
sourced locally.
c Security and
Social
During the construction phase there is the possibility of social ills
such as crime, the spread of HIV/AIDS etc., To prevent the
manifestation of these problems suitable mitigation will be put in
place.
d Traffic Due to construction activities there is the possibility of disruptions
to traffic flow in the area. With the establishment of the
development there will be increased pressure on the existing road
network. To alleviate the pressure, the road network improvements
will be carried out.
e Safety The safety of the public and construction staff could be
compromised unless adequate safety measures are implemented
f Housing It needs to be ensured that the development captures the housing
demand in the area.
g Energy
Consumption
With the consumption of energy it has been recommended that
renewable and / or alternative energy sources (where possible and
practical and Sustainable) be outlines in the conditions of
Establishment and encouraged to be utilized.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
130
S.No. Impact
DescriptionSummary of findings
k Spillage and
incidents
There is the potential for spillages, incidents, fires and explosions
during construction and operation activities. Procedures and specific
mitigation measures will be implemented to minimize the risk.
2 Socio-Economic Environment
a Employment The project has the potential to provide employment for local
people. During the construction phase 200 to 400 persons will be
employed and during the operation phase, the direct employment of
1000 person and indirect employment of 2500 person.
b Population
Changes
There should be minimum changes to the population dynamics of
the area as it is recommended that all labour for the project is
sourced locally.
c Security and
Social
During the construction phase there is the possibility of social ills
such as crime, the spread of HIV/AIDS etc., To prevent the
manifestation of these problems suitable mitigation will be put in
place.
d Traffic Due to construction activities there is the possibility of disruptions
to traffic flow in the area. With the establishment of the
development there will be increased pressure on the existing road
network. To alleviate the pressure, the road network improvements
will be carried out.
e Safety The safety of the public and construction staff could be
compromised unless adequate safety measures are implemented
f Housing It needs to be ensured that the development captures the housing
demand in the area.
g Energy
Consumption
With the consumption of energy it has been recommended that
renewable and / or alternative energy sources (where possible and
practical and Sustainable) be outlines in the conditions of
Establishment and encouraged to be utilized.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
130
S.No. Impact
DescriptionSummary of findings
k Spillage and
incidents
There is the potential for spillages, incidents, fires and explosions
during construction and operation activities. Procedures and specific
mitigation measures will be implemented to minimize the risk.
2 Socio-Economic Environment
a Employment The project has the potential to provide employment for local
people. During the construction phase 200 to 400 persons will be
employed and during the operation phase, the direct employment of
1000 person and indirect employment of 2500 person.
b Population
Changes
There should be minimum changes to the population dynamics of
the area as it is recommended that all labour for the project is
sourced locally.
c Security and
Social
During the construction phase there is the possibility of social ills
such as crime, the spread of HIV/AIDS etc., To prevent the
manifestation of these problems suitable mitigation will be put in
place.
d Traffic Due to construction activities there is the possibility of disruptions
to traffic flow in the area. With the establishment of the
development there will be increased pressure on the existing road
network. To alleviate the pressure, the road network improvements
will be carried out.
e Safety The safety of the public and construction staff could be
compromised unless adequate safety measures are implemented
f Housing It needs to be ensured that the development captures the housing
demand in the area.
g Energy
Consumption
With the consumption of energy it has been recommended that
renewable and / or alternative energy sources (where possible and
practical and Sustainable) be outlines in the conditions of
Establishment and encouraged to be utilized.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
131
S.No. Impact
DescriptionSummary of findings
h Planning and
Sustainable
Development
With the mixed use nature of the development, together with the
proposed intensities, densities and linkages to the surrounding
adjacent communities, enabling the creation of a sustainable
development.
4.3 Impact Assessment
A number of techniques are available for the assessment of impacts. Each of these
techniques has their own advantages and disadvantages. The selection of any of these
techniques for any particular project depends largely upon the choice of judgment of the
analysis. The technique chosen should be comprehensive, easy to understand,
systematic and flexible.
Table 4.5 Summary Matrix of Predicted Impacts and Mitigation Measures
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
1 Groundwater
Quality
Ground
water
Contaminati
on
Construction phase:
Waste water
generated from
temporary
structures being
developed for
labour.
Accumulation of
water during
excavations.
Minor negative
impact inside
Industrial Parks
premises.
No negative
impact outside
Industrial Parks
site. Short term.
Proper measures will
be implemented.
Wherever possible
care will be taken to
prevent water from
entering excavations.
Operation Phase:
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
131
S.No. Impact
DescriptionSummary of findings
h Planning and
Sustainable
Development
With the mixed use nature of the development, together with the
proposed intensities, densities and linkages to the surrounding
adjacent communities, enabling the creation of a sustainable
development.
4.3 Impact Assessment
A number of techniques are available for the assessment of impacts. Each of these
techniques has their own advantages and disadvantages. The selection of any of these
techniques for any particular project depends largely upon the choice of judgment of the
analysis. The technique chosen should be comprehensive, easy to understand,
systematic and flexible.
Table 4.5 Summary Matrix of Predicted Impacts and Mitigation Measures
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
1 Groundwater
Quality
Ground
water
Contaminati
on
Construction phase:
Waste water
generated from
temporary
structures being
developed for
labour.
Accumulation of
water during
excavations.
Minor negative
impact inside
Industrial Parks
premises.
No negative
impact outside
Industrial Parks
site. Short term.
Proper measures will
be implemented.
Wherever possible
care will be taken to
prevent water from
entering excavations.
Operation Phase:
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
131
S.No. Impact
DescriptionSummary of findings
h Planning and
Sustainable
Development
With the mixed use nature of the development, together with the
proposed intensities, densities and linkages to the surrounding
adjacent communities, enabling the creation of a sustainable
development.
4.3 Impact Assessment
A number of techniques are available for the assessment of impacts. Each of these
techniques has their own advantages and disadvantages. The selection of any of these
techniques for any particular project depends largely upon the choice of judgment of the
analysis. The technique chosen should be comprehensive, easy to understand,
systematic and flexible.
Table 4.5 Summary Matrix of Predicted Impacts and Mitigation Measures
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
1 Groundwater
Quality
Ground
water
Contaminati
on
Construction phase:
Waste water
generated from
temporary
structures being
developed for
labour.
Accumulation of
water during
excavations.
Minor negative
impact inside
Industrial Parks
premises.
No negative
impact outside
Industrial Parks
site. Short term.
Proper measures will
be implemented.
Wherever possible
care will be taken to
prevent water from
entering excavations.
Operation Phase:
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
132
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
Sewage treatment
sludge
disposal on land.
No negative
impact on
ground water
quality
Envisaged. Not
significant.
Individual industries
in Industrial Park will
establish STP/ ETP as
per the requirement in
their respective unit
premises to treat the
sewage / effluent
during operation
phase. Sludge will be
disposed through
nearest authorized
TSDF.
2. Surface Water
Quality
Surface
water
contaminati
on
Construction Phase:
Surface runoff
from site during
construction
activity.
No off site
impact
envisaged as no
surface water
present within
the site impact
zone.
Proper precautions
will be taken care to
prevent the
contamination.
Operation Phase:
Discharge of
domestic
wastewater to
surface water
body.
No off site
impact
envisaged.
Individual industries
in Industrial Park will
establish STP/ ETP as
per the requirement in
their respective unit
premises to treat the
sewage / effluent.
3. Air Quality Dust
Emissions
Construction phase:
Dust and air Minor negative Provision of spraying
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
132
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
Sewage treatment
sludge
disposal on land.
No negative
impact on
ground water
quality
Envisaged. Not
significant.
Individual industries
in Industrial Park will
establish STP/ ETP as
per the requirement in
their respective unit
premises to treat the
sewage / effluent
during operation
phase. Sludge will be
disposed through
nearest authorized
TSDF.
2. Surface Water
Quality
Surface
water
contaminati
on
Construction Phase:
Surface runoff
from site during
construction
activity.
No off site
impact
envisaged as no
surface water
present within
the site impact
zone.
Proper precautions
will be taken care to
prevent the
contamination.
Operation Phase:
Discharge of
domestic
wastewater to
surface water
body.
No off site
impact
envisaged.
Individual industries
in Industrial Park will
establish STP/ ETP as
per the requirement in
their respective unit
premises to treat the
sewage / effluent.
3. Air Quality Dust
Emissions
Construction phase:
Dust and air Minor negative Provision of spraying
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
132
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
Sewage treatment
sludge
disposal on land.
No negative
impact on
ground water
quality
Envisaged. Not
significant.
Individual industries
in Industrial Park will
establish STP/ ETP as
per the requirement in
their respective unit
premises to treat the
sewage / effluent
during operation
phase. Sludge will be
disposed through
nearest authorized
TSDF.
2. Surface Water
Quality
Surface
water
contaminati
on
Construction Phase:
Surface runoff
from site during
construction
activity.
No off site
impact
envisaged as no
surface water
present within
the site impact
zone.
Proper precautions
will be taken care to
prevent the
contamination.
Operation Phase:
Discharge of
domestic
wastewater to
surface water
body.
No off site
impact
envisaged.
Individual industries
in Industrial Park will
establish STP/ ETP as
per the requirement in
their respective unit
premises to treat the
sewage / effluent.
3. Air Quality Dust
Emissions
Construction phase:
Dust and air Minor negative Provision of spraying
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
133
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
emission
particularly due to
the excavation
activities,
movement of
vehicles resulting
in air pollution.
impact Inside
industrial
premises.
No negative
impact outside
industrial
premises site.
Short term.
water to reduce dust
emission on roads.
Excavated topsoil to
be preserved and
reused for
Landscaping.
The amount of
exposed ground and
stockpiles will be
minimized so that
resuspension due to
wind and subsequent
dust fall is prevented.
4 Emissions
of SPM,
SO2, NOx
and CO
Construction
Phase:
Dust and other
exhaust
atmospheric
emissions
generated by
vehicle
movement,
concrete mixing
machinery,
concrete
conveyers, bucket
conveyers, air
blowers,
pneumatic
vibrators,
Minor Negative
impact inside
the premises.
No impact
outside the
premises. Short
term
The construction
workers will be
provided with
appropriate protective
equipments wherever
high particulate
Emission is expected.
It is also
recommended that the
workers will not be
allowed to work over a
long time exposure.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
133
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
emission
particularly due to
the excavation
activities,
movement of
vehicles resulting
in air pollution.
impact Inside
industrial
premises.
No negative
impact outside
industrial
premises site.
Short term.
water to reduce dust
emission on roads.
Excavated topsoil to
be preserved and
reused for
Landscaping.
The amount of
exposed ground and
stockpiles will be
minimized so that
resuspension due to
wind and subsequent
dust fall is prevented.
4 Emissions
of SPM,
SO2, NOx
and CO
Construction
Phase:
Dust and other
exhaust
atmospheric
emissions
generated by
vehicle
movement,
concrete mixing
machinery,
concrete
conveyers, bucket
conveyers, air
blowers,
pneumatic
vibrators,
Minor Negative
impact inside
the premises.
No impact
outside the
premises. Short
term
The construction
workers will be
provided with
appropriate protective
equipments wherever
high particulate
Emission is expected.
It is also
recommended that the
workers will not be
allowed to work over a
long time exposure.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
133
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
emission
particularly due to
the excavation
activities,
movement of
vehicles resulting
in air pollution.
impact Inside
industrial
premises.
No negative
impact outside
industrial
premises site.
Short term.
water to reduce dust
emission on roads.
Excavated topsoil to
be preserved and
reused for
Landscaping.
The amount of
exposed ground and
stockpiles will be
minimized so that
resuspension due to
wind and subsequent
dust fall is prevented.
4 Emissions
of SPM,
SO2, NOx
and CO
Construction
Phase:
Dust and other
exhaust
atmospheric
emissions
generated by
vehicle
movement,
concrete mixing
machinery,
concrete
conveyers, bucket
conveyers, air
blowers,
pneumatic
vibrators,
Minor Negative
impact inside
the premises.
No impact
outside the
premises. Short
term
The construction
workers will be
provided with
appropriate protective
equipments wherever
high particulate
Emission is expected.
It is also
recommended that the
workers will not be
allowed to work over a
long time exposure.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
134
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
mechanical
vibrators and
water tankers
5 Operation Phase:
Vehicular
movement within
the Industrial
Parks.
Dust from
material handling
Emissions of SOX,
NOX, PM from
stacks.
No significant
negative impact.
Minor Negative
impact inside
the premises.
Negative impact
inside the
premises.
Vehicles will be well
maintained and will
have Pollution Under
Check (PUC)
Certificate.
Exhaust from vehicles
will be minimized
with use of fuel-
efficient vehicles.
Precautionary
measures will be
implemented by the
industries.
Water sprays will be
used
Dust extraction and
collection systems will
be established.
Individual Industries
will have proper APC
Measures to control
the Emission rates.
A 10.00 M wide buffer
zone with green belt
will be developed all
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
134
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
mechanical
vibrators and
water tankers
5 Operation Phase:
Vehicular
movement within
the Industrial
Parks.
Dust from
material handling
Emissions of SOX,
NOX, PM from
stacks.
No significant
negative impact.
Minor Negative
impact inside
the premises.
Negative impact
inside the
premises.
Vehicles will be well
maintained and will
have Pollution Under
Check (PUC)
Certificate.
Exhaust from vehicles
will be minimized
with use of fuel-
efficient vehicles.
Precautionary
measures will be
implemented by the
industries.
Water sprays will be
used
Dust extraction and
collection systems will
be established.
Individual Industries
will have proper APC
Measures to control
the Emission rates.
A 10.00 M wide buffer
zone with green belt
will be developed all
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
134
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
mechanical
vibrators and
water tankers
5 Operation Phase:
Vehicular
movement within
the Industrial
Parks.
Dust from
material handling
Emissions of SOX,
NOX, PM from
stacks.
No significant
negative impact.
Minor Negative
impact inside
the premises.
Negative impact
inside the
premises.
Vehicles will be well
maintained and will
have Pollution Under
Check (PUC)
Certificate.
Exhaust from vehicles
will be minimized
with use of fuel-
efficient vehicles.
Precautionary
measures will be
implemented by the
industries.
Water sprays will be
used
Dust extraction and
collection systems will
be established.
Individual Industries
will have proper APC
Measures to control
the Emission rates.
A 10.00 M wide buffer
zone with green belt
will be developed all
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
135
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
along the boundary of
Industrial park in
addition to the green
areas within the park.
6. Noise
Environment
Noise
Emissions
Construction Phase:
Construction
noise mainly due
to excavation,
vehicles
transportation,
operations of
cranes, JCBs,
Etc.,
Minor negative
impact near
noise generation
sources inside
premises.
No impact from
increased noise
levels is
expected from
the project
activities. Also,
there are no
sensitive
receptors
located within
or near the
vicinity of site.
Use of Personal
Protective Equipment
(PPE) like ear muffs
and ear plug during
Construction
activities.
The vehicles used will
be with the standard
limiting noise output.
Wherever this cannot
be achieved, the area
will be earmarked as
high noise level area
requiring use of ear
protection gadget.
7 Operation Phase:
Noise from
vehicles
movement.
Noise during
operations
Not significant
as nearest
receptor would
be at a distance
of 100 m from
the highway.
Use of Personal
Protective Equipment
(PPE) like ear muffs
and ear plug during
activities
8. Land Soil Construction Phase:
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
135
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
along the boundary of
Industrial park in
addition to the green
areas within the park.
6. Noise
Environment
Noise
Emissions
Construction Phase:
Construction
noise mainly due
to excavation,
vehicles
transportation,
operations of
cranes, JCBs,
Etc.,
Minor negative
impact near
noise generation
sources inside
premises.
No impact from
increased noise
levels is
expected from
the project
activities. Also,
there are no
sensitive
receptors
located within
or near the
vicinity of site.
Use of Personal
Protective Equipment
(PPE) like ear muffs
and ear plug during
Construction
activities.
The vehicles used will
be with the standard
limiting noise output.
Wherever this cannot
be achieved, the area
will be earmarked as
high noise level area
requiring use of ear
protection gadget.
7 Operation Phase:
Noise from
vehicles
movement.
Noise during
operations
Not significant
as nearest
receptor would
be at a distance
of 100 m from
the highway.
Use of Personal
Protective Equipment
(PPE) like ear muffs
and ear plug during
activities
8. Land Soil Construction Phase:
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
135
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
along the boundary of
Industrial park in
addition to the green
areas within the park.
6. Noise
Environment
Noise
Emissions
Construction Phase:
Construction
noise mainly due
to excavation,
vehicles
transportation,
operations of
cranes, JCBs,
Etc.,
Minor negative
impact near
noise generation
sources inside
premises.
No impact from
increased noise
levels is
expected from
the project
activities. Also,
there are no
sensitive
receptors
located within
or near the
vicinity of site.
Use of Personal
Protective Equipment
(PPE) like ear muffs
and ear plug during
Construction
activities.
The vehicles used will
be with the standard
limiting noise output.
Wherever this cannot
be achieved, the area
will be earmarked as
high noise level area
requiring use of ear
protection gadget.
7 Operation Phase:
Noise from
vehicles
movement.
Noise during
operations
Not significant
as nearest
receptor would
be at a distance
of 100 m from
the highway.
Use of Personal
Protective Equipment
(PPE) like ear muffs
and ear plug during
activities
8. Land Soil Construction Phase:
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
136
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
environment contaminati
on
Disposal of
construction
Debris
Contamination of
soil due to
leakage of oil
from vehicles
Minor negative
impact inside
Industrial
premises. No
negative impact
outside
Industrial site.
Short term.
The contamination of
soil will be avoided by
suitable management
of oil and fuel.
9 Operation Phase:
Dumping of
municipal solid
waste on land.
Since solid
waste /
hazardous waste
management
practices will be
adopted at
Industrial Park
level. Hence
waste dumping
would not be
allowed.
Thereby it’s Not
Significant.
The solid / hazardous
wastes are sent to
CPCB’s licensed
waste vendors.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
136
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
environment contaminati
on
Disposal of
construction
Debris
Contamination of
soil due to
leakage of oil
from vehicles
Minor negative
impact inside
Industrial
premises. No
negative impact
outside
Industrial site.
Short term.
The contamination of
soil will be avoided by
suitable management
of oil and fuel.
9 Operation Phase:
Dumping of
municipal solid
waste on land.
Since solid
waste /
hazardous waste
management
practices will be
adopted at
Industrial Park
level. Hence
waste dumping
would not be
allowed.
Thereby it’s Not
Significant.
The solid / hazardous
wastes are sent to
CPCB’s licensed
waste vendors.
Rakamcherla – IP Anticipated Impacts and Mitigation Measures
136
Sr.No.
Environmental
Components
Potential
Impacts
Potential Sourceof Impact
Impact
Evaluation
Mitigation Measures
environment contaminati
on
Disposal of
construction
Debris
Contamination of
soil due to
leakage of oil
from vehicles
Minor negative
impact inside
Industrial
premises. No
negative impact
outside
Industrial site.
Short term.
The contamination of
soil will be avoided by
suitable management
of oil and fuel.
9 Operation Phase:
Dumping of
municipal solid
waste on land.
Since solid
waste /
hazardous waste
management
practices will be
adopted at
Industrial Park
level. Hence
waste dumping
would not be
allowed.
Thereby it’s Not
Significant.
The solid / hazardous
wastes are sent to
CPCB’s licensed
waste vendors.
Rakamcherla IP – EIA Analysis of Alternatives
Chapter 5
Analysis of Alternatives
Rakamcherla IP – EIA Analysis of Alternatives
Chapter 5
Analysis of Alternatives
Rakamcherla IP – EIA Analysis of Alternatives
Chapter 5
Analysis of Alternatives
Rakamcherla IP – EIA Analysis of Alternatives
138
5 Analysis of Alternatives
5.1 Introduction
This chapter presents a comparative analysis of various alternatives considered to avoid
or minimize impacts that would be inevitable in technically advanced processes. Several
alternatives are analyzed for avoiding localized environmental impacts & arriving at the
proposed processes. Screening procedure for the alternatives considered is presented in
the following sections. The consideration of alternatives to a proposal is a requirement of
the EIA report. Range of alternatives selected for analysis is - Site alternatives.
Finalization of various options such as construction materials, keeping in view of the
obligatory points and environmental safety aspects and well connectivity to Sea port,
airport, road and rail are considered etc., The Project alternatives without mitigation
measures and with mitigation measures are analyzed before choosing the proposed
alternatives. The objective of this chapter is to highlight some of the salient issues
considered for exercising the alternative options.
5.2 Site Selection
No Alternative site examined. The area has been already finalized by TSIIC and the
Industrial Park is located. The site selected has the SH and Air port connectivity which
will be an added advantage for the business & socio-economic development and
improvement for the district. Good and broad road and railway network connects
Rangareddy district to various parts of the country. Hence TSIIC has proposed the plan
for the Industrial park in this district.
5.3 Alternative I - prepare the site on an as-needed basis
Under this alternative, the Government of Telangana would retain this land until such
time as industries desiring to locate on the site have been identified by a TSIIC. While
allowing more direct control over the specific site tenants, this alternative could result in
piecemeal site preparation inconsistent with a coherent strategy. The environmental
effects of this alternative would be similar to those associated with the preferred
alternative. However, overall quality might suffer because the site would be developed on
Rakamcherla IP – EIA Analysis of Alternatives
138
5 Analysis of Alternatives
5.1 Introduction
This chapter presents a comparative analysis of various alternatives considered to avoid
or minimize impacts that would be inevitable in technically advanced processes. Several
alternatives are analyzed for avoiding localized environmental impacts & arriving at the
proposed processes. Screening procedure for the alternatives considered is presented in
the following sections. The consideration of alternatives to a proposal is a requirement of
the EIA report. Range of alternatives selected for analysis is - Site alternatives.
Finalization of various options such as construction materials, keeping in view of the
obligatory points and environmental safety aspects and well connectivity to Sea port,
airport, road and rail are considered etc., The Project alternatives without mitigation
measures and with mitigation measures are analyzed before choosing the proposed
alternatives. The objective of this chapter is to highlight some of the salient issues
considered for exercising the alternative options.
5.2 Site Selection
No Alternative site examined. The area has been already finalized by TSIIC and the
Industrial Park is located. The site selected has the SH and Air port connectivity which
will be an added advantage for the business & socio-economic development and
improvement for the district. Good and broad road and railway network connects
Rangareddy district to various parts of the country. Hence TSIIC has proposed the plan
for the Industrial park in this district.
5.3 Alternative I - prepare the site on an as-needed basis
Under this alternative, the Government of Telangana would retain this land until such
time as industries desiring to locate on the site have been identified by a TSIIC. While
allowing more direct control over the specific site tenants, this alternative could result in
piecemeal site preparation inconsistent with a coherent strategy. The environmental
effects of this alternative would be similar to those associated with the preferred
alternative. However, overall quality might suffer because the site would be developed on
Rakamcherla IP – EIA Analysis of Alternatives
138
5 Analysis of Alternatives
5.1 Introduction
This chapter presents a comparative analysis of various alternatives considered to avoid
or minimize impacts that would be inevitable in technically advanced processes. Several
alternatives are analyzed for avoiding localized environmental impacts & arriving at the
proposed processes. Screening procedure for the alternatives considered is presented in
the following sections. The consideration of alternatives to a proposal is a requirement of
the EIA report. Range of alternatives selected for analysis is - Site alternatives.
Finalization of various options such as construction materials, keeping in view of the
obligatory points and environmental safety aspects and well connectivity to Sea port,
airport, road and rail are considered etc., The Project alternatives without mitigation
measures and with mitigation measures are analyzed before choosing the proposed
alternatives. The objective of this chapter is to highlight some of the salient issues
considered for exercising the alternative options.
5.2 Site Selection
No Alternative site examined. The area has been already finalized by TSIIC and the
Industrial Park is located. The site selected has the SH and Air port connectivity which
will be an added advantage for the business & socio-economic development and
improvement for the district. Good and broad road and railway network connects
Rangareddy district to various parts of the country. Hence TSIIC has proposed the plan
for the Industrial park in this district.
5.3 Alternative I - prepare the site on an as-needed basis
Under this alternative, the Government of Telangana would retain this land until such
time as industries desiring to locate on the site have been identified by a TSIIC. While
allowing more direct control over the specific site tenants, this alternative could result in
piecemeal site preparation inconsistent with a coherent strategy. The environmental
effects of this alternative would be similar to those associated with the preferred
alternative. However, overall quality might suffer because the site would be developed on
Rakamcherla IP – EIA Analysis of Alternatives
139
a piecemeal basis. This alternative would require greater resources for monitoring and
administrative costs of transferring individual tracts of land instead of handling one large
transfer. This alternative also would restrict the opportunity for self-direction by the local
community.
5.4 Alternative II - Proposed Development
This alternative provides the most economic benefits to the area while requiring fewer
resources. Appropriate mitigation measures would minimize environmental impacts. This
alternative would provide the best overall balance between site preparation and
environmental protection. By restricting development by way of protective covenants,
environmental quality would be maintained. CPCB/ SPCB Standards implemented by
TSIIC would assure a properly planned, quality Industrial Park. This alternative would
yield the best economic benefits and a better potential for community-based and directed
development. This alternative provides the community with more autonomy, with
restrictions limited to guidelines and commitments developed through the review process.
This alternative requires less staff and budgetary resources for implementation and
ensures a more even partnership. Under the proposed Development Alternative, the
project would maximize the utility of the site and thus creating employment. It would
provide jobs for the workers during construction and during operations.
5.5 Future Review and Approval
Potential environmental impact of units will be evaluated on a case-by-case basis when
they set up industrial units and apply for environmental clearance.
Individual units will be required to comply with the following two step process.
The investor must provide facility-specific information, for example, basic
operations, raw materials and their sources, type(s) of product(s), production
volume, and other data, as applicable.
The investor must provide detailed information on the production process, including
projected energy consumption, projected water consumption; potential waste
products generated by the facility, and proposed waste management processes. This
approach is consistent with procedures followed for Industrial Parks by TSIIC.
Rakamcherla IP – EIA Analysis of Alternatives
139
a piecemeal basis. This alternative would require greater resources for monitoring and
administrative costs of transferring individual tracts of land instead of handling one large
transfer. This alternative also would restrict the opportunity for self-direction by the local
community.
5.4 Alternative II - Proposed Development
This alternative provides the most economic benefits to the area while requiring fewer
resources. Appropriate mitigation measures would minimize environmental impacts. This
alternative would provide the best overall balance between site preparation and
environmental protection. By restricting development by way of protective covenants,
environmental quality would be maintained. CPCB/ SPCB Standards implemented by
TSIIC would assure a properly planned, quality Industrial Park. This alternative would
yield the best economic benefits and a better potential for community-based and directed
development. This alternative provides the community with more autonomy, with
restrictions limited to guidelines and commitments developed through the review process.
This alternative requires less staff and budgetary resources for implementation and
ensures a more even partnership. Under the proposed Development Alternative, the
project would maximize the utility of the site and thus creating employment. It would
provide jobs for the workers during construction and during operations.
5.5 Future Review and Approval
Potential environmental impact of units will be evaluated on a case-by-case basis when
they set up industrial units and apply for environmental clearance.
Individual units will be required to comply with the following two step process.
The investor must provide facility-specific information, for example, basic
operations, raw materials and their sources, type(s) of product(s), production
volume, and other data, as applicable.
The investor must provide detailed information on the production process, including
projected energy consumption, projected water consumption; potential waste
products generated by the facility, and proposed waste management processes. This
approach is consistent with procedures followed for Industrial Parks by TSIIC.
Rakamcherla IP – EIA Analysis of Alternatives
139
a piecemeal basis. This alternative would require greater resources for monitoring and
administrative costs of transferring individual tracts of land instead of handling one large
transfer. This alternative also would restrict the opportunity for self-direction by the local
community.
5.4 Alternative II - Proposed Development
This alternative provides the most economic benefits to the area while requiring fewer
resources. Appropriate mitigation measures would minimize environmental impacts. This
alternative would provide the best overall balance between site preparation and
environmental protection. By restricting development by way of protective covenants,
environmental quality would be maintained. CPCB/ SPCB Standards implemented by
TSIIC would assure a properly planned, quality Industrial Park. This alternative would
yield the best economic benefits and a better potential for community-based and directed
development. This alternative provides the community with more autonomy, with
restrictions limited to guidelines and commitments developed through the review process.
This alternative requires less staff and budgetary resources for implementation and
ensures a more even partnership. Under the proposed Development Alternative, the
project would maximize the utility of the site and thus creating employment. It would
provide jobs for the workers during construction and during operations.
5.5 Future Review and Approval
Potential environmental impact of units will be evaluated on a case-by-case basis when
they set up industrial units and apply for environmental clearance.
Individual units will be required to comply with the following two step process.
The investor must provide facility-specific information, for example, basic
operations, raw materials and their sources, type(s) of product(s), production
volume, and other data, as applicable.
The investor must provide detailed information on the production process, including
projected energy consumption, projected water consumption; potential waste
products generated by the facility, and proposed waste management processes. This
approach is consistent with procedures followed for Industrial Parks by TSIIC.
Rakamcherla IP – EIA Analysis of Alternatives
140
In general terms, the following uses will be considered for the proposed site.
Heavy, Light and medium manufacturing, assembling and warehousing for
distribution purposes.
Transportation and service facilities.
Retail sale of food, beverage, and other such convenience items to persons
employed on the property, as long as these items are not offered for sale to the
general public.
Temporary structures incidental to any construction activity.
Utility facilities necessary for the provision of public services and pollution control
facilities associated with site use.
Other industrial uses not listed above, subject to prior review and approval.
Any other purpose other than such as may be expressly approved by TSIIC.
Noise levels in areas of the industrial park used for office buildings shall not exceed
75 dB(A), and in areas to be used for wholesale, industrial, manufacturing and
utilities shall not exceed 80 dB (A).
All land disturbances shall be controlled using best management practices to control
erosion and sedimentation.
All construction in the proposed Industrial Park will comply with the DTCP
building conditions.
5.6 Comparison of Alternatives
5.6.1 Alternative Location
The prospect of alternative locations was considered in the initial phase. The site
under consideration is located in an area that the government has designated for
industrial development. The site has direct access to the main highway leading to
Hyderabad and Vikarabad.
A Market Demand Study was carried out and the following markets were found to be
of good scope in the District of Vikarabad and the given site is being proposed to
develop the potentials in this field. No offsite or other site alternatives have been
investigated due to the fact that this existing large parcel of land is strategically
located adjacent to the SH 4 and which can integrate naturally and positively into this
Rakamcherla IP – EIA Analysis of Alternatives
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In general terms, the following uses will be considered for the proposed site.
Heavy, Light and medium manufacturing, assembling and warehousing for
distribution purposes.
Transportation and service facilities.
Retail sale of food, beverage, and other such convenience items to persons
employed on the property, as long as these items are not offered for sale to the
general public.
Temporary structures incidental to any construction activity.
Utility facilities necessary for the provision of public services and pollution control
facilities associated with site use.
Other industrial uses not listed above, subject to prior review and approval.
Any other purpose other than such as may be expressly approved by TSIIC.
Noise levels in areas of the industrial park used for office buildings shall not exceed
75 dB(A), and in areas to be used for wholesale, industrial, manufacturing and
utilities shall not exceed 80 dB (A).
All land disturbances shall be controlled using best management practices to control
erosion and sedimentation.
All construction in the proposed Industrial Park will comply with the DTCP
building conditions.
5.6 Comparison of Alternatives
5.6.1 Alternative Location
The prospect of alternative locations was considered in the initial phase. The site
under consideration is located in an area that the government has designated for
industrial development. The site has direct access to the main highway leading to
Hyderabad and Vikarabad.
A Market Demand Study was carried out and the following markets were found to be
of good scope in the District of Vikarabad and the given site is being proposed to
develop the potentials in this field. No offsite or other site alternatives have been
investigated due to the fact that this existing large parcel of land is strategically
located adjacent to the SH 4 and which can integrate naturally and positively into this
Rakamcherla IP – EIA Analysis of Alternatives
140
In general terms, the following uses will be considered for the proposed site.
Heavy, Light and medium manufacturing, assembling and warehousing for
distribution purposes.
Transportation and service facilities.
Retail sale of food, beverage, and other such convenience items to persons
employed on the property, as long as these items are not offered for sale to the
general public.
Temporary structures incidental to any construction activity.
Utility facilities necessary for the provision of public services and pollution control
facilities associated with site use.
Other industrial uses not listed above, subject to prior review and approval.
Any other purpose other than such as may be expressly approved by TSIIC.
Noise levels in areas of the industrial park used for office buildings shall not exceed
75 dB(A), and in areas to be used for wholesale, industrial, manufacturing and
utilities shall not exceed 80 dB (A).
All land disturbances shall be controlled using best management practices to control
erosion and sedimentation.
All construction in the proposed Industrial Park will comply with the DTCP
building conditions.
5.6 Comparison of Alternatives
5.6.1 Alternative Location
The prospect of alternative locations was considered in the initial phase. The site
under consideration is located in an area that the government has designated for
industrial development. The site has direct access to the main highway leading to
Hyderabad and Vikarabad.
A Market Demand Study was carried out and the following markets were found to be
of good scope in the District of Vikarabad and the given site is being proposed to
develop the potentials in this field. No offsite or other site alternatives have been
investigated due to the fact that this existing large parcel of land is strategically
located adjacent to the SH 4 and which can integrate naturally and positively into this
Rakamcherla IP – EIA Analysis of Alternatives
141
existing industrial fabric as well as open up opportunities along the northern corridor.
The site is ideally suited to industrial development. The development, as noted above,
has a wide variety of objectives to meet and such objectives would not be possible to
achieve if the development was attempted elsewhere. Alternative sites could require
more infrastructure work, with potentially significant environmental impacts. This
development has been created to help create job opportunities in the rural Areas. The
Development Concept Plan structure is considered sound and critically delivers upon
the strategic objectives that have been identified by TSIIC. Furthermore, it is noted
that TSIIC have spent considerable amount of time and effort in the planning and
contextualization of the development and there is broad acceptance that the
development framework plan is appropriate and will add value to the region and
enable the development to fulfill its objectives and mandate. Therefore, alternative
sites were dropped from further consideration.
5.6.2 Comparison of Alternatives and the Preferred Alternative
The No Action Alternative leaves the site unchanged, ensuring continuation of
existing environmental conditions at the site, while precluding any immediate
opportunity for economic development.
Alternative 2, lease of land to industrial users on an as-needed basis, would allow
greater control over specific industries that could locate at the site. However, this
alternative would result in case-by-case decisions that may ultimately be inconsistent
with an overall industrial development plan. The environmental effects of Alternative
1 would be similar to Alternative 2, but overall site quality might be impaired because
development would proceed without the benefits of an overall site plan. Alternative 2,
the Preferred Alternative, would allow planned, coordinated preparation of the site.
Analyses in this EIA are based on the assumption that all land would be disturbed
under either Alternative 1 or 2. The site has been carefully screened to identify
sensitive resources. Land areas containing sensitive resources will be excluded from
development activities.
5.7 Conclusion
The site considered for the project is most suitable for the project with no objections.
Rakamcherla IP – EIA Analysis of Alternatives
141
existing industrial fabric as well as open up opportunities along the northern corridor.
The site is ideally suited to industrial development. The development, as noted above,
has a wide variety of objectives to meet and such objectives would not be possible to
achieve if the development was attempted elsewhere. Alternative sites could require
more infrastructure work, with potentially significant environmental impacts. This
development has been created to help create job opportunities in the rural Areas. The
Development Concept Plan structure is considered sound and critically delivers upon
the strategic objectives that have been identified by TSIIC. Furthermore, it is noted
that TSIIC have spent considerable amount of time and effort in the planning and
contextualization of the development and there is broad acceptance that the
development framework plan is appropriate and will add value to the region and
enable the development to fulfill its objectives and mandate. Therefore, alternative
sites were dropped from further consideration.
5.6.2 Comparison of Alternatives and the Preferred Alternative
The No Action Alternative leaves the site unchanged, ensuring continuation of
existing environmental conditions at the site, while precluding any immediate
opportunity for economic development.
Alternative 2, lease of land to industrial users on an as-needed basis, would allow
greater control over specific industries that could locate at the site. However, this
alternative would result in case-by-case decisions that may ultimately be inconsistent
with an overall industrial development plan. The environmental effects of Alternative
1 would be similar to Alternative 2, but overall site quality might be impaired because
development would proceed without the benefits of an overall site plan. Alternative 2,
the Preferred Alternative, would allow planned, coordinated preparation of the site.
Analyses in this EIA are based on the assumption that all land would be disturbed
under either Alternative 1 or 2. The site has been carefully screened to identify
sensitive resources. Land areas containing sensitive resources will be excluded from
development activities.
5.7 Conclusion
The site considered for the project is most suitable for the project with no objections.
Rakamcherla IP – EIA Analysis of Alternatives
141
existing industrial fabric as well as open up opportunities along the northern corridor.
The site is ideally suited to industrial development. The development, as noted above,
has a wide variety of objectives to meet and such objectives would not be possible to
achieve if the development was attempted elsewhere. Alternative sites could require
more infrastructure work, with potentially significant environmental impacts. This
development has been created to help create job opportunities in the rural Areas. The
Development Concept Plan structure is considered sound and critically delivers upon
the strategic objectives that have been identified by TSIIC. Furthermore, it is noted
that TSIIC have spent considerable amount of time and effort in the planning and
contextualization of the development and there is broad acceptance that the
development framework plan is appropriate and will add value to the region and
enable the development to fulfill its objectives and mandate. Therefore, alternative
sites were dropped from further consideration.
5.6.2 Comparison of Alternatives and the Preferred Alternative
The No Action Alternative leaves the site unchanged, ensuring continuation of
existing environmental conditions at the site, while precluding any immediate
opportunity for economic development.
Alternative 2, lease of land to industrial users on an as-needed basis, would allow
greater control over specific industries that could locate at the site. However, this
alternative would result in case-by-case decisions that may ultimately be inconsistent
with an overall industrial development plan. The environmental effects of Alternative
1 would be similar to Alternative 2, but overall site quality might be impaired because
development would proceed without the benefits of an overall site plan. Alternative 2,
the Preferred Alternative, would allow planned, coordinated preparation of the site.
Analyses in this EIA are based on the assumption that all land would be disturbed
under either Alternative 1 or 2. The site has been carefully screened to identify
sensitive resources. Land areas containing sensitive resources will be excluded from
development activities.
5.7 Conclusion
The site considered for the project is most suitable for the project with no objections.
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Chapter 6
Environmental Monitoring
Programme
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Chapter 6
Environmental Monitoring
Programme
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Chapter 6
Environmental Monitoring
Programme
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6 Environmental Monitoring Programme
6.1 Introduction
The Environmental Monitoring Program is laid out based on the following definition of
environmental monitoring.
“Environmental effects monitoring is the repetitive and systematic measurement of the
characteristics of environmental components to test specific hypotheses of the effects of
human activity on the environment. Environmental monitoring is undertaken primarily to
determine the environmental effects of human activities, and secondarily to increase
understanding of cause-effect relationships between human activity and environmental
change.”
Being an industrial park, it is necessary to have a comprehensive monitoring program that
covers all the industries in the proposed park so as to mitigate the environmental effects
from these industries and thereby controlling the harmful effects to the environment.
6.2 Environmental Effects Monitoring in EIA
Environmental effects monitoring programs provide the necessary information to:
Verify the accuracy of EIA predictions; and
Determine the effectiveness of measures to mitigate adverse effects of projects
on the environment.
Feedback from environmental monitoring programs may be used to:
Determine whether more or less stringent mitigation measures are needed; and
To improve the predictive capabilities of EIA’s.
Environmental monitoring program is a vital process of any management plan of the
development project. This helps in signaling the potential problems resulting from the
proposed project and will allow for prompt implementation of effective corrective
measures. As the industrial park will possess different types of industries, the industrial
park must give a special care in monitoring the emissions as a whole and each industry
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6 Environmental Monitoring Programme
6.1 Introduction
The Environmental Monitoring Program is laid out based on the following definition of
environmental monitoring.
“Environmental effects monitoring is the repetitive and systematic measurement of the
characteristics of environmental components to test specific hypotheses of the effects of
human activity on the environment. Environmental monitoring is undertaken primarily to
determine the environmental effects of human activities, and secondarily to increase
understanding of cause-effect relationships between human activity and environmental
change.”
Being an industrial park, it is necessary to have a comprehensive monitoring program that
covers all the industries in the proposed park so as to mitigate the environmental effects
from these industries and thereby controlling the harmful effects to the environment.
6.2 Environmental Effects Monitoring in EIA
Environmental effects monitoring programs provide the necessary information to:
Verify the accuracy of EIA predictions; and
Determine the effectiveness of measures to mitigate adverse effects of projects
on the environment.
Feedback from environmental monitoring programs may be used to:
Determine whether more or less stringent mitigation measures are needed; and
To improve the predictive capabilities of EIA’s.
Environmental monitoring program is a vital process of any management plan of the
development project. This helps in signaling the potential problems resulting from the
proposed project and will allow for prompt implementation of effective corrective
measures. As the industrial park will possess different types of industries, the industrial
park must give a special care in monitoring the emissions as a whole and each industry
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6 Environmental Monitoring Programme
6.1 Introduction
The Environmental Monitoring Program is laid out based on the following definition of
environmental monitoring.
“Environmental effects monitoring is the repetitive and systematic measurement of the
characteristics of environmental components to test specific hypotheses of the effects of
human activity on the environment. Environmental monitoring is undertaken primarily to
determine the environmental effects of human activities, and secondarily to increase
understanding of cause-effect relationships between human activity and environmental
change.”
Being an industrial park, it is necessary to have a comprehensive monitoring program that
covers all the industries in the proposed park so as to mitigate the environmental effects
from these industries and thereby controlling the harmful effects to the environment.
6.2 Environmental Effects Monitoring in EIA
Environmental effects monitoring programs provide the necessary information to:
Verify the accuracy of EIA predictions; and
Determine the effectiveness of measures to mitigate adverse effects of projects
on the environment.
Feedback from environmental monitoring programs may be used to:
Determine whether more or less stringent mitigation measures are needed; and
To improve the predictive capabilities of EIA’s.
Environmental monitoring program is a vital process of any management plan of the
development project. This helps in signaling the potential problems resulting from the
proposed project and will allow for prompt implementation of effective corrective
measures. As the industrial park will possess different types of industries, the industrial
park must give a special care in monitoring the emissions as a whole and each industry
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must strictly adhere to the emission standards and analyze accordingly. The
environmental monitoring will be required for the construction and operational phases.
The main objectives of environmental monitoring area:
To assess the changes in environmental conditions,
To monitor the effective implementation of mitigation measures,
Warn significant deteriorations in environmental quality for further prevention
action.
In order to meet the above objectives the following parameters need to be monitored:
Afforestation,
Water Quality and Public Health,
Air and Noise quality,
Soil Conservation,
Solid and Liquid Waste Disposal.
6.3 Environmental Monitoring Program – Construction and Operation
Phase:
The summarized form of post monitoring details is presented for both construction and
operation phase of the project by third party accredited Laboratory in the following
Table. This will be as per the Pollution Control Board Standards and the reports will be
submitted to Telangana State Pollution Control Board (TSPCB) as required in regular
intervals.
Table 6.1 Environmental Monitoring Program for Construction and Operation Phase
S. No Area of MonitoringFrequency of
Sampling
Parameters to be
Analyzed
Construction Phase
1 Ambient air quality at 3 locations
(1 at site, 1 at upwind direction and
1 at downwind direction)
Once in a month All 12 parameters as
given in NAAQS
2 Noise monitoring at 3 Locations Once in a month Noise levels in dB(A)
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must strictly adhere to the emission standards and analyze accordingly. The
environmental monitoring will be required for the construction and operational phases.
The main objectives of environmental monitoring area:
To assess the changes in environmental conditions,
To monitor the effective implementation of mitigation measures,
Warn significant deteriorations in environmental quality for further prevention
action.
In order to meet the above objectives the following parameters need to be monitored:
Afforestation,
Water Quality and Public Health,
Air and Noise quality,
Soil Conservation,
Solid and Liquid Waste Disposal.
6.3 Environmental Monitoring Program – Construction and Operation
Phase:
The summarized form of post monitoring details is presented for both construction and
operation phase of the project by third party accredited Laboratory in the following
Table. This will be as per the Pollution Control Board Standards and the reports will be
submitted to Telangana State Pollution Control Board (TSPCB) as required in regular
intervals.
Table 6.1 Environmental Monitoring Program for Construction and Operation Phase
S. No Area of MonitoringFrequency of
Sampling
Parameters to be
Analyzed
Construction Phase
1 Ambient air quality at 3 locations
(1 at site, 1 at upwind direction and
1 at downwind direction)
Once in a month All 12 parameters as
given in NAAQS
2 Noise monitoring at 3 Locations Once in a month Noise levels in dB(A)
Rakamcherla IP – EIA Environmental Monitoring Programme
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must strictly adhere to the emission standards and analyze accordingly. The
environmental monitoring will be required for the construction and operational phases.
The main objectives of environmental monitoring area:
To assess the changes in environmental conditions,
To monitor the effective implementation of mitigation measures,
Warn significant deteriorations in environmental quality for further prevention
action.
In order to meet the above objectives the following parameters need to be monitored:
Afforestation,
Water Quality and Public Health,
Air and Noise quality,
Soil Conservation,
Solid and Liquid Waste Disposal.
6.3 Environmental Monitoring Program – Construction and Operation
Phase:
The summarized form of post monitoring details is presented for both construction and
operation phase of the project by third party accredited Laboratory in the following
Table. This will be as per the Pollution Control Board Standards and the reports will be
submitted to Telangana State Pollution Control Board (TSPCB) as required in regular
intervals.
Table 6.1 Environmental Monitoring Program for Construction and Operation Phase
S. No Area of MonitoringFrequency of
Sampling
Parameters to be
Analyzed
Construction Phase
1 Ambient air quality at 3 locations
(1 at site, 1 at upwind direction and
1 at downwind direction)
Once in a month All 12 parameters as
given in NAAQS
2 Noise monitoring at 3 Locations Once in a month Noise levels in dB(A)
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S. No Area of MonitoringFrequency of
Sampling
Parameters to be
Analyzed
3 Ground water quality at 4 locations
within and near the project site
Once a season Physicochemical
properties, heavy metals
4 Soil monitoring at 4 locations
within and near the project site
Once a season Physicochemical
properties, Nutrients,
heavy metals
Operation Phase
1 Ambient air quality at 3 locations
(1 at site, 1 at upwind direction and
1 at downwind direction)
Once in a month All 12 parameters as
given in NAAQS
2 Noise monitoring at 3 Locations Once in a month Noise levels in dB(A)
3 Ground water quality at 4 locations
within and near the project site
Once a season Physicochemical
properties, heavy metals
4 Soil monitoring at 4 locations
within and near the project site
Once a season Physicochemical
properties, Nutrients,
heavy metals
5 Effluent analysis (ETP inlet and
outlet)
Once a month pH, Temp, Conductivity,
TSS, TDS, BOD, O&G,
Phenolics, Ammoniacal
Nitrogen, O & G
6 Sewage analysis (STP inlet and
outlet)
Once a month pH, TSS, TDS, O&G,
BOD, COD
7 Sewage Sludge Once a month Heavy metals, nutrients,
Physicochemical
properties
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S. No Area of MonitoringFrequency of
Sampling
Parameters to be
Analyzed
3 Ground water quality at 4 locations
within and near the project site
Once a season Physicochemical
properties, heavy metals
4 Soil monitoring at 4 locations
within and near the project site
Once a season Physicochemical
properties, Nutrients,
heavy metals
Operation Phase
1 Ambient air quality at 3 locations
(1 at site, 1 at upwind direction and
1 at downwind direction)
Once in a month All 12 parameters as
given in NAAQS
2 Noise monitoring at 3 Locations Once in a month Noise levels in dB(A)
3 Ground water quality at 4 locations
within and near the project site
Once a season Physicochemical
properties, heavy metals
4 Soil monitoring at 4 locations
within and near the project site
Once a season Physicochemical
properties, Nutrients,
heavy metals
5 Effluent analysis (ETP inlet and
outlet)
Once a month pH, Temp, Conductivity,
TSS, TDS, BOD, O&G,
Phenolics, Ammoniacal
Nitrogen, O & G
6 Sewage analysis (STP inlet and
outlet)
Once a month pH, TSS, TDS, O&G,
BOD, COD
7 Sewage Sludge Once a month Heavy metals, nutrients,
Physicochemical
properties
Rakamcherla IP – EIA Environmental Monitoring Programme
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S. No Area of MonitoringFrequency of
Sampling
Parameters to be
Analyzed
3 Ground water quality at 4 locations
within and near the project site
Once a season Physicochemical
properties, heavy metals
4 Soil monitoring at 4 locations
within and near the project site
Once a season Physicochemical
properties, Nutrients,
heavy metals
Operation Phase
1 Ambient air quality at 3 locations
(1 at site, 1 at upwind direction and
1 at downwind direction)
Once in a month All 12 parameters as
given in NAAQS
2 Noise monitoring at 3 Locations Once in a month Noise levels in dB(A)
3 Ground water quality at 4 locations
within and near the project site
Once a season Physicochemical
properties, heavy metals
4 Soil monitoring at 4 locations
within and near the project site
Once a season Physicochemical
properties, Nutrients,
heavy metals
5 Effluent analysis (ETP inlet and
outlet)
Once a month pH, Temp, Conductivity,
TSS, TDS, BOD, O&G,
Phenolics, Ammoniacal
Nitrogen, O & G
6 Sewage analysis (STP inlet and
outlet)
Once a month pH, TSS, TDS, O&G,
BOD, COD
7 Sewage Sludge Once a month Heavy metals, nutrients,
Physicochemical
properties
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6.4 Budget for Environmental Monitoring
The budget for Environmental Monitoring through external agency is given in Table 6-2.
Table 6.2 Budgetary Allocation for Environmental Monitoring
S. No Particulars Frequency of monitoring Budget per Year
(Rs.)
1. Air pollution monitoring
Ambient air quality within the
premises
Once in a month 60,000/-
At 1 location in Prevalent Down
Wind Direction
Once in a month 60,000/-
At 1 location in Up Wind
Direction
Once in a month 60,000/-
2. Noise monitoring
At 3 locations within the
premises
Once in a month 1,500/-
3 Ground water quality monitoring
At 4 locations Once a Season 1,20,000/-
4 Soil Quality monitoring
At 4 locations Once a Season 1,20,000/-
Total Budget for Environmental Monitoring through external Agency 4,21,500/-
During operation phase the approximate cost per year for monitoring would be Rs.
4,21,500/-
6.5 Monitoring Methodologies
Monitoring of environmental samples shall be done as per the guidelines provide by
MoEF&CC/ CPCB/ SPCB. The methods conducted or applied shall be approved or
sanctioned by the any recognized body or authority i.e. MoEF&CC/ CPCB/ SPCB. The
list of the used methods and approved /sanctioned methodologies are already provided in
Chapter 3- Description of Environment.
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6.4 Budget for Environmental Monitoring
The budget for Environmental Monitoring through external agency is given in Table 6-2.
Table 6.2 Budgetary Allocation for Environmental Monitoring
S. No Particulars Frequency of monitoring Budget per Year
(Rs.)
1. Air pollution monitoring
Ambient air quality within the
premises
Once in a month 60,000/-
At 1 location in Prevalent Down
Wind Direction
Once in a month 60,000/-
At 1 location in Up Wind
Direction
Once in a month 60,000/-
2. Noise monitoring
At 3 locations within the
premises
Once in a month 1,500/-
3 Ground water quality monitoring
At 4 locations Once a Season 1,20,000/-
4 Soil Quality monitoring
At 4 locations Once a Season 1,20,000/-
Total Budget for Environmental Monitoring through external Agency 4,21,500/-
During operation phase the approximate cost per year for monitoring would be Rs.
4,21,500/-
6.5 Monitoring Methodologies
Monitoring of environmental samples shall be done as per the guidelines provide by
MoEF&CC/ CPCB/ SPCB. The methods conducted or applied shall be approved or
sanctioned by the any recognized body or authority i.e. MoEF&CC/ CPCB/ SPCB. The
list of the used methods and approved /sanctioned methodologies are already provided in
Chapter 3- Description of Environment.
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6.4 Budget for Environmental Monitoring
The budget for Environmental Monitoring through external agency is given in Table 6-2.
Table 6.2 Budgetary Allocation for Environmental Monitoring
S. No Particulars Frequency of monitoring Budget per Year
(Rs.)
1. Air pollution monitoring
Ambient air quality within the
premises
Once in a month 60,000/-
At 1 location in Prevalent Down
Wind Direction
Once in a month 60,000/-
At 1 location in Up Wind
Direction
Once in a month 60,000/-
2. Noise monitoring
At 3 locations within the
premises
Once in a month 1,500/-
3 Ground water quality monitoring
At 4 locations Once a Season 1,20,000/-
4 Soil Quality monitoring
At 4 locations Once a Season 1,20,000/-
Total Budget for Environmental Monitoring through external Agency 4,21,500/-
During operation phase the approximate cost per year for monitoring would be Rs.
4,21,500/-
6.5 Monitoring Methodologies
Monitoring of environmental samples shall be done as per the guidelines provide by
MoEF&CC/ CPCB/ SPCB. The methods conducted or applied shall be approved or
sanctioned by the any recognized body or authority i.e. MoEF&CC/ CPCB/ SPCB. The
list of the used methods and approved /sanctioned methodologies are already provided in
Chapter 3- Description of Environment.
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6.6 Reporting & Documentation
All the necessary reports and documents shall be prepared complying with the statutory
rules & regulations. Proper and due care shall be taken to adhere to the laid down rules
and regulation by the government. Regular and periodic record shall be kept in order to
ensure easier, comparable and brisk review and projection of past, present and future
performances. Also, the management shall ensure to prepare separate records for water,
wastewater, solid waste, air, emission, soil & manure regularly and periodically in order
to provide better and smooth vigilance.
The management shall look into the fact that as soon as the preparation of reports gets
over it shall be forwarded to the concerned authority with due care for the purpose of
reviewing. Adhering to the rules and regulations the management shall ensure that the
outcome of the reports and the conclusions been drawn shall be prepared as per the laid
down regulations and procedures. No breach of any convention shall be availed.
These reports/documents shall be regularly and periodically reviewed and any
changes/discrepancies found in mitigation measures/ operation/ management/ technology
shall be brought into notice instantaneously and all possible corrective actions shall be
taken to match the discrepancies been witnessed.
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6.6 Reporting & Documentation
All the necessary reports and documents shall be prepared complying with the statutory
rules & regulations. Proper and due care shall be taken to adhere to the laid down rules
and regulation by the government. Regular and periodic record shall be kept in order to
ensure easier, comparable and brisk review and projection of past, present and future
performances. Also, the management shall ensure to prepare separate records for water,
wastewater, solid waste, air, emission, soil & manure regularly and periodically in order
to provide better and smooth vigilance.
The management shall look into the fact that as soon as the preparation of reports gets
over it shall be forwarded to the concerned authority with due care for the purpose of
reviewing. Adhering to the rules and regulations the management shall ensure that the
outcome of the reports and the conclusions been drawn shall be prepared as per the laid
down regulations and procedures. No breach of any convention shall be availed.
These reports/documents shall be regularly and periodically reviewed and any
changes/discrepancies found in mitigation measures/ operation/ management/ technology
shall be brought into notice instantaneously and all possible corrective actions shall be
taken to match the discrepancies been witnessed.
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6.6 Reporting & Documentation
All the necessary reports and documents shall be prepared complying with the statutory
rules & regulations. Proper and due care shall be taken to adhere to the laid down rules
and regulation by the government. Regular and periodic record shall be kept in order to
ensure easier, comparable and brisk review and projection of past, present and future
performances. Also, the management shall ensure to prepare separate records for water,
wastewater, solid waste, air, emission, soil & manure regularly and periodically in order
to provide better and smooth vigilance.
The management shall look into the fact that as soon as the preparation of reports gets
over it shall be forwarded to the concerned authority with due care for the purpose of
reviewing. Adhering to the rules and regulations the management shall ensure that the
outcome of the reports and the conclusions been drawn shall be prepared as per the laid
down regulations and procedures. No breach of any convention shall be availed.
These reports/documents shall be regularly and periodically reviewed and any
changes/discrepancies found in mitigation measures/ operation/ management/ technology
shall be brought into notice instantaneously and all possible corrective actions shall be
taken to match the discrepancies been witnessed.
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Chapter 7
Environmental Management Plan
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Chapter 7
Environmental Management Plan
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Chapter 7
Environmental Management Plan
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7 Environmental Management Plan
7.1 Introduction
An Environmental Management system is a tool to regulate, monitor and audit positive
and/or negative environmental impacts by considering day-to-day operations of an
organization. The EMS (Environmental Management System) coexists in an organization
similar to any other management systems such as financial or production management
systems. An environmental management system is a process which is used by an
organization to manage, review, correct, and improve the organization’s approach to
business. An Environment Management System (EMS) manages the impacts of an
organization’s activities on the environment. An EMS defines the environmental
management of any organization in order to monitors and check performance of the
company by incorporating all the sensitivity of individual environmental parameters such
as land, water, air, soil, noise, etc. An EMS is required to locate environmental issues of
an organization in order to integrate and implement better management and its
performance with and along the routine operations of a company. An EMS delivers
environmental quality management of any organization for long and short term planning.
In addition An EMS ensures regular check up to provide quality management system and
take positive steps in case of any diversion with a view to ensure better and enhanced
performance. Overall an EMS provides a well-organized and detailed way to incorporate
environmental considerations into day-to-day operations and it also promotes continual
improvement of the environment and human health.
The Environmental Management Plan is an integrated component of an EMS, which will
identify and address the impacts, where these are adverse in nature, and thereafter design
mitigation measures to manage such impacts in a manner as to conserve environment and
ecology of the area. The Environmental Management Plan gauges the current
environmental scenario of the area and then based on the activities of industries proposed,
to carry out Environmental Impact Assessment. The EMP is most important way to
deliver the objectives established in EMS in order to effective Environmental
management in any organization. Therefore the EMP has been prepared with a view to
ultimately ensure that the adverse impacts are minimized if these cannot be prevented
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7 Environmental Management Plan
7.1 Introduction
An Environmental Management system is a tool to regulate, monitor and audit positive
and/or negative environmental impacts by considering day-to-day operations of an
organization. The EMS (Environmental Management System) coexists in an organization
similar to any other management systems such as financial or production management
systems. An environmental management system is a process which is used by an
organization to manage, review, correct, and improve the organization’s approach to
business. An Environment Management System (EMS) manages the impacts of an
organization’s activities on the environment. An EMS defines the environmental
management of any organization in order to monitors and check performance of the
company by incorporating all the sensitivity of individual environmental parameters such
as land, water, air, soil, noise, etc. An EMS is required to locate environmental issues of
an organization in order to integrate and implement better management and its
performance with and along the routine operations of a company. An EMS delivers
environmental quality management of any organization for long and short term planning.
In addition An EMS ensures regular check up to provide quality management system and
take positive steps in case of any diversion with a view to ensure better and enhanced
performance. Overall an EMS provides a well-organized and detailed way to incorporate
environmental considerations into day-to-day operations and it also promotes continual
improvement of the environment and human health.
The Environmental Management Plan is an integrated component of an EMS, which will
identify and address the impacts, where these are adverse in nature, and thereafter design
mitigation measures to manage such impacts in a manner as to conserve environment and
ecology of the area. The Environmental Management Plan gauges the current
environmental scenario of the area and then based on the activities of industries proposed,
to carry out Environmental Impact Assessment. The EMP is most important way to
deliver the objectives established in EMS in order to effective Environmental
management in any organization. Therefore the EMP has been prepared with a view to
ultimately ensure that the adverse impacts are minimized if these cannot be prevented
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7 Environmental Management Plan
7.1 Introduction
An Environmental Management system is a tool to regulate, monitor and audit positive
and/or negative environmental impacts by considering day-to-day operations of an
organization. The EMS (Environmental Management System) coexists in an organization
similar to any other management systems such as financial or production management
systems. An environmental management system is a process which is used by an
organization to manage, review, correct, and improve the organization’s approach to
business. An Environment Management System (EMS) manages the impacts of an
organization’s activities on the environment. An EMS defines the environmental
management of any organization in order to monitors and check performance of the
company by incorporating all the sensitivity of individual environmental parameters such
as land, water, air, soil, noise, etc. An EMS is required to locate environmental issues of
an organization in order to integrate and implement better management and its
performance with and along the routine operations of a company. An EMS delivers
environmental quality management of any organization for long and short term planning.
In addition An EMS ensures regular check up to provide quality management system and
take positive steps in case of any diversion with a view to ensure better and enhanced
performance. Overall an EMS provides a well-organized and detailed way to incorporate
environmental considerations into day-to-day operations and it also promotes continual
improvement of the environment and human health.
The Environmental Management Plan is an integrated component of an EMS, which will
identify and address the impacts, where these are adverse in nature, and thereafter design
mitigation measures to manage such impacts in a manner as to conserve environment and
ecology of the area. The Environmental Management Plan gauges the current
environmental scenario of the area and then based on the activities of industries proposed,
to carry out Environmental Impact Assessment. The EMP is most important way to
deliver the objectives established in EMS in order to effective Environmental
management in any organization. Therefore the EMP has been prepared with a view to
ultimately ensure that the adverse impacts are minimized if these cannot be prevented
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altogether. Environmental clearance is a statutory requirement for any project of which
EIA has to be prepared and submitted to respective agencies of State and Central level in
line with Environmental Impact Assessment Notification, 2006.
An EMS can assist a company in the following ways:
EMS constantly manages an organization away from constraints imposed by
future regulations, material shortages, community complaints, and other issues
and minimizes environmental liabilities.
EMS reduces operating cost in nearly every case as an EMS reduces operating
inefficiencies, waste reduction and generates energy conservation, other savings.
It has been observed that the typical EMS payback period for any organization is
typically 9 months to 2 years.
EMS improvises the operational process therefore it maximizes the efficient use
of resources.
EMS provides regular feedback on environmental opportunities for continual
improvement.
EMS reduces waste by achieving regular implementation of operational process.
Well structured EMS demonstrates competitiveness within private industry sector.
Well structured EMS helps to achieve good corporate image for any organization.
Symbiotic relationship between experienced consultants and peers support thus
enhancing superior-subordinate relationship.
EMS improves the awareness of environmental concern among employees which
inspire and guide the occupants to achieve better positive environmental
performance.
EMS detailed and planned out requires all the policies which are going to be
implemented to achieve better positive environmental performance.
EMS provides better understanding of the environmental impacts of business
activities.
EMS provides a structured framework for identifying and meeting regulatory
requirements these results in fewer fines and other regulatory complications over
time which would avoid legal risk and potential liabilities.
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altogether. Environmental clearance is a statutory requirement for any project of which
EIA has to be prepared and submitted to respective agencies of State and Central level in
line with Environmental Impact Assessment Notification, 2006.
An EMS can assist a company in the following ways:
EMS constantly manages an organization away from constraints imposed by
future regulations, material shortages, community complaints, and other issues
and minimizes environmental liabilities.
EMS reduces operating cost in nearly every case as an EMS reduces operating
inefficiencies, waste reduction and generates energy conservation, other savings.
It has been observed that the typical EMS payback period for any organization is
typically 9 months to 2 years.
EMS improvises the operational process therefore it maximizes the efficient use
of resources.
EMS provides regular feedback on environmental opportunities for continual
improvement.
EMS reduces waste by achieving regular implementation of operational process.
Well structured EMS demonstrates competitiveness within private industry sector.
Well structured EMS helps to achieve good corporate image for any organization.
Symbiotic relationship between experienced consultants and peers support thus
enhancing superior-subordinate relationship.
EMS improves the awareness of environmental concern among employees which
inspire and guide the occupants to achieve better positive environmental
performance.
EMS detailed and planned out requires all the policies which are going to be
implemented to achieve better positive environmental performance.
EMS provides better understanding of the environmental impacts of business
activities.
EMS provides a structured framework for identifying and meeting regulatory
requirements these results in fewer fines and other regulatory complications over
time which would avoid legal risk and potential liabilities.
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altogether. Environmental clearance is a statutory requirement for any project of which
EIA has to be prepared and submitted to respective agencies of State and Central level in
line with Environmental Impact Assessment Notification, 2006.
An EMS can assist a company in the following ways:
EMS constantly manages an organization away from constraints imposed by
future regulations, material shortages, community complaints, and other issues
and minimizes environmental liabilities.
EMS reduces operating cost in nearly every case as an EMS reduces operating
inefficiencies, waste reduction and generates energy conservation, other savings.
It has been observed that the typical EMS payback period for any organization is
typically 9 months to 2 years.
EMS improvises the operational process therefore it maximizes the efficient use
of resources.
EMS provides regular feedback on environmental opportunities for continual
improvement.
EMS reduces waste by achieving regular implementation of operational process.
Well structured EMS demonstrates competitiveness within private industry sector.
Well structured EMS helps to achieve good corporate image for any organization.
Symbiotic relationship between experienced consultants and peers support thus
enhancing superior-subordinate relationship.
EMS improves the awareness of environmental concern among employees which
inspire and guide the occupants to achieve better positive environmental
performance.
EMS detailed and planned out requires all the policies which are going to be
implemented to achieve better positive environmental performance.
EMS provides better understanding of the environmental impacts of business
activities.
EMS provides a structured framework for identifying and meeting regulatory
requirements these results in fewer fines and other regulatory complications over
time which would avoid legal risk and potential liabilities.
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Improved bond ratings as a formal EMS can demonstrate to the lenders a reduced
risk that results in lower interest rates.
EMS increases profit, improving environmental performance, through more
efficient operations
The EMS system was established in order to achieve environmental quality control
within the private industries sector. It has been proved as a powerful tool hence it is
considered that it can also help public agencies. EMS does not impose new technical
requirements, nor do they act as a substitute for existing regulatory requirements. EMS
provide an exclusive way for an organization to manage its maximum possible
environmental efficiently and to minimize obligations. As a result EMS can improve any
organization overall environmental performance including areas not subject to legal
requirements. It can also help organizations to improve cost efficiency and health and
safety management.
Although the implementation of an EMS is essentially a voluntary initiative, it can also
become an effective tool for governments to protect the environment as it can assist
regulation and outlines the individual’s objectives of environmental protection. For
example, regulatory systems can encourage organizations to use EMS to meet standards,
by providing incentives for strong environmental performance. Likewise, organizations
can use EMS to ensure that their performance is within regulatory requirements, and to
keep ahead of more stringent regulations which might be introduced in the future.
7.2 Environmental Management Plan
An Environmental Management Plan (EMP) can be defined as “an environmental
management tool used to ensure that undue or reasonably avoidable adverse impacts of
the construction, operation and commissioning of a project are prevented; and that the
positive benefits of the projects are enhanced”. EMPs are therefore important tools for
ensuring that the management actions arising from Environmental Impact Assessment
(EIA) processes are clearly defined and implemented through all phases of the project
life-cycle. This plan also helps an organization map its progress toward achieving
continual improvements.
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Improved bond ratings as a formal EMS can demonstrate to the lenders a reduced
risk that results in lower interest rates.
EMS increases profit, improving environmental performance, through more
efficient operations
The EMS system was established in order to achieve environmental quality control
within the private industries sector. It has been proved as a powerful tool hence it is
considered that it can also help public agencies. EMS does not impose new technical
requirements, nor do they act as a substitute for existing regulatory requirements. EMS
provide an exclusive way for an organization to manage its maximum possible
environmental efficiently and to minimize obligations. As a result EMS can improve any
organization overall environmental performance including areas not subject to legal
requirements. It can also help organizations to improve cost efficiency and health and
safety management.
Although the implementation of an EMS is essentially a voluntary initiative, it can also
become an effective tool for governments to protect the environment as it can assist
regulation and outlines the individual’s objectives of environmental protection. For
example, regulatory systems can encourage organizations to use EMS to meet standards,
by providing incentives for strong environmental performance. Likewise, organizations
can use EMS to ensure that their performance is within regulatory requirements, and to
keep ahead of more stringent regulations which might be introduced in the future.
7.2 Environmental Management Plan
An Environmental Management Plan (EMP) can be defined as “an environmental
management tool used to ensure that undue or reasonably avoidable adverse impacts of
the construction, operation and commissioning of a project are prevented; and that the
positive benefits of the projects are enhanced”. EMPs are therefore important tools for
ensuring that the management actions arising from Environmental Impact Assessment
(EIA) processes are clearly defined and implemented through all phases of the project
life-cycle. This plan also helps an organization map its progress toward achieving
continual improvements.
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Improved bond ratings as a formal EMS can demonstrate to the lenders a reduced
risk that results in lower interest rates.
EMS increases profit, improving environmental performance, through more
efficient operations
The EMS system was established in order to achieve environmental quality control
within the private industries sector. It has been proved as a powerful tool hence it is
considered that it can also help public agencies. EMS does not impose new technical
requirements, nor do they act as a substitute for existing regulatory requirements. EMS
provide an exclusive way for an organization to manage its maximum possible
environmental efficiently and to minimize obligations. As a result EMS can improve any
organization overall environmental performance including areas not subject to legal
requirements. It can also help organizations to improve cost efficiency and health and
safety management.
Although the implementation of an EMS is essentially a voluntary initiative, it can also
become an effective tool for governments to protect the environment as it can assist
regulation and outlines the individual’s objectives of environmental protection. For
example, regulatory systems can encourage organizations to use EMS to meet standards,
by providing incentives for strong environmental performance. Likewise, organizations
can use EMS to ensure that their performance is within regulatory requirements, and to
keep ahead of more stringent regulations which might be introduced in the future.
7.2 Environmental Management Plan
An Environmental Management Plan (EMP) can be defined as “an environmental
management tool used to ensure that undue or reasonably avoidable adverse impacts of
the construction, operation and commissioning of a project are prevented; and that the
positive benefits of the projects are enhanced”. EMPs are therefore important tools for
ensuring that the management actions arising from Environmental Impact Assessment
(EIA) processes are clearly defined and implemented through all phases of the project
life-cycle. This plan also helps an organization map its progress toward achieving
continual improvements.
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Each organization has to achieve environmental protection objective and each
organization comprises of individual operations and affairs hence each organization
requires its own unique Environmental Management Plans. The component and content
of individual EMP varies to suite type of organization, the complexity of its processes
and the maturity of the organization in understanding its environmental responsibilities.
The level of detail and length of an EMP will vary depending on the type as well.
An EMP consists of:
Environment Protection Plan to reduce impacts and risks. Issues related to
existing legislation, codes of good engineering practice, proponent commitment,
and similar other tasks are also discussed here.
Summary of Impacts and Risks. These are the actual expected impacts and risks
of the projects, which will need to be managed, monitored, and reported.
Impact Management and Environmental Enhancement to balance adverse impacts
by providing alternate benefits to adversely impacted persons or biophysical
systems.
Environmental Effects Monitoring (monitoring plans).
Impact Reporting.
Environmental Management Planning gives the tools to assess and manage
environmental issues during every phase of the project or operations. In order to do such
the identification of environmental issues is very significant. The EMP provides guide for
the detailed design of specific measures as part of programme and project feasibility
studies. The outcome will minimize the risk of expensive and prolonged environmental
issues. Further it maximizes productivity, resultant performance and goodwill. It provides
a framework through which environmental priorities, responsibilities and risks are
systematically managed. EMPs, which are often a key component of a project's
regulatory filings, provide the basis for assurance that environmental factors will be
carefully managed throughout the project lifecycle.
7.3 Objectives of EMP
To establish the present environmental scenario.
To prepare a detailed action plan for implementation of mitigation measures.
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Each organization has to achieve environmental protection objective and each
organization comprises of individual operations and affairs hence each organization
requires its own unique Environmental Management Plans. The component and content
of individual EMP varies to suite type of organization, the complexity of its processes
and the maturity of the organization in understanding its environmental responsibilities.
The level of detail and length of an EMP will vary depending on the type as well.
An EMP consists of:
Environment Protection Plan to reduce impacts and risks. Issues related to
existing legislation, codes of good engineering practice, proponent commitment,
and similar other tasks are also discussed here.
Summary of Impacts and Risks. These are the actual expected impacts and risks
of the projects, which will need to be managed, monitored, and reported.
Impact Management and Environmental Enhancement to balance adverse impacts
by providing alternate benefits to adversely impacted persons or biophysical
systems.
Environmental Effects Monitoring (monitoring plans).
Impact Reporting.
Environmental Management Planning gives the tools to assess and manage
environmental issues during every phase of the project or operations. In order to do such
the identification of environmental issues is very significant. The EMP provides guide for
the detailed design of specific measures as part of programme and project feasibility
studies. The outcome will minimize the risk of expensive and prolonged environmental
issues. Further it maximizes productivity, resultant performance and goodwill. It provides
a framework through which environmental priorities, responsibilities and risks are
systematically managed. EMPs, which are often a key component of a project's
regulatory filings, provide the basis for assurance that environmental factors will be
carefully managed throughout the project lifecycle.
7.3 Objectives of EMP
To establish the present environmental scenario.
To prepare a detailed action plan for implementation of mitigation measures.
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Each organization has to achieve environmental protection objective and each
organization comprises of individual operations and affairs hence each organization
requires its own unique Environmental Management Plans. The component and content
of individual EMP varies to suite type of organization, the complexity of its processes
and the maturity of the organization in understanding its environmental responsibilities.
The level of detail and length of an EMP will vary depending on the type as well.
An EMP consists of:
Environment Protection Plan to reduce impacts and risks. Issues related to
existing legislation, codes of good engineering practice, proponent commitment,
and similar other tasks are also discussed here.
Summary of Impacts and Risks. These are the actual expected impacts and risks
of the projects, which will need to be managed, monitored, and reported.
Impact Management and Environmental Enhancement to balance adverse impacts
by providing alternate benefits to adversely impacted persons or biophysical
systems.
Environmental Effects Monitoring (monitoring plans).
Impact Reporting.
Environmental Management Planning gives the tools to assess and manage
environmental issues during every phase of the project or operations. In order to do such
the identification of environmental issues is very significant. The EMP provides guide for
the detailed design of specific measures as part of programme and project feasibility
studies. The outcome will minimize the risk of expensive and prolonged environmental
issues. Further it maximizes productivity, resultant performance and goodwill. It provides
a framework through which environmental priorities, responsibilities and risks are
systematically managed. EMPs, which are often a key component of a project's
regulatory filings, provide the basis for assurance that environmental factors will be
carefully managed throughout the project lifecycle.
7.3 Objectives of EMP
To establish the present environmental scenario.
To prepare a detailed action plan for implementation of mitigation measures.
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To suggest preventive and mitigation measures to minimize adverse impact and to
maximize beneficial impacts.
To prepare an afforestation or Greenbelt Development scheme.
To suggest a rain water harvesting scheme and energy conservation actions
To suggest a monitoring programmed to evaluate the effectiveness of mitigation
measures.
To suggest the formation of a core group (Environment Management Cell)
responsible for implementation of environmental control & protective measures
as well as monitoring of such implementation.
To prepare a capital cost estimate and annual recurring cost for Environmental
Management Plan.
7.4 EMP Structure and Organization
This EMP is designed as an overriding document in a hierarchy of control plans, and sets
out the overarching framework of environmental management principles that will be
applied to the project during preconstruction, construction and operation phase of the
project.
The EMP contains guiding environmental principles and procedures for communication,
reporting, training, monitoring and plan review to which all staff, contractors and
subcontractors are required to comply with throughout the preconstruction, construction
and operation phases of the proposed Industrial Park.
The EMP should also be considered as an overall framework document that establishes
the terms of reference for all project environmental and social sub-plans including the
following:
Environmental Supervision Plan (construction);
Environmental Monitoring Plan (construction and operation); and
Social and Health Management Plan (construction and operation).
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To suggest preventive and mitigation measures to minimize adverse impact and to
maximize beneficial impacts.
To prepare an afforestation or Greenbelt Development scheme.
To suggest a rain water harvesting scheme and energy conservation actions
To suggest a monitoring programmed to evaluate the effectiveness of mitigation
measures.
To suggest the formation of a core group (Environment Management Cell)
responsible for implementation of environmental control & protective measures
as well as monitoring of such implementation.
To prepare a capital cost estimate and annual recurring cost for Environmental
Management Plan.
7.4 EMP Structure and Organization
This EMP is designed as an overriding document in a hierarchy of control plans, and sets
out the overarching framework of environmental management principles that will be
applied to the project during preconstruction, construction and operation phase of the
project.
The EMP contains guiding environmental principles and procedures for communication,
reporting, training, monitoring and plan review to which all staff, contractors and
subcontractors are required to comply with throughout the preconstruction, construction
and operation phases of the proposed Industrial Park.
The EMP should also be considered as an overall framework document that establishes
the terms of reference for all project environmental and social sub-plans including the
following:
Environmental Supervision Plan (construction);
Environmental Monitoring Plan (construction and operation); and
Social and Health Management Plan (construction and operation).
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To suggest preventive and mitigation measures to minimize adverse impact and to
maximize beneficial impacts.
To prepare an afforestation or Greenbelt Development scheme.
To suggest a rain water harvesting scheme and energy conservation actions
To suggest a monitoring programmed to evaluate the effectiveness of mitigation
measures.
To suggest the formation of a core group (Environment Management Cell)
responsible for implementation of environmental control & protective measures
as well as monitoring of such implementation.
To prepare a capital cost estimate and annual recurring cost for Environmental
Management Plan.
7.4 EMP Structure and Organization
This EMP is designed as an overriding document in a hierarchy of control plans, and sets
out the overarching framework of environmental management principles that will be
applied to the project during preconstruction, construction and operation phase of the
project.
The EMP contains guiding environmental principles and procedures for communication,
reporting, training, monitoring and plan review to which all staff, contractors and
subcontractors are required to comply with throughout the preconstruction, construction
and operation phases of the proposed Industrial Park.
The EMP should also be considered as an overall framework document that establishes
the terms of reference for all project environmental and social sub-plans including the
following:
Environmental Supervision Plan (construction);
Environmental Monitoring Plan (construction and operation); and
Social and Health Management Plan (construction and operation).
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7.4.1 Roles and Responsibilities for EMP
This section describes the organizational structure and responsibilities for
implementation of the EMP as shown below in Table 7-1.
Table 7.1 Responsibility for EMP implementation
S.No Organization Responsibility
1 TSIIC Overall responsibility for environmental performance.
Decision-maker on applicable policies.
Overall supervisory role during the construction phase.
Overall responsibility for EMP implementation during the
operating phase.
Review reports of the Environmental Monitoring Consultant
(EMC).
Responsible for changes to the EMP as part of an adaptive
approach to environmental and social management.
Submission of six monthly compliance reports to MoEF.
Develop an environmental unit, headed by the Project
Environmental Officer to implement EMP responsibilities.
Oversight, implementation, monitoring and compliance of the
EMP and any approval conditions.
Review of EMP performance and implementation of correction
action, or stop work procedures, in the event of breaches of EMP
conditions, that may lead to serious impacts on local
communities, or affect the reputation of the project.
Report environmental performance of the project directly to
MoEF&CC.
Report on environmental performance also to other government
regulators as required.
Implementation of the Environmental Monitoring Plan during
construction and operation.
Reporting any incidents or non-compliance with the EMP to the
PCB.
Ensuring adequate training and education of all staff involved in
environmental supervision.
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7.4.1 Roles and Responsibilities for EMP
This section describes the organizational structure and responsibilities for
implementation of the EMP as shown below in Table 7-1.
Table 7.1 Responsibility for EMP implementation
S.No Organization Responsibility
1 TSIIC Overall responsibility for environmental performance.
Decision-maker on applicable policies.
Overall supervisory role during the construction phase.
Overall responsibility for EMP implementation during the
operating phase.
Review reports of the Environmental Monitoring Consultant
(EMC).
Responsible for changes to the EMP as part of an adaptive
approach to environmental and social management.
Submission of six monthly compliance reports to MoEF.
Develop an environmental unit, headed by the Project
Environmental Officer to implement EMP responsibilities.
Oversight, implementation, monitoring and compliance of the
EMP and any approval conditions.
Review of EMP performance and implementation of correction
action, or stop work procedures, in the event of breaches of EMP
conditions, that may lead to serious impacts on local
communities, or affect the reputation of the project.
Report environmental performance of the project directly to
MoEF&CC.
Report on environmental performance also to other government
regulators as required.
Implementation of the Environmental Monitoring Plan during
construction and operation.
Reporting any incidents or non-compliance with the EMP to the
PCB.
Ensuring adequate training and education of all staff involved in
environmental supervision.
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7.4.1 Roles and Responsibilities for EMP
This section describes the organizational structure and responsibilities for
implementation of the EMP as shown below in Table 7-1.
Table 7.1 Responsibility for EMP implementation
S.No Organization Responsibility
1 TSIIC Overall responsibility for environmental performance.
Decision-maker on applicable policies.
Overall supervisory role during the construction phase.
Overall responsibility for EMP implementation during the
operating phase.
Review reports of the Environmental Monitoring Consultant
(EMC).
Responsible for changes to the EMP as part of an adaptive
approach to environmental and social management.
Submission of six monthly compliance reports to MoEF.
Develop an environmental unit, headed by the Project
Environmental Officer to implement EMP responsibilities.
Oversight, implementation, monitoring and compliance of the
EMP and any approval conditions.
Review of EMP performance and implementation of correction
action, or stop work procedures, in the event of breaches of EMP
conditions, that may lead to serious impacts on local
communities, or affect the reputation of the project.
Report environmental performance of the project directly to
MoEF&CC.
Report on environmental performance also to other government
regulators as required.
Implementation of the Environmental Monitoring Plan during
construction and operation.
Reporting any incidents or non-compliance with the EMP to the
PCB.
Ensuring adequate training and education of all staff involved in
environmental supervision.
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S.No Organization Responsibility
Making recommendations to the MoEF regarding EMP
performance as part of an overall commitment to continuous
improvement.
2 Individual
Industry
Responsible for maintaining the Air quality levels within the
standards prescribed in NAAQS, 2009.
Regular maintenance & un-interrupted power supply shall be
ensured for continuous operation of Air Pollution Control
Devices.
Maintaining the traffic during the operation and construction
phase of the particular industry.
Specific disaster management plan for the specific industry.
Fire fighting measures specific for the industry.
Obtaining Environmental Clearance/ Consent for Establishment/
Hazardous Waste Authorization for individual industry as
applicable.
Maintain necessary records & documents of Hazardous waste
management/ disposal as per MoEF&CC/ CPCB guidelines.
7.4.2 Environmental Management Cell
In addition to preparing an EMP, it is also necessary to have a permanent
organizational set up to for the effective implementation of environmental
management plan. Environmental Management Cell increases the strength of the
environmental management team to deal with EMP effectively and efficiently. Hence
will create a team consisting of officers from various departments to co-ordinate the
activities concerned with management and implementation of the environmental
control measures. This team will undertake the activity of monitoring the stack
emissions, ambient air quality, noise level, and water quality etc. either
departmentally or by appointing external agencies wherever necessary. Regular
monitoring of environmental parameters will be carried out to find out any
deterioration in environmental quality and also to take corrective steps, if required,
through respective internal departments. The Environmental Management Cell will
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S.No Organization Responsibility
Making recommendations to the MoEF regarding EMP
performance as part of an overall commitment to continuous
improvement.
2 Individual
Industry
Responsible for maintaining the Air quality levels within the
standards prescribed in NAAQS, 2009.
Regular maintenance & un-interrupted power supply shall be
ensured for continuous operation of Air Pollution Control
Devices.
Maintaining the traffic during the operation and construction
phase of the particular industry.
Specific disaster management plan for the specific industry.
Fire fighting measures specific for the industry.
Obtaining Environmental Clearance/ Consent for Establishment/
Hazardous Waste Authorization for individual industry as
applicable.
Maintain necessary records & documents of Hazardous waste
management/ disposal as per MoEF&CC/ CPCB guidelines.
7.4.2 Environmental Management Cell
In addition to preparing an EMP, it is also necessary to have a permanent
organizational set up to for the effective implementation of environmental
management plan. Environmental Management Cell increases the strength of the
environmental management team to deal with EMP effectively and efficiently. Hence
will create a team consisting of officers from various departments to co-ordinate the
activities concerned with management and implementation of the environmental
control measures. This team will undertake the activity of monitoring the stack
emissions, ambient air quality, noise level, and water quality etc. either
departmentally or by appointing external agencies wherever necessary. Regular
monitoring of environmental parameters will be carried out to find out any
deterioration in environmental quality and also to take corrective steps, if required,
through respective internal departments. The Environmental Management Cell will
Rakamcherla IP - EIA Environmental Management Plan
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S.No Organization Responsibility
Making recommendations to the MoEF regarding EMP
performance as part of an overall commitment to continuous
improvement.
2 Individual
Industry
Responsible for maintaining the Air quality levels within the
standards prescribed in NAAQS, 2009.
Regular maintenance & un-interrupted power supply shall be
ensured for continuous operation of Air Pollution Control
Devices.
Maintaining the traffic during the operation and construction
phase of the particular industry.
Specific disaster management plan for the specific industry.
Fire fighting measures specific for the industry.
Obtaining Environmental Clearance/ Consent for Establishment/
Hazardous Waste Authorization for individual industry as
applicable.
Maintain necessary records & documents of Hazardous waste
management/ disposal as per MoEF&CC/ CPCB guidelines.
7.4.2 Environmental Management Cell
In addition to preparing an EMP, it is also necessary to have a permanent
organizational set up to for the effective implementation of environmental
management plan. Environmental Management Cell increases the strength of the
environmental management team to deal with EMP effectively and efficiently. Hence
will create a team consisting of officers from various departments to co-ordinate the
activities concerned with management and implementation of the environmental
control measures. This team will undertake the activity of monitoring the stack
emissions, ambient air quality, noise level, and water quality etc. either
departmentally or by appointing external agencies wherever necessary. Regular
monitoring of environmental parameters will be carried out to find out any
deterioration in environmental quality and also to take corrective steps, if required,
through respective internal departments. The Environmental Management Cell will
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also collect data about health of workers, green belt development etc. Organogram of
the Environmental Management Cell is presented in Figure 7-1 below;
Figure 7.1 Organogram for Environmental Management
7.4.3 Responsibilities of Environment Management Cell
The Environment Management Cell will be responsible for monitoring of the
individual industry’s safety and safety related systems which include;
Checking of safety related operating conditions.
Visual inspection of safety equipment’s.
Preparation of a maintenance plan and documentation of maintenance work
specifying different maintenance intervals and the type of work to be performed.
Other responsibilities of the cell will include;
Submit Annual Environmental statement (in Form–V). This will be submitted
every year before 30th September.
Timely renewal of Consents & Authorization from TSPCB.
CHIEF ENGINEER
GENERAL MANAGER
DEPUTY GENERALMANAGER
ENVIRONMENTALENGINEER
FIELD TECHNICIAN
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also collect data about health of workers, green belt development etc. Organogram of
the Environmental Management Cell is presented in Figure 7-1 below;
Figure 7.1 Organogram for Environmental Management
7.4.3 Responsibilities of Environment Management Cell
The Environment Management Cell will be responsible for monitoring of the
individual industry’s safety and safety related systems which include;
Checking of safety related operating conditions.
Visual inspection of safety equipment’s.
Preparation of a maintenance plan and documentation of maintenance work
specifying different maintenance intervals and the type of work to be performed.
Other responsibilities of the cell will include;
Submit Annual Environmental statement (in Form–V). This will be submitted
every year before 30th September.
Timely renewal of Consents & Authorization from TSPCB.
CHIEF ENGINEER
GENERAL MANAGER
DEPUTY GENERALMANAGER
ENVIRONMENTALENGINEER
FIELD TECHNICIAN
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also collect data about health of workers, green belt development etc. Organogram of
the Environmental Management Cell is presented in Figure 7-1 below;
Figure 7.1 Organogram for Environmental Management
7.4.3 Responsibilities of Environment Management Cell
The Environment Management Cell will be responsible for monitoring of the
individual industry’s safety and safety related systems which include;
Checking of safety related operating conditions.
Visual inspection of safety equipment’s.
Preparation of a maintenance plan and documentation of maintenance work
specifying different maintenance intervals and the type of work to be performed.
Other responsibilities of the cell will include;
Submit Annual Environmental statement (in Form–V). This will be submitted
every year before 30th September.
Timely renewal of Consents & Authorization from TSPCB.
CHIEF ENGINEER
GENERAL MANAGER
DEPUTY GENERALMANAGER
ENVIRONMENTALENGINEER
FIELD TECHNICIAN
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Submitting environmental monitoring report to TSPCB. Data monitored by
the cell will be submitted to TSPCB regularly.
The cell will also take mitigation or corrective measures as required or
suggested by the Board.
Keeping the management updated on regular basis about the conclusions /
results of monitoring activities and proposes measures to improve
environment preservation and protection.
Conducting regular safety drills and training programs to educate employees
on safety practices.
A qualified and experienced officer will be responsible for the identification
of the hazardous conditions and unsafe acts of workers and advise on
corrective actions, organize training programs and provide professional expert
advice on various issues related to occupational safety and health.
Individual Industry Conducting safety and health audits to ensure that
recommended safety and health measures.
7.4.4 Monitoring of Environment
A regular monitoring of environmental parameters like Air, Water, Industrial
Effluent, Noise and Soil as well as performance of pollution control facilities and
safety measures in the plant are important for proper environmental management of
any project.
Therefore, the environment and safety cell will handle monitoring of air and water
pollutants as well as the solid wastes generation as per the requirements of Telangana
State Pollution Control Board (TSPCB) and Central Pollution Control Board (CPCB).
Monitoring of various parameters will be carried out regularly to assess the pollution
level inside the plant and in nearby area. Useful to compile pollution related data for
remedial measures and find out efficiency level of pollution control measures
adopted.
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Submitting environmental monitoring report to TSPCB. Data monitored by
the cell will be submitted to TSPCB regularly.
The cell will also take mitigation or corrective measures as required or
suggested by the Board.
Keeping the management updated on regular basis about the conclusions /
results of monitoring activities and proposes measures to improve
environment preservation and protection.
Conducting regular safety drills and training programs to educate employees
on safety practices.
A qualified and experienced officer will be responsible for the identification
of the hazardous conditions and unsafe acts of workers and advise on
corrective actions, organize training programs and provide professional expert
advice on various issues related to occupational safety and health.
Individual Industry Conducting safety and health audits to ensure that
recommended safety and health measures.
7.4.4 Monitoring of Environment
A regular monitoring of environmental parameters like Air, Water, Industrial
Effluent, Noise and Soil as well as performance of pollution control facilities and
safety measures in the plant are important for proper environmental management of
any project.
Therefore, the environment and safety cell will handle monitoring of air and water
pollutants as well as the solid wastes generation as per the requirements of Telangana
State Pollution Control Board (TSPCB) and Central Pollution Control Board (CPCB).
Monitoring of various parameters will be carried out regularly to assess the pollution
level inside the plant and in nearby area. Useful to compile pollution related data for
remedial measures and find out efficiency level of pollution control measures
adopted.
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Submitting environmental monitoring report to TSPCB. Data monitored by
the cell will be submitted to TSPCB regularly.
The cell will also take mitigation or corrective measures as required or
suggested by the Board.
Keeping the management updated on regular basis about the conclusions /
results of monitoring activities and proposes measures to improve
environment preservation and protection.
Conducting regular safety drills and training programs to educate employees
on safety practices.
A qualified and experienced officer will be responsible for the identification
of the hazardous conditions and unsafe acts of workers and advise on
corrective actions, organize training programs and provide professional expert
advice on various issues related to occupational safety and health.
Individual Industry Conducting safety and health audits to ensure that
recommended safety and health measures.
7.4.4 Monitoring of Environment
A regular monitoring of environmental parameters like Air, Water, Industrial
Effluent, Noise and Soil as well as performance of pollution control facilities and
safety measures in the plant are important for proper environmental management of
any project.
Therefore, the environment and safety cell will handle monitoring of air and water
pollutants as well as the solid wastes generation as per the requirements of Telangana
State Pollution Control Board (TSPCB) and Central Pollution Control Board (CPCB).
Monitoring of various parameters will be carried out regularly to assess the pollution
level inside the plant and in nearby area. Useful to compile pollution related data for
remedial measures and find out efficiency level of pollution control measures
adopted.
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7.5 Corporate Social Responsibility (CSR)
Being a non-profit Organization the CSR component may not be applicable to us. If
applicable we will implement as per the norms.
7.6 Environmental Aspects -Construction Phase
The environmental impacts of the proposed industrial park covering the following aspects
and the measures for controlling the pollution within the values specified by Central
Pollution Control Board (CPCB)/ State Pollution Control Board (SPCB) are briefly
discussed in this chapter. This includes Air pollution, Water pollution, Noise pollution,
Hazardous substance handling and Waste Generation.
Construction and infrastructure development can change the land use for long term which
will create harmful and/or useful impacts to the environment. Therefore construction
activities are one of the most concern tasks for environmental aspects to be considered
during implementation of any project. If the proposed project is going to be beneficial to
environment than the mitigation measures are not necessary. The major concern while
implementing an EMP of an organization incorporates adverse impacts. While
formulating EMP shall be that the people concerned shall have their eyes and mind on the
adverse effects, catch them, make probable estimation of the impact, analyze the impact
and suggest some probable mitigation measures which can either alter or minimize the
negative impact to most considerate extent. For this purpose detailed information shall be
collected viz. details of the components responsible for the occurrence of the negative
impact, activity operation involved which led to occurrence of such impact, construction
material responsible, emissions from construction vehicles, prevailing geographical &
ecological conditions as well as other allied factors which have concern with occurrence
of adverse impacts.
These mentioned details are the most significant part of EMP as they provide core
structure of the EMP. Depending upon the analysis and result of these details proper
mitigation measures are formulated before the finalization of EMP. It has been noticed
that the use of open & undeveloped industrial land for development of the non-polluting
industrial setup will significantly add values in present status by affirmative industrial
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7.5 Corporate Social Responsibility (CSR)
Being a non-profit Organization the CSR component may not be applicable to us. If
applicable we will implement as per the norms.
7.6 Environmental Aspects -Construction Phase
The environmental impacts of the proposed industrial park covering the following aspects
and the measures for controlling the pollution within the values specified by Central
Pollution Control Board (CPCB)/ State Pollution Control Board (SPCB) are briefly
discussed in this chapter. This includes Air pollution, Water pollution, Noise pollution,
Hazardous substance handling and Waste Generation.
Construction and infrastructure development can change the land use for long term which
will create harmful and/or useful impacts to the environment. Therefore construction
activities are one of the most concern tasks for environmental aspects to be considered
during implementation of any project. If the proposed project is going to be beneficial to
environment than the mitigation measures are not necessary. The major concern while
implementing an EMP of an organization incorporates adverse impacts. While
formulating EMP shall be that the people concerned shall have their eyes and mind on the
adverse effects, catch them, make probable estimation of the impact, analyze the impact
and suggest some probable mitigation measures which can either alter or minimize the
negative impact to most considerate extent. For this purpose detailed information shall be
collected viz. details of the components responsible for the occurrence of the negative
impact, activity operation involved which led to occurrence of such impact, construction
material responsible, emissions from construction vehicles, prevailing geographical &
ecological conditions as well as other allied factors which have concern with occurrence
of adverse impacts.
These mentioned details are the most significant part of EMP as they provide core
structure of the EMP. Depending upon the analysis and result of these details proper
mitigation measures are formulated before the finalization of EMP. It has been noticed
that the use of open & undeveloped industrial land for development of the non-polluting
industrial setup will significantly add values in present status by affirmative industrial
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7.5 Corporate Social Responsibility (CSR)
Being a non-profit Organization the CSR component may not be applicable to us. If
applicable we will implement as per the norms.
7.6 Environmental Aspects -Construction Phase
The environmental impacts of the proposed industrial park covering the following aspects
and the measures for controlling the pollution within the values specified by Central
Pollution Control Board (CPCB)/ State Pollution Control Board (SPCB) are briefly
discussed in this chapter. This includes Air pollution, Water pollution, Noise pollution,
Hazardous substance handling and Waste Generation.
Construction and infrastructure development can change the land use for long term which
will create harmful and/or useful impacts to the environment. Therefore construction
activities are one of the most concern tasks for environmental aspects to be considered
during implementation of any project. If the proposed project is going to be beneficial to
environment than the mitigation measures are not necessary. The major concern while
implementing an EMP of an organization incorporates adverse impacts. While
formulating EMP shall be that the people concerned shall have their eyes and mind on the
adverse effects, catch them, make probable estimation of the impact, analyze the impact
and suggest some probable mitigation measures which can either alter or minimize the
negative impact to most considerate extent. For this purpose detailed information shall be
collected viz. details of the components responsible for the occurrence of the negative
impact, activity operation involved which led to occurrence of such impact, construction
material responsible, emissions from construction vehicles, prevailing geographical &
ecological conditions as well as other allied factors which have concern with occurrence
of adverse impacts.
These mentioned details are the most significant part of EMP as they provide core
structure of the EMP. Depending upon the analysis and result of these details proper
mitigation measures are formulated before the finalization of EMP. It has been noticed
that the use of open & undeveloped industrial land for development of the non-polluting
industrial setup will significantly add values in present status by affirmative industrial
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land use. Hence, mitigation measures for land use change are not suggested. However, it
is recommended to develop greenbelt is minimum 33% of total site area in which 14.94%
of open space area (greenbelt) provided by TSIIC and the adequate green belt will be
provided & maintained by individual industries. The major activities considered in the
construction phase while formulating EMP are civil works, mechanical works, machinery
works, transportation works and other related activities.
Majority of impacts would be washed off as the project is situated in better geographical
plain having capacity of natural mitigation of air pollutants due to efficient dispersion in
natural condition. As the main impacts of the construction phase are envisaged in terms
of air pollution only, this natural mitigation would be significantly helpful in elimination
of predicted impacts of the phase.
However the following principal major impacts to the environment are considered for
further planning of mitigation measures:
Release of construction materials and dust into the environment from the
construction site/materials can spoil the surrounding air quality
Improper disposal of construction wastes can damage air, water and land quality
The use of automobiles and machinery during construction can deteriorate the air
quality and generate temporary emission
The use of automobiles and machinery generates Noise pollution from
construction activities
The irregular working hours & traffic, night-working, flood-lighting and
transportation damage the socioeconomic balance of surrounding region
Effects may occur due to the accumulation of the contaminant in water resources
& soil due to uptake of construction material
Short term changes or exploitation of environment is expected during construction
which could affect life style of nearby habitants, health of the human, birds, other
terrestrial animals
Short term heavy construction might cause increase in noise level
Effects on work place condition & human health due to the accidents during the
construction works.
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land use. Hence, mitigation measures for land use change are not suggested. However, it
is recommended to develop greenbelt is minimum 33% of total site area in which 14.94%
of open space area (greenbelt) provided by TSIIC and the adequate green belt will be
provided & maintained by individual industries. The major activities considered in the
construction phase while formulating EMP are civil works, mechanical works, machinery
works, transportation works and other related activities.
Majority of impacts would be washed off as the project is situated in better geographical
plain having capacity of natural mitigation of air pollutants due to efficient dispersion in
natural condition. As the main impacts of the construction phase are envisaged in terms
of air pollution only, this natural mitigation would be significantly helpful in elimination
of predicted impacts of the phase.
However the following principal major impacts to the environment are considered for
further planning of mitigation measures:
Release of construction materials and dust into the environment from the
construction site/materials can spoil the surrounding air quality
Improper disposal of construction wastes can damage air, water and land quality
The use of automobiles and machinery during construction can deteriorate the air
quality and generate temporary emission
The use of automobiles and machinery generates Noise pollution from
construction activities
The irregular working hours & traffic, night-working, flood-lighting and
transportation damage the socioeconomic balance of surrounding region
Effects may occur due to the accumulation of the contaminant in water resources
& soil due to uptake of construction material
Short term changes or exploitation of environment is expected during construction
which could affect life style of nearby habitants, health of the human, birds, other
terrestrial animals
Short term heavy construction might cause increase in noise level
Effects on work place condition & human health due to the accidents during the
construction works.
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land use. Hence, mitigation measures for land use change are not suggested. However, it
is recommended to develop greenbelt is minimum 33% of total site area in which 14.94%
of open space area (greenbelt) provided by TSIIC and the adequate green belt will be
provided & maintained by individual industries. The major activities considered in the
construction phase while formulating EMP are civil works, mechanical works, machinery
works, transportation works and other related activities.
Majority of impacts would be washed off as the project is situated in better geographical
plain having capacity of natural mitigation of air pollutants due to efficient dispersion in
natural condition. As the main impacts of the construction phase are envisaged in terms
of air pollution only, this natural mitigation would be significantly helpful in elimination
of predicted impacts of the phase.
However the following principal major impacts to the environment are considered for
further planning of mitigation measures:
Release of construction materials and dust into the environment from the
construction site/materials can spoil the surrounding air quality
Improper disposal of construction wastes can damage air, water and land quality
The use of automobiles and machinery during construction can deteriorate the air
quality and generate temporary emission
The use of automobiles and machinery generates Noise pollution from
construction activities
The irregular working hours & traffic, night-working, flood-lighting and
transportation damage the socioeconomic balance of surrounding region
Effects may occur due to the accumulation of the contaminant in water resources
& soil due to uptake of construction material
Short term changes or exploitation of environment is expected during construction
which could affect life style of nearby habitants, health of the human, birds, other
terrestrial animals
Short term heavy construction might cause increase in noise level
Effects on work place condition & human health due to the accidents during the
construction works.
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Impacts to avifauna or other carnivores which may prey upon other organisms
affected by the contamination.
Effects on the socio-economic activity due to direct impacts or indirect impacts on
socio-economic activities.
The above mentioned points express that the heavy construction can contaminate Air,
Land, Water and Socioeconomic balance of surrounding region but they can substantially
be minimized or reduced to significant extent by practicing suitable and probable
mitigation methods suggested in the EMP. This explains that the EMP acts a core and
base structure of these issues and shall be formulated with due and ample care and
consideration. A slight negligence in the studying, selecting and implementing process
can prove hazardous to abiotic, biotic, social, and economical or other related attributes
of the environment. Hence, the areas of major focus of EMP shall be concentrated mainly
on operational and maintenance activity of construction phase, deciding proper manner
and route of working of the vehicles in order to avoid accidents and heavy traffic,
providing suitable facilities and effective conditions to avoid occupational hazards and
proper medical aid in case of occurrence of any accident so as to avoid any loss of life.
These were only the negative impacts but one shall never forget that every activity has an
effect followed by a side-effect therefore some of the major beneficial impacts to be
focused are:-
Employment opportunities: recruitment of local labourers
Trading opportunities: procurement of construction materials locally
Clean up operations, landscaping and plantations
Hence, the construction activities can have some moderate temporary and permanent
impacts on site. The construction phase activities could have some impacts on on-site
noise and air quality, land use and ecology. It might also develop minor impacts on on-
site soils, water quantity & quality. The other impacts of construction phase will be small
in magnitude as well as temporary in nature and are expected to wear out gradually once
the construction activity is completed. Further, the major and long term impacts can also
be reduced and minimized by proper and substantial implementation of mitigation
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Impacts to avifauna or other carnivores which may prey upon other organisms
affected by the contamination.
Effects on the socio-economic activity due to direct impacts or indirect impacts on
socio-economic activities.
The above mentioned points express that the heavy construction can contaminate Air,
Land, Water and Socioeconomic balance of surrounding region but they can substantially
be minimized or reduced to significant extent by practicing suitable and probable
mitigation methods suggested in the EMP. This explains that the EMP acts a core and
base structure of these issues and shall be formulated with due and ample care and
consideration. A slight negligence in the studying, selecting and implementing process
can prove hazardous to abiotic, biotic, social, and economical or other related attributes
of the environment. Hence, the areas of major focus of EMP shall be concentrated mainly
on operational and maintenance activity of construction phase, deciding proper manner
and route of working of the vehicles in order to avoid accidents and heavy traffic,
providing suitable facilities and effective conditions to avoid occupational hazards and
proper medical aid in case of occurrence of any accident so as to avoid any loss of life.
These were only the negative impacts but one shall never forget that every activity has an
effect followed by a side-effect therefore some of the major beneficial impacts to be
focused are:-
Employment opportunities: recruitment of local labourers
Trading opportunities: procurement of construction materials locally
Clean up operations, landscaping and plantations
Hence, the construction activities can have some moderate temporary and permanent
impacts on site. The construction phase activities could have some impacts on on-site
noise and air quality, land use and ecology. It might also develop minor impacts on on-
site soils, water quantity & quality. The other impacts of construction phase will be small
in magnitude as well as temporary in nature and are expected to wear out gradually once
the construction activity is completed. Further, the major and long term impacts can also
be reduced and minimized by proper and substantial implementation of mitigation
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Impacts to avifauna or other carnivores which may prey upon other organisms
affected by the contamination.
Effects on the socio-economic activity due to direct impacts or indirect impacts on
socio-economic activities.
The above mentioned points express that the heavy construction can contaminate Air,
Land, Water and Socioeconomic balance of surrounding region but they can substantially
be minimized or reduced to significant extent by practicing suitable and probable
mitigation methods suggested in the EMP. This explains that the EMP acts a core and
base structure of these issues and shall be formulated with due and ample care and
consideration. A slight negligence in the studying, selecting and implementing process
can prove hazardous to abiotic, biotic, social, and economical or other related attributes
of the environment. Hence, the areas of major focus of EMP shall be concentrated mainly
on operational and maintenance activity of construction phase, deciding proper manner
and route of working of the vehicles in order to avoid accidents and heavy traffic,
providing suitable facilities and effective conditions to avoid occupational hazards and
proper medical aid in case of occurrence of any accident so as to avoid any loss of life.
These were only the negative impacts but one shall never forget that every activity has an
effect followed by a side-effect therefore some of the major beneficial impacts to be
focused are:-
Employment opportunities: recruitment of local labourers
Trading opportunities: procurement of construction materials locally
Clean up operations, landscaping and plantations
Hence, the construction activities can have some moderate temporary and permanent
impacts on site. The construction phase activities could have some impacts on on-site
noise and air quality, land use and ecology. It might also develop minor impacts on on-
site soils, water quantity & quality. The other impacts of construction phase will be small
in magnitude as well as temporary in nature and are expected to wear out gradually once
the construction activity is completed. Further, the major and long term impacts can also
be reduced and minimized by proper and substantial implementation of mitigation
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161
measures. In brief during the construction phase following mitigation measures shall be
taken in consideration and implemented to prevent or minimize the respective impacts.
7.6.1 Air Environment
Air environment control and mitigation measures for the project during the
construction phase, includes the following steps, which has to be followed wherever
applicable during the construction and erection phase of the project:
To reduce the dust generation on site wherever & whenever required water
shall be sprinkled on ground or stock pile of excavated soil.
Unused construction material shall be stored immediately at designated area
Emission from the equipments/machineries shall be monitored on regular
basis and possible implementation shall be provided on site
Transport vehicles shall be monitored & maintain regularly to control the
emission quality and fuel consumption
Construction materials would be stored in covered stores or enclosed spaces to
prevent chance of airborne construction materials which can lead to air
pollution of local area.
Regular inspection of construction site shall be carried out to ensure regular
and timely removal of construction debris to the dumping sites or for
recycle/reuse.
Vehicles needs to be used for construction work shall be kept maintained and
highly efficient to keep emissions within the permissible limits
All necessary equipments/machineries shall be in good condition for proper
operation and minimal exhaust/emission.
Provision of necessary PPEs like face mask & eye-glasses are provided to
employees /labors engaged in construction activities.
7.6.2 Water Environment
Mitigation measures to protect the water environment for the project during the
construction phase, includes the following steps, which has to be followed wherever
applicable during the construction and erection phase of the project:
Rakamcherla IP - EIA Environmental Management Plan
161
measures. In brief during the construction phase following mitigation measures shall be
taken in consideration and implemented to prevent or minimize the respective impacts.
7.6.1 Air Environment
Air environment control and mitigation measures for the project during the
construction phase, includes the following steps, which has to be followed wherever
applicable during the construction and erection phase of the project:
To reduce the dust generation on site wherever & whenever required water
shall be sprinkled on ground or stock pile of excavated soil.
Unused construction material shall be stored immediately at designated area
Emission from the equipments/machineries shall be monitored on regular
basis and possible implementation shall be provided on site
Transport vehicles shall be monitored & maintain regularly to control the
emission quality and fuel consumption
Construction materials would be stored in covered stores or enclosed spaces to
prevent chance of airborne construction materials which can lead to air
pollution of local area.
Regular inspection of construction site shall be carried out to ensure regular
and timely removal of construction debris to the dumping sites or for
recycle/reuse.
Vehicles needs to be used for construction work shall be kept maintained and
highly efficient to keep emissions within the permissible limits
All necessary equipments/machineries shall be in good condition for proper
operation and minimal exhaust/emission.
Provision of necessary PPEs like face mask & eye-glasses are provided to
employees /labors engaged in construction activities.
7.6.2 Water Environment
Mitigation measures to protect the water environment for the project during the
construction phase, includes the following steps, which has to be followed wherever
applicable during the construction and erection phase of the project:
Rakamcherla IP - EIA Environmental Management Plan
161
measures. In brief during the construction phase following mitigation measures shall be
taken in consideration and implemented to prevent or minimize the respective impacts.
7.6.1 Air Environment
Air environment control and mitigation measures for the project during the
construction phase, includes the following steps, which has to be followed wherever
applicable during the construction and erection phase of the project:
To reduce the dust generation on site wherever & whenever required water
shall be sprinkled on ground or stock pile of excavated soil.
Unused construction material shall be stored immediately at designated area
Emission from the equipments/machineries shall be monitored on regular
basis and possible implementation shall be provided on site
Transport vehicles shall be monitored & maintain regularly to control the
emission quality and fuel consumption
Construction materials would be stored in covered stores or enclosed spaces to
prevent chance of airborne construction materials which can lead to air
pollution of local area.
Regular inspection of construction site shall be carried out to ensure regular
and timely removal of construction debris to the dumping sites or for
recycle/reuse.
Vehicles needs to be used for construction work shall be kept maintained and
highly efficient to keep emissions within the permissible limits
All necessary equipments/machineries shall be in good condition for proper
operation and minimal exhaust/emission.
Provision of necessary PPEs like face mask & eye-glasses are provided to
employees /labors engaged in construction activities.
7.6.2 Water Environment
Mitigation measures to protect the water environment for the project during the
construction phase, includes the following steps, which has to be followed wherever
applicable during the construction and erection phase of the project:
Rakamcherla IP - EIA Environmental Management Plan
162
Construction material shall be stored at adequate distance from the water
storage in order to prevent any chances of accidental leakage or spillage which
could pollute the water storage
Unused construction material shall be stored with utmost care
Wherever required impervious lining shall be provided to storage premises to
avoid accidental mixing or mixing due to fugitive losses
Runoff from the construction work shall not be unmanaged or haphazard to
prevent entry of contaminant arising from construction work/site.
For runoff water guidance runoff routes shall be provided and managed
properly so the runoff could be collected and treated before release if serious
contamination is observed.
Spillage or leakage of construction material can lead to groundwater
contamination and hence care shall be taken to minimize the chances of the
Spillage or leakage of construction material.
Construction materials like Ready Mix Concrete shall be used to prevent
impacts on water environment.
7.6.3 Noise Environment
Some of the mitigation measures proposed to protect the noise environment during
the construction phase is as follows:
The machineries/equipment used on site shall be of highly maintained so they
do work with optimum efficiency generating less noise pollution
Operation of machineries/equipment causing high noise level shall not be
operated during the night time and all such operations shall be planned for day
time only.
Transportation activities shall not be conducted during the night to avoid high
noise level in nearby villages/locality. Only in case of emergency the
transportation activities shall be allowed in night time.
The vehicles engaged in construction activities & transportation of materials
shall be equipped with the horn of low noise level as recommended by
Rakamcherla IP - EIA Environmental Management Plan
162
Construction material shall be stored at adequate distance from the water
storage in order to prevent any chances of accidental leakage or spillage which
could pollute the water storage
Unused construction material shall be stored with utmost care
Wherever required impervious lining shall be provided to storage premises to
avoid accidental mixing or mixing due to fugitive losses
Runoff from the construction work shall not be unmanaged or haphazard to
prevent entry of contaminant arising from construction work/site.
For runoff water guidance runoff routes shall be provided and managed
properly so the runoff could be collected and treated before release if serious
contamination is observed.
Spillage or leakage of construction material can lead to groundwater
contamination and hence care shall be taken to minimize the chances of the
Spillage or leakage of construction material.
Construction materials like Ready Mix Concrete shall be used to prevent
impacts on water environment.
7.6.3 Noise Environment
Some of the mitigation measures proposed to protect the noise environment during
the construction phase is as follows:
The machineries/equipment used on site shall be of highly maintained so they
do work with optimum efficiency generating less noise pollution
Operation of machineries/equipment causing high noise level shall not be
operated during the night time and all such operations shall be planned for day
time only.
Transportation activities shall not be conducted during the night to avoid high
noise level in nearby villages/locality. Only in case of emergency the
transportation activities shall be allowed in night time.
The vehicles engaged in construction activities & transportation of materials
shall be equipped with the horn of low noise level as recommended by
Rakamcherla IP - EIA Environmental Management Plan
162
Construction material shall be stored at adequate distance from the water
storage in order to prevent any chances of accidental leakage or spillage which
could pollute the water storage
Unused construction material shall be stored with utmost care
Wherever required impervious lining shall be provided to storage premises to
avoid accidental mixing or mixing due to fugitive losses
Runoff from the construction work shall not be unmanaged or haphazard to
prevent entry of contaminant arising from construction work/site.
For runoff water guidance runoff routes shall be provided and managed
properly so the runoff could be collected and treated before release if serious
contamination is observed.
Spillage or leakage of construction material can lead to groundwater
contamination and hence care shall be taken to minimize the chances of the
Spillage or leakage of construction material.
Construction materials like Ready Mix Concrete shall be used to prevent
impacts on water environment.
7.6.3 Noise Environment
Some of the mitigation measures proposed to protect the noise environment during
the construction phase is as follows:
The machineries/equipment used on site shall be of highly maintained so they
do work with optimum efficiency generating less noise pollution
Operation of machineries/equipment causing high noise level shall not be
operated during the night time and all such operations shall be planned for day
time only.
Transportation activities shall not be conducted during the night to avoid high
noise level in nearby villages/locality. Only in case of emergency the
transportation activities shall be allowed in night time.
The vehicles engaged in construction activities & transportation of materials
shall be equipped with the horn of low noise level as recommended by
Rakamcherla IP - EIA Environmental Management Plan
163
RTO/concern authority to avoid impacts on noise level. Further, adequate
silencers must be attached with all vehicles to reduce the noise.
Construction vehicles, equipments & machinery shall be turned off when not
in use.
Proponent shall ensure that the labors engaged in construction site of high
noise area are provided with necessary PPEs.
7.6.4 Social Environment
Construction activities shall be regulated by adequate safety codes and tools
The employees shall be provided with adequate safety equipment
Training must be given for the operational method, problem solving and
safety.
Employees/ contractors/ person associated with construction activities shall be
provided with proper training before starting their works.
During the construction phase proper traffic management shall be maintained
to avoid problems due to the construction activities.
Proper traffic schedule shall be prepared and made available to all transport
officers with adequate guidelines for the traffic management and easy
movement on approach road to national & state high ways.
Employment for the construction work priority shall be given to the local
villagers.
Any emission generation shall be monitored and possible mitigation measures
shall be provided to avoid disturbance in surrounding region.
7.7 Environment Management Plan - Operation Phase
The unit set up is ready for operation of the proposed industrial activities is about to
begin. The construction phase study and analysis includes only the impacts to be caused
to the area while posing construction activities which have envisaged being negligible
even in absence of any major mitigation measures. On the contrary, once the operation
phase gets started it can eventually cause innumerable adverse impacts on the
environment which could be severe. The pollution generates through operational phase
Rakamcherla IP - EIA Environmental Management Plan
163
RTO/concern authority to avoid impacts on noise level. Further, adequate
silencers must be attached with all vehicles to reduce the noise.
Construction vehicles, equipments & machinery shall be turned off when not
in use.
Proponent shall ensure that the labors engaged in construction site of high
noise area are provided with necessary PPEs.
7.6.4 Social Environment
Construction activities shall be regulated by adequate safety codes and tools
The employees shall be provided with adequate safety equipment
Training must be given for the operational method, problem solving and
safety.
Employees/ contractors/ person associated with construction activities shall be
provided with proper training before starting their works.
During the construction phase proper traffic management shall be maintained
to avoid problems due to the construction activities.
Proper traffic schedule shall be prepared and made available to all transport
officers with adequate guidelines for the traffic management and easy
movement on approach road to national & state high ways.
Employment for the construction work priority shall be given to the local
villagers.
Any emission generation shall be monitored and possible mitigation measures
shall be provided to avoid disturbance in surrounding region.
7.7 Environment Management Plan - Operation Phase
The unit set up is ready for operation of the proposed industrial activities is about to
begin. The construction phase study and analysis includes only the impacts to be caused
to the area while posing construction activities which have envisaged being negligible
even in absence of any major mitigation measures. On the contrary, once the operation
phase gets started it can eventually cause innumerable adverse impacts on the
environment which could be severe. The pollution generates through operational phase
Rakamcherla IP - EIA Environmental Management Plan
163
RTO/concern authority to avoid impacts on noise level. Further, adequate
silencers must be attached with all vehicles to reduce the noise.
Construction vehicles, equipments & machinery shall be turned off when not
in use.
Proponent shall ensure that the labors engaged in construction site of high
noise area are provided with necessary PPEs.
7.6.4 Social Environment
Construction activities shall be regulated by adequate safety codes and tools
The employees shall be provided with adequate safety equipment
Training must be given for the operational method, problem solving and
safety.
Employees/ contractors/ person associated with construction activities shall be
provided with proper training before starting their works.
During the construction phase proper traffic management shall be maintained
to avoid problems due to the construction activities.
Proper traffic schedule shall be prepared and made available to all transport
officers with adequate guidelines for the traffic management and easy
movement on approach road to national & state high ways.
Employment for the construction work priority shall be given to the local
villagers.
Any emission generation shall be monitored and possible mitigation measures
shall be provided to avoid disturbance in surrounding region.
7.7 Environment Management Plan - Operation Phase
The unit set up is ready for operation of the proposed industrial activities is about to
begin. The construction phase study and analysis includes only the impacts to be caused
to the area while posing construction activities which have envisaged being negligible
even in absence of any major mitigation measures. On the contrary, once the operation
phase gets started it can eventually cause innumerable adverse impacts on the
environment which could be severe. The pollution generates through operational phase
Rakamcherla IP - EIA Environmental Management Plan
164
can create more damage to the environment as it can get accumulated by the passing
time. The operational set up is mostly of long term establishment therefore it can create
imbalance in ecological balance of the premises.
To minimize the operational phase impacts EMP formulation shall be done keeping in
mind such adverse impacts and accordingly mitigation methods shall be designed in order
to nullify such impacts. Information like operational actions of the habitants, nature of the
substances or components, nature of emission, geological and ecological feature along
with other allied feature shall be systematically collected and analysed. Further, the
production process, utility operations, equipment/machineries/technologies used in
operations, maintenance works, technical & administrative work, etc. shall also be given
due consideration.
EMP planned for the project takes in to account the following mentioned impacts in
general which can be caused in operational and administrative phase:-
Pollution or Runoff generation on site due to waste water discharge
Emissions from the utilities - DG sets causing deterioration in air quality
Unmanaged solid & hazardous waste storage, handling & disposal can lead to
significant adverse impacts on all attributes of environment.
Soil contamination due to mixing of chemicals up on spill or leak during storage,
handling & transport.
Land contamination occurred from the irregular runoff and/or accidental mixing
Inappropriate use of land for dumping of garbage & disposal of untreated sewage
from the domestic activities of employees.
Fugitive losses and transfer losses create emission of airborne, wastewater and
solid particles.
Inappropriate storage or handling method can contaminate environment, loss of
raw material/coal dust and could affect the health & safety of the region.
Less effective and poorly managed operations could lead to excessive use of
power and groundwater.
Excessive use of groundwater can lowered the ground water level as well as
increases the possibility of ground water contamination.
Rakamcherla IP - EIA Environmental Management Plan
164
can create more damage to the environment as it can get accumulated by the passing
time. The operational set up is mostly of long term establishment therefore it can create
imbalance in ecological balance of the premises.
To minimize the operational phase impacts EMP formulation shall be done keeping in
mind such adverse impacts and accordingly mitigation methods shall be designed in order
to nullify such impacts. Information like operational actions of the habitants, nature of the
substances or components, nature of emission, geological and ecological feature along
with other allied feature shall be systematically collected and analysed. Further, the
production process, utility operations, equipment/machineries/technologies used in
operations, maintenance works, technical & administrative work, etc. shall also be given
due consideration.
EMP planned for the project takes in to account the following mentioned impacts in
general which can be caused in operational and administrative phase:-
Pollution or Runoff generation on site due to waste water discharge
Emissions from the utilities - DG sets causing deterioration in air quality
Unmanaged solid & hazardous waste storage, handling & disposal can lead to
significant adverse impacts on all attributes of environment.
Soil contamination due to mixing of chemicals up on spill or leak during storage,
handling & transport.
Land contamination occurred from the irregular runoff and/or accidental mixing
Inappropriate use of land for dumping of garbage & disposal of untreated sewage
from the domestic activities of employees.
Fugitive losses and transfer losses create emission of airborne, wastewater and
solid particles.
Inappropriate storage or handling method can contaminate environment, loss of
raw material/coal dust and could affect the health & safety of the region.
Less effective and poorly managed operations could lead to excessive use of
power and groundwater.
Excessive use of groundwater can lowered the ground water level as well as
increases the possibility of ground water contamination.
Rakamcherla IP - EIA Environmental Management Plan
164
can create more damage to the environment as it can get accumulated by the passing
time. The operational set up is mostly of long term establishment therefore it can create
imbalance in ecological balance of the premises.
To minimize the operational phase impacts EMP formulation shall be done keeping in
mind such adverse impacts and accordingly mitigation methods shall be designed in order
to nullify such impacts. Information like operational actions of the habitants, nature of the
substances or components, nature of emission, geological and ecological feature along
with other allied feature shall be systematically collected and analysed. Further, the
production process, utility operations, equipment/machineries/technologies used in
operations, maintenance works, technical & administrative work, etc. shall also be given
due consideration.
EMP planned for the project takes in to account the following mentioned impacts in
general which can be caused in operational and administrative phase:-
Pollution or Runoff generation on site due to waste water discharge
Emissions from the utilities - DG sets causing deterioration in air quality
Unmanaged solid & hazardous waste storage, handling & disposal can lead to
significant adverse impacts on all attributes of environment.
Soil contamination due to mixing of chemicals up on spill or leak during storage,
handling & transport.
Land contamination occurred from the irregular runoff and/or accidental mixing
Inappropriate use of land for dumping of garbage & disposal of untreated sewage
from the domestic activities of employees.
Fugitive losses and transfer losses create emission of airborne, wastewater and
solid particles.
Inappropriate storage or handling method can contaminate environment, loss of
raw material/coal dust and could affect the health & safety of the region.
Less effective and poorly managed operations could lead to excessive use of
power and groundwater.
Excessive use of groundwater can lowered the ground water level as well as
increases the possibility of ground water contamination.
Rakamcherla IP - EIA Environmental Management Plan
165
Noise generation from utilities and other moving machineries/equipments as well
as operational & maintenance area can lead to adverse effects on occupational
health.
Transportation of vehicles may have considerable impacts on noise level of the
villages falling under transport route.
Damage to surrounding area due to impacts on other environmental attributes of
operations.
Inefficiently managed plant produce impacts on the human health & ecology are
also associated with some workplace accident, hazards and risk.
Socio-economic aspect shall be benefited due to increase in employment & other
opportunities for improvement of local economy.
Issues related with all the major and significant impacts of operational phase shall be
combated by appropriate tools and methods suggested in the EMP because if neglected or
diverted can prove quiet hazardous to overall environment. The impacts even though
seems to be magnificent and colossal but implementation of proper and suitable and
planned operational procedures and maintenance activities can reduce it to magnificent
and maximum possible extent. Proper suggestive measures for operation activities shall
be implied and implemented followed by adequate and suitable measures for proper
treatment of waste deposits. Besides, provisions shall be made for synchronized and
mannered working to ensure effective and efficient operation of work with highest
possible level of occupational safety. Keeping all these in mind following mitigation
measures shall be taken into consideration so that the effects are brought down to
maximum possible extent.
7.7.1 Air Environment
Implementation of following mitigation measures is suggested to prevent air pollution
due to emissions:
Proper Storage area shall be designated for feed and finished products to
prevent any kind of fugitive emission from storage area.
Rakamcherla IP - EIA Environmental Management Plan
165
Noise generation from utilities and other moving machineries/equipments as well
as operational & maintenance area can lead to adverse effects on occupational
health.
Transportation of vehicles may have considerable impacts on noise level of the
villages falling under transport route.
Damage to surrounding area due to impacts on other environmental attributes of
operations.
Inefficiently managed plant produce impacts on the human health & ecology are
also associated with some workplace accident, hazards and risk.
Socio-economic aspect shall be benefited due to increase in employment & other
opportunities for improvement of local economy.
Issues related with all the major and significant impacts of operational phase shall be
combated by appropriate tools and methods suggested in the EMP because if neglected or
diverted can prove quiet hazardous to overall environment. The impacts even though
seems to be magnificent and colossal but implementation of proper and suitable and
planned operational procedures and maintenance activities can reduce it to magnificent
and maximum possible extent. Proper suggestive measures for operation activities shall
be implied and implemented followed by adequate and suitable measures for proper
treatment of waste deposits. Besides, provisions shall be made for synchronized and
mannered working to ensure effective and efficient operation of work with highest
possible level of occupational safety. Keeping all these in mind following mitigation
measures shall be taken into consideration so that the effects are brought down to
maximum possible extent.
7.7.1 Air Environment
Implementation of following mitigation measures is suggested to prevent air pollution
due to emissions:
Proper Storage area shall be designated for feed and finished products to
prevent any kind of fugitive emission from storage area.
Rakamcherla IP - EIA Environmental Management Plan
165
Noise generation from utilities and other moving machineries/equipments as well
as operational & maintenance area can lead to adverse effects on occupational
health.
Transportation of vehicles may have considerable impacts on noise level of the
villages falling under transport route.
Damage to surrounding area due to impacts on other environmental attributes of
operations.
Inefficiently managed plant produce impacts on the human health & ecology are
also associated with some workplace accident, hazards and risk.
Socio-economic aspect shall be benefited due to increase in employment & other
opportunities for improvement of local economy.
Issues related with all the major and significant impacts of operational phase shall be
combated by appropriate tools and methods suggested in the EMP because if neglected or
diverted can prove quiet hazardous to overall environment. The impacts even though
seems to be magnificent and colossal but implementation of proper and suitable and
planned operational procedures and maintenance activities can reduce it to magnificent
and maximum possible extent. Proper suggestive measures for operation activities shall
be implied and implemented followed by adequate and suitable measures for proper
treatment of waste deposits. Besides, provisions shall be made for synchronized and
mannered working to ensure effective and efficient operation of work with highest
possible level of occupational safety. Keeping all these in mind following mitigation
measures shall be taken into consideration so that the effects are brought down to
maximum possible extent.
7.7.1 Air Environment
Implementation of following mitigation measures is suggested to prevent air pollution
due to emissions:
Proper Storage area shall be designated for feed and finished products to
prevent any kind of fugitive emission from storage area.
Rakamcherla IP - EIA Environmental Management Plan
166
Adequate methods & facilities for handling shall be developed &
implemented to prevent contamination of air due to the chemicals used.
Upmost priority shall be given to regular maintenance & un-interrupted
operation of Air pollution control devices.
Monitoring of emission as per Environmental Monitoring Plan and records
shall be maintain for further review & improvement in EMP as well as Air
Pollution Control Activities/ Technologies.
Emission level shall be maintained below permissible limits prescribed by
concern environmental authority.
Greenbelt shall be provided for 33% of total land of the proposed project. In
which 14.94% of open space area used for greenbelt and the remaining
adequate green belt will be provided and maintained by individual industries
in their premises.
Greenbelt development shall be maintained and grown appropriately as it will
help to improve air environment of the premises.
Greenbelt development program shall be monitored to develop healthy &
adequate vegetation in the premise as per CPCB norms.
Regular Monitoring & Analysis of Emission, Ambient Air for Safety &
Environment Management to prevent air contamination/pollution & hazards
due to air contamination.
Ambient Air Quality Monitoring shall be done at least at three locations in
premises and preferred angle between the locations shall be 120 degree. The
monitoring shall be done at least once a month.
The record of the monitoring programs & measured quality shall be
maintained regularly.
Annual Environmental Audit shall be conducted as per TSPCB guidelines and
the measures/actions suggested in the audit report for prevention pollution
shall be strictly implemented to comply with applicable environmental norms.
Work place monitoring for PM level in the ambient air shall be scheduled for
regular monitoring to eliminate any case of effects on occupation health of
workers/personnel by individual industry.
Rakamcherla IP - EIA Environmental Management Plan
166
Adequate methods & facilities for handling shall be developed &
implemented to prevent contamination of air due to the chemicals used.
Upmost priority shall be given to regular maintenance & un-interrupted
operation of Air pollution control devices.
Monitoring of emission as per Environmental Monitoring Plan and records
shall be maintain for further review & improvement in EMP as well as Air
Pollution Control Activities/ Technologies.
Emission level shall be maintained below permissible limits prescribed by
concern environmental authority.
Greenbelt shall be provided for 33% of total land of the proposed project. In
which 14.94% of open space area used for greenbelt and the remaining
adequate green belt will be provided and maintained by individual industries
in their premises.
Greenbelt development shall be maintained and grown appropriately as it will
help to improve air environment of the premises.
Greenbelt development program shall be monitored to develop healthy &
adequate vegetation in the premise as per CPCB norms.
Regular Monitoring & Analysis of Emission, Ambient Air for Safety &
Environment Management to prevent air contamination/pollution & hazards
due to air contamination.
Ambient Air Quality Monitoring shall be done at least at three locations in
premises and preferred angle between the locations shall be 120 degree. The
monitoring shall be done at least once a month.
The record of the monitoring programs & measured quality shall be
maintained regularly.
Annual Environmental Audit shall be conducted as per TSPCB guidelines and
the measures/actions suggested in the audit report for prevention pollution
shall be strictly implemented to comply with applicable environmental norms.
Work place monitoring for PM level in the ambient air shall be scheduled for
regular monitoring to eliminate any case of effects on occupation health of
workers/personnel by individual industry.
Rakamcherla IP - EIA Environmental Management Plan
166
Adequate methods & facilities for handling shall be developed &
implemented to prevent contamination of air due to the chemicals used.
Upmost priority shall be given to regular maintenance & un-interrupted
operation of Air pollution control devices.
Monitoring of emission as per Environmental Monitoring Plan and records
shall be maintain for further review & improvement in EMP as well as Air
Pollution Control Activities/ Technologies.
Emission level shall be maintained below permissible limits prescribed by
concern environmental authority.
Greenbelt shall be provided for 33% of total land of the proposed project. In
which 14.94% of open space area used for greenbelt and the remaining
adequate green belt will be provided and maintained by individual industries
in their premises.
Greenbelt development shall be maintained and grown appropriately as it will
help to improve air environment of the premises.
Greenbelt development program shall be monitored to develop healthy &
adequate vegetation in the premise as per CPCB norms.
Regular Monitoring & Analysis of Emission, Ambient Air for Safety &
Environment Management to prevent air contamination/pollution & hazards
due to air contamination.
Ambient Air Quality Monitoring shall be done at least at three locations in
premises and preferred angle between the locations shall be 120 degree. The
monitoring shall be done at least once a month.
The record of the monitoring programs & measured quality shall be
maintained regularly.
Annual Environmental Audit shall be conducted as per TSPCB guidelines and
the measures/actions suggested in the audit report for prevention pollution
shall be strictly implemented to comply with applicable environmental norms.
Work place monitoring for PM level in the ambient air shall be scheduled for
regular monitoring to eliminate any case of effects on occupation health of
workers/personnel by individual industry.
Rakamcherla IP - EIA Environmental Management Plan
167
Individual industries shall take timely action for necessary maintenance to
ensure adequate & efficient operations as well as good condition of the APC
Devices & stacks.
Individual industries shall follow necessary provisions/guidelines related to
APC & stack installation.
Steel Re-Rolling and other similar activities in the industries will take proper mitigationmeasures for the following:
The emissions from induction furnace include suspended particulate matter,
Oxides of Sulphur, Oxides of Nitrogen, and CO2. Emissions will be more during
charging of material to furnace.
Slag Handling: Slag generated from the induction furnace needs to be disposed
off. A few rolling mills are grinding the slag and recovering iron content in it
through magnetic separation. During this process, dust will be generated and
proper dust collection system will be implemented by Individual industries.
Re-Heating furnace: Various fuels are used in re-heating furnace. Pulverized
coals, producer gas, furnace oil, are few to mention. In case of coal based furnace,
large quantities of emissions are generated where the stacks with proper Air
pollution control measures has to be proposed by individual industries.
Fly ash handling: In case of coal based units and producer gas based units, the ash
handling creates dust emissions and for that adequate control measures will be
implemented.
Air emissions from D.G sets are presently governed by adequate stack height to
be provided on the D.G. sets depending on its capacity. Emission Regulation part-
IV published by CPCB has given the formula for working out the stack height.
For regulation of stack emissions of D.G sets of capacity more than 0.80 MW,
separate standards are laid down vide GSR 489 (E) dated 9.07.2002 which needs
to be complied with.
7.7.2 Water Environment
Implementation of following mitigation measures is suggested to prevent water
pollution;
Rakamcherla IP - EIA Environmental Management Plan
167
Individual industries shall take timely action for necessary maintenance to
ensure adequate & efficient operations as well as good condition of the APC
Devices & stacks.
Individual industries shall follow necessary provisions/guidelines related to
APC & stack installation.
Steel Re-Rolling and other similar activities in the industries will take proper mitigationmeasures for the following:
The emissions from induction furnace include suspended particulate matter,
Oxides of Sulphur, Oxides of Nitrogen, and CO2. Emissions will be more during
charging of material to furnace.
Slag Handling: Slag generated from the induction furnace needs to be disposed
off. A few rolling mills are grinding the slag and recovering iron content in it
through magnetic separation. During this process, dust will be generated and
proper dust collection system will be implemented by Individual industries.
Re-Heating furnace: Various fuels are used in re-heating furnace. Pulverized
coals, producer gas, furnace oil, are few to mention. In case of coal based furnace,
large quantities of emissions are generated where the stacks with proper Air
pollution control measures has to be proposed by individual industries.
Fly ash handling: In case of coal based units and producer gas based units, the ash
handling creates dust emissions and for that adequate control measures will be
implemented.
Air emissions from D.G sets are presently governed by adequate stack height to
be provided on the D.G. sets depending on its capacity. Emission Regulation part-
IV published by CPCB has given the formula for working out the stack height.
For regulation of stack emissions of D.G sets of capacity more than 0.80 MW,
separate standards are laid down vide GSR 489 (E) dated 9.07.2002 which needs
to be complied with.
7.7.2 Water Environment
Implementation of following mitigation measures is suggested to prevent water
pollution;
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Individual industries shall take timely action for necessary maintenance to
ensure adequate & efficient operations as well as good condition of the APC
Devices & stacks.
Individual industries shall follow necessary provisions/guidelines related to
APC & stack installation.
Steel Re-Rolling and other similar activities in the industries will take proper mitigationmeasures for the following:
The emissions from induction furnace include suspended particulate matter,
Oxides of Sulphur, Oxides of Nitrogen, and CO2. Emissions will be more during
charging of material to furnace.
Slag Handling: Slag generated from the induction furnace needs to be disposed
off. A few rolling mills are grinding the slag and recovering iron content in it
through magnetic separation. During this process, dust will be generated and
proper dust collection system will be implemented by Individual industries.
Re-Heating furnace: Various fuels are used in re-heating furnace. Pulverized
coals, producer gas, furnace oil, are few to mention. In case of coal based furnace,
large quantities of emissions are generated where the stacks with proper Air
pollution control measures has to be proposed by individual industries.
Fly ash handling: In case of coal based units and producer gas based units, the ash
handling creates dust emissions and for that adequate control measures will be
implemented.
Air emissions from D.G sets are presently governed by adequate stack height to
be provided on the D.G. sets depending on its capacity. Emission Regulation part-
IV published by CPCB has given the formula for working out the stack height.
For regulation of stack emissions of D.G sets of capacity more than 0.80 MW,
separate standards are laid down vide GSR 489 (E) dated 9.07.2002 which needs
to be complied with.
7.7.2 Water Environment
Implementation of following mitigation measures is suggested to prevent water
pollution;
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The operational set up shall be provided with upmost accuracy in order to
produce most efficient system which will use only necessary amount of water.
The operational set up shall be kept leak proof at all the times to reduce
consumption of water.
The raw effluents from operation/process shall be treated by Individual
Industry in their ETP for efficient treatment to meet the prescribed norms by
CPCB.
The treated wastewater from individual industries after confirming the
prescribed norms will be reused for gardening in their premises.
To conserve the water, wastage of water shall be prevented by adequate water
management practices as well as regular maintenance of pipelines & tanks etc.
to prevent leak & spill.
Rainwater harvesting program shall also be implemented for conservation of
water.
Proponent shall attempt to reduce the losses by continuous inspection, R&D
and implementation of necessary adequate management practices.
Steel Re-Rolling and other similar activities in the industries will take proper mitigationmeasures for the following:
Rolling Mill: Rolling mill generates waste water used for cooling purpose. As
heavier suspended solids settles down easily this water will be recycled back
after removing mill waste.
Mill waste: The mill waste is primarily iron waste and having market value.
The sludge generated from cooling water, settling tanks should be handled
properly to avoid land contamination.
Utilities The steel Re-rolling mills units may have utilities such as raw water
treatment system, diesel generator(s), boilers (s), cooling tower(s), laboratory,
workshop(s), fuel storage facilities, waste water treatment plant,
administrative block, canteen etc. The pollution potential from these
operations should be assessed and suitable mitigation measures should be
planned.
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The operational set up shall be provided with upmost accuracy in order to
produce most efficient system which will use only necessary amount of water.
The operational set up shall be kept leak proof at all the times to reduce
consumption of water.
The raw effluents from operation/process shall be treated by Individual
Industry in their ETP for efficient treatment to meet the prescribed norms by
CPCB.
The treated wastewater from individual industries after confirming the
prescribed norms will be reused for gardening in their premises.
To conserve the water, wastage of water shall be prevented by adequate water
management practices as well as regular maintenance of pipelines & tanks etc.
to prevent leak & spill.
Rainwater harvesting program shall also be implemented for conservation of
water.
Proponent shall attempt to reduce the losses by continuous inspection, R&D
and implementation of necessary adequate management practices.
Steel Re-Rolling and other similar activities in the industries will take proper mitigationmeasures for the following:
Rolling Mill: Rolling mill generates waste water used for cooling purpose. As
heavier suspended solids settles down easily this water will be recycled back
after removing mill waste.
Mill waste: The mill waste is primarily iron waste and having market value.
The sludge generated from cooling water, settling tanks should be handled
properly to avoid land contamination.
Utilities The steel Re-rolling mills units may have utilities such as raw water
treatment system, diesel generator(s), boilers (s), cooling tower(s), laboratory,
workshop(s), fuel storage facilities, waste water treatment plant,
administrative block, canteen etc. The pollution potential from these
operations should be assessed and suitable mitigation measures should be
planned.
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The operational set up shall be provided with upmost accuracy in order to
produce most efficient system which will use only necessary amount of water.
The operational set up shall be kept leak proof at all the times to reduce
consumption of water.
The raw effluents from operation/process shall be treated by Individual
Industry in their ETP for efficient treatment to meet the prescribed norms by
CPCB.
The treated wastewater from individual industries after confirming the
prescribed norms will be reused for gardening in their premises.
To conserve the water, wastage of water shall be prevented by adequate water
management practices as well as regular maintenance of pipelines & tanks etc.
to prevent leak & spill.
Rainwater harvesting program shall also be implemented for conservation of
water.
Proponent shall attempt to reduce the losses by continuous inspection, R&D
and implementation of necessary adequate management practices.
Steel Re-Rolling and other similar activities in the industries will take proper mitigationmeasures for the following:
Rolling Mill: Rolling mill generates waste water used for cooling purpose. As
heavier suspended solids settles down easily this water will be recycled back
after removing mill waste.
Mill waste: The mill waste is primarily iron waste and having market value.
The sludge generated from cooling water, settling tanks should be handled
properly to avoid land contamination.
Utilities The steel Re-rolling mills units may have utilities such as raw water
treatment system, diesel generator(s), boilers (s), cooling tower(s), laboratory,
workshop(s), fuel storage facilities, waste water treatment plant,
administrative block, canteen etc. The pollution potential from these
operations should be assessed and suitable mitigation measures should be
planned.
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Good housekeeping shall be maintained by keeping check on leaking valves,
crack and fissures in pipes, faulty equipment etc. so as to avoid wastage of
water and other raw materials/resources.
Industries will strive for adopting process/plant modifications which result in
to waste minimization and conservation of water.
The waste water generated from the Steel Re-rolling Mills industry is required
to be treated by a suitable mechanism and to be re-utilized. Typically the
conventional ETP in Steel Re-rolling Mills includes oil & grease trap,
equalization and raise pH from 1 to >8 by lime, coagulation & flocculation by
Alum, primary settling tank. Activated sludge treatment or two-stage aeration,
clarifier in secondary treatment system. Although Metals, COD and acidity
reductions are achieved through this conventional treatment system,
objectionable high TDS levels of effluents remain and effluents are not fit to
be discharged to surface water or on land. This treated waste water may be
reused in the process after filtration in dual media filter.
7.7.3 Noise Environment
Individual industries should ensure that acoustic enclosure shall be provided
to high noise generating equipment/ machineries/ utilities or such facilities
shall be housed in closed room to prevent noise propagation in surrounding
area.
Proper maintenance & lubrication of the plant machineries & equipments shall
be done regularly to reduce the level of noise generation.
Management shall provided necessary PPEs to eliminate the impacts of noise
in workplace.
Regular noise monitoring shall be done in area of noise to track noise change
above 10 dB(A) for timely action for noise reduction.
The noise level in the plant area shall confirm to the norms prescribed by
SPCB/CPCB/MoEF&CC as well as indicated in GOI Rules.
Shift planning shall be done with respect to the exposure level of noise at
various plant areas following guidelines of Factory Act and/or NIOSH.
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Good housekeeping shall be maintained by keeping check on leaking valves,
crack and fissures in pipes, faulty equipment etc. so as to avoid wastage of
water and other raw materials/resources.
Industries will strive for adopting process/plant modifications which result in
to waste minimization and conservation of water.
The waste water generated from the Steel Re-rolling Mills industry is required
to be treated by a suitable mechanism and to be re-utilized. Typically the
conventional ETP in Steel Re-rolling Mills includes oil & grease trap,
equalization and raise pH from 1 to >8 by lime, coagulation & flocculation by
Alum, primary settling tank. Activated sludge treatment or two-stage aeration,
clarifier in secondary treatment system. Although Metals, COD and acidity
reductions are achieved through this conventional treatment system,
objectionable high TDS levels of effluents remain and effluents are not fit to
be discharged to surface water or on land. This treated waste water may be
reused in the process after filtration in dual media filter.
7.7.3 Noise Environment
Individual industries should ensure that acoustic enclosure shall be provided
to high noise generating equipment/ machineries/ utilities or such facilities
shall be housed in closed room to prevent noise propagation in surrounding
area.
Proper maintenance & lubrication of the plant machineries & equipments shall
be done regularly to reduce the level of noise generation.
Management shall provided necessary PPEs to eliminate the impacts of noise
in workplace.
Regular noise monitoring shall be done in area of noise to track noise change
above 10 dB(A) for timely action for noise reduction.
The noise level in the plant area shall confirm to the norms prescribed by
SPCB/CPCB/MoEF&CC as well as indicated in GOI Rules.
Shift planning shall be done with respect to the exposure level of noise at
various plant areas following guidelines of Factory Act and/or NIOSH.
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Good housekeeping shall be maintained by keeping check on leaking valves,
crack and fissures in pipes, faulty equipment etc. so as to avoid wastage of
water and other raw materials/resources.
Industries will strive for adopting process/plant modifications which result in
to waste minimization and conservation of water.
The waste water generated from the Steel Re-rolling Mills industry is required
to be treated by a suitable mechanism and to be re-utilized. Typically the
conventional ETP in Steel Re-rolling Mills includes oil & grease trap,
equalization and raise pH from 1 to >8 by lime, coagulation & flocculation by
Alum, primary settling tank. Activated sludge treatment or two-stage aeration,
clarifier in secondary treatment system. Although Metals, COD and acidity
reductions are achieved through this conventional treatment system,
objectionable high TDS levels of effluents remain and effluents are not fit to
be discharged to surface water or on land. This treated waste water may be
reused in the process after filtration in dual media filter.
7.7.3 Noise Environment
Individual industries should ensure that acoustic enclosure shall be provided
to high noise generating equipment/ machineries/ utilities or such facilities
shall be housed in closed room to prevent noise propagation in surrounding
area.
Proper maintenance & lubrication of the plant machineries & equipments shall
be done regularly to reduce the level of noise generation.
Management shall provided necessary PPEs to eliminate the impacts of noise
in workplace.
Regular noise monitoring shall be done in area of noise to track noise change
above 10 dB(A) for timely action for noise reduction.
The noise level in the plant area shall confirm to the norms prescribed by
SPCB/CPCB/MoEF&CC as well as indicated in GOI Rules.
Shift planning shall be done with respect to the exposure level of noise at
various plant areas following guidelines of Factory Act and/or NIOSH.
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Transport vehicles shall be set in operation only at time convenient with the
residents equipped with low noise engine
Vehicles with low horn noise shall be used equipped with silencers
Noise generating and vibrating equipments/machineries shall be provided with
rubber padded foundations.
7.7.4 Land Environment and Solid/Hazardous Waste Management
The storages area of any kinds and production unit shall be lined properly to
ensure impervious lining to prevent seepage of chemical in soil.
Emergency Response protocol shall be prepared for all chemical material &
shall be available at all places having potential of chemical spill/leakage.
Immediate action shall be taken upon first reporting of incident of spill/leak of
chemical material.
Emergency actions shall be taken by responsible personnel as per guidelines
provided in specific Emergency Response Protocol for spilled/leaked
chemical.
Designated Hazardous waste area shall be provided within the premises as per
MoEF&CC/ CPCB guidelines.
Hazardous / Solid waste generation shall be within the limit and the method of
disposal / management shall be followed strictly in accordance with the
guidelines of MoEF&CC/ CPCB.
Apart from these individual Industries will be insisted to dispose their
hazardous waste generated to the common TSDF at Dundigal Village,
Qutbullapur Mandal, and Vikarabad District which is located approximately at
80 Km from site.
Greenbelt shall be developed in 33% area of total land of proponent at any
time of operation of production unit.
Individual industries shall maintain necessary records & documents of
Hazardous waste management/disposal as per MoEF&CC/ CPCB guidelines.
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Transport vehicles shall be set in operation only at time convenient with the
residents equipped with low noise engine
Vehicles with low horn noise shall be used equipped with silencers
Noise generating and vibrating equipments/machineries shall be provided with
rubber padded foundations.
7.7.4 Land Environment and Solid/Hazardous Waste Management
The storages area of any kinds and production unit shall be lined properly to
ensure impervious lining to prevent seepage of chemical in soil.
Emergency Response protocol shall be prepared for all chemical material &
shall be available at all places having potential of chemical spill/leakage.
Immediate action shall be taken upon first reporting of incident of spill/leak of
chemical material.
Emergency actions shall be taken by responsible personnel as per guidelines
provided in specific Emergency Response Protocol for spilled/leaked
chemical.
Designated Hazardous waste area shall be provided within the premises as per
MoEF&CC/ CPCB guidelines.
Hazardous / Solid waste generation shall be within the limit and the method of
disposal / management shall be followed strictly in accordance with the
guidelines of MoEF&CC/ CPCB.
Apart from these individual Industries will be insisted to dispose their
hazardous waste generated to the common TSDF at Dundigal Village,
Qutbullapur Mandal, and Vikarabad District which is located approximately at
80 Km from site.
Greenbelt shall be developed in 33% area of total land of proponent at any
time of operation of production unit.
Individual industries shall maintain necessary records & documents of
Hazardous waste management/disposal as per MoEF&CC/ CPCB guidelines.
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Transport vehicles shall be set in operation only at time convenient with the
residents equipped with low noise engine
Vehicles with low horn noise shall be used equipped with silencers
Noise generating and vibrating equipments/machineries shall be provided with
rubber padded foundations.
7.7.4 Land Environment and Solid/Hazardous Waste Management
The storages area of any kinds and production unit shall be lined properly to
ensure impervious lining to prevent seepage of chemical in soil.
Emergency Response protocol shall be prepared for all chemical material &
shall be available at all places having potential of chemical spill/leakage.
Immediate action shall be taken upon first reporting of incident of spill/leak of
chemical material.
Emergency actions shall be taken by responsible personnel as per guidelines
provided in specific Emergency Response Protocol for spilled/leaked
chemical.
Designated Hazardous waste area shall be provided within the premises as per
MoEF&CC/ CPCB guidelines.
Hazardous / Solid waste generation shall be within the limit and the method of
disposal / management shall be followed strictly in accordance with the
guidelines of MoEF&CC/ CPCB.
Apart from these individual Industries will be insisted to dispose their
hazardous waste generated to the common TSDF at Dundigal Village,
Qutbullapur Mandal, and Vikarabad District which is located approximately at
80 Km from site.
Greenbelt shall be developed in 33% area of total land of proponent at any
time of operation of production unit.
Individual industries shall maintain necessary records & documents of
Hazardous waste management/disposal as per MoEF&CC/ CPCB guidelines.
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7.7.5 Green Belt Design Methodology and Approach
A green belt has been proposed all around the periphery of the Industrial Park.
Plantation site would be cleared from all wild vegetation. Suitable soil and water
conservation measures will be adopted, if required. Since planting area is large, it
would be divided into blocks inter-linked by paths laid out in such a way that every
tree is accessible for all post plantation care. The planting arrangement and size
would be based on the optimum use of the available land and quantum of irrigation
water. A tree requires sufficient space below and above the ground to spread its roots
and branches. However, spacing varies with the type of trees, soil fertility, and
availability of moisture and purpose of plantation.
Planting of the tree would be done in suitable width. While planting the trees, care
would be taken that the installation structure would be difficult to see through the
foliage when seen from a point outside the green envelope. For preventing the
horizontal dispersion of the pollutants, the trees would be planted in alternate rows in
straight line. Tree trunk being free from foliage up to a height of 2-3 meters, it is
advisable to grow shrubs in front of tree so as to give coverage to the open portion.
Plantation would be done two weeks after the rain starts, as the trees benefit from the
seasonal rains. It is advised to avoid planting during the dry season, as this will
require watering. It is advantageous to plant trees on cloudy days.
Protection of Greenbelt
Gap filling in the greenbelt would be done in the same season to avoid gaps.
Protection of young plants from the ravages of cattle, sheep and goat and other
animals.
Timely replacement of damaged plant and thereafter care is important.
7.7.6 Material Management
The following pollution abatement measures will be implemented by the individual
industries.
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7.7.5 Green Belt Design Methodology and Approach
A green belt has been proposed all around the periphery of the Industrial Park.
Plantation site would be cleared from all wild vegetation. Suitable soil and water
conservation measures will be adopted, if required. Since planting area is large, it
would be divided into blocks inter-linked by paths laid out in such a way that every
tree is accessible for all post plantation care. The planting arrangement and size
would be based on the optimum use of the available land and quantum of irrigation
water. A tree requires sufficient space below and above the ground to spread its roots
and branches. However, spacing varies with the type of trees, soil fertility, and
availability of moisture and purpose of plantation.
Planting of the tree would be done in suitable width. While planting the trees, care
would be taken that the installation structure would be difficult to see through the
foliage when seen from a point outside the green envelope. For preventing the
horizontal dispersion of the pollutants, the trees would be planted in alternate rows in
straight line. Tree trunk being free from foliage up to a height of 2-3 meters, it is
advisable to grow shrubs in front of tree so as to give coverage to the open portion.
Plantation would be done two weeks after the rain starts, as the trees benefit from the
seasonal rains. It is advised to avoid planting during the dry season, as this will
require watering. It is advantageous to plant trees on cloudy days.
Protection of Greenbelt
Gap filling in the greenbelt would be done in the same season to avoid gaps.
Protection of young plants from the ravages of cattle, sheep and goat and other
animals.
Timely replacement of damaged plant and thereafter care is important.
7.7.6 Material Management
The following pollution abatement measures will be implemented by the individual
industries.
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7.7.5 Green Belt Design Methodology and Approach
A green belt has been proposed all around the periphery of the Industrial Park.
Plantation site would be cleared from all wild vegetation. Suitable soil and water
conservation measures will be adopted, if required. Since planting area is large, it
would be divided into blocks inter-linked by paths laid out in such a way that every
tree is accessible for all post plantation care. The planting arrangement and size
would be based on the optimum use of the available land and quantum of irrigation
water. A tree requires sufficient space below and above the ground to spread its roots
and branches. However, spacing varies with the type of trees, soil fertility, and
availability of moisture and purpose of plantation.
Planting of the tree would be done in suitable width. While planting the trees, care
would be taken that the installation structure would be difficult to see through the
foliage when seen from a point outside the green envelope. For preventing the
horizontal dispersion of the pollutants, the trees would be planted in alternate rows in
straight line. Tree trunk being free from foliage up to a height of 2-3 meters, it is
advisable to grow shrubs in front of tree so as to give coverage to the open portion.
Plantation would be done two weeks after the rain starts, as the trees benefit from the
seasonal rains. It is advised to avoid planting during the dry season, as this will
require watering. It is advantageous to plant trees on cloudy days.
Protection of Greenbelt
Gap filling in the greenbelt would be done in the same season to avoid gaps.
Protection of young plants from the ravages of cattle, sheep and goat and other
animals.
Timely replacement of damaged plant and thereafter care is important.
7.7.6 Material Management
The following pollution abatement measures will be implemented by the individual
industries.
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7.7.6.1 Storage Piles and Bins
the Wherever feasible, free falling transfer points from conveyors of sponge
iron and ash should be fitted with flexible curtains or be enclosed with chutes
designed to minimize the droop height. Water sprays should also be; used to
prevent the dust from going in to air.
All open stocks of sponge iron and ash must be kept in closed sheds only with
sufficiently wet by water spraying. The stockpiles of aggregates 5mm in size
or less must be suitably covered to ensure that the same is not carried away for
whipped out the wind.
Scattered piles gathered beneath belt conveyors, inside and around enclosures
must be cleared regularly.
7.7.6.2 Materials Transportation
Active hauls roads inside the works should be adequately wetted with water
Exhausts of trucks for transportations of rock materials within the site should
be directed upward.
The handling and storage of the dust collected by the dust collection system
must be carried out without fugitive particulate emissions.
7.7.7 Hazardous Waste Management
The Hazardous waste management will be followed by Individual industries as perthe waste generation.
The hazardous waste needs to be stored under covered shed so that
problems like odour, surface water contamination, ground water
contamination etc. do not occur
No hazardous waste can be stored beyond a period of 90 days except with
the prior permission of the State Board as per rule 7 of the HWMR, 2008.
Transfer of hazardous waste for sale, recycling, reprocessing or disposal
shall be done through the manifest system through manifest in form no. 13
only as per rule 21 of HWMR, 2008.
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7.7.6.1 Storage Piles and Bins
the Wherever feasible, free falling transfer points from conveyors of sponge
iron and ash should be fitted with flexible curtains or be enclosed with chutes
designed to minimize the droop height. Water sprays should also be; used to
prevent the dust from going in to air.
All open stocks of sponge iron and ash must be kept in closed sheds only with
sufficiently wet by water spraying. The stockpiles of aggregates 5mm in size
or less must be suitably covered to ensure that the same is not carried away for
whipped out the wind.
Scattered piles gathered beneath belt conveyors, inside and around enclosures
must be cleared regularly.
7.7.6.2 Materials Transportation
Active hauls roads inside the works should be adequately wetted with water
Exhausts of trucks for transportations of rock materials within the site should
be directed upward.
The handling and storage of the dust collected by the dust collection system
must be carried out without fugitive particulate emissions.
7.7.7 Hazardous Waste Management
The Hazardous waste management will be followed by Individual industries as perthe waste generation.
The hazardous waste needs to be stored under covered shed so that
problems like odour, surface water contamination, ground water
contamination etc. do not occur
No hazardous waste can be stored beyond a period of 90 days except with
the prior permission of the State Board as per rule 7 of the HWMR, 2008.
Transfer of hazardous waste for sale, recycling, reprocessing or disposal
shall be done through the manifest system through manifest in form no. 13
only as per rule 21 of HWMR, 2008.
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7.7.6.1 Storage Piles and Bins
the Wherever feasible, free falling transfer points from conveyors of sponge
iron and ash should be fitted with flexible curtains or be enclosed with chutes
designed to minimize the droop height. Water sprays should also be; used to
prevent the dust from going in to air.
All open stocks of sponge iron and ash must be kept in closed sheds only with
sufficiently wet by water spraying. The stockpiles of aggregates 5mm in size
or less must be suitably covered to ensure that the same is not carried away for
whipped out the wind.
Scattered piles gathered beneath belt conveyors, inside and around enclosures
must be cleared regularly.
7.7.6.2 Materials Transportation
Active hauls roads inside the works should be adequately wetted with water
Exhausts of trucks for transportations of rock materials within the site should
be directed upward.
The handling and storage of the dust collected by the dust collection system
must be carried out without fugitive particulate emissions.
7.7.7 Hazardous Waste Management
The Hazardous waste management will be followed by Individual industries as perthe waste generation.
The hazardous waste needs to be stored under covered shed so that
problems like odour, surface water contamination, ground water
contamination etc. do not occur
No hazardous waste can be stored beyond a period of 90 days except with
the prior permission of the State Board as per rule 7 of the HWMR, 2008.
Transfer of hazardous waste for sale, recycling, reprocessing or disposal
shall be done through the manifest system through manifest in form no. 13
only as per rule 21 of HWMR, 2008.
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All the industries having metal finishing operations viz pickling, metal
finishing, D.G. Sets etc., generating hazardous waste.
All the units generate the hazardous waste shall submit the Annual Report
for each financial year to the State Board.
In case the industry wants to utilize the hazardous waste as a
supplementary resource or for energy recovery, or after processing then
the industry needs to obtain approval from the competent authority.
The table below provides the detail on the type of Hazardous waste
generated from Steel rerolling mills and other similar activities and
method of disposal
Table 7.2 Hazardous waste category and disposal method
Sr.No
Waste GeneratingProcess
Hazardous waste Category Suggesteddisposal
pathways
1. System oil from D.G setscompressors andhydraulic machines.
Used/Spent oil 5.1 Sold byauthorizedvendors
2.Oil soak clothes/cottonetc
Waste/ residuecontainingOil
5.2 Incineration
3.Pickling process Acid residues 12.1 TSDF
4.Cleaning operations Alkali residues 12.2 TSDF
5.Recovery of acids frompickling waste
Sludge from acidrecovery Units
13.2 TSDF
6.Containers used forstorage of hazardouswaste
Discardedcontainerscontaminated withhazardous wastes
33.3 TSDF
7.Purification/ controlequipments of exhaustair
Flue gas cleaningresidues
34.1 TSDF
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All the industries having metal finishing operations viz pickling, metal
finishing, D.G. Sets etc., generating hazardous waste.
All the units generate the hazardous waste shall submit the Annual Report
for each financial year to the State Board.
In case the industry wants to utilize the hazardous waste as a
supplementary resource or for energy recovery, or after processing then
the industry needs to obtain approval from the competent authority.
The table below provides the detail on the type of Hazardous waste
generated from Steel rerolling mills and other similar activities and
method of disposal
Table 7.2 Hazardous waste category and disposal method
Sr.No
Waste GeneratingProcess
Hazardous waste Category Suggesteddisposal
pathways
1. System oil from D.G setscompressors andhydraulic machines.
Used/Spent oil 5.1 Sold byauthorizedvendors
2.Oil soak clothes/cottonetc
Waste/ residuecontainingOil
5.2 Incineration
3.Pickling process Acid residues 12.1 TSDF
4.Cleaning operations Alkali residues 12.2 TSDF
5.Recovery of acids frompickling waste
Sludge from acidrecovery Units
13.2 TSDF
6.Containers used forstorage of hazardouswaste
Discardedcontainerscontaminated withhazardous wastes
33.3 TSDF
7.Purification/ controlequipments of exhaustair
Flue gas cleaningresidues
34.1 TSDF
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All the industries having metal finishing operations viz pickling, metal
finishing, D.G. Sets etc., generating hazardous waste.
All the units generate the hazardous waste shall submit the Annual Report
for each financial year to the State Board.
In case the industry wants to utilize the hazardous waste as a
supplementary resource or for energy recovery, or after processing then
the industry needs to obtain approval from the competent authority.
The table below provides the detail on the type of Hazardous waste
generated from Steel rerolling mills and other similar activities and
method of disposal
Table 7.2 Hazardous waste category and disposal method
Sr.No
Waste GeneratingProcess
Hazardous waste Category Suggesteddisposal
pathways
1. System oil from D.G setscompressors andhydraulic machines.
Used/Spent oil 5.1 Sold byauthorizedvendors
2.Oil soak clothes/cottonetc
Waste/ residuecontainingOil
5.2 Incineration
3.Pickling process Acid residues 12.1 TSDF
4.Cleaning operations Alkali residues 12.2 TSDF
5.Recovery of acids frompickling waste
Sludge from acidrecovery Units
13.2 TSDF
6.Containers used forstorage of hazardouswaste
Discardedcontainerscontaminated withhazardous wastes
33.3 TSDF
7.Purification/ controlequipments of exhaustair
Flue gas cleaningresidues
34.1 TSDF
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8.Treatment of wastewater.
Chemical sludgefromwaste watertreatment plant
34.3 TSDF
9.Treatment of wastewater.
Oil and greaseskimmingResidue
34.4 TSDF/Incinerator
7.7.8 Energy Conservation Measures Proposed
It is proposed to provide CFL/ LEDs for street light and common facilities.
TSIIC will also insist on providing solar lighting CFLs to the individual
industries wherever applicable.
7.7.9 Fire Safety Facility
Some precautions and remedial measures proposed to be adopted by individual
industries to prevent fire are:
Compartmentation of cable galleries, use of proper sealing techniques of cable
passages and crevices in all directions would help in localizing and identifying
the area of occurrence of fire as well as ensure effective automatic and manual
fire fighting operations;
Spread of fire in horizontal direction would be checked by providing fire stops
for cable shafts;
Reliable and dependable type of fire detection system with proper zoning and
interlocks for alarms are effective protection methods for conveyor galleries;
Housekeeping of high standard helps in eliminating the causes of fire and
regular fire watching system strengthens fire prevention and fire fighting and
Proper fire watching by all concerned would be ensured.
7.7.10 Occupational Health and Safety
7.7.10.1 Construction Phase
The problems envisaged at construction and erection phase can mainly be due to
accident and noise. To overcome these problems, the contractor in charge of
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174
8.Treatment of wastewater.
Chemical sludgefromwaste watertreatment plant
34.3 TSDF
9.Treatment of wastewater.
Oil and greaseskimmingResidue
34.4 TSDF/Incinerator
7.7.8 Energy Conservation Measures Proposed
It is proposed to provide CFL/ LEDs for street light and common facilities.
TSIIC will also insist on providing solar lighting CFLs to the individual
industries wherever applicable.
7.7.9 Fire Safety Facility
Some precautions and remedial measures proposed to be adopted by individual
industries to prevent fire are:
Compartmentation of cable galleries, use of proper sealing techniques of cable
passages and crevices in all directions would help in localizing and identifying
the area of occurrence of fire as well as ensure effective automatic and manual
fire fighting operations;
Spread of fire in horizontal direction would be checked by providing fire stops
for cable shafts;
Reliable and dependable type of fire detection system with proper zoning and
interlocks for alarms are effective protection methods for conveyor galleries;
Housekeeping of high standard helps in eliminating the causes of fire and
regular fire watching system strengthens fire prevention and fire fighting and
Proper fire watching by all concerned would be ensured.
7.7.10 Occupational Health and Safety
7.7.10.1 Construction Phase
The problems envisaged at construction and erection phase can mainly be due to
accident and noise. To overcome these problems, the contractor in charge of
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174
8.Treatment of wastewater.
Chemical sludgefromwaste watertreatment plant
34.3 TSDF
9.Treatment of wastewater.
Oil and greaseskimmingResidue
34.4 TSDF/Incinerator
7.7.8 Energy Conservation Measures Proposed
It is proposed to provide CFL/ LEDs for street light and common facilities.
TSIIC will also insist on providing solar lighting CFLs to the individual
industries wherever applicable.
7.7.9 Fire Safety Facility
Some precautions and remedial measures proposed to be adopted by individual
industries to prevent fire are:
Compartmentation of cable galleries, use of proper sealing techniques of cable
passages and crevices in all directions would help in localizing and identifying
the area of occurrence of fire as well as ensure effective automatic and manual
fire fighting operations;
Spread of fire in horizontal direction would be checked by providing fire stops
for cable shafts;
Reliable and dependable type of fire detection system with proper zoning and
interlocks for alarms are effective protection methods for conveyor galleries;
Housekeeping of high standard helps in eliminating the causes of fire and
regular fire watching system strengthens fire prevention and fire fighting and
Proper fire watching by all concerned would be ensured.
7.7.10 Occupational Health and Safety
7.7.10.1 Construction Phase
The problems envisaged at construction and erection phase can mainly be due to
accident and noise. To overcome these problems, the contractor in charge of
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175
construction and erection activities have to maintain noise levels within threshold
limit values and the workers should be provided with personal protective
equipment.
a) Air Environment - Dust generated as a result of clearing, leveling and site
grading operations will be suppressed by using water sprinklers. It will be
ensured that the construction machinery using diesel driven prime movers are
properly maintained to minimize exhaust emissions of CO2, PM and
Hydrocarbons. Construction actively will be restricted to daytime as far as
possible to avoid disturbance to surrounding areas.
b) Noise Environment - All noise generating equipment used during the
construction phase shall be provided with noise control devices. Wherever
required, personal protective equipment such as earplugs, earmuffs etc., will
be provided to the persons engaged in noisy operations. This will minimize
their exposure to noise.
c) Storage of Hazardous materials -The hazardous materials expected to be
stored at the construction site will be limited to HSD. It will be stored as per
the statutory regulations in line with manufactures, Storage and Import of
Hazardous Chemical Rules, 1989 under Environment (Protection) Act, 1986.
d) Safety Measures - The site will have necessary security arrangements to
prevent entry of unauthorized personnel and proper control of hazardous
materials on site. All the employees as well as contracted labor will be trained
in safety aspects related to their job. There will be a special emphasis on safe
handling of material, safety in welding and fabrication activities will be
provided to staff working at heights. All the personnel will be provided with
safety appliance such as face shields, helmets safety goggles, safety shoes,
hand gloves etc., as per the job requirement. To ensure that the local
inhabitants are not exposed to these hazards, the site will be secured by
fencing and manned at entry points.
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construction and erection activities have to maintain noise levels within threshold
limit values and the workers should be provided with personal protective
equipment.
a) Air Environment - Dust generated as a result of clearing, leveling and site
grading operations will be suppressed by using water sprinklers. It will be
ensured that the construction machinery using diesel driven prime movers are
properly maintained to minimize exhaust emissions of CO2, PM and
Hydrocarbons. Construction actively will be restricted to daytime as far as
possible to avoid disturbance to surrounding areas.
b) Noise Environment - All noise generating equipment used during the
construction phase shall be provided with noise control devices. Wherever
required, personal protective equipment such as earplugs, earmuffs etc., will
be provided to the persons engaged in noisy operations. This will minimize
their exposure to noise.
c) Storage of Hazardous materials -The hazardous materials expected to be
stored at the construction site will be limited to HSD. It will be stored as per
the statutory regulations in line with manufactures, Storage and Import of
Hazardous Chemical Rules, 1989 under Environment (Protection) Act, 1986.
d) Safety Measures - The site will have necessary security arrangements to
prevent entry of unauthorized personnel and proper control of hazardous
materials on site. All the employees as well as contracted labor will be trained
in safety aspects related to their job. There will be a special emphasis on safe
handling of material, safety in welding and fabrication activities will be
provided to staff working at heights. All the personnel will be provided with
safety appliance such as face shields, helmets safety goggles, safety shoes,
hand gloves etc., as per the job requirement. To ensure that the local
inhabitants are not exposed to these hazards, the site will be secured by
fencing and manned at entry points.
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175
construction and erection activities have to maintain noise levels within threshold
limit values and the workers should be provided with personal protective
equipment.
a) Air Environment - Dust generated as a result of clearing, leveling and site
grading operations will be suppressed by using water sprinklers. It will be
ensured that the construction machinery using diesel driven prime movers are
properly maintained to minimize exhaust emissions of CO2, PM and
Hydrocarbons. Construction actively will be restricted to daytime as far as
possible to avoid disturbance to surrounding areas.
b) Noise Environment - All noise generating equipment used during the
construction phase shall be provided with noise control devices. Wherever
required, personal protective equipment such as earplugs, earmuffs etc., will
be provided to the persons engaged in noisy operations. This will minimize
their exposure to noise.
c) Storage of Hazardous materials -The hazardous materials expected to be
stored at the construction site will be limited to HSD. It will be stored as per
the statutory regulations in line with manufactures, Storage and Import of
Hazardous Chemical Rules, 1989 under Environment (Protection) Act, 1986.
d) Safety Measures - The site will have necessary security arrangements to
prevent entry of unauthorized personnel and proper control of hazardous
materials on site. All the employees as well as contracted labor will be trained
in safety aspects related to their job. There will be a special emphasis on safe
handling of material, safety in welding and fabrication activities will be
provided to staff working at heights. All the personnel will be provided with
safety appliance such as face shields, helmets safety goggles, safety shoes,
hand gloves etc., as per the job requirement. To ensure that the local
inhabitants are not exposed to these hazards, the site will be secured by
fencing and manned at entry points.
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176
7.7.10.2 Operation and Maintenance Phase
In the case of Industrial Parks during operation and maintenance, the men, materials
and machineries are the basic inputs. Along with the boons, the industrialization has
brought several problems like occupational health and safety. The industry planner,
therefore, has to properly plan and take the steps to minimize the impacts of
industrialization to ensure appropriate occupational health safety including fire. All
these activities again may be classified under construction, erection and operation and
maintenance. Occupational health needs attention both in construction and erection
and operation and maintenance phases. However, the problems vary in magnitude and
type of industries in the above phases.
The problem of occupational health, in the operation and maintenance phase is due to
noise hearing losses, exposure to dust and heat, exposure to arc lights & welding
lights, exposure to chemicals, gases, acids, and alkalis etc. Engineering controls are
provided in design itself to contain these hazards; otherwise the employees are
isolated from the source of hazards. Suitable personnel protective equipment is also
given to employees. To overcome these hazards, arrangements are made to reduce it
within threshold limit values and required personnel protective equipment shall also
be supplied to workers.
The following Personnel Protective Equipment (PPE) shall be provided to workers
under their specific job requirement by Individual Industries as per the requirement.
Industry safety helmet for work at high level, Gas yard and at plant in general.
Zero power plain goggles with cut type filters on both ends to work under
highly dusty areas.
Welders equipment for eye and face protection during welding activity.
Cylindrical type earplug at moderate level noise like wagon tippler, ID fans
etc.
Ear muffs at high-level noise area like Gas mill, boiler etc.
Dust respirator with filter at high dust level area like Gas yard.
Canister Gas mask for maintenance in contained space viz. inside vessels,
storage tank, boiler furnace etc.
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7.7.10.2 Operation and Maintenance Phase
In the case of Industrial Parks during operation and maintenance, the men, materials
and machineries are the basic inputs. Along with the boons, the industrialization has
brought several problems like occupational health and safety. The industry planner,
therefore, has to properly plan and take the steps to minimize the impacts of
industrialization to ensure appropriate occupational health safety including fire. All
these activities again may be classified under construction, erection and operation and
maintenance. Occupational health needs attention both in construction and erection
and operation and maintenance phases. However, the problems vary in magnitude and
type of industries in the above phases.
The problem of occupational health, in the operation and maintenance phase is due to
noise hearing losses, exposure to dust and heat, exposure to arc lights & welding
lights, exposure to chemicals, gases, acids, and alkalis etc. Engineering controls are
provided in design itself to contain these hazards; otherwise the employees are
isolated from the source of hazards. Suitable personnel protective equipment is also
given to employees. To overcome these hazards, arrangements are made to reduce it
within threshold limit values and required personnel protective equipment shall also
be supplied to workers.
The following Personnel Protective Equipment (PPE) shall be provided to workers
under their specific job requirement by Individual Industries as per the requirement.
Industry safety helmet for work at high level, Gas yard and at plant in general.
Zero power plain goggles with cut type filters on both ends to work under
highly dusty areas.
Welders equipment for eye and face protection during welding activity.
Cylindrical type earplug at moderate level noise like wagon tippler, ID fans
etc.
Ear muffs at high-level noise area like Gas mill, boiler etc.
Dust respirator with filter at high dust level area like Gas yard.
Canister Gas mask for maintenance in contained space viz. inside vessels,
storage tank, boiler furnace etc.
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176
7.7.10.2 Operation and Maintenance Phase
In the case of Industrial Parks during operation and maintenance, the men, materials
and machineries are the basic inputs. Along with the boons, the industrialization has
brought several problems like occupational health and safety. The industry planner,
therefore, has to properly plan and take the steps to minimize the impacts of
industrialization to ensure appropriate occupational health safety including fire. All
these activities again may be classified under construction, erection and operation and
maintenance. Occupational health needs attention both in construction and erection
and operation and maintenance phases. However, the problems vary in magnitude and
type of industries in the above phases.
The problem of occupational health, in the operation and maintenance phase is due to
noise hearing losses, exposure to dust and heat, exposure to arc lights & welding
lights, exposure to chemicals, gases, acids, and alkalis etc. Engineering controls are
provided in design itself to contain these hazards; otherwise the employees are
isolated from the source of hazards. Suitable personnel protective equipment is also
given to employees. To overcome these hazards, arrangements are made to reduce it
within threshold limit values and required personnel protective equipment shall also
be supplied to workers.
The following Personnel Protective Equipment (PPE) shall be provided to workers
under their specific job requirement by Individual Industries as per the requirement.
Industry safety helmet for work at high level, Gas yard and at plant in general.
Zero power plain goggles with cut type filters on both ends to work under
highly dusty areas.
Welders equipment for eye and face protection during welding activity.
Cylindrical type earplug at moderate level noise like wagon tippler, ID fans
etc.
Ear muffs at high-level noise area like Gas mill, boiler etc.
Dust respirator with filter at high dust level area like Gas yard.
Canister Gas mask for maintenance in contained space viz. inside vessels,
storage tank, boiler furnace etc.
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177
Asbestos apron at high temperature area near furnace, turbine etc.
Rubberized apron at acid/alkali leak prone area viz. chlorine handling, caustic
handling etc.
Boiler suit-for maintenance work in boiler unit during plant shut down.
Safety belt/ line man’s safety belt-work at high level viz. stack monitoring,
Gas mill etc.
Asbestos hard gloves for handling of hot material viz. dry bottom ash,
equipment near furnace, boiler or turbine.
Acid/Alkali proof rubberized hand gloves-work at switch, maintenance of
transmission lines, turbo generator etc.
Industrial safety shoes with steel, while working near process equipment.
Electrical safety shoes without steel toe gum boots-essential for a
wireman/electrician.
All working personnel will be medically examined at least once every year and at the
end of his term of employment. This is in addition to the pre-employment medical
examination.
7.7.11 Safety and Emergency Plan
Safety of both men and material during construction and operation stages is of
concern to industries. The preparedness of an industry for the occurrence of possible
disasters is known as emergency plan. The disaster is possible due to leakage of
hazardous chemicals collapse of structures and fire/explosion etc. Keeping in view,
the safety requirement during construction, operation and maintenance phase the
proponent would formulate safety policy keeping in view the following requirements:
To allocate sufficient resources to maintain safe and healthy conditions at work.
To take steps to ensure that all known safety factors are taken into account in the
design, construction, operation and maintenance of plants, machinery and
equipments.
To ensure that adequate safety instructions are given to all employees.
Rakamcherla IP - EIA Environmental Management Plan
177
Asbestos apron at high temperature area near furnace, turbine etc.
Rubberized apron at acid/alkali leak prone area viz. chlorine handling, caustic
handling etc.
Boiler suit-for maintenance work in boiler unit during plant shut down.
Safety belt/ line man’s safety belt-work at high level viz. stack monitoring,
Gas mill etc.
Asbestos hard gloves for handling of hot material viz. dry bottom ash,
equipment near furnace, boiler or turbine.
Acid/Alkali proof rubberized hand gloves-work at switch, maintenance of
transmission lines, turbo generator etc.
Industrial safety shoes with steel, while working near process equipment.
Electrical safety shoes without steel toe gum boots-essential for a
wireman/electrician.
All working personnel will be medically examined at least once every year and at the
end of his term of employment. This is in addition to the pre-employment medical
examination.
7.7.11 Safety and Emergency Plan
Safety of both men and material during construction and operation stages is of
concern to industries. The preparedness of an industry for the occurrence of possible
disasters is known as emergency plan. The disaster is possible due to leakage of
hazardous chemicals collapse of structures and fire/explosion etc. Keeping in view,
the safety requirement during construction, operation and maintenance phase the
proponent would formulate safety policy keeping in view the following requirements:
To allocate sufficient resources to maintain safe and healthy conditions at work.
To take steps to ensure that all known safety factors are taken into account in the
design, construction, operation and maintenance of plants, machinery and
equipments.
To ensure that adequate safety instructions are given to all employees.
Rakamcherla IP - EIA Environmental Management Plan
177
Asbestos apron at high temperature area near furnace, turbine etc.
Rubberized apron at acid/alkali leak prone area viz. chlorine handling, caustic
handling etc.
Boiler suit-for maintenance work in boiler unit during plant shut down.
Safety belt/ line man’s safety belt-work at high level viz. stack monitoring,
Gas mill etc.
Asbestos hard gloves for handling of hot material viz. dry bottom ash,
equipment near furnace, boiler or turbine.
Acid/Alkali proof rubberized hand gloves-work at switch, maintenance of
transmission lines, turbo generator etc.
Industrial safety shoes with steel, while working near process equipment.
Electrical safety shoes without steel toe gum boots-essential for a
wireman/electrician.
All working personnel will be medically examined at least once every year and at the
end of his term of employment. This is in addition to the pre-employment medical
examination.
7.7.11 Safety and Emergency Plan
Safety of both men and material during construction and operation stages is of
concern to industries. The preparedness of an industry for the occurrence of possible
disasters is known as emergency plan. The disaster is possible due to leakage of
hazardous chemicals collapse of structures and fire/explosion etc. Keeping in view,
the safety requirement during construction, operation and maintenance phase the
proponent would formulate safety policy keeping in view the following requirements:
To allocate sufficient resources to maintain safe and healthy conditions at work.
To take steps to ensure that all known safety factors are taken into account in the
design, construction, operation and maintenance of plants, machinery and
equipments.
To ensure that adequate safety instructions are given to all employees.
Rakamcherla IP - EIA Environmental Management Plan
178
To provide wherever necessary protective equipment, safety appliances and clothing,
and to ensure their proper use.
To inform employees about materials, equipment or processes used in their work,
which are known to be potentially hazardous to health and safety
To keep all operations and methods of work under regular review for making
necessary changes from the point of view of safety in the light of experience and up
to date knowledge.
To provide appropriate instruction, training, retraining and supervision in health and
safety, first aid and to ensure that adequate publicity is given to these matters.
To ensure proper implementation of fire prevention and an appropriate fire fighting
service together with training facilities for personnel involved in this service.
To ensure that professional advice is made available wherever potentially hazardous
situations exist or might arise.
To organize collection, analysis and presentation of data on accident sickness and
incident involving personal injury or cause of sickness with a view to taking
corrective, remedial and preventive action.
To promote through the established machinery, joint consultation in health and safety
matters to ensure effective participation by all employees.
To publish/notify regulations, instructions and notices in the common language of
employees.
To prepare separate safety rules for each type of occupation/process involved in a
power station.
To ensure regular safety inspection by a competent person at suitable intervals of all
buildings, equipment, work places and operations.
7.7.12 Fire Protection
The fire fighting system in the Individual units is proposed to be comprising of water
hydrant system, fire detection and alarm and extinguishers will be extended to cover
all the areas as per local government requirements. It is proposed to provide a fire
station within the Industrial Park with following facilities. Some of the salient
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178
To provide wherever necessary protective equipment, safety appliances and clothing,
and to ensure their proper use.
To inform employees about materials, equipment or processes used in their work,
which are known to be potentially hazardous to health and safety
To keep all operations and methods of work under regular review for making
necessary changes from the point of view of safety in the light of experience and up
to date knowledge.
To provide appropriate instruction, training, retraining and supervision in health and
safety, first aid and to ensure that adequate publicity is given to these matters.
To ensure proper implementation of fire prevention and an appropriate fire fighting
service together with training facilities for personnel involved in this service.
To ensure that professional advice is made available wherever potentially hazardous
situations exist or might arise.
To organize collection, analysis and presentation of data on accident sickness and
incident involving personal injury or cause of sickness with a view to taking
corrective, remedial and preventive action.
To promote through the established machinery, joint consultation in health and safety
matters to ensure effective participation by all employees.
To publish/notify regulations, instructions and notices in the common language of
employees.
To prepare separate safety rules for each type of occupation/process involved in a
power station.
To ensure regular safety inspection by a competent person at suitable intervals of all
buildings, equipment, work places and operations.
7.7.12 Fire Protection
The fire fighting system in the Individual units is proposed to be comprising of water
hydrant system, fire detection and alarm and extinguishers will be extended to cover
all the areas as per local government requirements. It is proposed to provide a fire
station within the Industrial Park with following facilities. Some of the salient
Rakamcherla IP - EIA Environmental Management Plan
178
To provide wherever necessary protective equipment, safety appliances and clothing,
and to ensure their proper use.
To inform employees about materials, equipment or processes used in their work,
which are known to be potentially hazardous to health and safety
To keep all operations and methods of work under regular review for making
necessary changes from the point of view of safety in the light of experience and up
to date knowledge.
To provide appropriate instruction, training, retraining and supervision in health and
safety, first aid and to ensure that adequate publicity is given to these matters.
To ensure proper implementation of fire prevention and an appropriate fire fighting
service together with training facilities for personnel involved in this service.
To ensure that professional advice is made available wherever potentially hazardous
situations exist or might arise.
To organize collection, analysis and presentation of data on accident sickness and
incident involving personal injury or cause of sickness with a view to taking
corrective, remedial and preventive action.
To promote through the established machinery, joint consultation in health and safety
matters to ensure effective participation by all employees.
To publish/notify regulations, instructions and notices in the common language of
employees.
To prepare separate safety rules for each type of occupation/process involved in a
power station.
To ensure regular safety inspection by a competent person at suitable intervals of all
buildings, equipment, work places and operations.
7.7.12 Fire Protection
The fire fighting system in the Individual units is proposed to be comprising of water
hydrant system, fire detection and alarm and extinguishers will be extended to cover
all the areas as per local government requirements. It is proposed to provide a fire
station within the Industrial Park with following facilities. Some of the salient
Rakamcherla IP - EIA Environmental Management Plan
179
features for a fire protection system that has to be installed in the Industrial park are
as follows:
7.7.12.1 General
The systems to be included in the Fire Protection System design include thefollowing;
Fire Water Reserves and Fire Pump Station
Signal and piping connection from the above.
Fire Hydrants, Smoke Alarm and Fire Alarm System
Portable Fire Extinguisher
Fire system Monitoring.
7.7.12.2 Standards and Regulations
The fire protection system design will be undertaken on the basis of the following
Standards and Regulations as applicable:
NFPA (National Fire Protection Association of the USA)
Factory Manual
Indian standards
7.7.12.3 Pipe Work
All pipe work shall be above ground/underground depending on the soil
properties as per Indian standards if the pipe work is above ground.
Valves will be chain locked, as appropriate.
Water flow switches and wet alarms will be installed. These signals will be
displayed on the Fire Alarm Monitor Panel indicating within zone of fire
hose station is being used, and triggers the sounding of the general alarm.
7.7.12.4 Portable Fire Extinguisher
Dry chemical fire extinguishers have to be provided in all general areas.
Carbon Dioxide extinguishers to be provided for switchboard rooms, MCC
rooms.
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179
features for a fire protection system that has to be installed in the Industrial park are
as follows:
7.7.12.1 General
The systems to be included in the Fire Protection System design include thefollowing;
Fire Water Reserves and Fire Pump Station
Signal and piping connection from the above.
Fire Hydrants, Smoke Alarm and Fire Alarm System
Portable Fire Extinguisher
Fire system Monitoring.
7.7.12.2 Standards and Regulations
The fire protection system design will be undertaken on the basis of the following
Standards and Regulations as applicable:
NFPA (National Fire Protection Association of the USA)
Factory Manual
Indian standards
7.7.12.3 Pipe Work
All pipe work shall be above ground/underground depending on the soil
properties as per Indian standards if the pipe work is above ground.
Valves will be chain locked, as appropriate.
Water flow switches and wet alarms will be installed. These signals will be
displayed on the Fire Alarm Monitor Panel indicating within zone of fire
hose station is being used, and triggers the sounding of the general alarm.
7.7.12.4 Portable Fire Extinguisher
Dry chemical fire extinguishers have to be provided in all general areas.
Carbon Dioxide extinguishers to be provided for switchboard rooms, MCC
rooms.
Rakamcherla IP - EIA Environmental Management Plan
179
features for a fire protection system that has to be installed in the Industrial park are
as follows:
7.7.12.1 General
The systems to be included in the Fire Protection System design include thefollowing;
Fire Water Reserves and Fire Pump Station
Signal and piping connection from the above.
Fire Hydrants, Smoke Alarm and Fire Alarm System
Portable Fire Extinguisher
Fire system Monitoring.
7.7.12.2 Standards and Regulations
The fire protection system design will be undertaken on the basis of the following
Standards and Regulations as applicable:
NFPA (National Fire Protection Association of the USA)
Factory Manual
Indian standards
7.7.12.3 Pipe Work
All pipe work shall be above ground/underground depending on the soil
properties as per Indian standards if the pipe work is above ground.
Valves will be chain locked, as appropriate.
Water flow switches and wet alarms will be installed. These signals will be
displayed on the Fire Alarm Monitor Panel indicating within zone of fire
hose station is being used, and triggers the sounding of the general alarm.
7.7.12.4 Portable Fire Extinguisher
Dry chemical fire extinguishers have to be provided in all general areas.
Carbon Dioxide extinguishers to be provided for switchboard rooms, MCC
rooms.
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180
The installation and rating of portable fire extinguishers will be in
accordance with standards.
7.7.13 Green belt Development
TSIIC has prepared Master layout and provided greenbelt of 16.81 acres (14.94%) of
the total plot area. Individual industries will be emphasized to provide adequate green
belt area, so that 33% of green belt area will be achieved during operation of the
Industrial Park. Furthermore 10m wide green belt is proposed all along the I.P.
Adequate numbers of saplings will be planted all along the periphery of the plant,
roadways and available open spaces. The major aim of greenbelt development plan is
to attenuate air pollutants released into the environment but it can also help in overall
improvement in the environmental conditions of the project site. The plan will
address the following issues such as attenuation of air pollution, noise reduction,
improving the biodiversity of the region, adding aesthetics and combating soil erosion
and prevention of land degradation.
7.7.13.1 Protection of Greenbelt
Gap filling in the greenbelt would be done in the same season to avoid gaps.
Protection of young plants from the ravages of cattle, sheep and goat and
other animals.
Timely replacement of damaged plant and thereafter care is important.
7.7.14 Corporate Social Responsibility
The concept and implementation of Corporate Social Responsibilities (CSR) has
become imperative due to the intense debate of developmental growth versus welfare
based development. As long as the business development is in synergy with social
development, the social conflict will not arise. Some of the proposals of CSR are
suggested for TSIIC to be implemented are follows:
a. Health: Public health facilities are not sufficient in the project area. The existing
infrastructure can be upgraded or additional health centre may be provided. There
are only 2 Government health centers in Pargi mandal and 4 in Pudur mandal.
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180
The installation and rating of portable fire extinguishers will be in
accordance with standards.
7.7.13 Green belt Development
TSIIC has prepared Master layout and provided greenbelt of 16.81 acres (14.94%) of
the total plot area. Individual industries will be emphasized to provide adequate green
belt area, so that 33% of green belt area will be achieved during operation of the
Industrial Park. Furthermore 10m wide green belt is proposed all along the I.P.
Adequate numbers of saplings will be planted all along the periphery of the plant,
roadways and available open spaces. The major aim of greenbelt development plan is
to attenuate air pollutants released into the environment but it can also help in overall
improvement in the environmental conditions of the project site. The plan will
address the following issues such as attenuation of air pollution, noise reduction,
improving the biodiversity of the region, adding aesthetics and combating soil erosion
and prevention of land degradation.
7.7.13.1 Protection of Greenbelt
Gap filling in the greenbelt would be done in the same season to avoid gaps.
Protection of young plants from the ravages of cattle, sheep and goat and
other animals.
Timely replacement of damaged plant and thereafter care is important.
7.7.14 Corporate Social Responsibility
The concept and implementation of Corporate Social Responsibilities (CSR) has
become imperative due to the intense debate of developmental growth versus welfare
based development. As long as the business development is in synergy with social
development, the social conflict will not arise. Some of the proposals of CSR are
suggested for TSIIC to be implemented are follows:
a. Health: Public health facilities are not sufficient in the project area. The existing
infrastructure can be upgraded or additional health centre may be provided. There
are only 2 Government health centers in Pargi mandal and 4 in Pudur mandal.
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180
The installation and rating of portable fire extinguishers will be in
accordance with standards.
7.7.13 Green belt Development
TSIIC has prepared Master layout and provided greenbelt of 16.81 acres (14.94%) of
the total plot area. Individual industries will be emphasized to provide adequate green
belt area, so that 33% of green belt area will be achieved during operation of the
Industrial Park. Furthermore 10m wide green belt is proposed all along the I.P.
Adequate numbers of saplings will be planted all along the periphery of the plant,
roadways and available open spaces. The major aim of greenbelt development plan is
to attenuate air pollutants released into the environment but it can also help in overall
improvement in the environmental conditions of the project site. The plan will
address the following issues such as attenuation of air pollution, noise reduction,
improving the biodiversity of the region, adding aesthetics and combating soil erosion
and prevention of land degradation.
7.7.13.1 Protection of Greenbelt
Gap filling in the greenbelt would be done in the same season to avoid gaps.
Protection of young plants from the ravages of cattle, sheep and goat and
other animals.
Timely replacement of damaged plant and thereafter care is important.
7.7.14 Corporate Social Responsibility
The concept and implementation of Corporate Social Responsibilities (CSR) has
become imperative due to the intense debate of developmental growth versus welfare
based development. As long as the business development is in synergy with social
development, the social conflict will not arise. Some of the proposals of CSR are
suggested for TSIIC to be implemented are follows:
a. Health: Public health facilities are not sufficient in the project area. The existing
infrastructure can be upgraded or additional health centre may be provided. There
are only 2 Government health centers in Pargi mandal and 4 in Pudur mandal.
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181
Health Check up and free medical camp can be conducted with the help of social
service organizations/Govt. organizations.
b. Education: There are 38 primary schools Pudur mandal and 48 primary schools
in Pargi mandal. The infrastructure facilities like Compound walls, Toilets, Play
ground amenities can be provided. Books, Computers and other study materials,
sports goods can be provided for the students. Purified drinking water facility can
be provided.
c. Public hygiene and sanitation: The awareness of hygiene and sanitation is very
low in the area. With help of NGOs and Schools, the awareness campaign can be
conducted.
d. Skill development: Rural youth can be trained by capacity building, vocational
education for their better opportunities in local and other areas. Migration can be
mitigated by providing job opportunities for local youths by imparting them
training and education.
e. Women welfare: More specific initiatives can be taken up for women health
programme, skill development and women entrepreneurship can be organized to
improve the stature of the women in the district.
f. Cultural activities: Sponsoring sports events, local cultural programs, campaign
for adverse effects of social evils like smoking, drinking can be done to improve
the societal status of the people around the district.
7.7.15 Budget for Environmental Management
The Budget for Environmental Management with capital and operation cost is given
below in Table 7-3. Capital cost of 79.85 Lakhs and recurring cost of 13.2 Lakhs/
Annum is estimated for the project.
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181
Health Check up and free medical camp can be conducted with the help of social
service organizations/Govt. organizations.
b. Education: There are 38 primary schools Pudur mandal and 48 primary schools
in Pargi mandal. The infrastructure facilities like Compound walls, Toilets, Play
ground amenities can be provided. Books, Computers and other study materials,
sports goods can be provided for the students. Purified drinking water facility can
be provided.
c. Public hygiene and sanitation: The awareness of hygiene and sanitation is very
low in the area. With help of NGOs and Schools, the awareness campaign can be
conducted.
d. Skill development: Rural youth can be trained by capacity building, vocational
education for their better opportunities in local and other areas. Migration can be
mitigated by providing job opportunities for local youths by imparting them
training and education.
e. Women welfare: More specific initiatives can be taken up for women health
programme, skill development and women entrepreneurship can be organized to
improve the stature of the women in the district.
f. Cultural activities: Sponsoring sports events, local cultural programs, campaign
for adverse effects of social evils like smoking, drinking can be done to improve
the societal status of the people around the district.
7.7.15 Budget for Environmental Management
The Budget for Environmental Management with capital and operation cost is given
below in Table 7-3. Capital cost of 79.85 Lakhs and recurring cost of 13.2 Lakhs/
Annum is estimated for the project.
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181
Health Check up and free medical camp can be conducted with the help of social
service organizations/Govt. organizations.
b. Education: There are 38 primary schools Pudur mandal and 48 primary schools
in Pargi mandal. The infrastructure facilities like Compound walls, Toilets, Play
ground amenities can be provided. Books, Computers and other study materials,
sports goods can be provided for the students. Purified drinking water facility can
be provided.
c. Public hygiene and sanitation: The awareness of hygiene and sanitation is very
low in the area. With help of NGOs and Schools, the awareness campaign can be
conducted.
d. Skill development: Rural youth can be trained by capacity building, vocational
education for their better opportunities in local and other areas. Migration can be
mitigated by providing job opportunities for local youths by imparting them
training and education.
e. Women welfare: More specific initiatives can be taken up for women health
programme, skill development and women entrepreneurship can be organized to
improve the stature of the women in the district.
f. Cultural activities: Sponsoring sports events, local cultural programs, campaign
for adverse effects of social evils like smoking, drinking can be done to improve
the societal status of the people around the district.
7.7.15 Budget for Environmental Management
The Budget for Environmental Management with capital and operation cost is given
below in Table 7-3. Capital cost of 79.85 Lakhs and recurring cost of 13.2 Lakhs/
Annum is estimated for the project.
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182
Table 7.3 Budget for Environmental Management
S.No Components Capital Cost (inLakhs)
Operational Cost/ Year (in Lakhs)
1 Green Belt development 10 22 Environmental Management
Plan67.85 3
3 MSW Management 2 44 Environmental Monitoring -- 4.2
Total 79.85 13.2
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Table 7.3 Budget for Environmental Management
S.No Components Capital Cost (inLakhs)
Operational Cost/ Year (in Lakhs)
1 Green Belt development 10 22 Environmental Management
Plan67.85 3
3 MSW Management 2 44 Environmental Monitoring -- 4.2
Total 79.85 13.2
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Table 7.3 Budget for Environmental Management
S.No Components Capital Cost (inLakhs)
Operational Cost/ Year (in Lakhs)
1 Green Belt development 10 22 Environmental Management
Plan67.85 3
3 MSW Management 2 44 Environmental Monitoring -- 4.2
Total 79.85 13.2
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183
Chapter 8
Additional Studies
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183
Chapter 8
Additional Studies
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183
Chapter 8
Additional Studies
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184
8 Additional Studies
8.1 Risk AssessmentAccident can occur in every industry in spite of efforts to prevent them. Frequently they
give rise to suffering and damage, the extent of which is, in part, determined by the
potential for loss, surrounding the event. Some of the industries coming up in the
Rakamcherla Industrial Park have high potential for loss and there have been cases, where
loss, measured in both human and monetary terms, has been severe. It is equally true to
say that there have been other cases where, because of effective action taken at the time,
the full potential loss has been largely avoided. Effective action, in these cases, has been
possible due to the existence of pre-planned and practiced procedures for handling major
emergencies utilizing the combined resources of the industrial concern and outside
services.
Section 41-B (4) of the Factories Act, 1948 requires that every occupier of a Hazardous
and Non-hazardous factor shall draw up and onsite emergency plan and detailed disaster
control measures for the factory and make known to the workers and the general public in
the vicinity, the safety measures required to be taken in the event of an emergency taking
place.
8.2 Disaster Management Plan
Despite of all efforts made accidents do occur which need immediate attention. The risks
involved in this project have been identified and their mitigation measures have been
proposed. But when serious accidents occur & negligence could result in loss of life the
whole thing has to be handled in a systematic well planned manner. Accordingly
following plan of disaster management has been evolved:-
8.2.1 Major Activities
Broadly Disaster Management Plan mainly includes;
Pre - Emergency Preparedness
Emergency actions and
Post Emergency activities
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184
8 Additional Studies
8.1 Risk AssessmentAccident can occur in every industry in spite of efforts to prevent them. Frequently they
give rise to suffering and damage, the extent of which is, in part, determined by the
potential for loss, surrounding the event. Some of the industries coming up in the
Rakamcherla Industrial Park have high potential for loss and there have been cases, where
loss, measured in both human and monetary terms, has been severe. It is equally true to
say that there have been other cases where, because of effective action taken at the time,
the full potential loss has been largely avoided. Effective action, in these cases, has been
possible due to the existence of pre-planned and practiced procedures for handling major
emergencies utilizing the combined resources of the industrial concern and outside
services.
Section 41-B (4) of the Factories Act, 1948 requires that every occupier of a Hazardous
and Non-hazardous factor shall draw up and onsite emergency plan and detailed disaster
control measures for the factory and make known to the workers and the general public in
the vicinity, the safety measures required to be taken in the event of an emergency taking
place.
8.2 Disaster Management Plan
Despite of all efforts made accidents do occur which need immediate attention. The risks
involved in this project have been identified and their mitigation measures have been
proposed. But when serious accidents occur & negligence could result in loss of life the
whole thing has to be handled in a systematic well planned manner. Accordingly
following plan of disaster management has been evolved:-
8.2.1 Major Activities
Broadly Disaster Management Plan mainly includes;
Pre - Emergency Preparedness
Emergency actions and
Post Emergency activities
Rakamcherla IP - EIA Additional Studies
184
8 Additional Studies
8.1 Risk AssessmentAccident can occur in every industry in spite of efforts to prevent them. Frequently they
give rise to suffering and damage, the extent of which is, in part, determined by the
potential for loss, surrounding the event. Some of the industries coming up in the
Rakamcherla Industrial Park have high potential for loss and there have been cases, where
loss, measured in both human and monetary terms, has been severe. It is equally true to
say that there have been other cases where, because of effective action taken at the time,
the full potential loss has been largely avoided. Effective action, in these cases, has been
possible due to the existence of pre-planned and practiced procedures for handling major
emergencies utilizing the combined resources of the industrial concern and outside
services.
Section 41-B (4) of the Factories Act, 1948 requires that every occupier of a Hazardous
and Non-hazardous factor shall draw up and onsite emergency plan and detailed disaster
control measures for the factory and make known to the workers and the general public in
the vicinity, the safety measures required to be taken in the event of an emergency taking
place.
8.2 Disaster Management Plan
Despite of all efforts made accidents do occur which need immediate attention. The risks
involved in this project have been identified and their mitigation measures have been
proposed. But when serious accidents occur & negligence could result in loss of life the
whole thing has to be handled in a systematic well planned manner. Accordingly
following plan of disaster management has been evolved:-
8.2.1 Major Activities
Broadly Disaster Management Plan mainly includes;
Pre - Emergency Preparedness
Emergency actions and
Post Emergency activities
Rakamcherla IP - EIA Additional Studies
185
These activities are aimed at facing any emergency so that at the required time there isno disaster and everything is handled in a very effective manner.
8.2.2 Pre-Emergency Preparedness
The activities falling in this category are carried out in a normal situation without any
reference to any particular accident / hazard. They are of a precautionary nature. These
normally include:
Internal safety
Non-destructive testing (NDT)
Fire fighting system testing
Mock drills
Training
Productive equipment
Communication
Emergency lights
Emergency control Room
Assembly points
Liaison with state authorities
Hospital activities
Outside shelters
8.2.3 Emergency Actions
During emergency the staff at various levels is expected to work in coordinated
manner with pre-assigned duties to meet the emergency situation and bring normally
with the help of the resources available within and outside the premises. Availability
and correct use of different means of communication and control is very important
during emergency time. Duties of the various persons shall be defined properly.
8.2.4 Post Emergency Procedures
After the emergency is over investigations are required to be made to establish the
reasons for emergency and preventative measures needed for future happenings.
These activities include:
Rakamcherla IP - EIA Additional Studies
185
These activities are aimed at facing any emergency so that at the required time there isno disaster and everything is handled in a very effective manner.
8.2.2 Pre-Emergency Preparedness
The activities falling in this category are carried out in a normal situation without any
reference to any particular accident / hazard. They are of a precautionary nature. These
normally include:
Internal safety
Non-destructive testing (NDT)
Fire fighting system testing
Mock drills
Training
Productive equipment
Communication
Emergency lights
Emergency control Room
Assembly points
Liaison with state authorities
Hospital activities
Outside shelters
8.2.3 Emergency Actions
During emergency the staff at various levels is expected to work in coordinated
manner with pre-assigned duties to meet the emergency situation and bring normally
with the help of the resources available within and outside the premises. Availability
and correct use of different means of communication and control is very important
during emergency time. Duties of the various persons shall be defined properly.
8.2.4 Post Emergency Procedures
After the emergency is over investigations are required to be made to establish the
reasons for emergency and preventative measures needed for future happenings.
These activities include:
Rakamcherla IP - EIA Additional Studies
185
These activities are aimed at facing any emergency so that at the required time there isno disaster and everything is handled in a very effective manner.
8.2.2 Pre-Emergency Preparedness
The activities falling in this category are carried out in a normal situation without any
reference to any particular accident / hazard. They are of a precautionary nature. These
normally include:
Internal safety
Non-destructive testing (NDT)
Fire fighting system testing
Mock drills
Training
Productive equipment
Communication
Emergency lights
Emergency control Room
Assembly points
Liaison with state authorities
Hospital activities
Outside shelters
8.2.3 Emergency Actions
During emergency the staff at various levels is expected to work in coordinated
manner with pre-assigned duties to meet the emergency situation and bring normally
with the help of the resources available within and outside the premises. Availability
and correct use of different means of communication and control is very important
during emergency time. Duties of the various persons shall be defined properly.
8.2.4 Post Emergency Procedures
After the emergency is over investigations are required to be made to establish the
reasons for emergency and preventative measures needed for future happenings.
These activities include:
Rakamcherla IP - EIA Additional Studies
186
Collection of records
Conducting enquiries
Making insurance claims, if any,
Preparation of enquiry report and suggestion
Implementation of enquiry report and recommendations.
Rehabilitation of affected persons.
8.2.5 Emergency Plan
This includes following actions;
A. Site Layout
Site plan of the Plant will be kept at a conveniently approachable place. The plan will
show the storage site of the various materials along with the details of the surrounding
areas. This gives a layout of the Buildings and other facilities like roads, open and
work areas etc.
B. Emergency Control Centre
The Control Centre will be established within the premises which will be marked on
the site plan. It will be the focal point from where all operations to handle the
emergency will be directed and coordinated. It will have internal and external
telephone communications along with list of essential telephone numbers and list of
key persons and their addresses.
C. Assembly Point
Assembly area will be earmarked for the people to get together in case of emergency
which will be away from material storage. A list of all the employees/ will be
available at this site so that their roll call could be taken and missing person, if any,
could be located.
D. Emergency Alarm System
An audible emergency alarm system will be installed in the premises. It will be
operated from at least 4 different points spread over the entire area and clearly
marked as “Emergency Area Switch”. The system will be tested regularly. The alarm
Rakamcherla IP - EIA Additional Studies
186
Collection of records
Conducting enquiries
Making insurance claims, if any,
Preparation of enquiry report and suggestion
Implementation of enquiry report and recommendations.
Rehabilitation of affected persons.
8.2.5 Emergency Plan
This includes following actions;
A. Site Layout
Site plan of the Plant will be kept at a conveniently approachable place. The plan will
show the storage site of the various materials along with the details of the surrounding
areas. This gives a layout of the Buildings and other facilities like roads, open and
work areas etc.
B. Emergency Control Centre
The Control Centre will be established within the premises which will be marked on
the site plan. It will be the focal point from where all operations to handle the
emergency will be directed and coordinated. It will have internal and external
telephone communications along with list of essential telephone numbers and list of
key persons and their addresses.
C. Assembly Point
Assembly area will be earmarked for the people to get together in case of emergency
which will be away from material storage. A list of all the employees/ will be
available at this site so that their roll call could be taken and missing person, if any,
could be located.
D. Emergency Alarm System
An audible emergency alarm system will be installed in the premises. It will be
operated from at least 4 different points spread over the entire area and clearly
marked as “Emergency Area Switch”. The system will be tested regularly. The alarm
Rakamcherla IP - EIA Additional Studies
186
Collection of records
Conducting enquiries
Making insurance claims, if any,
Preparation of enquiry report and suggestion
Implementation of enquiry report and recommendations.
Rehabilitation of affected persons.
8.2.5 Emergency Plan
This includes following actions;
A. Site Layout
Site plan of the Plant will be kept at a conveniently approachable place. The plan will
show the storage site of the various materials along with the details of the surrounding
areas. This gives a layout of the Buildings and other facilities like roads, open and
work areas etc.
B. Emergency Control Centre
The Control Centre will be established within the premises which will be marked on
the site plan. It will be the focal point from where all operations to handle the
emergency will be directed and coordinated. It will have internal and external
telephone communications along with list of essential telephone numbers and list of
key persons and their addresses.
C. Assembly Point
Assembly area will be earmarked for the people to get together in case of emergency
which will be away from material storage. A list of all the employees/ will be
available at this site so that their roll call could be taken and missing person, if any,
could be located.
D. Emergency Alarm System
An audible emergency alarm system will be installed in the premises. It will be
operated from at least 4 different points spread over the entire area and clearly
marked as “Emergency Area Switch”. The system will be tested regularly. The alarm
Rakamcherla IP - EIA Additional Studies
187
will signify to the persons & staff that the emergency has occurred and emergency
services should be put in operation. The Public Address System will also be activated
and specific instructions for eventualities will be passed on to the staff.
8.2.6 Service & Control
8.2.6.1 Emergency Services
This includes Fire fighting, First Aid and rescue teams. Alternative source of power
supply for operating fire pumps and communication with local bodies and fire brigade
etc. shall be given.
8.2.6.2 Control Centre
The control centre could be either in Security room or Fire Station and shall have:
Adequate No. of Internal and external telephones
Layout Plan of the buildings showing
Sources of safety equipment
Fire hydrant system and alternate supply source
Stock of other fire fighting materials
Assembly points & first aid centers
Surrounding habitation within ½ km distance
Additional work plans which may illustrate during emergency
areas affected / endangered
deployment of emergency vehicles and personnel
Areas where particular problems arise e.g. fractured pipe-line.
Areas evacuated
Normal roll of employees
List of key persons and their addresses with telephone numbers
Note pads, pencils, etc, to record messages received and instructions to be
passed on through runners
A tape recorder on which the incident and actions, being taken and progress
could be recorded
Rakamcherla IP - EIA Additional Studies
187
will signify to the persons & staff that the emergency has occurred and emergency
services should be put in operation. The Public Address System will also be activated
and specific instructions for eventualities will be passed on to the staff.
8.2.6 Service & Control
8.2.6.1 Emergency Services
This includes Fire fighting, First Aid and rescue teams. Alternative source of power
supply for operating fire pumps and communication with local bodies and fire brigade
etc. shall be given.
8.2.6.2 Control Centre
The control centre could be either in Security room or Fire Station and shall have:
Adequate No. of Internal and external telephones
Layout Plan of the buildings showing
Sources of safety equipment
Fire hydrant system and alternate supply source
Stock of other fire fighting materials
Assembly points & first aid centers
Surrounding habitation within ½ km distance
Additional work plans which may illustrate during emergency
areas affected / endangered
deployment of emergency vehicles and personnel
Areas where particular problems arise e.g. fractured pipe-line.
Areas evacuated
Normal roll of employees
List of key persons and their addresses with telephone numbers
Note pads, pencils, etc, to record messages received and instructions to be
passed on through runners
A tape recorder on which the incident and actions, being taken and progress
could be recorded
Rakamcherla IP - EIA Additional Studies
187
will signify to the persons & staff that the emergency has occurred and emergency
services should be put in operation. The Public Address System will also be activated
and specific instructions for eventualities will be passed on to the staff.
8.2.6 Service & Control
8.2.6.1 Emergency Services
This includes Fire fighting, First Aid and rescue teams. Alternative source of power
supply for operating fire pumps and communication with local bodies and fire brigade
etc. shall be given.
8.2.6.2 Control Centre
The control centre could be either in Security room or Fire Station and shall have:
Adequate No. of Internal and external telephones
Layout Plan of the buildings showing
Sources of safety equipment
Fire hydrant system and alternate supply source
Stock of other fire fighting materials
Assembly points & first aid centers
Surrounding habitation within ½ km distance
Additional work plans which may illustrate during emergency
areas affected / endangered
deployment of emergency vehicles and personnel
Areas where particular problems arise e.g. fractured pipe-line.
Areas evacuated
Normal roll of employees
List of key persons and their addresses with telephone numbers
Note pads, pencils, etc, to record messages received and instructions to be
passed on through runners
A tape recorder on which the incident and actions, being taken and progress
could be recorded
Rakamcherla IP - EIA Additional Studies
188
It would be useful if these plans be covered with plastic/glass sheets on which felt ink
markings can be deciphered.
8.2.7 Roll Call
A Roll Call board listing the names of all persons department wise and shift wise
should be placed in the allocated places called assembly points. All personnel
including visitors and contractors except those who are detailed to fight emergency to
man such services, shall proceed to such allocated points as soon as an evacuation is
ordered over PAS or orally by the section in charge and roll call taken. Section
incharge should see that these boards are always kept up-to-date. The assembly point
incharge shall report to control room immediately any absentee/unaccounted for
persons. He will also keep the group until advised to move or return to work by the
site controller or any other person pre-nominated by him.
8.2.7.1 Key Personnel and Their Duties
Following persons will be designated for emergency situation;
1. Site Controller
2. Incident Controller
3. Personnel / Administrative Managers
4. Communication Officers
5. Telephone Operator
6. Engineer Incharge and Electrician
7. Fire Pump Attendants
8. First Aid
8.3 Public Hearing
As per the ToR issued by the project, Public Hearing shall be conduct for the project and
the draft EIA report is submitting for conducting Public Hearing.
Rakamcherla IP - EIA Additional Studies
188
It would be useful if these plans be covered with plastic/glass sheets on which felt ink
markings can be deciphered.
8.2.7 Roll Call
A Roll Call board listing the names of all persons department wise and shift wise
should be placed in the allocated places called assembly points. All personnel
including visitors and contractors except those who are detailed to fight emergency to
man such services, shall proceed to such allocated points as soon as an evacuation is
ordered over PAS or orally by the section in charge and roll call taken. Section
incharge should see that these boards are always kept up-to-date. The assembly point
incharge shall report to control room immediately any absentee/unaccounted for
persons. He will also keep the group until advised to move or return to work by the
site controller or any other person pre-nominated by him.
8.2.7.1 Key Personnel and Their Duties
Following persons will be designated for emergency situation;
1. Site Controller
2. Incident Controller
3. Personnel / Administrative Managers
4. Communication Officers
5. Telephone Operator
6. Engineer Incharge and Electrician
7. Fire Pump Attendants
8. First Aid
8.3 Public Hearing
As per the ToR issued by the project, Public Hearing shall be conduct for the project and
the draft EIA report is submitting for conducting Public Hearing.
Rakamcherla IP - EIA Additional Studies
188
It would be useful if these plans be covered with plastic/glass sheets on which felt ink
markings can be deciphered.
8.2.7 Roll Call
A Roll Call board listing the names of all persons department wise and shift wise
should be placed in the allocated places called assembly points. All personnel
including visitors and contractors except those who are detailed to fight emergency to
man such services, shall proceed to such allocated points as soon as an evacuation is
ordered over PAS or orally by the section in charge and roll call taken. Section
incharge should see that these boards are always kept up-to-date. The assembly point
incharge shall report to control room immediately any absentee/unaccounted for
persons. He will also keep the group until advised to move or return to work by the
site controller or any other person pre-nominated by him.
8.2.7.1 Key Personnel and Their Duties
Following persons will be designated for emergency situation;
1. Site Controller
2. Incident Controller
3. Personnel / Administrative Managers
4. Communication Officers
5. Telephone Operator
6. Engineer Incharge and Electrician
7. Fire Pump Attendants
8. First Aid
8.3 Public Hearing
As per the ToR issued by the project, Public Hearing shall be conduct for the project and
the draft EIA report is submitting for conducting Public Hearing.
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189
Chapter 9
Project benefits
Rakamcherla IP - EIA Project Benefits
189
Chapter 9
Project benefits
Rakamcherla IP - EIA Project Benefits
189
Chapter 9
Project benefits
Rakamcherla IP - EIA Project Benefits
190
9 Project Benefits
The proposed Industrial Park at Rakamcherla will promote industrial activity in the
region to meet a growing demand in the services sector, and to enhance future economic
growth within the region. The sub region surrounding the site is undergoing significant
change in recent year as a result of both commercial and industrial activity. Some of the
major benefits from the proposed project are as follows:
The proposed project will create employment opportunities for the surrounding
populations directly or indirectly during and after plant setup, which will enhance the
overall growth of the surrounding regions.
This apart, the park setup will create an environment of indirect employment for loading,
unloading, transportation and other peripheral activities including cultural, educational,
small industries and hotel industries around the area.
This is a very positive socio-economic benefit to the region, which will help contribute to
the metal re-rolling sector, and will assist in the overall growth of the adjacent areas.
The proposed industrial park will also help to accommodate the relocation of several
industries from the densely populated state capital.
There is no R&R study involved for the project. The project site shall require no
displacement of habitation and away from the habitation area.
Socio-economic benefit to the locals as it would provide employment during construction
and in operation phase
TSIIC is providing 14.94% of green belt. Individual industries will be emphasized to
provide adequate green belt, so that 33% green belt is achieved.
The project site will have special approach roads being developed by the government and
thus will lead to hindrance free approach for transportation of heavy equipment without
causing any problems for the public.
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190
9 Project Benefits
The proposed Industrial Park at Rakamcherla will promote industrial activity in the
region to meet a growing demand in the services sector, and to enhance future economic
growth within the region. The sub region surrounding the site is undergoing significant
change in recent year as a result of both commercial and industrial activity. Some of the
major benefits from the proposed project are as follows:
The proposed project will create employment opportunities for the surrounding
populations directly or indirectly during and after plant setup, which will enhance the
overall growth of the surrounding regions.
This apart, the park setup will create an environment of indirect employment for loading,
unloading, transportation and other peripheral activities including cultural, educational,
small industries and hotel industries around the area.
This is a very positive socio-economic benefit to the region, which will help contribute to
the metal re-rolling sector, and will assist in the overall growth of the adjacent areas.
The proposed industrial park will also help to accommodate the relocation of several
industries from the densely populated state capital.
There is no R&R study involved for the project. The project site shall require no
displacement of habitation and away from the habitation area.
Socio-economic benefit to the locals as it would provide employment during construction
and in operation phase
TSIIC is providing 14.94% of green belt. Individual industries will be emphasized to
provide adequate green belt, so that 33% green belt is achieved.
The project site will have special approach roads being developed by the government and
thus will lead to hindrance free approach for transportation of heavy equipment without
causing any problems for the public.
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9 Project Benefits
The proposed Industrial Park at Rakamcherla will promote industrial activity in the
region to meet a growing demand in the services sector, and to enhance future economic
growth within the region. The sub region surrounding the site is undergoing significant
change in recent year as a result of both commercial and industrial activity. Some of the
major benefits from the proposed project are as follows:
The proposed project will create employment opportunities for the surrounding
populations directly or indirectly during and after plant setup, which will enhance the
overall growth of the surrounding regions.
This apart, the park setup will create an environment of indirect employment for loading,
unloading, transportation and other peripheral activities including cultural, educational,
small industries and hotel industries around the area.
This is a very positive socio-economic benefit to the region, which will help contribute to
the metal re-rolling sector, and will assist in the overall growth of the adjacent areas.
The proposed industrial park will also help to accommodate the relocation of several
industries from the densely populated state capital.
There is no R&R study involved for the project. The project site shall require no
displacement of habitation and away from the habitation area.
Socio-economic benefit to the locals as it would provide employment during construction
and in operation phase
TSIIC is providing 14.94% of green belt. Individual industries will be emphasized to
provide adequate green belt, so that 33% green belt is achieved.
The project site will have special approach roads being developed by the government and
thus will lead to hindrance free approach for transportation of heavy equipment without
causing any problems for the public.
Rakamcherla IP - EIA Summary & Conclusion
191
Chapter 10
Summary and Conclusion
Rakamcherla IP - EIA Summary & Conclusion
191
Chapter 10
Summary and Conclusion
Rakamcherla IP - EIA Summary & Conclusion
191
Chapter 10
Summary and Conclusion
Rakamcherla IP - EIA Summary & Conclusion
192
10 Summary and Conclusion
The proposed industrial park at Rakamcherla is a significant development within the
context of the Pudur Mandal, in the Vikarabad District of Telangana and potentially India.
In line with the requirements of the EIA Regulations (2006), this Environmental Impact
Assessment (EIA) Report has provided a description of the development and its associated
activities including descriptions of the pre-development environmental, specifically in
terms of the biophysical and socio-economic environment of the study area. In addition,
there is a full explanation of the methodology undertaken during the EIA Phase and public
participation Process. Most importantly the report addresses the impacts identified during
the scoping phase that were anticipated for the development, as well as providing
mitigation measures to ensure environmentally sustainable development of Rakamcherla
Industrial Park. The Rakamcherla IP will contribute to sustainable job creation of direct
and indirect employments. While such job creation will lead to concentration within this
heavy industrial and business hub will result in the influx of people to the area and the
associated social ills, these can be curbed by ensuring local employment and proper
security. The negative impacts will be minimal when compared to the positive.
1 However, it is important to take cognizance of the fact that in its present state, the site has
little negative impact on the natural environment when compared with the proposed
development. These impacts however, can be carefully mitigated to validate and support
the fact that such a development will contribute significantly to the socio-economic
progress of the area.
2 The Incremental GLC of SOX, NOX, PM analyzed and modeled along with baseline data
and found all the parameters are well within NAAQ permissible limits of air quality.
3 With mitigation and management measures adhered to, there are no negative impacts in
the impact assessment; therefore the impacts associated with the Rakamcherla industrial
park are at an acceptable level.
4 The Rakamcherla Industrial Park positively offers the potential of creating a vibrant,
integrated commercial business park as well as brings the needed infrastructure services,
jobs and revenue to Pudur Mandal.
Rakamcherla IP - EIA Summary & Conclusion
192
10 Summary and Conclusion
The proposed industrial park at Rakamcherla is a significant development within the
context of the Pudur Mandal, in the Vikarabad District of Telangana and potentially India.
In line with the requirements of the EIA Regulations (2006), this Environmental Impact
Assessment (EIA) Report has provided a description of the development and its associated
activities including descriptions of the pre-development environmental, specifically in
terms of the biophysical and socio-economic environment of the study area. In addition,
there is a full explanation of the methodology undertaken during the EIA Phase and public
participation Process. Most importantly the report addresses the impacts identified during
the scoping phase that were anticipated for the development, as well as providing
mitigation measures to ensure environmentally sustainable development of Rakamcherla
Industrial Park. The Rakamcherla IP will contribute to sustainable job creation of direct
and indirect employments. While such job creation will lead to concentration within this
heavy industrial and business hub will result in the influx of people to the area and the
associated social ills, these can be curbed by ensuring local employment and proper
security. The negative impacts will be minimal when compared to the positive.
1 However, it is important to take cognizance of the fact that in its present state, the site has
little negative impact on the natural environment when compared with the proposed
development. These impacts however, can be carefully mitigated to validate and support
the fact that such a development will contribute significantly to the socio-economic
progress of the area.
2 The Incremental GLC of SOX, NOX, PM analyzed and modeled along with baseline data
and found all the parameters are well within NAAQ permissible limits of air quality.
3 With mitigation and management measures adhered to, there are no negative impacts in
the impact assessment; therefore the impacts associated with the Rakamcherla industrial
park are at an acceptable level.
4 The Rakamcherla Industrial Park positively offers the potential of creating a vibrant,
integrated commercial business park as well as brings the needed infrastructure services,
jobs and revenue to Pudur Mandal.
Rakamcherla IP - EIA Summary & Conclusion
192
10 Summary and Conclusion
The proposed industrial park at Rakamcherla is a significant development within the
context of the Pudur Mandal, in the Vikarabad District of Telangana and potentially India.
In line with the requirements of the EIA Regulations (2006), this Environmental Impact
Assessment (EIA) Report has provided a description of the development and its associated
activities including descriptions of the pre-development environmental, specifically in
terms of the biophysical and socio-economic environment of the study area. In addition,
there is a full explanation of the methodology undertaken during the EIA Phase and public
participation Process. Most importantly the report addresses the impacts identified during
the scoping phase that were anticipated for the development, as well as providing
mitigation measures to ensure environmentally sustainable development of Rakamcherla
Industrial Park. The Rakamcherla IP will contribute to sustainable job creation of direct
and indirect employments. While such job creation will lead to concentration within this
heavy industrial and business hub will result in the influx of people to the area and the
associated social ills, these can be curbed by ensuring local employment and proper
security. The negative impacts will be minimal when compared to the positive.
1 However, it is important to take cognizance of the fact that in its present state, the site has
little negative impact on the natural environment when compared with the proposed
development. These impacts however, can be carefully mitigated to validate and support
the fact that such a development will contribute significantly to the socio-economic
progress of the area.
2 The Incremental GLC of SOX, NOX, PM analyzed and modeled along with baseline data
and found all the parameters are well within NAAQ permissible limits of air quality.
3 With mitigation and management measures adhered to, there are no negative impacts in
the impact assessment; therefore the impacts associated with the Rakamcherla industrial
park are at an acceptable level.
4 The Rakamcherla Industrial Park positively offers the potential of creating a vibrant,
integrated commercial business park as well as brings the needed infrastructure services,
jobs and revenue to Pudur Mandal.
Rakamcherla IP - EIA Summary & Conclusion
193
5 The development of Rakamcherla Industrial Park is therefore not only inevitable but a
necessity and will ultimately provide a significant overall societal gain including
environmental, social and economic benefits which will provide the basis for a value
adding sustainable development. There is a huge need for new industrial space in the city
and the need for new subsidy housing is unquestionable.
6 The ‘negative’ impacts on environmental resources are, in the broader context,
insignificant and immaterial to the ultimate success of the development.
7 The development will actually enable management of a substantial amount of open space
provided such space is an integral component of the development and enabled to be
appropriately utilized by the resident community.
8 Careful planning has created value by incorporating the open space within the design
conceived in a manner that serves as a lattice that allows for continuity for habitat and for
recreational purposes.
With the above benefits, and the environmental and societal commitment and readiness of
the project, the environmental impact assessment report strongly affirms and recommends
the proposed project.
Rakamcherla IP - EIA Summary & Conclusion
193
5 The development of Rakamcherla Industrial Park is therefore not only inevitable but a
necessity and will ultimately provide a significant overall societal gain including
environmental, social and economic benefits which will provide the basis for a value
adding sustainable development. There is a huge need for new industrial space in the city
and the need for new subsidy housing is unquestionable.
6 The ‘negative’ impacts on environmental resources are, in the broader context,
insignificant and immaterial to the ultimate success of the development.
7 The development will actually enable management of a substantial amount of open space
provided such space is an integral component of the development and enabled to be
appropriately utilized by the resident community.
8 Careful planning has created value by incorporating the open space within the design
conceived in a manner that serves as a lattice that allows for continuity for habitat and for
recreational purposes.
With the above benefits, and the environmental and societal commitment and readiness of
the project, the environmental impact assessment report strongly affirms and recommends
the proposed project.
Rakamcherla IP - EIA Summary & Conclusion
193
5 The development of Rakamcherla Industrial Park is therefore not only inevitable but a
necessity and will ultimately provide a significant overall societal gain including
environmental, social and economic benefits which will provide the basis for a value
adding sustainable development. There is a huge need for new industrial space in the city
and the need for new subsidy housing is unquestionable.
6 The ‘negative’ impacts on environmental resources are, in the broader context,
insignificant and immaterial to the ultimate success of the development.
7 The development will actually enable management of a substantial amount of open space
provided such space is an integral component of the development and enabled to be
appropriately utilized by the resident community.
8 Careful planning has created value by incorporating the open space within the design
conceived in a manner that serves as a lattice that allows for continuity for habitat and for
recreational purposes.
With the above benefits, and the environmental and societal commitment and readiness of
the project, the environmental impact assessment report strongly affirms and recommends
the proposed project.
Rakamcherla IP - EIA Disclosure of Consultants
194
Chapter 11Disclosure of consultants
Rakamcherla IP - EIA Disclosure of Consultants
194
Chapter 11Disclosure of consultants
Rakamcherla IP - EIA Disclosure of Consultants
194
Chapter 11Disclosure of consultants
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195
11 Disclosure of Consultants Engaged
Details of the consultant engaged are as follows:
Table 11-1 Details of the Consultant
Consultant Hubert Enviro Care Systems Pvt. Ltd., Chennai
NABET Sr. No 89
Following are the Accreditations of the consultant;
National Accreditation Board for Testing and Calibration Laboratories (NABL)
accreditation for Laboratory services for ISO17025
MoEF&CC Recognized Laboratory
ISO 9001:2008 qualified and certification by URS
Environmental Management System complying AS/NZS ISO 14001:2004
Occupational Health & Safety Management System OHSAS 18001:2007
Approved by Karnataka PCB and Kerala PCB.
Achilles joint qualification system. Achilles Id.15148
Kiwa Quality Management System
Closed Piping systemSolid Handling System
Mass Flow Meter
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195
11 Disclosure of Consultants Engaged
Details of the consultant engaged are as follows:
Table 11-1 Details of the Consultant
Consultant Hubert Enviro Care Systems Pvt. Ltd., Chennai
NABET Sr. No 89
Following are the Accreditations of the consultant;
National Accreditation Board for Testing and Calibration Laboratories (NABL)
accreditation for Laboratory services for ISO17025
MoEF&CC Recognized Laboratory
ISO 9001:2008 qualified and certification by URS
Environmental Management System complying AS/NZS ISO 14001:2004
Occupational Health & Safety Management System OHSAS 18001:2007
Approved by Karnataka PCB and Kerala PCB.
Achilles joint qualification system. Achilles Id.15148
Kiwa Quality Management System
Closed Piping systemSolid Handling System
Mass Flow Meter
Rakamcherla IP - EIA Disclosure of Consultants
195
11 Disclosure of Consultants Engaged
Details of the consultant engaged are as follows:
Table 11-1 Details of the Consultant
Consultant Hubert Enviro Care Systems Pvt. Ltd., Chennai
NABET Sr. No 89
Following are the Accreditations of the consultant;
National Accreditation Board for Testing and Calibration Laboratories (NABL)
accreditation for Laboratory services for ISO17025
MoEF&CC Recognized Laboratory
ISO 9001:2008 qualified and certification by URS
Environmental Management System complying AS/NZS ISO 14001:2004
Occupational Health & Safety Management System OHSAS 18001:2007
Approved by Karnataka PCB and Kerala PCB.
Achilles joint qualification system. Achilles Id.15148
Kiwa Quality Management System
Closed Piping systemSolid Handling System
Mass Flow Meter