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Draft Environment Impact Assessment
Report
Expansion of Sugar Industry from
7500 TCD to 10000 TCD
By
M/s. Shree Renuka Sugars limited
Survey R.S No. 367/1, Munoli Village,
Saundatti Taluk, Belagavi District,
Karnataka State.
Prepared by
SAMRAKSHAN,
F- 4, Ist Floor, Swastik Manandi Arcade,
SC Road, Sheshadripuram,
Bangalore - 560 020
SL NO DESCRIPTION PAGE NO
CHAPTER 1 INTRODUCTION 01 - 23
1.0 Purpose of the report 01
1.1 Identification of the Project & Project Proponent 01
1.1.1 Introduction to the Project Proponent 01
1.1.2 Introduction to the Project 02
1.2 Brief Description of Nature, Size, Location of the Project & its importance to the Country, Region
02
1.2.1 Nature, Size & Location of the Project 02
1.2.2 Importance to the Country and Region 04
1.2.2.1 Scenario of Production of Sugar Cane 05 1.2.3 Demand Supply Gap, Imports Vs Indigenous Production 06
1.2.4 Export Possibility 07
1.3 Scope Of Study – Details of Regulatory Scoping Carried Out (As Per Terms of Reference)
07
1.3.1 Scope of Study 07
1.3.1.1 Details of the Study 07 1.3.1.2 Methodology of the Study 07
1.3.1.3 Study Area Details 08
1.4 Generic Structure of EIA Document 22
CHAPTER 2 PROJECT DESCRIPTION 24 - 67
2.0 Type of Project 24
2.1 Need for the Project 24
2.2 Location of the Proposed Industry 24 2.3 Size or Magnitude of Operation 28
2.4 Proposed Schedule for Approval & Implementation 28
2.5 Proposed Layout Plan 28
2.6 Site Bearings 29 2.7 Raw Materials 33
2.7.1 Power and Steam requirement 33
2.8 Technology & Process description 34
2.8.1 Manufacture of Sugar 34 2.8.2 Storage facility for Raw Materials and Products 42
2.8.2.1 Sugar Cane storage 42
2.8.2.2 Refined Sugar and Ethanol 42
2.8.2.3 Molasses storage capacity 43 2.8.2.4 Alcohol storage capacity 43
2.9 Project description including Drawings showing Project Layout, Components of Project.
44
2.10 Mitigation measures incorporated into the project to meet Environmental Standards, Environmental operating conditions or other EIA requirements (As required by the scope)
44
2.10.1 Water demand and wastewater/Effluent discharge 44
2.10.1.1 Source of water supply 44
2.10.1.2 Water demand and wastewater discharge during operation phase 44 2.10.1.3 Process Effluent characteristics 49
2.10.1.4 Description of wastewater treatment scheme & Effluent treatment procedure 50
2.10.2 Power 58 2.10.3 Air Pollution sources 58
2.10.4 Noise generation and its management 62
2.10.5 Solid Waste generation and management 62
2.10.5.1 Bagasse 63 2.10.5.2 Molasses 63
2.10.5.3 Press Mud 63
2.10.5.4 Boiler Ash 63
2.10.5.5 ETP Sludge 63 2.10.5.6 Lime Sludge 64
2.10.6 Hazardous Waste Generation and its Management 64
2.10.7 Composting of Press Mud with Spent Wash 64
2.10.7.1 Composting Process 65 2.10.7.2 Construction of Compost Yard 65
2.10.7.3 Equipments and Machineries for Compost Process 65
2.11 Schematic representations of the Feasibility Drawing which give information of EIA Purpose.
66
2.12 Rainwater Harvesting & Groundwater Recharging 67
2.13 Assessment of New & Untested Technology for the Risk of technological failure 67 CHAPTER 3 DESCRIPTION OF THE ENVIRONMENT 68 - 119
3.0 Introduction 68
3.1 Study Area, Period, Components & Methodology 68
3.2 Establishment of baseline 71
3.2.1 Meteorological Data 71 3.2.1.1 Temperature 73
3.2.1.2 Rainy days 73
3.2.1.3 Wind Speed 73
3.2.1.4 Humidity & Cloud 79 3.2.1.5 Atmospheric Pressure 79
3.2.1.6 Mixing Height or Inversion 79
3.3 Baseline Data 80
3.3.1 Baseline Monitoring 80 3.3.1.1 Sampling and Analytical techniques 80
3.4 Air Quality 81
3.4.1 Air Quality at the Project Site and other locations 82
3.4.2 Observations 85 3.5 Noise Environment 86
3.5.1 Observations 87
3.5.2 Traffic Study 87
3.6 Water Environment 88
3.6.1 Reconnaissance Survey 88
3.6.2 Surface Water 88
3.6.3 Observations of Surface Water Quality 95 3.6.4 Ground Water 96
3.6.5 Observations 101
3.7 Soil and Geology 102 3.7.1 Observations 106
3.8 Hydrology and Hydrogeology 107
3.9 Ecology 108
3.9.1 Anticipated Impacts 108 3.9.2 Flora 108
3.9.3 Fauna 110
3.10 Socio-Economic Environment 111
3.10.1 Demographic structure 111 3.10.2 Literacy levels 112
3.10.3 Social Infrastructure available 113
3.11 Connectivity 113
3.12 Base Maps of all Environmental components 118 CHAPTER 4
ANTICIPATED ENVIRONMENTAL IMPACTS & MITIGATION MEASURES
120 - 133
4.0 Details of Investigated Environmental Impacts due to Project Location, Possible Accidents, Project Design, Project Construction, Regular Operations, Final Decommissioning or Rehabilitation of completed Project
120
4.1 Environmental Impacts due to Project Location, Possible accidents, Project design
120
4.1.1 Introduction 120
4.1.2 Impact due to Project Location 120
4.1.3 Project Design 121 4.2 Measures for minimizing & / or offsetting adverse impacts identified 121
4.2.1 Air Environment 121
4.2.1.1 Air Environment mitigation measures 123
4.2.2 Noise Environment 123
4.2.2.1 Noise Environment mitigation measures: 124
4.2.3 Water Environment 124 4.2.3.1 Water Environment mitigation measures 126
4.2.4 Land and Biological Environment 127
4.2.4.1 Land Environment mitigation measures 127 4.2.5 Socio-Economic Environment 128
4.2.6 Odor Management for Sugar Unit 129
4.2.6.1 Odor Mitigation measures 129
4.3 Irreversible & Irretrievable constraints of Environmental components 129 4.4 Assessment of significance of Impacts (Criteria for Determining Significance,
Assigning Significance) 130
4.4.1 Impact Matrix 130
4.4.2 Environmental Impact Assessment 130
CHAPTER 5
ANALYSIS OF ALTERNATIVES
(TECHNOLOGY & SITE)
134
CHAPTER 6
ENVIRONMENTAL MONITORING PROGRAM
135 – 140
6.0 Technical aspects of monitoring the effectiveness of mitigation measures (Including Measurement Methodologies, Frequency, Location, Data Analysis, Reporting Schedules, Emergency Procedures, Detailed Budget & Procurement schedules)
135
6.1 Measurement methodology 135
6.2 Frequency, Location, Data Analysis, Reporting schedules 136
6.3 Budget provisions for Environmental monitoring program 137
6.4 Emergency procedures 138 6.4.1 Emergency organization structure 139
6.4.2 Emergency co-ordinates 139
6.5 Compliances to Environmental statutes 139
6.6 Monitoring of compliances to statutory conditions 140 CHAPTER 7
ADDITIONAL STUDIES
141 -
7.0 Public consultation 141
7.1 Risk assessment and Hazard analysis 141
7.1.1 Introduction 141 7.1.2 On-Site Emergency 142
7.1.3 Off-Site Emergency 142
7.2 Risk Assessment 142
7.3 Structure of Emergency management 144
7.3.1 Emergency organization 145
7.3.2 Emergency Control Room (ECR) 145
7.3.3 Implements for repair safety gears 147
7.3.4 Assembly points 149 7.4 Action Plan for control of Emergency 149
7.4.1 Identification and Assessment of Hazards 149
7.4.2 Declaration of Emergency 150
7.4.3 Functions of Emergency management personnel 150 7.5 Emergency shut down of plants 153
7.6 Evacuation of personnel 153
7.7 Accounting of personnel 154
7.8 Information to the relatives of affected people 154 7.9 Medical Treatment 154
7.10 Security 155
7.11 Law and Order 155
7.12 All Clear signal 155 7.13 Intimation to authorities 156
7.14 Relief and rehabilitation 157 7.15 Review of incidence 157
7.16 Update of Emergency plan 157
7.17 Training and rehearsal 157 7.18 Air Pollution dispersion modelling studies 158
7.18.1 Introduction 158
7.18.2 Model Input Data 158
7.18.3 Presentation of results 159 7.18.4 Comments 169
7.19 Social Impact Assessment, R&R Action Plans 170
CHAPTER 8 PROJECT BENEFITS
171 - 172
8.0 Improvements in the Physical Infrastructure 171
8.1 Social Infrastructure 171
8.2 Employment Potential & Tangible Benefits 172
CHAPTER 9 ENVIRONMENTAL MANAGEMENT PLAN (EMP)
173 - 183
9.0 Introduction 173
9.1 Environment components 173 9.2 Environmental monitoring schedule 178
9.3 Schedules 178
9.4 Environmental Management Plan (EMP) 180 9.5 EMP Implementation Schedule 182
9.6 Environmental Policy 182
9.7 Description of the administrative aspects of ensuring that mitigative measures are implemented & their effectiveness monitored, after Approval, Implementation and during operation
183
9.8 Environment Management Cell 183
CHAPTER 10 SUMMARY & CONCLUSION
184 - 185
10.0 Overall justification for implementation of the project 184 10.1 Explanation of how adverse effects have been mitigated 185
CHAPTER 11 DISCLOSURE OF CONSULTANTS ENGAGED
186 - 188
11.0 The names of the consultants engaged with their brief resume & nature of consultancy rendered
186
11.1 Introductory Profile 186
11.2 Professional services offered 186
LIST OF TABLES
Sl. No Description Page No.
1.1 The Capacities of the industry existing and after proposed expansion 02
1.2 Project at glance 03 1.3 Terms of Reference (ToR) 08
2.1 Location features of the Project Site 25
2.2 Cost of the Project 28
2.3 Land-Use Pattern 28 2.4 Raw Materials for Sugar Plant 33
2.5 Details of ware house 35
2.6 Operation Details of the Plant after expansion 41
2.7 Existing water consumption and wastewater Discharge-Sugar Unit, M3/D
45
2.8 After expansion water consumption & wastewater Discharge-Sugar Unit, M3/D
47
2.9 Characteristics of wastewater 49
2.10 Air Pollution sources and control measures 58
2.11 Solid Wastes Management 62
3.1 Co-ordinates W.R.T. all corners 70 3.2 Meteorological Data of Belagavi for the year 2017 72
3.3 Ambient Air Sampling Stations 81
3.4 Air Quality Data Analysis at the Project Site 82
3.5 Ambient Air Quality Standards – MoEF As Per the Notification dated 16th November 2009 for Industrial, Residential & Rural Areas
85
3.6 Observations 86
3.7 Noise Level Monitoring Stations 86 3.8 Noise Quality data analysis at all the locations 87
3.9 Limits as per Environmental Protection Rules, 1986 87
3.10 Surface Water sampling stations 89
3.11 Surface Water Quality Results 90 3.12 Surface Water Quality Standards 95
3.13 Ground Water Quality 97
3.14 Soil Sampling Stations 102
3.15 Physico-Chemical Characteristics of Soil 103 3.16 Flora in the Study Area 109
3.17 Fauna in the Study Area 110
3.18 Distribution of Population 112
3.19 Distribution of literates and literacy levels in the study area for the year 2011
112
3.20 List of infrastructural facilities in the surroundings 113
3.21 Connectivity from the Project Site 114
3.22 Existing Land-Use Pattern 118
4.1 Environmental Impact Assessment 130 4.2 Impact Matrix 132
6.1 Monitoring Schedule for Environmental Parameters 135
7.1 Addresses of Authorities and Services 156 7.2 Data considered for calculation of GLC 158
7.3 Predicted incremental Short-term concentrations due to the Expansion Project
159
7.4 Resultant maximum 24 hourly concentrations 169
9.1 Environmental Management Plan during operation of the Facilities/Utilities
180
9.2 Implementation Schedule for EMP 182
10.1 Measures adopted to Mitigate the Impacts 185
LIST OF FIGURES Sl. No Description Page No.
1.0 Location map 03
2.0 Maps showing project boundary & Project site location 26
2.1 Map showing the project site location on District Map of Belagavi 27 2.2 Plant Layout Plan 30
2.3 Photographs of the Industry 31
2.4 Site Photos showing Greenery Development 32
2.5 Flow Chart for Manufacture of Sugar 39 2.6 Process Flow Chart with Material Balance for Sugar and Co-Gen Unit 40
2.7 Effluent Treatment Plant flow chart 55
2.8 Photographs of the ETP and Online Monitoring Facility 56
2.9 Schematic representations of the Feasibility drawing which give information of EIA purpose.
66
3.0 Location Map of the Project Site 69 3.1 Topo Map of the Study Area 70
3.2 Temperature Chart 73
3.3 Average Rainfall Chart 73
3.4 Windspeed Chart 74 3.5 Humidity Chart 79
3.6 Pressure 79
3.7 Location of Sampling Stations 106
3.8 Google Map showing connectivity to Project Site 114 3.9 Google Map showing surrounding water bodies 115
3.10 Google Map covering 1 Km aerial distance from the project site 116
3.11 Google Map covering 5 Km aerial distance From the project site 117
3.12 Google Map covering 10 Km aerial distance From the project site 118 7.0 Suspended particulate Matter Isotherm 160
7.1 Sulphur Di-Oxide Isotherm 163
7.2 Oxides Of Nitrogen (NOx) Isotherms 166
ANNEXURES
Sl No ANNEXURE 1 Previous EC and CFO
2 Stack emission reports
3 Monitoring reports
4 Annual health status reports
5 Topo map
6 Google map, Site layout
Shree Renuka Sugars limited
Environmental Impact Assessment Report 1
CHAPTER 1 INTRODUCTION
1.0 PURPOSE OF THE REPORT
M/s. Shree Renuka Sugars Ltd (SRSL) is established in the year 1999 at R.S.No.367/1, Munoli
Village, Saundatti Taluk & Belagavi District in Karnataka State for the manufacture of sugar from
sugarcane. In the year 2008 it was expanded to 7,500 TCD of sugar cane crushing with 20.5 MW
to 35.5 MW Cogen power plant. Department of Forests, Environment and Ecology, Bangalore
vide letter no. SEIAA 16 IND 2007 dated 1-7-2008 has issued Environmental Clearance for the
expansion. The Karnataka State Pollution Control Board has issued the consent to establish vide
no PCB/569/CFE/08/275 dated 21.9.2008.
M/s. Shree Renuka Sugars Limited is now operating with 7,500 TCD Sugar Cane crushing (sugar
900 MT/day), 35.5 MW Co-gen power plant and 120 KLD Distillery Unit.
Now it is proposed to expand sugar crushing capacity from 7,500 to 10,000 TCD. The proposed
project will be established in the open area already available in the existing industry.
The sugar industry activity is listed under serial No. 5(j) Category-B in the schedule of the EIA
Notification dated 14-09-2006 of Ministry of Environment and Forests (MoEF & CC),
Government of India. The expansion of Sugar Plant has to obtain Environmental Clearance from
SEIAA before expansion. It is also required to obtain Consent to Establish under the Water Act
& the Air Act from State Pollution Control Board.
The pre-feasibility report was submitted to State Level Expert Appraisal Committee (SEIAA) for
this expansion. The proposal was appraised by SEAC on 28th December 2017 and Project No:
SEIAA 22 IND 2017. The State Level Expert Appraisal Committee, Karnataka, vide letter no.
SEIAA/22/IND 2017 dated 26-03-2018 communicated the Terms of Reference (TOR) for the
study and preparation of EIA report.
The Draft EIA report is prepared for public hearing as per the Terms of Reference issued by
SEIAA.
1.1 IDENTIFICATION OF THE PROJECT & PROJECT PROPONENT
1.1.1 INTRODUCTION TO THE PROJECT PROPONENT
Shree Renuka Sugars Limited (SRSL), the public limited company was registered in the year
1995 to venture agro-based industrial and related activities and is into the business of
Shree Renuka Sugars limited
Environmental Impact Assessment Report 2
production of Sugar, co-gen power and Alcohol. In Karnataka Shree Renuka Sugars Ltd., has
their units and the following location Munoli Village-Saundatti Taluk, Burlatti village-Athani
Taluk, lease of Raibag SSK, Raibag Village-Raibag taluk, Gokak Sugars Limited, Kolavi Village-
Gokak Taluk and Belagavi District, Havalga Village-Afzalpur Taluk, Gulbarga District.
The Company is headed by a dynamic, progressive and visionary Chairmen Shri. Atul Chaturvedi
He is a successful industrialist with wide experience. The company is managed by Executive
Director, Shri Vijendra Shinga under the guidance of Board of Directors.
1.1.2 INTRODUCTION TO THE PROJECT
Shree Renuka Sugars Ltd, Saundatti Taluk, Belagavi District is established in the year 1999, with
valid consent from KSPCB at Survey.R.S.No.367/1 Munoli Village. The land area is 104.18 acres.
The consent for operation under The Water (Prevention and Control of Pollution) Act 1974 and
The Air (Prevention and Control of Pollution) Act 1981 for the existing activity viz.,
manufacturing sugar of 900 MT/day, co-gen power plant of capacity 35.5 MW and Distillery of
capacity 120 KLD from KSPCB and is valid up to 30.06.2021. The company has the Authorization
under the Hazardous & Other Wastes (Management and Transboundary Movement) Rules,
2016. With validity, up to 30.06.2018. Now the industry proposes to expand the sugar unit from
existing 7,500 TCD of cane crushing to 10,000 TCD.
In the proposed expansion, no additional buildings are envisaged. In the existing infrastructure
industry proposes to add some new Machineries/equipments to meet the expansion capacity.
Table: - 1.1 The capacities of the industry existing and after proposed expansion
Sl
No
Product Name Production Capacity in MTPA
Existing Proposed Expansion Total (after expansion)
1 Sugar 900 MT/Day 300 MT/Day 1200 MT/Day
2 Co-gen Power Plant 35.5 MWH - 35.5 MWH
3 Alcohol 120 KLD - 120 KLD
1.2 BRIEF DESCRIPTION OF NATURE, SIZE, LOCATION OF THE PROJECT & ITS IMPORTANCE TO
THE COUNTRY, REGION
1.2.1 NATURE, SIZE & LOCATION OF THE PROJECT
M/s Shree Renuka Sugars Ltd., Munoli Village, Saundatti Taluk, Belagavi District is a Large Scale
industry under Red Category as per the classification made by the State and Central PCB. The
Total Project cost of the plant is Rs. 400.6 Crores (Including Expansion cost towards Plant and
Shree Renuka Sugars limited
Environmental Impact Assessment Report 3
Machineries – Rs.18.78 Crores). The table 1.1 gives the salient feature of the existing plant and
the proposed expansion.
The locations of the Project site are as below in fig 1.0.
Fig 1.0 LOCATION MAP
The projects at glance details are given in table 1.1 below.
Table 1.2:- Project at Glance
Sl No Description Details
1 Location Survey.R.S.No.367/1, Munoli Village, Saundatti Taluk,
Belagavi District
2 Co-ordinates Points Latitude Longitude
A 15051’14.60” N 75006’23.76” E
B 15051’17.63” N 75006’16.61” E
C 15051’29.62” N 75006’19.46” E
D 15051’29.66” N 75005’51.11” E
E 15051’19.97” N 75005’49.98” E
F 15051’01.73” N 75006’10.12” E
G 15051’12.12” N 75006’14.66” E
3 Project location Survey.R.S.No.367/1, Munoli Village, Saundatti Taluk,
Shree Renuka Sugars limited
Environmental Impact Assessment Report 4
Belagavi District
4 Site elevation 609 M above sea level
4 Constitution Public Limited Company
5 Products
manufactured
Product Production Capacity in MTPA
Existing Proposed
Expansion
Total (after
expansion)
Sugar Unit 900 MTD 300 MTD 1200 MTD
Co-Gen 35.5 MWH - 35.5 MWH
Distillery 120 KLD - 120 KLD
6 Total Area 104.18 Acres
7 Across road SH 103-Yaragatti – Munoli Road at 10 Mtrs away
8 District Headquarters Belagavi – 50 Km towards W
9 Nearest Water body Renuka Sagar reservoir nearest water spread location to
industry is 3.7 Kms towards South-west. Malaprabha river
downstream of the reservoir is- 1.4 Kms from the nearest
factory building.
10 Nearest Town Saundatti -10 Km towards SSE
11 Nearest Railway
Station
Belagavi railway Station-63 Km towards W
12 Nearest Airport Belagavi Airport- 51.52 Km towards W
1.2.2 IMPORTANCE TO THE COUNTRY AND/REGION
India is the second largest producers of sugar over the globe. With more than 45 million of
sugar cane growers in the country, the bulk of the rural population in India depends on this
industry. The sugar industry is the second largest agricultural industry followed after the textile
industry.
Around Munoli Village and in the area allotted by Government of Karnataka, there is potential
to harness additional sugar cane by encouraging the formers to adopt the latest agriculture
technics for which the company is giving necessary financial and technical support to the
formers. This will not only improve the economic position of the farmers around but also
improve the economic performance of the industry which in turn help the State in higher sugar
production the present project will also contribute to the revenue of the central and State
exchequer.
Sugar is one of the main requirements in Indian food. Its demand for making sweets and other
uses are increasing day by day. Sugar cane being a seasonal crop and its production is directly
depending on the irrigation potential, rainfall etc., also by and large alternate years Karnataka is
Shree Renuka Sugars limited
Environmental Impact Assessment Report 5
experiencing short fall in sugar cane production, thereby the demand for sugar gets affected.
Therefore, it is required to capitalize on the sugar cane boom season and to produce sugar for
the lean seasons.
Initially sugar industry sector in India has developed in cooperative sectors. Agricultural
technology for sugar cane production in terms of high yielding sugar cane crop and high sugar
content in the sugar cane has made India self-sufficient in sugar cane production. India is well
versed in sugar manufacturing technology and competent in production.
1.2.2.1 SCENARIO OF PRODUCTION OF SUGAR CANE
India achieved a record production of 362 million tons of sugarcane in 2014- 15 but declined to
352 million tons in 2015-16. Of this, about 64 percent was crushed for sugar production and the
remaining was used for production of jaggery, khandsari etc. Two back-to-back droughts in
major sugarcane growing areas are likely to pull down India’s production of sugar to about 25
million tons (a fall of about 3 million tons compared to last year) in 2016-17 sugar season (Chart
1.1). As per fourth advance estimates, sugarcane acreage in Maharashtra is estimated to be
lower by 4.2 percent from 10.30 lakh ha in 2014-15 to 9.87 lakh ha in 2015-16 and yield is also
expected to be lower by 11 percent. In Karnataka and Tamil Nadu the sugarcane acreage has
decreased by 6.25 percent and 2.28 percent respectively whereas in Uttar Pradesh there has
been a marginal increase (1.31 percent) in sugarcane acreage.
Shree Renuka Sugars limited
Environmental Impact Assessment Report 6
In India, production of sugarcane has increased from 328.3 million tons in2007-08 to 355.5
million tons in 2015-16 and more than two-third of this growth has been driven by area
expansion while yield has contributed about one third of the growth. The production of sugar
has increased at an annual compound growth rate of about 3.5 percent during 2005-06 to
2014-15, much higher than growth in sugarcane production (1.82 percent), which indicates
improvement in sugar recovery.
The area under sugarcane, which increased from 49.93 lakh hectares in 2013-14to 50.67 lakh
hectares in 2014-15, declined by 2.2 percent to 49.53 lakh hectare in 2015-16.
Karnataka has been a major gainer in the share of sugar production (8.7 percent to 16.9
percent) primarily due to high sugar recovery. State-wise production of sugar is given below.
State-wise Share in Production of Sugarcane and Sugar
1.2.3 DEMAND SUPPLY GAP, IMPORTS VS INDIGENOUS PRODUCTION
Sugar is one of the main requirements in Indian food. Its demand for making sweets and other
uses are increasing day by day. Sugar cane being a seasonal crop and its production is directly
depending on the irrigation potential, rainfall etc., also by and large alternate years Karnataka is
experiencing short fall in sugar cane production, thereby the demand for sugar gets affected.
Therefore, it is required to capitalize on the sugar cane boom season and to produce sugar for
the lean seasons.
Shree Renuka Sugars limited
Environmental Impact Assessment Report 7
1.2.4 EXPORT POSSIBILITY
In the present project export of sugar is not envisaged. The entire production will be for the
domestic market.
1.3 SCOPE OF STUDY – DETAILS OF REGULATORY SCOPING CARRIED OUT (AS PER TERMS OF
REFERENCE)
1.3.1 SCOPE OF STUDY
Environmental baseline monitoring has been carried out during January 2018 to March 2018.
The scope of the present study is in line with the TOR granted by SEIAA.
1.3.1.1 DETAILS OF THE STUDY
The scope of study broadly includes:
Literature review and collect data relevant to the study area.
Environmental monitoring so as to establish so as to establish the baseline
environmental status of the study area.
Predict incremental levels of pollutants in the terrestrial study area due to the project
activities.
Evaluate the predicted impacts on the various environmental attributes in the study
area by using scientifically developed and widely accepted environmental impact
assessment methodologies.
EMP and monitoring planning to outline the measures for improving the environmental
quality and scope for future expansions for environmentally sustainable development
1.3.1.2 METHODOLOGY OF THE STUDY
Reconnaissance was conducted by the monitoring team and concerned officials from the
project proponent. Sampling locations were identified by considering the below factors.
Existing topography, drainage pattern and location of surface water bodies like ponds, canals, rivers, and sea.
Location of villages/towns/sensitive areas.
Areas which represent baseline conditions and
Collection and analysis of baseline data for various environmental attributes. The field observations are used to,
Identify extent of negative impacts on community / natural resources and
Identify mitigation measures and monitoring requirements.
Shree Renuka Sugars limited
Environmental Impact Assessment Report 8
1.3.1.3 STUDY AREA DETAILS
The study area for the present EIA study is 10 km radius from the plant boundary.
The project well connected by Yarlagatti – Munoli road, SH-103 road is at a distance of 10
Meters towards Eastern direction. Belagavi City Railway Station is at a distance of about 63 km
towards Western direction. Hence the raw materials and the other utilities required by the
industry can be easily transported.
Terms of Reference (TOR) prescribed by the State Level Expert Appraisal Committee, Karnataka,
vide letter no. SEIAA/22/IND 2017 dated 26-03-2018 for the study and preparation of project
report for the proposed Expansion Of Sugar Industry Plant Capacity From 7500 TCD To 10000
TCD of M/s. Shree Renuka Sugars Ltd.,. The list of TOR and their compliances is appended in the
table 1.4 below.
Table 1.3: Terms of Reference (ToR)
Sl No TOR issued by SEIAA Details
1 Executive summary Executive summary of project is given EIA
report.
2 Introduction
i Details of the EIA consultant including
NABET Accreditation.
Detailed in chapter – 12.
ii Information about the project
proponent
Detailed in Chapter – 1, Section 1.1.
iii Importance and benefits of the
project.
Detailed in Chapter - 8
3 Project Description
i Cost of project and time of
completion
Existing Capital investment – Rs.381.82 Crores
Proposed expansion – Rs.18.78 Crores
Time of completion - 2018 crushing season.
ii Products with capacities for the
proposed project
Detailed in Chapter – 1, Table 1.1.
iii If expansion project, details of existing
products with capacities and whether
adequate land is available for
expansion, reference of earlier EC if
any.
The proposed project is expansion of sugar &
Co-gen power plant within the existing
premises and adequate land is available.
Products and its details are given in Chapter –
1, Table 1.1. Early EC details are given in
Section 1.0.
Shree Renuka Sugars limited
Environmental Impact Assessment Report 9
i. iv List of raw materials required and
their source along with mode of
transportation.
Detailed in Chapter – 2, Section 2.7.
ii. v Other chemicals and materials
required with quantities and storage
capacities.
Detailed in Chapter – 2, Section 2.7.
iii. vi Details of emission, effluents,
hazardous waste generation and their
management.
Detailed in Chapter – 2, Section 2.10.1.4,
2.10.3 & 2.10.6
iv. vii Requirement of water, power, with
source of supply, status of approval,
water balance diagram, man-power
requirement (regular and contract).
Requirement of water with source of supply,
status of approval, water balance is detailed in
chapter – 2, Section 2.10.1.
Power requirement detail is detailed in
chapter – 2, section 2.10.2.
Total manpower required for the industry is
450 people.
v. viii Process description along with major
equipments and machineries, process
flow sheet (quantitative) from raw
material to products to be provided.
Detailed in Chapter – 2, Section 2.8
vi. ix Hazard identification and details of
proposed safety systems.
Detailed in Chapter – 7, Section 7.1.
vii. x Expansion/modernization proposals.
a. Copy of all the environmental
clearance(s) including amendments
thereto obtained for the project from
MOEF / SEIAA shall be attached as an
annexure. A certified copy of the
latest monitoring report of the
regional office of the ministry of
environment and forests as per
circular dated 30th May, 2012 on the
status of compliance of conditions
stipulated in all the existing
environmental clearances including
amendments shall be provided. In
addition, status of compliance of
Detailed in Annexure – 1
Shree Renuka Sugars limited
Environmental Impact Assessment Report 10
consent to operate for the ongoing
existing operation of the project from
SPCB shall be attached with the EIA-
EMP report.
b. In case the existing project has not
obtained environmental clearance,
reasons for not taking EC under the
provisions of the EIA notification 1994
and/or EIA notification 2006 shall be
provided. Copies of consent to
Establish/No Objection Certificate and
consent to operate (in case of units
operating prior to EIA notification
2006, CFE and CFO of FY 2005-2006)
obtained from the SPCB shall be
submitted.
EC is obtained for the existing activity.
4. Site details
I. A Location of the project site covering
village, Taluk/Tehsil, District and state,
justification for selecting the site,
whether other sites were considered.
Detailed in chapter -2, Section 2.2
i A topo sheet of the study area of
radius of 10 KM and site location on
1:50,000/1:25,000 scale on an A3/A2
sheet. (including all eco sensitive
areas and environmentally sensitive
places)
Topo sheet is attached as Annexure - 5
ii Details with respect to option analysis
for selection of site.
Detailed in chapter -2, Section 2.2
iii Co – ordinates (lat –long) of all four
corners of the site.
Detailed in Chapter -2, Section 2.2 fig 2.0
iv Google map – Earth Downloaded of
the project site.
Detailed in chapter -2, fig 2.0
v Layout maps indicating existing unit as
well as proposed unit indicating
storage area, plant area, greenbelt
area, utilities etc., if located within an
industrial area/ estate/complex,
Detailed in chapter -2, Fig :- 2.2 & Annexure-
6
Shree Renuka Sugars limited
Environmental Impact Assessment Report 11
layout of industrial area indicating
location of unit within the industrial
area/ Estate.
vi Photographs of the proposed and
existing (if applicable) plant site. If
existing, show photographs of
planation/ greenbelt, in particular.
Detailed in chapter -2, Fig :- 2.3.1 & 2.3.2
vii Land use break up of total land of the
project site (identified and acquired),
government /private – agricultural,
forest wasteland, water bodies,
settlements, etc., shall be
included.(not required for industrial
area)
Detailed in Chapter -2, Table 2.3
viii A list of major industries with name
and type within study area (10 KM
radius) shall be incorporated. Land
use details of the study area.
No major industries within 10 km radius.
Primarily land is used for agriculture with rural
settings.
ix Geological features and geo –
hydrological status of the study area
shall be included.
Detailed in Chapter – 3, Section – 3.8.
x Details of drainage of the project up
to 5 km radius of study area. If the
site is within 1 km radius of any major
river, peak and lean season river
discharge as well as flood occurrence
frequency based on peak rainfall data
of the past 30 years. Details of flood
level of the project site and maximum
flood level of the river shall also be
provided. (Mega green field projects).
Malaprabha river is flowing at a distance of
1.4 Km from the factory building.
The terrain in the project site is flat. The MSL
at site is 609 m. The MSL of the river is 603 m.
The land is gently sloping towards the river. NI
between the factory and river there are
agricultural lands.
xi Status of acquisition of land. If
acquisition is not complete, stage of
the acquisition process and expected
time of complete possession of the
land.
The proposed project is expansion of sugar
crushing unit within the existing industry.
Hence there is no acquisition of additional
land.
xii R & R details in respect of land in line
with state government policy.
Not applicable as there is no additional land
acquired.
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Environmental Impact Assessment Report 12
5. Forest and wildlife related issues (if applicable)
i Permission and approval for the use
of forest land, if any, and
recommendations of the State Forest
Department.(If applicable)
Not applicable as there is no Forest land is
involved.
ii Land use map based on high
resolution satellite imagery (GPS) of
the proposed site delineating the
forest land (in case of projects
involving forest land more than 40 Ha)
iii Status of application submitted for
obtaining the stage I forestry
clearance along with latest status
shall be submitted
iv The projects to be located within 10
Km radius of the National Parks,
Sanctuaries, Bio sphere reserves,
Mitigatory corridors of wild animals,
the project proponent shall submit
the map duly authenticated by chief
wild life warden showing these
features vis-à-vis the project location
and the recommendations or
comments of the chief wild life
warden there on
v Wild life conservation plan duly
authenticated by chief wild life
warden of the State Govt for
conservation of Schedule I fauna, if
any exists in the area.
vi Copy of application submitted for
clearance under the Wildlife
(Protection) Act, 1972, to the Standing
Committee of the National Board for
Wildlife
6. Environmental Status :
i Determination of atmospheric
inversion level at the project site and
Detailed in chapter -3 , Section – 3.2.1.6
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Environmental Impact Assessment Report 13
site – specific micrometeorological
data using temperature, relative
humidity, hourly wind speed and
direction and rainfall.
ii AAQ data (except monsoon) at 8
locations for PM10, PM2.5, SO2, NOx,
CO and other parameters relevant to
the project shall be collected. The
monitoring stations shall be based
CPCB guidelines and take into account
the pre- dominant wind direction,
population zone and sensitive
receptors including reserved forests.
Detailed in chapter -3 , Section – 3.4.1
iii Raw data of all AAQ measurement for
12 weeks of all stations as per
frequency given in the NAAQM
notification of Nov. 2009 along with –
min, max, average and 98 % values for
each of the AAQ parameters from
data of all AAQ stations should be
provided as an annexure to the EIA
report.
Detailed in chapter -3 , Section – 3.4.1
iv Surface water quality of nearby river
(100 m upstream and downstream of
discharge point) and other surface
drains at eight locations as per
CPCB/MoEF & CC guidelines.
Surface water quality results are provided in
Chapter 3, Section 3.6.2 and table 3.10
I. v Whether the site falls near to polluted
stretch of river identified by the
CPCB/MoEF & CC, if yes give details.
No.
II. vi Ground water monitoring at minimum
at 8 locations shall be included.
Detailed in chapter -3 , Section - 3.6.4 and
table 3.12
III. vii Noise levels monitoring at 8 locations
within the study area.
Detailed in chapter -3 , Section – 3.5 and table
3.3
IV. viii Soil characteristic as per CPCB
guidelines.
Detailed in chapter -3 , Section - 3.7 and table
3.17
V. ix Traffic study of the area, type of
vehicles, frequency of vehicles for
Detailed in chapter -3, Section – 3.5.1.
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Environmental Impact Assessment Report 14
transportation of materials, additional
traffic due to proposed project,
parking arrangement etc.,
VI. x Detailed description of flora and
fauna (terrestrial and aquatic) existing
in the study area shall be given with
special reference to rare, endemic
and endangered species. If schedule –
I fauna are found within the study
area, wildlife conservation plan shall
be prepared and furnished.
Detailed in chapter -3 , Section -3.9.2 and
3.9.3
VII. xi Socio – economic status of the study
area.
The industry has conducted the Socio-
economic study of the study area comprising
of 10km from plant site. Detailed in chapter -3
, Section -3.10
7. Impact and Environment Management Plan
i Assessment of ground level
concentration of pollutants from the
stack emission based onsite- specific
meteorological features. In case the
project is located on a hilly terrain, the
AQIP modeling shall be done using
inputs of the specific terrain
characteristics for determining the
potential impacts of the project on the
AAQ. Cumulative impact of all sources
of emissions (including transportation)
on the AAQ of the area shall be
assessed.
Details of the model used and the input
data used for modelling shall also be
provided. The air quality contours shall
be plotted on a location map showing
the location of project site, Habitation
nearby, sensitive receptors, if any.
The project is not in a hilly terrain.
As there is no additional air pollution
sources. The present background air quality
is conducted when the plant is in operation.
The air quality is meeting the national AAQ
Standards.
AAQ monitoring was conducted to assess the
baseline air quality status of the study area.
GLC of AAQ were estimated using industrial
source complex (ISCST3) USEPA, Lakes
Environmental complex terrain dispersion
model based on a steady state Gaussian
plume dispersion designed for point sources
and short term modeling as per MOEF
guidelines for the expansion project. The
estimated AAQ were within permissible
limits. The details are furnished in chapter -
3, Section – 3.4.1.
i. ii Water quality modelling – in case of
discharge in water body.
Effluent is not discharged in to any water
body.
ii. iii Impact of the transport of the raw The sugar plant is agro based. The raw
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Environmental Impact Assessment Report 15
materials and end products on the
surrounding environment shall be
assessed and provided. In this regard,
options for transport of raw materials
and finished products and wastes (large
quantities) by rail or rail – cum road
transport or conveyor cum – rail
transport shall be examined.
material that is sugarcane is procured from
the farmers in a radius of about 25 Km from
the plant. Therefore, the ideal transport in
the present setting is by Bullock carts,
tractors and trucks.
The finished products are transported by
road to the destination and also through
railways for longer distances.
iii. iv A note on treatment of waste water
from different plant operations, extent
recycled and reused for different
purposes shall be included. Complete
scheme of effluent treatment.
Characteristics of untreated and
treated effluent to meet the prescribed
standers of discharge under E(P) rules.
Detailed in Chapter 2, Section 2.10.1.4
iv. v Details of stack emission and action
plan for control of emissions to meet
standards.
Stacks of adequate height are provided to
all the boiler emission sources. It is as per
the KSPCB stipulation.
ESP of proven make is provided to reduce
SPM in flue gas to the permissible levels.
Online monitoring facilities is provided
Stack emission reports are attached as
Annexure 2
v. vi Measures for fugitive emission control. Detailed in Chapter 4, Section 4.2.1.1
vi. vii Details of hazardous waste generation
and their storage, utilization and
management. Copies of MOU regarding
utilization of solid and hazardous waste
in cement plant shall also be included.
EMP shall include the concept of waste
minimization, recycle/reuse/recover
techniques, energy conservation and
natural resource conservation.
Detailed in Chapter 2, Section 2.10.6
vii. vii Proper utilization of fly ash shall be
ensured as per fly ash notification,
2009. A detailed plan of action shall be
provided.
1. Fly ash is being collected in wet conditions
only and transported in covered vehicles.
2. Fly ash is used for composting of distillery
spent wash as filler material along with press
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Environmental Impact Assessment Report 16
mud. Local farmers also use fly ash as soil
conditioner and compost.
viii. ix Action plan for the green belt
development plan in 33 % area i.e. land
with not less than 1,500 trees per ha.
Giving details of species, width of
plantation, planning schedule etc., shall
be included. The green belt shall be
around the project boundary and a
scheme for greening of the roads used
for the project shall also be
incorporated.
Detailed in Chapter – 9, Section 9.1 (v) point
ix. x Action plan for rain water harvesting
measures at plant site shall be
submitted to harvest rainwater from
the rooftops and storm water drains to
recharge the ground water and also to
use for the various activities at the
project site to conserve fresh water and
reduce the water requirement from
other sources
Detailed in Chapter – 2, Section 2.12
x. xi Total capital cost and recurring
cost/annum for environmental
pollution control measures shall be
included.
Detailed in Chapter – 6, Section:- 6.3.
xi. xii Action plan for post-project
environmental monitoring shall be
submitted.
Detailed in Chapter – 6.
xii. Xiii Onsite and offsite disaster (natural and
man-made) preparedness and
emergency management plan including
Risk assessment and damage control.
Disaster management plan should be
linked with district disaster
management plan.
Detailed in Chapter – 7, Section 7.1.2 and
7.1.3
8. Occupational Health :
i Plan and fund allocation to ensure
occupational health & safety of all
Environment cum Safety officer is appointed
in the industry to manage safety and
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Environmental Impact Assessment Report 17
contract and casual workers. Occupational health care program.
Safety training is given to the employees.
Safety appliances, first aid medical kits and
Personnel protective equipments are
provided.
Health and safety related displays will be
provided in the work place and premise.
Firefighting facility including Fire hydrants,
fire extinguishers and fire protective
appliances is provided.
Medical Check-ups and health records of
employees is maintained.
Rs. 2,07,000/- is allocated from the industry management to ensure occupational health and safety of workers.
i. ii Details of exposure specific health
status evolution of worker. If the
workers’ health is being evaluated by
pre designed format, chest x rays,
audiometry, spirometry, Vision testing
(far & near vision, color vision and any
other ocular defect) ECG, during pre-
placement and periodical
examinations give the details of the
same. Details regarding last month
analyzed data of above mentioned
parameters as per age, sex, duration
of exposure and department wise.
Since the industry is agro based industry, not
much occupational health hazards are
anticipated. However, all the employees are
provided with Personnel Protective
equipment. In any eventuality, the employees
are provided with the general and private
hospital facilities at Belagavi. Any medical
facilities availed outside and the expenditure
towards the same reimbursed to such
employees.
ii. iii Details of existing occupational &
safety hazards. What are the
exposure levels of hazards and
whether they are within Permissible
Exposure level (PEL). If these area not
within PEL, what measures the
company has adopted to keep them
within PEL so that health of the
workers can be preserved.
All the employees are provided with
personnel protective devices such as earplugs
for those employees working in cane crushing
area apart from gum boots and safety
helmets. The noise exposure will be
maintained with the noise exposure index by
providing work rotation to employees and
providing intermittent rest.
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Environmental Impact Assessment Report 18
The noise levels within the plant area are
controlled by using acoustics. The noise
monitored levels within the plant is in chapter
-3 , Section – 3.5 and table 3.3
iii. iv Annual report of health status of
workers with special reference to
occupational health and safety.
Appended as Annexure - 4
9. Corporate Environment Policy
i Does the company have a well laid
down environment policy approved
by its board of directors? If so, it may
be detailed in the EIA report.
Details are given in chapter 9 and section 9.6
i. ii Does the environment policy
prescribe for standard operating
process/ procedures to bring into
focus any infringement
/deviation/violation of the
environmental or forest norms
/conditions? If so, it may be detailed
in the EIA.
No
ii. iii What is the hierarchical system or
administrative order of the company
to deal with the environmental issues
and for ensuring compliance with the
environmental clearance conditions?
Details of this system may be given.
The Company is headed by a dynamic,
progressive and visionary Chairmen Shri. Atul
Chaturvedi He is a successful industrialist with
wide experience. The company is managed by
Executive Director, Shri Vijendra Shinga under
the guidance of Board of Directors.
iii. iv Does the company have system of
reporting of non-compliances
/violations of environmental norms to
the board of directors of the company
and / or shareholders or stakeholders
at large? This reporting mechanism
shall be detailed in the EIA report.
The reporting of non-compliance to the top
management (Board of Directors of the
company and/or shareholders or
stakeholders) will be through lower
management, Middle management of the
project.
10. Details regarding infrastructure
facilities such as sanitation, fuel,
restroom etc. to be provided to the
labour force during construction as
well as to the casual workers including
This is an expansion project. there is no major
construction involved. For the labour during
the erection of machineries for the expansion
already available sanitation infrastructure
such as restrooms, PPEs, will be extended to
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Environmental Impact Assessment Report 19
truck drivers during operation phase. them.
11. Enterprise Social Commitment (ESC)
i Adequate funds (at least 2.5 % of the
project cost) shall be earmarked towards
the enterprise social commitment based
on public hearing issues and item – wise
details along with time bound action plan
shall be included. Social – economic
development activities need to be
elaborated upon.
The details of social activities carried out
by the industry is detailed in chapter 4,
Section – 4.2.5
12. Any litigation pending against the project
and/or any direction /order passes by any
court of law against the project, if so
details thereof shall be included. Has the
unit received any notice under the section
5 of Environment (protection) act, 1986 or
relevant sections of air and water acts? If
so, details thereof and compliance /ATR to
the notice(s) and present status of the
case.
No
B. SPECIFIC TERMS OF REFERENCE FOR EIA STUDIES FOR SUGAR INDUSTRY
1 Complete process flow diagram describing
each unit, its processes and operations in
production of sugar, along with material
and energy inputs and outputs (material
and energy balance).
Detailed in Chapter – 2, Section 2.8
2 Details on water balance including
quantity of effluent generated, recycled &
reused. Efforts to minimize effluent
discharge and to maintain quality of
receiving water body.
Detailed in chapter – 2, Section 2.10.1
3 Details of effluent treatment plant, inlet
and treated water quality with specific
efficiency of each treatment unit in
reduction in respect to all concerned /
regulated environmental parameters.
Detailed in Chapter 2, Section 2.10.1.4
4 Number of working days of the sugar Sugar plant :200
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Environmental Impact Assessment Report 20
production unit. Power plant:330
5 Details of the use of steam from the
boiler.
In sugar industry steam is used primarily
for:
(a) Generating power
(b) Concentrating sugar juices.
Steam also plays important role in every
step of raw sugar process, especially in
juice extraction, clarification, evaporation
and sugar drying. Thus selection of steam
boilers becomes very important for sugar
plant.
6 Details of proposed source – specific
pollution control schemes and equipments
to meet the national standards.
Detailed in chapter -2, Section 2.10.3
7 Collection, storage, handling and
transportation of molasses.
Detailed in chapter – 2, Section 2.8.2.3
8 Collection, storage and handling of
bagasse and press mud.
Molasses is used in the distillery plant of
SRSL. Press mud and ash is disposed as
raw material to distillery plant for spent
wash composting. The farmers are also
using it as filler material in manure.
Bagasse will be used as fuel in the boiler.
9 Fly ash management plan for coal based
and bagasse and action plan
As the boilers in the power plant utilize
bagasse and bio-mass as fuel for power
generation. Boiler ash will be given to
farmers for use as nutrient cum soil
conditioner in agricultural lands.
Coal is used at 25 % of the total bagasse
requirement when there is shortage of
fuel.
10 Details on water quality parameter such as
Temperature, color, pH, BOD, COD, total
Kjeldhal Nitrogen, Phosphates, Oil &
grease, total suspended solids, total coli
form bacteria etc.,
Detailed in chapter -3, Section - 3.6.2 and
table – 3.10
11 Details on existing ambient air quality and
expected, stack and fugitive emissions for
PM10, PM2.5, SO2*, Nox*, etc., and
The project is not in a hilly terrain.
As there is no additional air pollution
sources. The present background air
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Environmental Impact Assessment Report 21
evaluation of the adequacy of the
proposed pollution control devices to
meet standards for print sources and to
meet AAQ standards. (*-as applicable)
quality is conducted when the plant is in
operation. The air quality is meeting the
national AAQ Standards.
Detailed in chapter -3 , Section – 3.4.1
Additional ToRs for EIA studies
1 To submit the details of methodology
adopted to convert press mud into
value added composts
The details are provided in the Chapter - 2,
Section – 2.10.7 of report.
2 To submit the mitigation measures to
control odour from the effluent
Details are provided in the Chapter – 4,
Section - 4.2.6
3 To furnish the required design
changes for equalization tanks to
accommodate for peak loading
The existing equalization tank in the ETP is
adequate to handle the effluent peak loading.
Also there is a separate collection tank for
monthly wash collection. From this the flow is
regulated.
4 To submit the proposal for
strengthening the existing green belt
with broad leaved native species
Details of the green belt are given in Chapter –
9, Section 9.1 (v) point. The tree species
planted are varied varieties of native species.
5 To furnish the measures to address
the concerns raised during public
hearing and assurance given along
with the financial provisions and
action plan to implement the
commitment
6 To submit the proposal for alternative
sanitary measures to the septic tanks
The sewage from different areas is connected
to septic tank. The overflow is taken to a
common collection tank and regulated to the
sugar plant ETP. It acts as a nutrient for the
treatment. During off season the sewage
generation is minimal and treated in septic
tank and generally it will not overflow.
7 Compliance to the earlier EC along
with the certified report of the status
of compliance of the conditions
stipulated in earlier EC for the
ongoing existing project in accordance
with circular No. J-11011/618/2010-
IA-II(I) dated 30.05.2012
The certified compliance report to the
conditions stipulated in the EC is submitted to
Regional office MoEF on 7/10/2017. They are
yet to conduct inspection.
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1.4 GENERIC STRUCTURE OF EIA DOCUMENT:
The generic structure in terms of Appendix – III of the EIA Notification of the MoEF dated 14th
September 2006, is followed for preparing the EIA document. The details of the structure are as
under:
Chapter 1: Introduction
Introductory information is presented in this Chapter. The introduction provides a Background
to the project and describes the objective of this document. This Chapter also includes the
outline of the project and its proponent. The purpose of project and organization details of the
promoter is also presented in this chapter.
Chapter 2: Project Description
This Chapter includes Project Description and Infrastructure Facilities delineating all industrial
and environmental aspect of the industry of M/s. Shree Renuka Sugars Limited. Construction
and operation phase activities as well as process details of proposed scenario. This Chapter
gives information about storage and handling, water and wastewater quantitative details, air
pollution and control system, sludge storage facility, utilities, greenbelt and safety measures for
proposed plant.
Chapter 3: Description of the Environment
This Chapter provides Baseline Environmental Status of Environmental components (Primary
data) delineating meteorological details of the project site and surrounding area.
Chapter 4: Anticipated Environmental Impacts & Mitigation Measures
This Chapter presents the analysis of impacts on the environmental and social aspects of the
project as a result of establishment of plan and thereby suggesting the mitigation measures.
Chapter 5: Analysis of Alternatives
This chapter includes the justification for the selection of the project site from Environmental
point of view as well as from economic point of view.
Chapter 6: Environmental Monitoring Plan
This chapter will include the technical aspects of monitoring, the effectiveness of mitigation
measures which will include the measurement methodologies, frequency, location, data
analysis, reporting schedules etc.,
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Environmental Impact Assessment Report 23
Chapter 7: Additional Studies
This chapter will include the details about the Public Consultation. It will also identify the risks
of the Project in relation to the general public and the surrounding environment vis-a-vis
management plan.
Chapter 8 & 9: Project Benefits & Environmental Cost Benefit Analysis.
The realization of the project activity is envisaged to impart benefits to the areas in concern.
This Chapter will identify the benefits from the project and summarize them.
Chapter 10: Environmental Management Plan
This chapter presents the mitigation plan, covers the institutional and monitoring requirements
to implement environmental mitigation measures and to assess their adequacy during project
implementation.
Chapter 11: Summary and Conclusion
This chapter summarizes the information given in Chapters in this EIA/EMP report and the
conclusion based on the environmental study, impact identification, mitigation measures and
the environmental management plan.
Chapter 12: Disclosure of the Consultant
Names of consultants engaged in the preparation of the EIA/EMP report along with their brief
resume and nature of Consultancy rendered are included in this Chapter.
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CHAPTER 2
PROJECT DESCRIPTION
2.0 TYPE OF PROJECT
Shree Renuka Sugars Ltd., Munoli unit proposed to expand the sugar unit by enhancing sugar
crushing capacity from existing 7,500 TCD of cane crushing to 10,000 TCD.
2.1 NEED FOR THE PROJECT
India is the second largest producers of sugar over the globe. With more than 45 million of
sugar cane growers in the country, the bulk of the rural population in India depends on this
industry. The sugar industry is the second largest agricultural industry followed after the textile
industry.
Around Munoli Village and in the area allotted by Government of Karnataka, there is potential
to harness additional sugar cane by encouraging the formers to adopt the latest agriculture
technics for higher yield, for which the company is giving necessary financial and technical
support to the formers. This will not only improve the economic position of the farmers around
but also improve the economic performance of the industry which in turn help the State in
higher sugar production. The present project will also contribute the revenue of the central and
state exchequer.
2.2 LOCATION OF THE PROPOSED INDUSTRY
M/s SHREE RENUKA SUGARS LIMITED (SRSL) is located at Survey no’s Survey.R.S.No.367/1,
Munoli Village, Saundatti Taluk, Belagavi District, Karnataka. Munoli village is adjacent to the
industry. The location features of site are given in Table-2.1. Google map is given in fig 2.1 & 2.2
There are no eco-sensitive locations such as national park, wild life sanctuary, protected forests,
and bio-sphere reserve in the vicinity of the project site. The salient feature of the project is
shown in Table 2.1
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TABLE 2.1: LOCATION FEATURES OF THE PROJECT SITE
Sl No Feature Particulars
1 Location Survey.R.S.No.367/1, Munoli Village, Saundatti
Taluk, Belagavi District
2 Latitude/Longitude points Latitude Longitude
A 15051’14.60” N 75006’23.76” E
B 15051’17.63” N 75006’16.61” E
C 15051’29.62” N 75006’19.46” E
D 15051’29.66” N 75005’51.11” E
E 15051’19.97” N 75005’49.98” E
F 15051’01.73” N 75006’10.12” E
G 15051’12.12” N 75006’14.66” E
3 Average altitude above mean
MSL
609 m above MSL
4 Soil type The district has Shallow to Very deep black soils,
red loamy soils, lateritic soils etc.
5 Nearest highway SH 103-Yaragatti – Munoli Road at 10Mtrs away
6 Railway station Belagavi railway Station-63 Km towards W
7 Nearest airport Belagavi Airport- 51.52 Km towards W
8 Nearest Villages Munoli – 1.36 Kms, Teggihal – 3.2 Kms, Shindhogi
– 4.37 Kms, Hirur – 5.5 Kms etc.,
9 Nearest town Saundatti -10 Km towards SSE
10 Nearest major city Belagavi – 64.23 Kms towards SSW
11 Nearest water body Renuka sugar reservoir nearest water spread
location to industry is 3.7 Kms towards South-west.
Malaprabha river downstream of the reservoir is-
1.4 Kms from the nearest factory building.
12 Sensitive locations such as
protected forests, monuments,
national park, zoos etc.
No such sensitive locations within 25 km from the
site
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Fig 2.0: Maps showing project boundary & project site location
Note: Latitude: 14019’48’’ N ; Longitude: 75052’51’’E ; 578 m above MSL
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Environmental Impact Assessment Report 27
Fig 2.1 Map showing the Project Site Location on District Map of Belagavi
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2.3 SIZE OR MAGNITUDE OF OPERATION
The industry M/s. Shree Renuka Sugars Limited is a large scale industry. The total project cost
towards expansion is Rs.18.78 Crores.
The estimated cost for the existing and proposed expansion and for pollution Control facilities
are given below table 2.2.
Table 2.2:- COST OF THE PROJECT
Sl
No
Description Existing
Amount in
Crores (In Rs)
Proposed
Amount in Crores
(In Rs)
1 Land and Development 5.7 -
2 Building 49.07 -
3 Plant and Machinery 317.3 18.78
4 Other Assets 9.75 -
TOTAL 381.82 400.6
2.4 PROPOSED SCHEDULE FOR APPROVAL & IMPLEMENTATION
The enhancement in production can be taken up once Environmental Clearance is granted by
SEIAA & CTE from KSPCB. It is proposed to start the expanded capacity during 2018 sugarcane
crushing season.
2.5 PROPOSED LAYOUT PLAN
The extent of land with the industry is 104.18 Acres. In the proposed expansion there is no
additional land and additional buildings envisaged. In the existing infrastructure industry
proposed to add some new machineries/equipment to meet the expansion capacity. Land use
pattern is given in Table2.3 & Layout pan is shown in Fig 2.2.
Table 2.3: - Land-use pattern
Sl No Particulars Area
(Acres)
In %
1 Ground coverage area (total built up area)
including paved and roads
54.88 52.68
2 Vacant Area 13.86 13.31
3 Landscape Area (Green belt area (minimum
34.01% of total plot area))
35.44 34.01
Total Plot Area 104.18 100
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2.6 SITE BEARINGS
The proposed project site is surrounded by vacant land and predominantly agricultural lands in
all directions. Details are shown in the below table.
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Fig 2.2 Plant layout plan
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Figure 2.3: Photographs of the industry
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Figure 2.4: SITE PHOTOS SHOWING GREENERY DEVELOPMENT
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2.7 RAW MATERIALS
Sugar Cane is the main raw material. In 50 KM radius of the industry about 360 No’s of
farmers are located. The raw materials required for all products are given in table 2.7
TABLE 2.4: RAW MATERIALS FOR SUGAR PLANT
Sl No Raw Materials Existing Quantity Expansion Quantity
1 Cane Crushing 7500 TCD 10000 TCD
2 Lime 7.5 MT/day 10 MT/day
3 O.P. Acid 650 kg/day 850 kg/day
4 Caustic Soda 290 kg/day 390 kg/day
5 Sulphonic acid 4.5 kg/day 6 kg /day
6 Anti Scalant 75 kg/day 100 kg/day
7 Magnofloc 7991 60 kg/day 90 kg/day
8 MagnoflocLT-27 20 kg /day 25 kg/day
2.7.1 POWER AND STEAM REQUIREMENT
POWER REQUIREMENT
The power requirement will be through co-generation unit. DG Set will act as backup
facilities in case of power failure. The details of power requirement given in below table;
DURING SEASON:
1. Power Generation : 34 MW (3 turbines of 15 + 9.3 + 9.7 MW)
2. Power consumption at Co-Gen unit
3. Power consumption for Sugar Unit 12.5 MW
4. Power Consumption for Distillery unit
5. Export to KPTCL : 13 to 21.5 MW
DURING OFF-SEASON:
1. Power Generation : 7.5 MWh
2. Power consumption at Co-Gen unit : 1.0 MWh
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3. Power consumption for Sugar Unit :
4. Power Consumption for Distillery unit : 1.5 MWh
5. Export to KPTCL : 5.0 MWh
2.8 TECHNOLOGY & PROCESS DESCRIPTION
2.8.1 MANUFACTURE OF SUGAR
Sugar cane is the raw material for manufacture of sugar. Juice is extracted from sugar cane,
which is then processed to recover sugar. Bagasse, which is the left-out fiber material after
extraction of juice from sugar cane, is used as fuel in boiler to produce steam. Steam is
used for generation of electric power and exhaust steam is used for evaporation of water in
the juice. The flow diagram of sugar manufacturing process and a brief description of the
process is given bellow.
REFINED SUGAR MANUFACTURING PROCESS:
Process Description:
The Sugarcane Plant
Sugarcane is a tropical grass belonging to the same tribe as sorghum. Modern sugarcane is a
complex hybrid of two or more of the five species of the genus saccharin.
Varieties
Majority of the sugarcane produced in the following hybrid varieties: CO1148, CO 740, CO
671, CO 86032, CO 8011 and COS 767.
Harvesting
The goal of the harvest is to deliver sugarcane stalks of good quality to the mill. Quality
measured by sucrose & trash content is reduced by damaging cane, increasing trash in
delivered cane, and delaying cane delivery. Payment based on quality as well as tonnage
increases the incentive for improving quality.
Delivery of Cane
The factory takes delivery of the cane, either directly at the factory weigh bridge or at
auxiliary weigh bridges or at certain important or remote points in the area from which the
mill draws its supplies. Transport is arranged by the factory, either by bull-carts, or more
often by Lorries or by tractors and trailers.
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Table 2.5: - Details of Ware house
Ware house details
No. of Warehouses Capacity in MT Type of
Construction
Remarks
I & II 17000 Roof AC sheets 25/50/100 Kg storage
III 15000 Quoted GI sheets 25/50/100 Kg storage
IV 22000 Quoted GI sheets 25/50/100 Kg storage
V 25000 Roof AC sheets 25/50/100 Kg storage
VI 30000 Quoted GI sheets 25/50/100 Kg storage
A' Frame 60000 Quoted GI sheets Bulk storage
Unloading of Cane
All modern factories employ mechanical unloaders also called as 'crane'. The cane is often
loaded in bundles, bound by three chains or slings. At one end these slings slide in a special
hook fitted with a pawl, while a ring is attached to the other end.
Handling (Preparation) of cane
The milling process may be separated into two steps; the preparation of the cane by
breaking down the hard structure and rupturing the cells and the actual grinding of the
cane. The preparation of the cane is accomplished in several ways.
1. By revolving cane knives that cut the cane into chips but extract no juice.
2. By shredders that tear the cane into shreds but extract no juice.
Composition of sugar cane:
Generally composition of sugar cane is as under and it is varies with the region and aging.
Sugar 10 to 15 %
Water 75 to 65 %
Fiber 11 to 15 %
Organic Matter 4 to 3.5 %
Sugar Manufacturing Process
The process Extraction of juice from sugar cane is mostly common or uniform throughout
the world.
Milling – consist of multiple unit of roller combinations through which the cane is crushed
with the help of imbibition process.
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Purification of Juice: Clarification
The dark-green juice from the mills is acidic & turbid. The clarification process, designed to
remove both soluble & insoluble impurities by employing lime & heat with small addition of
phosphate agent.
Clarification Process
Defecation Process - Clarification by Heat & Lime, known as the Simple defecation process.
In this process sufficient lime is added to neutralize the organic acids present in the juice,
after which the temperature is raised up to 1020 °C & above, which forms a heavy
precipitate of complex composition, heavier than the juice.
Settling Process
After liming & Heating, the treated juice is delivered to large cylindrical tank for settling of
heavy precipitate complex called MUD. The design & concept of cylindrical tank is such type
of that withdrawal of clear juice from upside & settled Mud is drawn from bottom side.
Treatment of Clarified Juice & Mud in almost all raw sugar manufactures the clarified juice
goes directly to the evaporators without further treatment. The Mud are filtered on Rotary
drum vacuum filter, the filtered juice returns to the process, and the press cake is discarded
or send to the fields for fertilization.
Evaporation
The clarified juice, having much the same composition as the raw extracted juice accepts for
the precipitated impurities removed by the purification process. It contains about 85%
water. Two third of this water is evaporated in vacuum multiple effects. The syrup leaves is
about 65% solids & 35% water.
Crystallization
Crystallization takes place in single-effect vacuum pans, where the syrup is evaporated until
saturated with sugar.
Centrifugation
The sugar mass is then sent to the sugar centrifuge, where by the centrifuge force the
saccharosis crystals are separated from the molasses that involves them. The molasses is
returned to the process for the residual sugar that is still found in the same be crystallized
again.
Drying
After centrifugation sugar is sent to the drying where its moisture is lowered from 1.0-1.5%
to 0.04-0.08%, and posterior cooling, where its temperature is reduced up to 37-40 deg. C.
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This obtained sugar is the named Raw Sugar, and it will serve as raw material for the
conventional process of refined sugar. In the integrated process, this sugar is dissolved in
one or more dissolvers called as “Melting Process”.
Melting Process
In the melter, the sugar is mixed with heated water and is subjected to agitation, up to the
formation of the sugar melt in the desired concentration. Next, this melt is send to a
filtration system in a manner to eliminate a portion of the impurities and after it is pumped
to a decolorization system.
Decolorisation process
The decolorisation can be performed by several known process, such as Phosphofloatation,
Carbonation, Ion Exchange, Activated carbon process for the desired quality in the final
product.
Phosphofloatation Process
This process is based on the creation of calcium phosphate floc that captures the suspended
impurities and the coloring matter precipitate formed by the use of special color
precipitants. The conglomerate of these flocs, precipitates, and suspended impurities is
floated with the aid of air and removed as scum, & Clear Melt drawn out through weir box.
Filtration Process
Clear melt is then passed through Deep Bed Filter to separate the minute scum particles
carried along with the melt. The filtered melt coming out of the DBF is called fine liquor,
which is sent to pan house for crystallization. In clarification, the color reduction from raw
melt to fine liquor is about 35-45%.
Refined Sugar
The clarified liquor is boiled in the vacuum pan in several stages. The commercial sugar is
produced from first three boiling stages called as R1, R2, and R3 Sugar. The R1 R2 and R3
wet sugars are dried. Dried pure sugar is collected in sugar bins, weighed and packed in
either 50 Kg bags or in 100 Kg bags as per the requirement.
By Products
In the sugar manufacturing process, there are two main by products are produced known as
Bagasse & Molasses.
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Bagasse – The residue of milling or diffusing process, the woody fiber of cane, in which the
residual juice and the moisture from the extraction process remain, is 'Bagasse'.
The great majority of the Bagasse supplies the fuel for the generation of steam from Boiler.
Molasses – The Final Molasses or black-strap a heavy, viscous material containing
approximately 1/3rd sucrose, 1/5th reducing sugars, and the remainder ash, organic non-
sugars, and water, serves as a base for cattle feed, or in the manufacture of industrial
alcohol and so on. On an average 45000 MT of molasses is generated during the season
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FIGURE 2.5: FLOW CHART FOR MANUFACTURE OF SUGAR
Step 1:
Step 2:
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FIGURE 2.6: PROCESS FLOW CHART WITH MATERIAL BALANCE FOR SUGAR AND CO-GEN
UNIT
Process Flow Chart:
650 Brix
Cane
Milling
A.H. Molasses ‘A’ Sugar
‘B’ Molasses ‘B’ Sugar
‘C’ Sugar Final Molasses
Mixed juice
Reaction Tank
Juice Heating
Power
Milk of lime
Muddy Juice
Vacuum Filter
Filter cake
Boiler
Scum
‘A’ Pan Boiling
Syrup
Evaporation
Clear Juice
Clarifier
Juice Heating
DISTILLERY
COMPOSTING
A, B & R4 sugar Imported Sugar
Melter
Raw Melt
Melt reaction
Clarifier
Clear melt
Deep Bed
Filtered Melt
R1
Massecuit
e
Sweet
Water
REFINED
SUGAR R4 sugar
R3 Molasses
R4 Massecuite
R3 sugar
R2 Molasses
R3 Massecuite
R2 sugar
R1 Molasses
R2 Massecuite
R1
sugar
Scum
Scum de-
sweetening
R4 Molasses
SULPHUR-
LESS WHITE
SUGAR
Scum to
muddy juice
P205 Decolorizer Lime Sucrate Flocculent
To cane syrup
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TABLE 2.6: OPERATION DETAILS OF THE PLANT AFTER EXPANSION
Sl No Description Unit Quantity
1 Crushing Capacity TPD 10,000
2 Crushing rate (hourly crushing) TPH 455
3 Duration of crushing season Days 200
4 Duration of Co-gen during off season Days 90
5 Sugar % cane % 12.4
6 Bagasse % Cane % 30.0
7 Molasses % Cane % 4.0
8 Press Mud % Cane % 4.0
9 Steam temperature 0C 121
Crushing season operation
1 Sugar Process steam requirement TPH 90
2 Bagasse required TPH 97.6
3 Steam generation TPH 194
4 Bagasse generation (max.) MT/D 3000
5 Molasses generation (max.) MT/D 400
6 Press mud generation (max.) MT/D 400
7 Total steam inlet to turbine TPH 194
8 Total Power Gen. (3 turbines of 15 + 9.3 + 9.7 MW)
Power consumption (captive power)
a) Sugar plant
b) Distillery unit
c) Power plant & lightning
MW 34
12.5
9 Power exportable MW 13 to 21.5
12 Sugar production per day MT 1,200
13 Power/day (Season only) MW 35.5
POWER PLANT
During Season:
1. Power Generation : 34 MW (3 turbines of 15 + 9.3 + 9.7 MW)
2. Power consumption at Co-Gen unit
3. Power consumption for Sugar Unit 12.5 MW
4. Power Consumption for Distillery unit
5. Export to KPTCL : 13 to 21.5 MW
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During Off-Season:
1. Power Generation : 7.5 MWh
2. Power consumption at Co-Gen unit : 1.0 MWh
3. Power consumption for Sugar Unit : -
4. Power Consumption for Distillery unit : 1.5 MWh
5. Export to KPTCL : 5.0MWh
2.8.2 STORAGE FACILITY FOR RAW MATERIALS AND PRODUCTS
2.8.2.1 Sugar Cane Storage
The factory takes delivery of the cane, either directly at the factory weighbridge or at
auxiliary weighbridges located important or remote points in the area from which the mill
draws its supplies. Transport is arranged by the factory, either by bull-carts, or more often
by Lorries or by tractors and trailers.
Details of Ware house:
Ware house details
No. of Warehouses Capacity in MT Type of Construction Remarks
I & II 17000 Roof AC sheets 25/50/100 Kg storage
III 15000 Quoted GI sheets 25/50/100 Kg storage
IV 22000 Quoted GI sheets 25/50/100 Kg storage
V 25000 Roof AC sheets 25/50/100 Kg storage
VI 30000 Quoted GI sheets 25/50/100 Kg storage
A' Frame 60000 Quoted GI sheets Bulk storage
2.8.2.2 Refined Sugar and Ethanol
Refined Sugar and ethanol are flammable solvents and these are stored in ground level MS
tanks. The tanks are constructed as per standards. Total storage capacity of the solvents will
be 10,000 KL. The Company has obtained necessary permissions for storage and handling of
these solvents. The storage capacity of these tanks is:
500 kl : 6
1500 kl : 4
100 kl : 3
50 kl : 2
200 kl : 3
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2.8.2.3 Molasses Storage Capacity:
At Distillery location molasses is stored in three storage tanks each of capacity 6000 MT
is provided.
At Sugar Plant location molasses storage tanks of capacity of 1 X 4500 MT and 3 X 6000
MT is provided. The storage tanks are well secured with tank forms with collection
facility for spilled molasses if any.
2.8.2.4 Alcohol Storage capacity:
Details of Alcohol storage capacity
Sl No Vessel No Material storage Storage Capacity in LTR
1 RSS-1 ENA Storage 1 1161108
2 RSS-2 ENA Storage 2 1161108
3 RSS-3 ENA Storage 3 1161108
4 ENS-1 Ethanol Storage 1 1468670.94
5 ENS-2 Ethanol Storage 2 1470118
6 ENS-3 Ethanol Storage 3 1470118
7 ENS-4 Ethanol Storage 4 1470118
8 ENS-5 Ethanol Storage 5 2302674.65
9 ENS-6 Ethanol Storage 6 2302674.65
10 ISS-1 RS below 65 OP tank 150648.96
11 ISS-2 RS receiver 2 150648.96
12 ISS-3 ENA Receiver 3 150648.96
13 RSR-1 ENA Receiver 1 65579.41
14 RSR-2 ENA Receiver 2 65579.41
15 RSR-3 Ethanol Feed Tank 65579.41
16 ISR-1 IS Receiver 1 8230.95
17 ISR-2 IS Receiver 2 8210.85
18 ISR-3 IS Receiver 3 8220.9
19 DSS-1 Ethanol Receiver 1 65731.35
20 DSS-2 Ethanol Receiver 2 64885.38
21 DSS-3 Ethanol Receiver 3 65731.35
22 F.O tank Fuel Oil Tank 15924.87
Total Storage Capacity 14853319 Lit
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2.9 PROJECT DESCRIPTION INCLUDING DRAWINGS SHOWING PROJECT LAYOUT,
COMPONENTS OF PROJECT.
Site plan drawing showing project site layout & various components is appended as Fig 2.2
in this chapter.
2.10 MITIGATION MEASURES INCORPORATED INTO THE PROJECT TO MEET
ENVIRONMENTAL STANDARDS, ENVIRONMENTAL OPERATING CONDITIONS OR OTHER
EIA REQUIREMENTS (AS REQUIRED BY THE SCOPE)
2.10.1. WATER DEMAND AND WASTEWATER/EFFLUENT DISCHARGE
2.10.1.1. SOURCE OF WATER SUPPLY
The source of water for the industry is Malaprabha River.
The sugar cane has about 60 to 70 % water content of which about 30 to 40 % of surplus
condensate is available and could be utilized. This water is recovered during the process at
various stages as condensates and reused for boiler, cooling, imbibition etc., therefore the
fresh water requirement is very less. The water consumption should not exceed 0.4 m3/ton
of cane crushed (general standards under EP rules schedule 6 part b Serial no. 2.) Further,
the standards prescribed for sugar plant effluent generation stipulated in the Notification
issued by MoEF under EP rules, No G.S.R 35 (E) dated 14th January 2016 is as under.
Final treated effluent discharge is restricted to 100 liter per tonne of cane crushed and
Waste water from spray pond overflow or cooling tower blow down to be restricted to 100
liter per tonne of cane crushed and only single outlet point from unit is allowed.
2.10.1.2 WATER DEMAND AND WASTEWATER DISCHARGE DURING OPERATION PHASE
The requirement of water for the unit is for industrial and domestic purposes.
Total number of employees: 450 people
The fresh water requirement of the industry is around 230 KLD including existing and
expansion project .Break-up of the consumption of water and waste water generation is as
presented in Table 2.8 & 2.9.
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Table 2.7 Existing water consumption and wastewater discharge-sugar unit, m3/d
Water available from Sugar cane:
Existing:
1. Water available from Sugar cane:
Sl
No
Water In Qty
cum/D
Water Out Qty
Cum/D
1 Water available
from Sugar cane
68% of Sugar
Plant 7500 TCD
5100 Loss of Water through Bagasse 15 % on
cane
1125
Loss of Water through Press mud 2.8 %
on cane
210
Loss of Water through F.M. 0.4% on cane 30
Loss of Water through Lime Grit 0.24%
on cane
18
Loss of Water through vapour vent of
Evap.& Pans 0.5%
41
Loss of Water through Clarifier flash
vapour 0.75% on cane
56
Loss of Water through Cooling tower
evaporation 24% on cane
1800
Surplus condensate water 1820
Total 5100 5100
Condensate utilization -1820 cum/day
After Cooling, surplus condensate 1820-100 = 1720 cum/day
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2. Sugar and Co-generation Water Consumption and Effluent generation in cum/day
Sl
No
Particulars Water
Consumption
Effluent
generation
Disposal
A. River water
1 Domestic (Fresh water) 50 45
No. of qtrs-
110 &
Population-
500 No.s
Total 50 45 Septic tank &
by soak pit
B. Surplus Water from Cane
utilization
2 Sugar Lab 15 15 Treated in
existing ETP
(Activated
Sludge
process).
3 Sugar Plant 75 75
4 Boiler make up & DM back wash
after Sugar condensate polishing
unit
(Fresh water-164
+ reuse- 209)=
374 cum/day
346
6 Cooling tower (Cogen) make up
after Sugar Condensate polishing
unit
760 50
Total 1059 486
NOTE: The treated sugar CPU remaining 661 cum/day is reused in distillery & Cooling tower
makeup. Therefore, the waste water generation and water use is within the stipulated limits
under the EP rules.
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3. Distillery Water Consumption and Effluent generation in cum/day
Sl
No
Particulars Water
Consumption
Effluent generation Disposal
A. Process
1 Fresh water 180 Spentwash-360 Composting
2 Reuse from distillery
CPU
545 Process condensate and
spent lees-545
Treated in
Distillery
CPU & reuse 3 Cooling tower makeup
from Sugar CPU
661 Blow down-50
NOTE: Total fresh water requirement is 394 cum/day
Table: - 2.8 After expansion water consumption & wastewater discharge-sugar unit, m3/d
1. Water available from Sugar cane:
Sl
No
Water In Qty
cum/D
Water Out Qty
Cum/D
1 Water available
from Sugar cane
68% of Sugar
Plant 10000 TCD
6800 Loss of Water through Bagasse 15 % on
cane
1500
Loss of Water through Press mud 2.8 %
on cane
280
Loss of Water through F.M. 0.4% on cane 40
Loss of Water through Lime Grit 0.24%
on cane
24
Loss of Water through vapour vent of
Evap.& Pans 0.5%
50
Loss of Water through Clarifier flash
vapour 0.75% on cane
75
Loss of Water through Cooling tower
evaporation 24% on cane
2400
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Surplus condensate water 2431
Total 6800 6800
Condensate utilization -2431 cum/day
After Cooling, surplus condensate 2431-120 = 2311 cum/day
2. Sugar and Co-generation Water Consumption and Effluent generation in cum/day
Sl
No
Particulars Water
Consumption
Effluent
generation
Disposal
A. River water
1 Domestic (Fresh water) 50 45
No. of qtrs-110 &
Population-500 No.s
Total 50 45
Septic tank & by
soak pit
B. Surplus Water from Cane
utilization
2 Sugar Lab 20 20 To be treated in
existing ETP
(Activated Sludge
process). We have
proposed to
Anaerobic digester
with existing
Activated sludge
process
3 Sugar Plant 200 200
4 Boiler make up & DM back
wash after Sugar condensate
polishing unit
580 500
6 Cooling tower (Cogen) make
up after Sugar Condensate
polishing unit
850 50
Total 1650 770
NOTE: The treated sugar CPU remaining 661 cum/day is reused in distillery & Cooling tower
makeup. Therefore, the waste water generation and water use is within the stipulated limits
under the EP rules.
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3. Distillery Water Consumption and Effluent generation in cum/day
Sl No Particulars Water
Consumption
Effluent
generation
Disposal
A Process
1 Fresh water 180 Spentwash-360 Composting
2 Reuse from distillery CPU 545 Process
condensate and
spent lees-545
Treated in
Distillery
CPU &
reuse 3 Cooling tower makeup from
Sugar CPU
661 Blow down-50
NOTE: Total fresh water requirement is 230 cum/day.
1.10.1.3 PROCESS EFFLUENT CHARACTERISTICS
The characteristics of wastewater are indicated in the table 2.10 below.
Table 2.9: Characteristics of wastewater
Sl
No
Parameters Process effluent,
(High BOD
effluent)
Excess
condensate
water
Domestic
effluent
1 Flow rate (m3/day) 770 2311 45
2 Temperature (0C) 38 32 42
3 pH 5.5 7.2 6.6-7.0
4 Dissolved solids (mg/lit) 1800 200 360
5 Suspended solids
(mg/lit)
320 Traces 60
6 BOD(mg/lit) 1500 100 250
7 COD(mg/lit) 3000 200 400
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2.10.1.4 DESCRIPTION OF WASTEWATER TREATMENT SCHEME & EFFLUENT TREATMENT
PROCEDURE
The effluent generated from the industry is treated in the Existing ETP of capacity 800 KLD.
Waste water conservation and pollution control management
1. Establishment of cooling arrangement and condensate polishing unit is provided for
recycling the excess condensate water to process or utilities or allied units.
2. Effluent Treatment Plant to be stabilized one month prior to the start of the crushing
season and continue to operate one month after the crushing season.
3. During no demand period for irrigation, the treated effluent to be stored in a seepage
proof lined pond having 15 days holding capacity only.
4. Flow meter to be installed in all water abstraction points and usage of fresh water to be
minimized.
Effluent Treatment Plant Process: -
The sugar factory effluent emanates mainly from washing cleaning operation thereby
entraining organic load in the form of sugar juice, sugar particles, bagasse etc. In the wash
waters leading to effluent generation. An in-plant control in the form of controlled washing
(absolutely nil washing is a theoretical phenomenon as periodic cleaning is a must for better
machinery operation) can reduce the (unnecessary) hydraulic load to a great extent. Also
there is a practice in the sugar factories to have open gutters and all gutters leading to the
main drain, ultimately joining the effluent treatment plant.
In this process a lot of clean/partially clean water leads to effluent treatment plant
unnecessarily. Experiments at other sister factories to segregate these streams (e.g. excess
condensates, pump cooling etc.) and to recycle them/ subject them to partial treatment and
reuse the same have yielded good results in terms of water saving and optimum hydraulic
load for the effluent treatment plant which is desirable from its effective operation. Same
work approach is implemented, so as to have minimum effluent volume and strength.
Observing the characteristics, it is evident that all the effluents are highly biodegradable.
However before subjecting the same to bio treatment, a ‘Preliminary Treatment’ unit is
devised to remove floating matter, grit oil and grease and for the measurement of flow. It is
essential for any biological treatment to have uniform organic loading in order to maintain
necessary Food/Bio culture ratio.
The characterization study has revealed an equalization period of one shift operation. An
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eight-hour retention time equalization tank would therefore be provided with mechanical
agitation for complete mixing by adding of lime for neutralization. Next it goes to primary
clarifier, here waste water will leave to settled down the sludge content in the bottom of the
tank only the overflow of the water will go for further treatment after chemical dosing. The
settled sludge in primary clarifier tank will pump to sludge drying bed. For further Aerobic
Treatment, effluent is treated in ‘High rate Activated Sludge’ system where the F/M is kept
low and MLSS concentration high by optimum sludge recirculation, the sludge being
separated in a ‘Secondary Clarifier’.
The small quantity of excess sludge is taken to ‘Sludge Drying Bed’ and the collected in
Treated Water is reused for Process, dilution of molasses and for cooling purposes.
Details of the Sugar ETP
i) Main gutter is constructed of stone /brick masonry with the following size. It is covered
with 75 mm thick R.C.C or stone slabs.
Flow Rate : 50 m3/h
Velocity : 0.6 m/s
Gradient : 1:200
Width : 0.30 mm
Height : 0.40 m
Oil : 60 ppm
ii. Screen
Coarse screen of 25 mm gap followed by the screen of 10 mm gap is provided in the main
gutter. Velocity through screen is 3 m/s at average flow and 0.6 m/s at peak load. Head loss
through screen at maximum flow is 0.15m, the floating entrapped on the screen are
removed manually. The bar is fabricated with 6mm x 25 mm flats. The flats are suitably
supported on 10mm x 10 mm cross bars. The bar screen is located at 300 inclination to the
flow direction.
Screen size : 0.6m x 0.8m
Screen chamber size : 0.6m x 1.2m x 0.55m
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iii. Oil separator (Oil and grease trap)
An oil separation tank of sufficient size is provided close to the grit chamber. Floating scum
consisting of oil, grease, fiber matter is periodically skimmed off. These tanks are provide in
duplicate with a common wall in between. Gates are provided on either side of each tank
for is independent operation.
Tank size (each) : 4.5m x 2.5m x 1.5m
iv. Effluent Collection Tank
Sump is constructed of stone / brick masonry. The tank is also used as equalizer tank to take
care of shock loads in the plant.
v. Neutralizer
Sump is constructed of stone/ brick masonry. It is provided with mechanical agitator. The
neutralized effluent is pumped to aeration tank. The tank is also used as equalizer tank to
take care of shock loads in the plant.
vi. Lime preparation tank
It is a Mild Steel rectangular tank. The tank is provided with mechanical agitator.
viii. Primary Clarifier
It is a circular type mechanical clarifier with central feed and peripheral discharge
arrangement. It is provided with continuous sludge removal facilitates, and is constructed of
R.C.C structure.
ix. Aeration tank – 1
The aeration tank is rectangular in section. It is constructed of stone masonry and R.C.C.
Structure. Aeration tank is provided with 4 nos. mechanical surface aerators, each of 15 HP
capacity. Aerators are supported on R.C.C platform. The sludge from secondary clarifier is
recycled to the aeration tank.
The mixing capacity of surface aerators is sufficient to keep the sludge in suspension.
x. Secondary Clarifier
It is circular type mechanical clarifier with central feed and peripheral discharge
arrangement. It is also provided with continues sludge discharge facilitates. It is constructed
of RCC structure.
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Environmental Impact Assessment Report 53
xvi Secondary Stage aeration System:
The Second stage Aeration tank with diffused Aeration system is provided. The total volume
of the tank is 510 cum and 80 diffusers are provided with 530 Nm3/hr capacity Air blower &
for clarification Hydro cyclone is provided.
xi. Sludge Sump
The sump is constructed of stone masonry.
Size of sump : 2m x 2m x 6m
Free board : 1m
xii. Sludge drying beds
The tank are constructed of stone masonry and they are filled with graded sand and pebbles
to a height of 0.6m
Size of sludge bed : 6m x 4.8m x 1m, 4 Nos.
Free board : 0.3m
Drying cycles : 6 days
Capacity of each bed : 28.8m2
xiii. Sludge Drying Bed Filtrate Sump:
Size of the sump : 2 m x 2m x 2.5m 1 No.
xiv. Pumps
Pumps are of C.I, non – clogging type with self-priming arrangement
A. Effluent Pump
Flow rate : 40m3
Head : Suction 5m Discharge: 10 m
S.S. In efficient : 1000 PPM
Density : 1.01 Gm/m1
Nos. : 2
B. Sludge pump
Flow rate : 30 m3/h (2 Nos.) and 10 m3/h (1 Nos.)
Head : Suction: 5m discharge: 10m
S.S. In efficient : 10,000 PPM
Density : 1.1 gm/ml
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Environmental Impact Assessment Report 54
xv. Polishing pond
The tank is rectangular in section and constructed of SPM work. The tank is provided inlet
and outlet chambers.
Flow rate : 800 m3/d
Tank size : 8.5m x 8.5m x 2m
Free board : 0.3m
Detention period : 3 hrs
Xvii Tertiary Treatment system:
The tertiary system comprising of Activated Carbon filter, Multimedia filter and softener is
provided for recycling and reuse of condensate and treated water.
Civil units and its dimensions
Sl No ETP Structure Dimensions in Meter Capacity Cum
1 Primary collection tank 10.4 X 8.1 X 2 168
2 Equalization Tank 8 X 8 X 2.1 134
3 Primary Clarifier(Scrapper type) 8 M Dia X 2.5 m Height 125
4 Aeration Tank I 23.5 X 23.5 X 3.3 1822
5 Diffused Aeration 3 x 20 HP Air blowers 700 cum/hr
6 Secondary Clarifier II (Scrapper
type)
Dia.10 m x 3.6 m
Height
282
7 Aeration tank II(Diffused ) 17 .1 X 8.4 X 3.2 459
8 Diffused Aeration 2 x 20 HP Air blowers 700 cum/hr
9 Hydro Cyclone 20 HP Two pumps 60 cum/hr
10 Treated Sump 8.4 X 4.2 X 2.9 102
11 MMF,ACF Capacity 22cum/hr
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Environmental Impact Assessment Report 55
Figure 2.7: Effluent Treatment Plant Flow Chart
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Environmental Impact Assessment Report 56
Figure 2.8: Photographs of the ETP and Online Monitoring Facility
ONLINE MONITORING REPORT
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Environmental Impact Assessment Report 57
TREATED EFFLUENT ONLINE MONITORING
Calender Dust Avg pH Avg COD Avg TSS Avg BOD Avg Flow Avg Dust Avg
Plant Station Units Range
SRSL-1 Dust analyser-
50TPH mg/Nm3
SRSL-1 ETP SUGAR
pH
SRSL-1 ETP SUGAR
mg/1
SRSL-1 ETP SUGAR
mg/1
SRSL-1 ETP SUGAR
mg/1
SRSL-1 ETP SUGAR
M3/hr
SRSL-1 Dust analyser-
44TPH mg/Nm3
01-12-2017 00:00 60.1 7.5 66.7 33.8 47.0 11.3 64.6
02-12-2017 00:00 71.2 7.7 67.9 33.1 47.8 4.0 75.3
03-12-2017 00:00 51.5 7.8 67.2 36.4 47.2 6.0 39.0
04-12-2017 00:00 72.7 7.9 63.2 38.9 45.0 14.4 68.2<
05-12-2017 00:00 33.8 7.6 57.9 47.0 41.6 11.5 34.5
06-12-2017 00:00 59.4 7.5 57.0 44.5 41.1 11.1 62.4
07-12-2017 00:00 45.6 7.6 58.8 40.0 42.7 16.2 29.2
08-12-2017 00:00 87.4 7.7 55.3 44.4 40.0 15.3 42.7<
09-12-2017 00:00 54.5< 7.7< 47.4< 53.1< 35.3< 12.1< 112.4<
10-12-2017 00:00 59.8< 7.6< 31.5< 63.2< 26.0< 11.6< 38.3<
11-12-2017 00:00 52.3 7.3 30.3 63.3 25.7 21.4 49.5<
12-12-2017 00:00 69.1 7.4 68.6 42.5 43.6 20.6 53.4
13-12-2017 00:00 51.2 7.0 138.6 53.1 81.2 12.8 82.3
14-12-2017 00:00 73.3 6.9 141.7 51.9 82.8 21.1 31.6
15-12-2017 00:00 63.1 6.9 111.0 34.4 66.2 13.3 45.2
16-12-2017 00:00 66.4 6.7 98.4 22.4 59.4 16.9 42.3
17-12-2017 00:00 76.6 6.5 99.2 23.1 60.0 22.0 57.2
18-12-2017 00:00 84.0 6.8 109.0 40.3 65.0 16.6 83.8<
19-12-2017 00:00 31.2 4.4 88.0 26.3 53.8 15.7< 53.5<
20-12-2017 00:00 33.9 2.1 88.4 31.5 46.5 18.2 62.8
21-12-2017 00:00 50.0 6.4 50.8 8.7 20.2 10.4 57.4
22-12-2017 00:00 69.3 6.4 66.0 20.3 27.4 16.0 71.5
23-12-2017 00:00 68.6 7.3 98.9 43.4 43.7 9.5 73.3
24-12-2017 00:00 32.2 7.3 102.0 38.3 45.2 10.5 40.5
25-12-2017 00:00 44.6 65.8 88.6 39.0 38.5 2.5 28.0
26-12-2017 00:00 67.0 6.6 47.8 45.5 18.5 9.9< 63.0
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Environmental Impact Assessment Report 58
2.10.2 POWER
The power requirement will be through co-generation unit. DG Set will act as backup facilities
in case of power failure. The details of power requirement given in below table;
During Season:
1. Power Generation : 34 MW (3 turbines of 15 + 9.3 + 9.7 MW)
2. Power consumption at Co-Gen unit
3. Power consumption for Sugar Unit 12.5 MW
4. Power Consumption for Distillery unit
5. Export to KPTCL : 13 to 21.5 MW
During Off-Season:
1. Power Generation : 7.5 MWh
2. Power consumption at Co-Gen unit : 1.0 MWh
3. Power consumption for Sugar Unit : -
4. Power Consumption for Distillery unit : 1.5 MWh
5. Export to KPTCL : 5.0MWh
2.10.3 AIR POLLUTION SOURCES
The major source of emission is from boiler & DG stack. The industry is presently operating 4
boilers each of capacity 100 TPH, 50 TPH, 44 TPH & 26 TPH respectively. A diesel generator of
1165 KVA- 1 No. and 1 No. of 1010 KVA DG Set are also present in the industry. APC measures
are adequate to disperse the pollutant. Adequate green belt will be developed to mitigate the
pollution arising due to movement of vehicles. The air pollution source and control measures
are given below;
Table 2.10: Air Pollution Sources and control measures
Stac
k No
Stack attached to Type
of
fuel
Fuel
Consumption
Stack
height
Emission Limits Air
pollution
control
measures
Existing Proposed L/h T/h
1 100 TPH
Boiler
No
change
Bagas
se
-- 46.2 Comm
on
chimne
y of
SPM
150
ESP
2 50 TPH
Boiler
No
change
-- 22.0 ESP
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Environmental Impact Assessment Report 59
65m
AGL
3 44 TPH
Boiler
No
change
-- 20.0 Comm
on
chimne
y
of 58m
AGL
Wet
Scrubber
4 26 TPH
Boiler
No
change
-- 11.5 Wet
Scrubber
5 1165
KVA DG
No
change
Diesel 244 -- 30m
AGL
No2 &
PM
710
&
100
Acoustic
Enclosures
6 1010
KVA DG
No
change
212 -- 30m
AGL
Acoustic
Enclosures
The standard prescribed under EP rules for emission from sugar plant, boiler sources is
particulate not to exceed 150 mg/Nm3 (G.S.R 35 (E) date 14th January 2016). The consent issued
by KSPCB is also as per the EP rules. The emissions standards are meet with the existing APC
equipment’s.
In the present expansion no new boiler is proposed.
Gaseous emissions discharged from the industry are flue gas from boilers and diesel
generators. The stack emissions in the existing unit are regularly monitored for the pollution
parameters SPM, SOx and NOx. Online monitoring facility is also provided. The generator is
used only during the emergency and power failure to operated essential service.
The boiler of 44 TPH and 26 TPH are connected to stack 1 of 58m AGL height and boiler of 100
TPH and 50 TPH are connected to stack 2 of 65m AGL Height. During off-season only the 50 TPH
boiler will be operated mainly to supply steam and power to the distillery and to reprocess the
accumulated raw sugar in the plant. The boiler is connected to the stack-2 of 65 m height.
During off-season the boiler is run on bagasse or coal depending on the availability of fuel.
However, as a conservative measure the chimney is designed based on coal as a fuel.
Nitrogen and sulphur content in bagasse is low. Hence, toxic gases such as nitrogen oxides and
sulphur dioxide in flue gases are very small. The main contamination in flue gases is a
particulate suspended matter due to fly ash and un burnt carbon particles, which need suitable
device for physical separation. The bagasse fired boilers are connected to Chimney-1 and
Chimney-2. The height of chimneys is sufficient to dissipate the pollution away from the
premises over a wide atmospheric area. The chimneys are provided with port holes, working
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Environmental Impact Assessment Report 60
platform and ladder for sampling of the flue gases. Wet scrubber is connected to the 44 TPH &
26 TPH boiler and Electro static precipitator (ESP) is connected to 100 TPH and 50 TPH boilers.
The cleaned gas is then discharged to atmosphere through chimney.
During off-season the existing boiler of 50 TPH will be fired with low sulphur coal. Sulphur
dioxide is the significant pollutant in flue gases. The boiler is connected to the chimney of 65 m
height. The height is sufficient to dissipate the pollution away from the premises over a wide
atmospheric area. The chimney is provided with port holes, working platform and ladder for
sampling of the flue gases. The boiler will be provided with ESP. The cleaned gas is then
discharged to atmosphere through chimney. Details of emissions and chimney are furnished in
Details of Emissions and Chimney
Operation during Season
Chimney-1
Connected Boiler : 44 TPH boiler and 26 TPH Boiler
Total Steam generation : 70 T/hr
Fuel : Bagasse
Steaming capacity of Bagasse : 2.2 T steam per Ton of bagasse
Ash content in bagasse : 1.0 %
Fuel consumption (70/2.2) : 31.5 T/hr
Quantity of flue gas : 110 T/hr (94303 Nm3/hr)
Diameter of chimney : 3.0 m
Height of chimney : 58 m
SPM in fuel gas at chimney : 137 mg/Nm3
Velocity at chimney top : 7.75 m/s
Flue gas Temp. at chimney : 100 0C
Ambient temperature : 30 0C
Boiler ash : Bottom ash 0.013 T/hr (0.312 T/d), Ash at Wet scrubber 0.037 T/hr (0.888/d), Fly ash 0.15
T/hr (3.6T/d) and Total ash 0. 20 T/hr (4.8 T/d)
Chimney-2
Connected Boiler : 50 TPH boiler & 100 TPH boiler
Total Steam generation : 150 T/hr
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Fuel : Bagasse
Steaming capacity of bagasse : 2.2 T steam per Tonne of bagasse
Ash content in bagasse : 1.0 %
Fuel consumption (150/2.2) : 68.2 T/hr
Quantity of flue gas : 375 T/hr (321485 Nm3/hr)
Diameter of chimney : 4.4 m
Height of chimney : 65 m
SPM in fuel gas at chimney : 140 mg/Nm3
Velocity at chimney : 6.80 m/s
Flue gas temp. at chimney : 150 0C
Ambient temperature : 30 0C
Boiler ash : Bottom ash 0.045T/hr (1.08 T/d), Ash at ESP 0.135 T/hr (3.24 T/d) Fly ash 0.50 T/hr (12 T/d)
and Total ash 0.680 T/hr (16.32 T/d)
Operation During Off-Season
Chimney-2
Connected Boiler : 50 TPH boiler
Total Steam generation : 50 T/hr
Fuel : Coal
Fuel consumption : 10.0 T/hr
Sulphur in coal : 0.8 %
Sulphur dioxide in flue gases : 0.16 T/hr
Steaming capacity of coal : 5.0 T steam per Ton of coal
Ash content in coal : 10 %
Quantity of flue gas : 110 T/hr (94303 Nm3/hr)
Diameter of chimney : 4.4 m
Height of chimney : 65 m
SPM in fuel gas at chimney : 150mg/Nm3
Velocity at chimney top : 2.4 m/s
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Environmental Impact Assessment Report 62
Flue gas Temp. at chimney : 150 0C
Ambient temperature : 30 0C
Boiler ash : Bottom ash 0.045 T/hr (1.08T/d), Ash at ESP 0.135 T/hr (3.24 T/d), Fly ash 0.50T/hr (12T/d)
and Total ash 1.00 T/hr (24T/d)
2.10.4 NOISE GENERATION AND ITS MANAGEMENT
The major source of noise pollution in the industry is the Boiler and DG sets for which acoustic
enclosures are provided. Also ambient noise levels will be ensured within the ambient
standards by inbuilt design of mechanical equipment and building apart from vegetation (tree
plantations) along the periphery and at various locations within the industry premises.
2.10.5 SOLID WASTE GENERATION AND MANAGEMENT
The solid wastes or by-products produced in sugar industry such as bagasse, press mud and
molasses are made use as valuable resources. Other solid wastes in the industry are boiler ash,
lime sludge and ETP sludge. The solid wastes generated from different operations are given
below said Table;
Table 2.11: Solid wastes management
Sl
No
Solid Waste Mode of collection Mode of disposal
1 Boiler- bottom ash Mechanical conveyor
into common silo or
further disposal
Ash collected from ash silo is mixed press
mud and used for making compost. 2 Boiler fly ash
3 Lime grit Mechanical screw
conveyor
Collected in trailers used for land filling
4 Press mud Mechanical conveyor Utilized as raw material for making
compost
5 Sludge from ETP Sludge drying beds Dried Sludge id mixed with compost and
used for making compost
Domestic solid waste (garbage trash/ garden litters) will be stored in garbage collection
pits and disposed to nearby municipality.
Any other solid waste generated from the facility will be disposed of by using proper
disposal mechanism.
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2.10.5.1 BAGASSE
0.30 T/d of bagasse is produced per tonne of cane crushed in the sugar plant. Bagasse is mainly
utilized in boiler. A small quantity of bagasse is also used in clarifier for purification muddy
juice.
The bagasse with 50% moisture is a combustible material with the heating value of about 2000
k cal per kg, and therefore it is mainly used as a fuel in boiler for generation of steam. The
steam in turn is used for generation of electric power and also to meet the process
requirement of low-pressure steam. Bagasse is a fibrous material containing mainly cellulose
material and therefore it can be used as a raw material in the manufacture of pulp and paper.
2.10.5.2 MOLASSES
Large quantity of molasses is produced in the industry. It contains large percentage of non
crystallisable sugar and is a valuable source of raw material for manufacture ethyl alcohol or
other products such as oxalic acid, lactic acid etc. Molasses is also used as nutritive additive in
manufacture of cattle feed. In the present industry the molasses is supplied mainly to
distilleries for production of ethanol.
2.10.5.3 PRESS MUD
Large quantity of press mud is produced in the industry. It contains fibrous material and crop
nutrients such as phosphorous and potassium and therefore it is disposed to farmers for use in
agricultural land. The press may be composted along with other nutrients. The composted
press mud is a bio- manure containing, fortified plant nutrient such as potassium, phosphorous
and nitrogen.
2.10.5.4 BOILER ASH
Boiler ash is produced from the boiler. It contains silica, and other metal oxides. It is a non-toxic
material. It can be used in manufacturing bricks. It is also used along with the agro wastes for
composting and production of fortified green manure. The ash produced in the industry will be
disposed to farmers as soil conditioner for agricultural land.
2.10.5.5 ETP SLUDGE
ETP sludge is a non-toxic material containing mainly organic material and mineral nutrients. It is
mixed with compost and used for making compost
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Environmental Impact Assessment Report 64
2.10.5.6 LIME SLUDGE
Small quantity of sludge is produced from primary and secondary clarifiers in the industry.
Major quantity of the sludge from secondary clarifiers is re-circulated to the aeration tank.
Excess sludge of from clarifiers is dewatered and partially dried in sludge drying beds.
Hydrated lime is used in the plant for purification of juice and therefore, the quantity of lime
sludge produced from the plant is small. The sludge with an average moisture content of 50 %
produced from lime plant.
2.10.6 HAZARDOUS WASTE GENERATION AND ITS MANAGEMENT
There is no Hazardous Waste generation from the process, only waste oil from the D G Sets is
the hazardous waste generation from the industry. The hazardous waste is being disposed to
KSPCB Authorized agencies. The quantity and disposal details are given below;
Hazardous waste management
Waste
category
Hazardous waste
generated
Quantity Method of handling
Existing After Expansion
5.1 Used Oil 0.4 KLPA 0.5 KLPA Stored in secure manner and
disposed to KSPCB authorized
agencies
2.10.7 COMPOSTING OF PRESS MUD WITH SPENT WASH
Composting is a process wherein the waste bio mass is decomposed and/or stabilized in the
presence of micro-organism (culture) and moisture to produce bio-manure containing stable
humus and soil like product. In the present industry the bio mass is composted along with
spent wash and it is carried out on the specially constructed yard (compost yard) to avoid
spillage and seepage of material. The bio mass consists of mainly press mud. Nutrients such as
potash and phosphate present in spent wash are passed on to the composted product. The bio-
manure thus produced is a valuable substitute to chemical fertilizer for use in agriculture.
Present compost yard has a capacity to utilize 360 m3/d of spent wash produced from the
existing ethanol plant. The performance of the compost yard and process is satisfactory. After
expansion, the quantity of spent wash will be same and therefore, the capacity of existing
compost yard will be adequate for the purpose
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Environmental Impact Assessment Report 65
2.10.7.1 COMPOSTING PROCESS
The press mud and the other bio-mass brought from different sources is collected on the bio-
mass storage yard. Bio-mass is then transported through tractor trolley to compost yard and
laid into 100 m x 3 m x 1.2 m windrows. Aerobic microbial culture is applied to the windrows.
Spent wash is drawn from spent wash storage tank through pump and hose pipes and then
sprayed on windrows on a regular interval of 2 to 3 days for about 6 to 8 weeks. With the
application of spent wash the moisture content in press mud increases to about 65% to 70%.
In the presence of culture and adequate moisture the microbial reaction starts and heat is
generated. It increases temperature of the press mud to about 60 – 65° C. At such
temperatures some of the water is evaporated and moisture content in press mud reduces.
This slows down the reaction and thereby the temperature of press mud reduces. In the
meantime, the windrows are again sprayed with spent wash to enhance its moisture content
and composting process. The wind roses are intermittently aerated by reshuffling with
mechanical aero tiller to keep the mass under aerobic condition.
The optimum moisture content and temperature for composting is 55% and 45 °C, respectively.
After composting brown colored free flowing bio manure is produced. The product is cured for
about 2 weeks on the yard. The product is pulverized, screened, packed in 50 Kg HDPE bags and
then stored in the godown. The product is dispatched to farmers through lorry or tractor
transport.
2.10.7.2 CONSTRUCTION OF COMPOST YARD
For construction of compost yard, the ground was leveled and covered with 0.3m thick
imperious soils. The compost yard was designed and constructed as per MOEF guidelines.
The floor is sloped (1:100) to provide free flow of surface run off. A garland gutter is provided
all around the yard to receive and lead the surface runoff to the leachate collection tank. A
parapet wall of 0.6 m height is constructed all around the yard to prevent the spillage of
material. Piping network with pump and nozzles is provided in the yard to spray the spent wash
on windrows.
2.10.7.3 EQUIPMENTS AND MACHINERIES FOR COMPOST PROCESS
Following equipments are provided for composting of press mud:
i. Tractor for transportation of press mud
ii. Aero tiller with spraying arrangement (for churning up to bottom)
iii. Front end loader with tractor
iv. Pulverizes and sieving machine
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Environmental Impact Assessment Report 66
2.11 Schematic representations of the feasibility drawing which give information of EIA
purpose.
A schematic representation of the overall feasibility and environmental assessment process is
shown below.
Fig :- 2.9 Schematic representations of the feasibility
ACTVITIES OVERVIEW OF SOURCE OF INFORMATION E.I.A STUDIES
RECONNAISANCE SURVEY OF
EXISTING PLANT
MONITORING OF AIR, WATER &
SOIL QUALITY NOISE LEVELS
DATA ON METEOROLOGY
SOCIO-ECONOMIC STATUS &
BASIC ANIMITIES SITES VISITS
BY AN INTERVIEWS WITH
LOCALS
CONSEQUENCE ANALYSIS
PREPARASTION OF DISASTER
MANAGEMENT PLAN
DESCRIPTION OF EFFLUENT
TREATMEN PLAN, AIR
POLLUTION CONTROL,
HAZARDOUS WASTE
MANAGEMENT, GREEN BELT
DEVELOPMENT MONITORING
PROGRAM
SAFTEY, HEALTH & ENVIRONMENTAL
POLICY, GUIDELINES BY DIRECTOR
GENERAL OF FACTORY SAFTEY,
MINISTRY OF LABOUR
IDENTIFICATION &
ASSESSMENT OF IMPACTS
EVALUATION OF IMPACTS BY
MATRIX METHOD
FACILITY DESCRIPTION
ENVIRONMENTAL INFORMATION CENTER
CENTRAL GROUND WATER BOARD
KARNATAKA STATE POLLUTION CONTROL BOARD
AGRICULTURE DEPARTMENT
IRRIGATION DEPARTMENT
CENSUS FROM SECANDARY SOURCE
INDIAN METHADOLOGICAL DEPARTMENT
ANNUAL REPORT
MARKET ASSESSMENT
FINANCIAL REPORT
PROJECT REPORT
ENVIRONMENTAL
MANAGEMENT PLAN
IMPACTS
METHODOLOGY OF
IMPACT ASSESSMENT
PROPOSED PLANT
SOCIO ECONOMIC
STATUS &
INFRASTRUCTURE
BASELINE
ENVIRONMENTAL
STATUS
INTRODUCTION
RISK ANALYSIS
STUDIES &DISASTER
MANAGEMENT PLAN
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Environmental Impact Assessment Report 67
2.12 RAINWATER HARVESTING & GROUNDWATER RECHARGING
Large quantity of storm water is generated during rainy days. Rain water collection and
harvesting plan is implemented to conserve the water resources and to improve the
underground water table. The factory area is segregated into different premises for effective
management of storm water. Storm water gutters are designed and constructed based on
contour data of the premise and rainfall data of the region. Total land area of the project is
104.18 acres of which green belt is 35.44 acre, built up area is 54.88 acre including paved area
and roads. Vacant land is 13.86 acres. The cane yard, bagasse yard and press mud yard contain
solid matter. Necessary measures are taken to control the quality of the storm water.
Therefore these premises are isolated with garland channels. The floorings are suitably
compacted to minimize percolation to avoid ground water contamination.
STORM WATER
Storm water gutters are constructed in the premise as per the standards. The storm water
drains are led to rain water reservoirs constructed at the lowest level of the premises. The rain
water thus collected is used for greenery development in the industry. It can also be used as a
source of water for the industry. The storm water collected from different locations of the
factory premise is estimated as given below.
There are two numbers of Rain water storage tanks of following specifications are constructed
in earthen work as per standard practices.
Reservoirs Capacity in m3 Average storage height
in m
Size in m
Tank 1
Tank 2
128
120
2
2.5
5
8 x 8 x 2
6 x 8 x 2.5
2.13 ASSESSMENT OF NEW & UNTESTED TECHNOLOGY FOR THE RISK OF TECHNOLOGICAL
FAILURE
The project is expansion of existing sugar plant. The manufacturing process for these products
is a tried & tested method & therefore there is no risk of technological failure.
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Environmental Impact Assessment Report 68
CHAPTER 3
DESCRIPTION OF THE ENVIRONMENT
3.0 INTRODUCTION
This chapter illustrates the description of the existing environmental status of the study area
with reference to the prominent environmental attributes. The environmental influence due to
the project is likely to be restricted to project site and its surroundings consisting of about 10
km around the factory premises.
The existing environmental setting is considered to establish the baseline conditions which are
described with respect to climate, hydro geological aspects, atmospheric conditions, water
quality, soil quality, vegetation pattern, ecology, socio economic profile, land use, and places of
archaeological importance. The baseline studies are carried out for one season covering
variations in various domains of environment.
The data is collected from both primary and secondary sources. Primary source data were
collected through environmental monitoring and survey of the study area. For reconnaissance
survey the sampling locations were identified based on:
• Existing topography and meteorological conditions
• Locations of water bodies.
• Location of human habilitation and other sensitive areas present in the vicinity of the
proposed project site.
• Representative areas for baseline conditions.
• Accessibility for sampling
3.1 STUDY AREA, PERIOD, COMPONENTS & METHODOLOGY
STUDY AREA: An area, covering 10 km radial distance around the project site is considered as
the study area for conducting baseline studies as per the Terms of Reference issued by SEIAA.
PERIOD: Baseline study in this Rapid Environmental Impact Assessment report was conducted
for a period of three months during January 2018 to March 2018.
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Environmental Impact Assessment Report 69
COMPONENTS: Environmental attributes Air, noise, water & soil analysis studies were carried
out. Survey of flora & fauna in the surroundings & demographic pattern of the survey area
were also studied.
METHODOLOGY: Baseline environmental studies were conducted to know the status of various
environmental attributes, viz. climatic and atmospheric conditions, air, water, noise, soil, land
use pattern, ecological, socio economic environment. The studies involved conducting field
studies, monitoring and analyzing various parameters that might be affected due to the
expansion and conducting socio-economic survey among the people. Secondary data was
collected from State/Central Government organizations and semi-Government.
Methodology used for conducting the monitoring and analysis of ambient air quality is as per
the National Ambient Air Quality Standards. The other attributes are monitor using standard
sampling procedures and analyzed as per the American Public Health Publication and Manual
Published by CPCB.
The location & topo map of the plant is in fig 3.1 &3.2
Fig 3.0: Location map of the project site
Note: Latitude: 15” 51.375’ N, Longitude: 75” 6.105’ E; 609 m above MSL
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Environmental Impact Assessment Report 70
Table: - 3.1 Co-ordinates w.r.t. all corners
Sl no Points Latitude Longitude
1 A 15051’14.60” N 75006’23.76” E
2 B 15051’17.63” N 75006’16.61” E
3 C 15051’29.62” N 75006’19.46” E
4 D 15051’29.66” N 75005’51.11” E
5 E 15051’19.97” N 75005’49.98” E
6 F 15051’01.73” N 75006’10.12” E
7 G 15051’12.12” N 75006’14.66” E
Fig 3.1: Topo map of the study area
Source: Survey of India; Scale 1:50000
Source: Survey of India; Scale: 1:50000
Note: Topo map of 10 km radius is appended as Annexure 5
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3.2 ESTABLISHMENT OF BASELINE
3.2.1 Meteorological data
Assessment of the micro and macro meteorology is important from the standpoint of
understanding the nature and extent of air pollution in the study area. Climate has an
important role in the build-up of pollution levels. The climatic condition of the area may be
classified as moderately or seasonally dry, tropical or temperate savanna climate with four
seasons in a year. Winter is critical for air pollution build-up because of frequent calm
conditions with temperature inversions resulting in poor atmospheric mixing, natural
ventilation and high emission loads.
The classification of months according to the seasons is given in the following table.
Season Period Summer March to May
Monsoon June to September
Post monsoon October to November
Winter December to
February
The metrological data reflecting minimum, maximum temperature in 0C, relative humidity in %,
rainfall in mm/hr, wind speed in m/s, mixing height in m, cloud cover in tenths and atmospheric
pressure in mb for the year 2017 obtained from
https://www.worldweatheronline.com/belagavi-weather-averages/karnataka/in.aspx has
been appended as table 3.1.
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Table 3.2: Meteorological data of Belagavi for the year 2017
Month Temperature 0C Relative
humidity %
Precipitation
rate (mm)
Atmospheric
Pr. (mb)
Wind speed
(m/hr)
Cloud
cover (%) Min Max
Jan 17 33 46 0.6 1013.3 4.5 7
Feb 19 36 39 0.0 1012.9 4.7 1
Mar 20 39 41 2.4 1010.3 4.5 5
Apr 21 40 49 4.5 1009.2 5.1 4
May 23 32 70 68.7 1008.4 6.9 21
June 21 26 87 100.6 1007.4 8.9 74
July 21 27 87 79.2 1008.2 11.0 83
Aug 21 27 86 104.8 1007.4 10.7 82
Sept 21 27 86 440.3 1008.4 6.7 63
Oct 20 28 78 195.2 1009.2 5.6 39
Nov 19 29 56 26.1 10011 6.0 14
Dec 19 28 53 10.4 1012.9 7.4 16
The following charts show yearly weather trends with information on monthly weather
averages and extremes.
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3.2.1.1 Temperature
The chart below plots the average high and low temperature for each month of the
year.
Fig – 3.2 Temperature Chart
3.2.1.2 Rainy days
The chart below plots the average number of days in any month that you can expect to
see rain falling.
Fig – 3.3 Average Rainfall Chart
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3.2.1.3 Wind Speed
The chart below plots the average daily wind speed you can expect for any month. It
also shows the maximum recorded sustained wind speed for each month.
Fig – 3.4 Windspeed Chart
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WIND ROSE DIAGRAMS
1) March to May
WRPLOT View - Lakes Environmental Software
WIND ROSE PLOT:
October to December
COMMENTS: COMPANY NAME:
Shilpa Medicare Ltd. Unit I
MODELER:
Samrakshan
DATE:
4/12/2018
PROJECT NO.:
NORTH
SOUTH
WEST EAST
3%
6%
9%
12%
15%
WIND SPEED
(m/s)
>= 11.1
8.8 - 11.1
5.7 - 8.8
3.6 - 5.7
2.1 - 3.6
0.5 - 2.1
Calms: 8.51%
TOTAL COUNT:
2208 hrs.
CALM WINDS:
8.51%
DATA PERIOD:
2011 Mar 1 - May 3100:00 - 23:00
AVG. WIND SPEED:
2.60 m/s
DISPLAY:
Wind SpeedDirection (blowing from)
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2) June to September
WRPLOT View - Lakes Environmental Software
WIND ROSE PLOT:
June to september
COMMENTS: COMPANY NAME:
M/s. Gadag Envirotech
MODELER:
Samrakshan
DATE:
4/12/2018
PROJECT NO.:
NORTH
SOUTH
WEST EAST
14%
28%
42%
56%
70%
WIND SPEED
(m/s)
>= 11.1
8.8 - 11.1
5.7 - 8.8
3.6 - 5.7
2.1 - 3.6
0.5 - 2.1
Calms: 0.17%
TOTAL COUNT:
2928 hrs.
CALM WINDS:
0.17%
DATA PERIOD:
2011 Jun 1 - Sep 3000:00 - 23:00
AVG. WIND SPEED:
4.57 m/s
DISPLAY:
Wind SpeedDirection (blowing from)
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Shree Renuka Sugars Ltd
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Environmental Impact Assessment Report 77
3) October to November
WRPLOT View - Lakes Environmental Software
WIND ROSE PLOT:
October to November
COMMENTS: COMPANY NAME:
M/s. Gadag Envirotech
MODELER:
Samrakshan
DATE:
4/12/2018
PROJECT NO.:
NORTH
SOUTH
WEST EAST
6%
12%
18%
24%
30%
WIND SPEED
(m/s)
>= 11.1
8.8 - 11.1
5.7 - 8.8
3.6 - 5.7
2.1 - 3.6
0.5 - 2.1
Calms: 11.54%
TOTAL COUNT:
1464 hrs.
CALM WINDS:
11.54%
DATA PERIOD:
2011 Oct 1 - Nov 3000:00 - 23:00
AVG. WIND SPEED:
2.77 m/s
DISPLAY:
Wind SpeedDirection (blowing from)
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Environmental Impact Assessment Report 78
4) December to February
WRPLOT View - Lakes Environmental Software
WIND ROSE PLOT:
December to February
COMMENTS: COMPANY NAME:
M/s. Gadag Envirotech
MODELER:
Samrakshan
DATE:
4/12/2018
PROJECT NO.:
NORTH
SOUTH
WEST EAST
6%
12%
18%
24%
30%
WIND SPEED
(m/s)
>= 11.1
8.8 - 11.1
5.7 - 8.8
3.6 - 5.7
2.1 - 3.6
0.5 - 2.1
Calms: 13.75%
TOTAL COUNT:
2160 hrs.
CALM WINDS:
13.75%
DATA PERIOD:
2011 Check Date Range Report00:00 - 23:00
AVG. WIND SPEED:
2.38 m/s
DISPLAY:
Wind SpeedDirection (blowing from)
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3.2.1.4 Humidity & Cloud
Fig 3.5 Humidity Chart
3.2.1.5 Atmospheric Pressure
Fig 3.6 Pressure
3.2.1.6 Mixing height or inversion
The inversion layer is a dynamic region, which changes depending on the atmospheric
condition. Mixing height is the region between the bottom of the inversion layer and the
ground. The mixing height can be calculated based on the vertical temperature profile of
the atmosphere.
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3.3 BASELINE DATA
Primary data collected
Environmental
Parameters
Locations for proposed
data collection
Source
Air Quality 8 locations Primary
Meteorology 1 location Secondary data
Water 8 locations Primary
Soil 8 locations Primary
Noise 8 locations Primary
Ecology Study Area Primary and Secondary
Geology and Hydrology Study Area Primary and Secondary
Land use Study area Primary and Secondary
Socio-Economic Study Area Primary and Secondary
3.3.1 BASELINE MONITORING
3.3.1.1 SAMPLING AND ANALYTICAL TECHNIQUES
Environment
Aspect
Parameter Frequency Method
Ambient Air
Quality
PM10, PM2.5, SO2 & NOx, CO,
O3
8 Locations
24 hours for 3
months.
PM10, PM2.5 : Gravimetric method
SO2 : Modified West and Gaeke
Method (IS : 5182, Part II)
NOx : Jacobs and Hochheiser
Method (IS 5182 Part VI)
Water
Quality
pH, EC, Total alkalinity,
Chlorides, Hardness, Ca,
Mg, TDS, DO, COD, BOD,
Sulphate, Phosphate, Na, K,
Cu, Fe, Total coliform &
E.coli
Surface
water 4
locations
Ground
water 8
locations
3 months
Physical, chemical & bacteriological
as per APHA and Manual Published
by CPCB.
Noise Quality Noise levels in dB(A) 8 locations
3 months
IS: 9989-1981 (Reaffirmed 2001)
as adopted by CPCB.
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Soil Quality Physical, Chemical
Characteristics, Soil Texture
8 locations
3 months
Lab standard operating procedures
and department of agriculture and
cooperation ministry of agriculture
Govt of India, New Delhi
3.4 AIR QUALITY
The baseline air quality was established by monitoring major air pollutants like
particulate matter, oxides of sulfur & nitrogen at various locations near the project site.
High volume samplers were used for ambient air sampling. Particulate Matter (PM) i.e.
PM2.5& PM10, sulfur dioxide (SO2), oxides of nitrogen (NOx), NH3, Pb, O3, Benzo(a)
pyrene in particulate phase, As, Ni, CO etc. were monitored. Samples were collected
continuously from all the stations for 24 hours for two consecutive days.
Baseline data for ambient air quality was collected during the month of January to
march 2018. The sampling stations along with their distance and direction from the
project site, ambient air quality monitoring stations, wind rose diagram showing the
direction of the blowing wind during the analysis period, ambient air quality analysis
data & National Ambient Air Quality Standards specified by MoEF are detailed
subsequently.
The observations made during the study period are presented under the forthcoming
sub-sections. The Ambient air sampling stations details are shown in the below table
3.2.
Table 3.3: Ambient air sampling stations
Sl
No
Code
No
Name of the
station
Distance from
the site(km)
Direction from
site
1 A1 Project site - -
2 A2 Ujjanakoppa 7.0 North
3 A3 Munoli 0.8 East
4 A4 Naviluteertha 3.8 South
5 A5 Jakabal 6.5 North East
6 A6 Shindogi 5.0 South East
7 A7 Shrirangapura 6.0 North West
8 A8 Karlakatti 8.5 South West
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3.4.1 AIR QUALITY AT THE PROJECT SITE AND OTHER LOCATIONS:
Ambient air quality analysis was conducted at 8 locations from January to March
2018. The Air quality data analysis at the project site are tabulated in the table 3.3, Air
quality data analysis at other locations are in the table 3.4 & Ambient air quality
standards prescribed in Environment protection Rules 1986, as per the notification
dated 16th November 2009 for industrial, residential & rural areas is shown table 3.5
below.
Table 3.4: Air quality data analysis at the project site
Sl
No
Parameter Monitoring
Period
24 Hrs
concentration
(µg/m3)
Monitoring
station
1
PM2.5, µg/m3
Jan 46.13
Feb 53.62
Mar 57.93
Average 52.56
2
PM10, µg/m3
Jan 88.38
Feb 91.26
Mar 91.67
Average 90.43
3
SO2, µg/m3
Jan 4.73
Feb 4.95
Mar 4.37
Average 4.68
4
NOx, µg/m3
Jan 9.74
Feb 10.52
Mar 9.20
Average 9.82
5
CO, mg/m3
Jan 0.20
Feb 0.48
Mar 2.82
Average 1.16
6 Ozone (O3) Jan BDL
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Feb
Mar
Average
7
Lead
Jan
BDL Feb
Mar
Average
8
Ammonia
Jan
BDL Feb
Mar
Average
9
Benzene
Jan
BDL Feb
Mar
Average
10
Benzo (a)
pyrene
Jan
BDL Feb
Mar
Average
11
Arsenic
Jan
BDL Feb
Mar
Average
12
Nickel
Jan
BDL Feb
Mar
Average
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AIR QUALITY DATA ANALYSIS AT ALL LOCATIONS (EXCEPT PROJECT SITE)
(JANUARY, FEBRUARY AND MARCH 2018)
Sl.
No.
Parameter Monitoring
Period
24 Hrs concentration (µg/m3)
Monitoring station
A2 A 3
A 4 A 5 A 6
A 7 A 8
1 PM2.5,
µg/m3
Jan 41.66 51.38 30.38 38.29 32.23 38.90 35.99
Feb 36.60 49.36 37.88 47.57 41.84 39.62 38.11
Mar 53.92 55.52 48.26 54.33 53.84 48.26 58.28
Average 44.06 52.08 38.84 46.73 42.63 42.26 44.12
2 PM10,
µg/m3
Jan 83.57 90.12 66.81 80.62 70.86 73.81 76.67
Feb 75.58 87.98 70.18 85.74 79.50 78.10 73.36
Mar 72.54 84.15 69.10 83.27 68.24 75.44 77.49
Average 77.23 87.41 68.69 83.21 72.86 75.78 75.84
3 SO2, µg/m3 Jan 4.71 4.86 4.32 4.69 4.39 4.37 4.79
Feb 4.80 5.50 4.73 5.34 5.28 4.86 4.42
Mar 4.28 4.77 4.80 4.32 4.35 4.30 4.88
Average 4.59 5.04 4.61 4.78 4.67 4.51 4.69
4 NOx,
µg/m3
Jan 9.67 9.97 9.46 9.62 9.63 9.58 9.82
Feb 9.85 10.63 9.71 10.35 10.22 9.97 10.07
Mar 9.37 9.42 9.85 9.09 9.52 9.42 9.63
Average 9.63 10.00 9.67 9.68 9.79 9.65 9.84
5 CO, mg/m3 Jan 0.10 2.38 0.84 0.15 0.96 0.08 1.13
Feb 0.28 0.46 0.61 0.36 0.52 0.39 0.19
Mar 1.38 2.20 1.00 2.75 1.60 1.88 2.00
Average 0.58 1.68 0.81 1.08 1.02 0.78 1.10
Note:
PM10 & PM2.5 - Particulate matter; SO2 – Sulfur dioxide; NOx– Oxides of nitrogen;
NH3 – Ammonia ; Pb – Lead; O3 – Ozone; CO – Carbon monoxide; ND – not detected,
BDL – Below Detectable Levels
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Table 3.5: Ambient air quality standards – MoEF as per the notification dated 16th
November 2009 for industrial, residential & rural areas
Air quality parameter Concentration
24 hrs Annual
1 Particulate matter (size less than 2.5 µm), (PM2.5),µg/m3 60 40
2 Particulate matter (size less than 10 µm), (PM10), µg/m3 100 60
3 Sulfur-di-oxide (SO2), µg/m3 80 50
4 Nitrogen dioxide (NOx), µg/m3 80 40
5 Ammonia (NH3), µg/m3 400 100
6 Lead (Pb), µg/m3 1 0.5
7 Ozone (O3), µg/m3 180 – 1
hr
100 – 8
hrs
8 Benzene (C6H6), µg/m3 - 5
9 Carbon monoxide (CO), mg/m3 4 – 1 hr 2 – 8 hrs
10 Arsenic (As), ng/m3 - 6
11 Nickel (Ni), ng/m3 - 20
12 Benzo(a) pyrene in particulate phase, ng/m3 - 1
13 Volatile organic compounds (VOCs), µg/m3 - NS
Note:
24 hourly or 08 hourly or 01 hourly monitored values, as applicable, shall be
complied with 98% of the time in a year. 2% of the time, they may exceed the limits
but not on two consecutive days of monitoring.
3.4.2 OBSERVATIONS
The monitored values observed at the project site & other location are stated in below
table.
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TABLE 3.6:- OBSERVATIONS
Sl
No
Parameter 24 Hrs concentration (µg/m3)
Monitoring station
A 1 A 2 A 3
A 4
1 PM2.5,µg/m3 46.13 - 57.93 36.60 – 41.66 49.36 – 55.52 30.38 - 48.26
2 PM10,µg/m3 88.38 - 91.67 72.54 – 83.57 84.15 – 90.12 66.81- 70.18
3 SO2, µg/m3 4.37 – 57.93 4.28 - 4.80 4.77 – 5.50 4.32 – 4.80
4 NOx, µg/m3 9.20 – 10.52 9.37 – 9.85 9.42 – 10.63 9.46 – 9.85
5 CO, mg/m3 0.20 – 2.82 0.10 – 1.38 0.46 -2.38 0.61 – 1.00
Sl
No
Parameter 24 Hrs concentration (µg/m3)
Monitoring station
A5 A6 A7 A8
1 PM2.5,µg/m3 38.29 - 54.33 32.23 – 53.84 38.90 – 48.26 35.99 - 58.28
2 PM10,µg/m3 80.62 - 85.74 68.24 – 79.50 73.81 – 78.10 73.36 - 77.49
3 SO2, µg/m3 4.32 – 5.34 4.35 – 5.28 4.30 – 4.86 4.42 – 4.88
4 NOx, µg/m3 9.09 – 10.35 9.52 – 10.22 9.42 – 9.97 9.63 – 10.07
5 CO, mg/m3 0.15 – 2.75 0.52 – 2.75 0.08 – 1.88 0.19 – 2.00
3.5 NOISE ENVIRONMENT
Background noise levels were measured in 8 locations within the study area. Sound level
meter was used for measuring the noise level.
The Noise level monitoring stations & lowest and highest noise levels are presented in
table 3.3 and the limits as per Environmental Protection Rules, 1986 for industrial,
commercial & residential areas are presented in table 3.11
Table 3.7: Noise level monitoring stations
Sl
No
Code
no
Name of the
station
Distance from
the site(km)
Direction from
site
1 N1 Project site - -
2 N2 Ujjanakoppa 7.0 North
3 N3 Munoli 0.8 East
4 N4 Naviluteertha 3.8 South
5 N5 Jakabal 6.5 North East
6 N6 Shindogi 5.0 South East
7 N7 Shrirangapura 6.0 North West
8 N8 Karlakatti 8.5 South West
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Table 3.8: Noise quality data analysis at all the locations
(DURING JANUARY, FEBRUARY AND MARCH 2018)
Sl No
Code No
Station January February March
Lmin dB
Lmax dB
Leq
dB Lmin dB
Lmax dB
Leq
dB Lmin dB
Lmax dB
Leq
dB
1 N1 Project site 56.7 67.8 62.2 61.4 64.3 62.6 68.8 71.0 70.1
2 N2 Ujjanakoppa 70.3 72.9 72.2 70.9 73.4 72.2 46.0 51.2 48.7
3 N3 Munoli 70.3 72.4 71.9 60.1 69.9 69.0 44.9 51.0 47.3
4 N4 Naviluteertha 67.2 72.0 69.9 73.3 74.1 73.5 40.9 50.1 49.2
5 N5 Jakabal 69.4 72.0 70.4 69.5 70.9 70.2 62.8 65.8 64.5
6 N6 Shindogi 71.8 76.9 73.8 70.5 72.8 71.6 60.9 69.9 64.2
7 N7 Shrirangapur 67.3 69.9 68.9 60.9 68.4 67.1 50.1 58.0 53.5
8 N8 Karlakatti 58.4 62.5 61.8 61.7 64.9 64.3 61.4 71.4 70.9
Table 3.9: Limits as per Environmental Protection Rules, 1986
Limits as per Env. Protection Rules, 1986 in dB(A)Leq
Industrial area Commercial area Residential area Silent zone
Day Night Day Night Day Night Day Night
75 70 65 55 55 45 50 40
3.5.1 OBSERVATIONS
The baseline noise levels have been monitored at different locations as indicated in the
table above. The noise levels in the study area vary between 40.9 – 50.1 dB (A) (Lowest
during March) & 73.3 – 74.1 dB (A) (highest during February). It has been observed that
the maximum noise levels at all the locations are within the limits specified for
industrial/residential areas.
3.5.1 Traffic Study:
Transportation Due to the Proposed Expansion Project
The project is expansion of existing sugar crushing unit. The movement of personnel
from their residence to industry and movement of finished products will not result in
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Environmental Impact Assessment Report 88
any drastic change in either the existing traffic pattern or noise levels the area. The
sugar plant procures sugarcane from farmers around the industry in a radius of 25 Km.
The main mode of transportation of raw materials is by Bullock carts, Tractors and
Trucks. The other vehicles that play on the road leading to the factory in the study area
are cars, buses and two wheelers. Approximately 120 Nos of Bullock carts are used for
the sugar cane transportation. The traffic is significant during the sugarcane crushing
season which will be for a period of 6 – 9 months. The traffic count indicates there will
not be any drastic change in the existing traffic pattern of the area. The movement of
personnel from their residence to industry and movement of finished products will not
result in any increase in noise levels or traffic of the area.
The location of the factory is 10 m away from the major roads i.e. SH 103-Yaragatti –
Munoli Road. Major highway SH- 45 connecting Gokak – Nargund and SH – 83
connecting Munoli – Konnur pass near the industry.
Two
wheelers
Auto Cars Vans Mini
bus
Bus Truc
ks
2
axle
3
axle
Mult
i
axle
Tractors
450 50 300 180 13 204 650 185 44 39 650
3.6 WATER ENVIRONMENT
3.6.1 RECONNAISSANCE SURVEY
The impact has been assessed on randomly selected surface and ground water sources
falling within the impact zone.
3.6.2 SURFACE WATER
The major fresh water source within the study zone is Malaprabha river and the water
requirement for the proposed project will be sourced from the same. The surface water
sampling stations are given in table 3.9. The results of the analysis of surface water
samples are appended as table 3.10
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Table 3.10: Surface Water sampling stations
Sl No
Code no
Name of the Station Distance from site (km)
Direction from the site
1 SWI Malapraba river downstream of the reservoir (Near factory building)
1.4 South West
2 SW2 Renuka sagar reservoir 3.7 South West
3 SW3 Kalloli (upstream) 2.0 South
4 SW4 Jakhabal (downstream) 6.5 North East
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Environmental Impact Assessment Report 90
Table 3.11: Surface water quality results
JANUARY 2018
Sl
No
Characteristics Unit SW1 SW2 SW3 SW4 IS 10500-2012 Specifications for
drinking water
Acceptable Limit Permissible Limit
1 Color, Hazen Unit Hz BDL BDL BDL BDL 5 15
2 Odour Unobjecti
onable
Unobject
ionable
Unobjecti
onable
Unobjection
able
Unobjectionable Unobjectionable
3 Total dissolved
solids
mg/L 130.00 140.00 170.00 140.00 500 2000
4 pH - 8.20 8.00 6.80 8.10 6.5 – 8.5 6.5 – 8.5
5 Total alkalinity as
CaCO3
mg/L 66.50 70.30 76.00 74.10 200 600
6 Total hardness as
CaCO3
mg/L 69.84 71.78 73.72 73.72 200 600
7 Nitrate nitrogen (as
NO3N)
mg/L 0.47 BDL 2.07 BDL 45 No relaxation
8 Chloride as Cl mg/L 15.43 16.87 18.80 16.87 250 1000
9 Sulphates, as SO4 mg/L 14.76 15.76 9.54 9.24 200 400
10 Calcium as Ca mg/L 17.09 17.87 18.64 18.64 75 200
11 Magnesium as Mg mg/L 6.60 6.60 6.60 6.60 30 100
12 Iron as Fe mg/L 0.88 0.55 0.27 0.33 1.0 No relaxation
13 Turbidity NTU 6.50 6.60 BDL 1.30 1 5
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14 Free residual
chlorine
mg/L BDL BDL BDL BDL 0.2 1.0
15 Boron, as B mg/L BDL BDL BDL BDL 0.5 1.0
16 Copper, as Cu mg/L 0.10 0.081 0.068 0.070 0.05 1.5
17 Manganese, as Mn mg/L BDL BDL BDL BDL 0.1 0.3
18 Total solids mg/L 210 110.00 120.00 95.00 - *
19 Anionic detergents mg/L BDL BDL BDL BDL 0.2 1.0
Mineral oil mg/L Negative Negative Negative Negative 0.5 No relaxation
Alumina mg/L BDL BDL BDL BDL 0.03 0.2
Aldrin ppb BDL BDL BDL BDL 0.03 -
23 Total coliforms MPN/
100 ml
21 14 8 14 ND
FEBRUARY 2018
Sl
No
Characteristics Unit SW1 SW2 SW3 SW4 IS 10500-2012 Specifications for
drinking water
Acceptable Limit Permissible Limit
1 Color, Hazen Unit Hz BDL BDL BDL BDL 5 15
2 Odour Unobjecti
onable
Unobject
ionable
Unobjecti
onable
Unobjection
able
Unobjectionable Unobjectionable
3 Total dissolved
solids
mg/L 120.00 130.00 160.00 130.00 500 2000
4 pH - 8.00 7.95 6.90 7.90 6.5 – 8.5 6.5 – 8.5
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5 Total alkalinity as
CaCO3
mg/L 64.60 68.40 74.10 70.30 200 600
6 Total hardness as
CaCO3
mg/L 67.90 69.84 71.78 71.78 200 600
7 Nitrate nitrogen (as
NO3N)
mg/L 0.32 BDL 1.94 BDL 45 No relaxation
8 Chloride as Cl mg/L 15.43 16.39 17.36 16.39 250 1000
9 Sulphates, as SO4 mg/L 14.26 14.76 9.24 9.14 200 400
10 Calcium as Ca mg/L 16.31 17.09 17.87 17.87 75 200
11 Magnesium as Mg mg/L 6.60 6.60 6.60 6.60 30 100
12 Iron as Fe mg/L 0.90 0.49 0.24 0.31 1.0 No relaxation
13 Turbidity NTU 6.60 6.40 BDL BDL 1 5
14 Free residual
chlorine
mg/L BDL BDL BDL BDL 0.2 1.0
15 Boron, as B mg/L BDL BDL BDL BDL 0.5 1.0
16 Copper, as Cu mg/L 0.090 0.081 0.071 0.068 0.05 1.5
17 Manganese, as Mn mg/L BDL BDL BDL BDL 0.1 0.3
18 Total solids mg/L 245 92.00 140.00 115.00 - *
19 Anionic detergents mg/L BDL BDL BDL BDL 0.2 1.0
20 Mineral oil mg/L Negative Negative Negative Negative 0.5 No relaxation
21 Alumina mg/L BDL BDL BDL BDL 0.03 0.2
22 Aldrin ppb BDL BDL BDL BDL 0.03 -
23 Total coliforms MPN/
100 ml
21 21 14 14 ND
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Sl
No
Characteristics Unit SW1 SW2 SW3 SW4 IS 10500-2012 Specifications for
drinking water
Acceptable Limit Permissible Limit
1 Color, Hazen Unit Hz BDL BDL BDL BDL 5 15
2 Odour Unobjecti
onable
Unobject
ionable
Unobjecti
onable
Unobjection
able
Unobjectionable Unobjectionable
3 Total dissolved
solids
mg/L 150.00 140.00 180.00 150.00 500 2000
4 pH - 7.90 8.50 6.77 8.22 6.5 – 8.5 6.5 – 8.5
5 Total alkalinity as
CaCO3
mg/L 73.50 69.30 79.80 75.60 200 600
6 Total hardness as
CaCO3
mg/L 75.24 71.28 79.20 77.22 200 600
7 Nitrate nitrogen (as
NO3N)
mg/L BDL 0.57 2.37 BDL 45 No relaxation
8 Chloride as Cl mg/L 17.84 16.79 19.94 17.84 250 1000
9 Sulphates, as SO4 mg/L 15.85 16.07 10.92 9.53 200 400
10 Calcium as Ca mg/L 18.23 17.44 19.03 19.03 75 200
11 Magnesium as Mg mg/L 7.22 6.74 7.70 7.22 30 100
12 Iron as Fe mg/L 0.66 0.99 0.26 0.35 1.0 No relaxation
13 Turbidity NTU 6.80 6.70 BDL 1.30 1 5
14 Free residual mg/L BDL BDL BDL BDL 0.2 1.0
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chlorine
15 Boron, as B mg/L BDL BDL BDL BDL 0.5 1.0
16 Copper, as Cu mg/L 0.098 0.072 0.076 0.078 0.05 1.5
17 Manganese, as Mn mg/L BDL BDL BDL BDL 0.1 0.3
18 Total solids mg/L 230.00 100.00 130.00 104.00 - *
19 Anionic detergents mg/L BDL BDL BDL BDL 0.2 1.0
Mineral oil mg/L Negative Negative Negative Negative 0.5 No relaxation
Alumina mg/L BDL BDL BDL BDL 0.03 0.2
Aldrin ppb BDL BDL BDL BDL 0.03 -
23 Total coliforms MPN/
100 ml
21 21 14 14 ND
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Table 3.12 Surface water quality standards
Designated-Best-Use Designated-Best-Use Criteria
Drinking Water Source
without conventional
treatment but after
disinfection
A Total Coliforms Organism MPN/100ml
shall be 50 or less.
pH between 6.5 and 8.5
Dissolved Oxygen 6mg/l or more
Biochemical Oxygen Demand 5 days
20°C 2mg/l or less
Total Coliforms Organism MPN/100ml
shall be 500 or less pH between 6.5
and 8.5 Dissolved Oxygen 5mg/l or
more
Biochemical Oxygen Demand 5 days
20°C 3mg/l or less
Total Coliforms Organism MPN/100ml
shall be 5000 or less pH between 6 to
9 Dissolved Oxygen 4mg/l or more
Biochemical Oxygen Demand 5 days
20°C 3mg/l or less
pH between 6.5 to 8.5 Dissolved
Oxygen 4mg/l or more
Free Ammonia (as N) 1.2 mg/l or less
pH between 6.0 to 8.5
Electrical Conductivity at 25°C micro
mhos/cm Max.2250
Sodium absorption Ratio Max. 26
Sodium absorption Ratio Max. 26
Outdoor bathing
(Organized
B
Drinking water source
after conventional
treatment and
disinfection
C
Propagation of Wild life
and Fisheries
D
Irrigation, Industrial
Cooling, Controlled Waste
disposal
E
Below-E Not Meeting A, B, C, D & E Criteria
3.6.3 Observations of Surface water quality
The results for the parameters analysed for surface water samples are presented and
are compared with IS:10500-2012 Standards
There are four surface water bodies within the study area
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The pH of the surface water samples collected ranges in between 6.77 – 8.50. The iron
concentrations varied between 0.24 mg/l and 0.99 mg/l. Manganese values are in the
not detectable range at all the sampling locations.
Total solids in the water samples range between 92 to 245 mg/l
3.6.4 GROUND WATER
In order to assess the existing water quality, the ground water samples were collected
from 8 different locations within the study area and analyzed as per the procedure
specified in standard methods for examination of water and wastewater published by
American Public Health Association and Bureau of Indian Standards (APHA/BIS). Name
of the locations, orientation with respect to the project site has been depicted in the
below table:
Sl No
Station No
Name of the station Distance from site (km)
Direction from the site
1 GW 1 Project Site - -
2 GW 2 Ujjanakoppa 7.0 North
3 GW 3 Manoli 0.8 East
4 GW 4 Naviluteertha Colony 3.8 South
5 GW 5 Jakabal 6.5 North East 6 GW 6 Shindogi 5.0 South East
7 GW 7 Shrirangapura 6.0 North West
8 GW 8 Karlakatti 8.5 South West
The results of the analysis of Ground water samples collected from the project site and
others locations is appended in the following table 3.13
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Table 3.13: Ground water quality
JANUARY 2018
Sl No
Tests Unit Results Acceptable Limit as per
IS:10500-2012
Maximum Permissible Limits in the Absence of Alternate
Source As Per IS:10500-2012
GW1
GW2
GW3
GW4
GW5
GW6
GW7
GW8
1 Colour, Max Hazen Units
BDL BDL BDL BDL BDL BDL BDL BDL 5 15
2 Odour* Agreeable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Un objectionable
Un objectionable
3 Total dissolved solids (TDS), Max
mg/L 230.0 600.00 440.00 460.00 430.0 540.00 550.00 860.00 500 2000
4 pH @ 250C - 6.52 7.00 6.50 7.25 7.00 6.50 7.60 7.20 6.5 - 8.5 6.5 – 8.5
5 Total Alkalinity as CaCO3, Max
mg/L 84.00 346.50 207.90 199.50 243.6 243.60 315.00 375.90 200 600
6 Total hardness (TH) as CaCO3,
mg/L 126.7 374.22 215.82 194.04 201.9 322.74 312.00 465.30 200 600
7 Nitrate Nitrogen (as NO3N), Max
mg/L 0.57 52.68 34.87 13.17 18.45 3.82 33.09 67.31 45 No relaxation
8 Chloride (as Cl),
mg/L 27.28 82.90 91.82 51.42 49.84 60.34 94.44 177.34 250 1000
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9 Sulphate (as SO4),Max
mg/L 35.34 37.27 26.78 25.70 22.49 67.47 24.10 33.20 200 400
10 Calcium (as Ca), Max
mg/L 23.78 80.07 31.71 41.23 43.60 45.98 53.91 103.20 75 200
11 Magnesium (as Mg), Max
mg/L 16.36 42.34 33.20 22.13 22.61 50.52 43.30 50.52 30 100
12 Fluoride (as F), Max
mg/L 0.27 0.71 0.35 0.81 0.78 0.52 00.46 0.84 1.0 1.5
13 Iron as Fe, Max mg/L 2.75 0.10 0.20 0.20 0.22 0.35 0.46 0.11 1.0 No relaxation 14 Turbidity, Max mg/L 22.50 BDL BDL BDL BDL 3.80 8.20 1.00 1 5
15 Potassium mg/L 4.80 3.82 10.00 2.20 2.10 5.20 2.44 1.10 - -
16 Sodium mg/L 15.20 74.53 43.24 62.00 62.00 31.99 58.00 80.50 - -
FEBRUARY 2018
Sl No
Tests Unit Results Acceptable Limit as per
IS:10500-2012
Maximum Permissible Limits in the Absence of Alternate
Source As Per IS:10500-2012
GW1
GW2
GW3
GW4
GW5
GW6
GW7
GW8
1 Colour, Max Hazen Units
BDL BDL BDL BDL BDL BDL BDL BDL 5 15
2 Odour* Agreeable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
3 Total mg/L 240.0 610.00 470.00 470.00 440.00 550.0 560.00 870.0 500 2000
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dissolved solids (TDS), Max
4 pH @ 250C - 6.55 7.10 6.50 7.20 7.10 6.50 7.55 7.50 6.5 - 8.5 6.5 – 8.5
5 Total Alkalinity as CaCO3, Max
mg/L 86.10 350.70 203.70 205.80 247.80 247.8 319.20 378.0 200 600
6 Total hardness (TH) as CaCO3, max
mg/L 128.7 376.20 217.80 198.00 207.90 326.7 316.80 471.2 200 600
7 Nitrate Nitrogen (as NO3N), Max
mg/L 0.73 54.30 34.71 13.58 18.29 4.23 35.44 68.93 45 No relaxation
8 Chloride (as Cl), Max
mg/L 28.33 83.95 92.34 52.47 51.42 61.91 99.69 178.3 250 1000
9 Sulphate (as SO4),Max
mg/L 35.77 37.49 28.38 26.78 21.96 69.40 25.06 33.74 200 400
10 Calcium (as Ca), Max
mg/L 23.78 79.28 31.71 43.60 48.98 47.57 55.50 102.27
75 200
11 Magnesium (as Mg), Max
mg/L 16.84 43.30 33.68 21.65 22.61 50.52 43.30 52.44 30 100
12 Fluoride (as F), Max
mg/L 0.28 0.75 0.33 0.88 0.87 0.49 0.45 0.87 1.0 1.5
13 Iron as Fe, Max
mg/L 2.86 0.11 0.22 0.13 0.20 0.54 0.49 0.16 1.0 No relaxation
14 Turbidity, Max mg/L 21.50 BDL BDL BDL BDL 4.00 8.50 2.00 1 5
15 Potassium mg/L 4.00 2.80 9.50 2.10 2.00 5.00 2.10 1.00 - -
16 Sodium mg/L 13.20 72.00 41.24 60.10 60.20 29.99 58.20 78.50 - -
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Tests Unit Results Acceptable Limit as per
IS:10500-2012
Maximum Permissible Limits in the Absence of Alternate
Source As Per IS:10500-2012
GW1
GW2
GW3
GW4
GW5
GW6
GW7
GW8
1 Colour, Max Hazen Units
BDL BDL BDL BDL BDL BDL BDL BDL 5 15
2 Odour* Agreeable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
Unobjectionable
3 Total dissolved solids (TDS), Max
mg/L 250.0 620.00 480.00 480.00 470.00 570.0 580.00 870.0 500 2000
4 pH @ 250C - 6.60 7.26 6.57 7.43 7.44 6.70 7.60 7.50 6.5 - 8.5 6.5 – 8.5
5 Total Alkalinity as CaCO3, Max
mg/L 90.30 354.90 207.90 210.00 256.20 252.0 323.40 378.0 200 600
6 Total hardness (TH) as CaCO3, max
mg/L 132.66 380.16 221.76 201.96 215.82 332.6 318.78 471.2 200 600
7 Nitrate Nitrogen (as NO3N), Max
mg/L 0.89 56.58 36.01 13.82 19.92 4.63 35.44 68.93 45 No relaxation
8 Chloride (as Cl), Max
mg/L 29.38 84.99 93.39 53.52 52.47 62.96 100.73 178.3 250 1000
9 Sulphate (as mg/L 35.99 38.02 29.24 28.38 24.85 69.19 25.28 33.74 200 400
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SO4),Max
10 Calcium (as Ca), Max
mg/L 24.58 80.86 33.30 45.19 46.77 48.36 57.08 102.27
75 200
11 Magnesium (as Mg), Max
mg/L 17.32 43.30 33.68 21.65 24.06 51.48 42.82 52.44 30 100
12 Fluoride (as F), Max
mg/L 2.92 0.10 0.26 0.15 0.24 0.60 0.53 0.87 1.0 1.5
13 Iron as Fe, Max mg/L 0.30 0.78 0.35 0.88 0.85 0.47 0.47 0.16 1.0 No relaxation
14 Turbidity, Max mg/L 23.20 BDL BDL BDL BDL 4.30 8.70 2.00 1 5
15 Potassium mg/L 5.22 3.95 10.03 2.46 2.55 5.49 2.99 1.00 - -
16 Sodium mg/L 17.03 76.54 44.32 64.33 64.52 33.99 60.92 78.50 - -
3.6.5 OBSERVATIONS
The results for the parameters analysed for ground water samples are presented and are compared with standards for drinking
water as per IS:10500-2012 "Specifications for Drinking Water"
Total 8 water samples were collected from different sources around the project site within the periphery of 7 km.
The pH of the water samples collected ranges in between 6.50 to 7.55.
Chlorides concentrations ranged from 27.28 mg/l to 178.3 mg/l indicating that the concentrations are well within the
permissible limits.
Sulphates concentrations ranged from 21.96 mg/l to 69.19 mg/l indicating that the concentrations are within the permissible
limits.
Total hardness expressed as CaCO3 ranges from 126.7 mg/l to 471.2 mg/l, which shows that total hardness is within the
permissible, limits at all the locations.
The concentration of Nitrate fluctuates between 0.57 mg/l and 68.93 mg/l indicating that the values are within the permissible
limits
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3.7 SOIL AND GEOLOGY
Soil characteristics, erosion aspects, soil fertility etc., have direct bearing on the
environment. Knowledge of soil parameters is essential for the planning and
implementation of green belt. Hence it becomes important to study the soil characteristics.
Baseline data for land environment was collected at 8 locations in order to assess the soil
quality of the study area. The list of locations and the orientation with reference to the
project site are listed in table 3.16. Soil sampling locations are shown in the map appended
as fig 3.9. Soil samples were analyzed for physical and chemical parameters the results of
which are given in table 3.17
Table 3.14: Soil sampling stations
Sl No Station No
Name of the station Distance from site (km)
Direction from the site
1 S1 Project Site - - 2 S2 Ujjanakoppa 7.0 North
3 S3 Manoli 0.8 East
4 S4 Naviluteertha Colony 3.8 South
5 S5 Jakabal 6.5 North East 6 S6 Shindogi 5.0 South East
7 S7 Shrirangapura 6.0 North West
8 S8 Karlakatti 8.5 South West
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Table 3.15: Physico-chemical characteristics of soil
JANUARY 2018
Sl No
Characteristics Unit Results S1 S2 S3 S4 S5 S6
S7
S8
1 Electrical
Conductivity (1:2) dS/m 0.409 0.376 0.264 0.238 0.204 0.338 0.452 0.314
2 pH (1:2) - 6.20 7.02 7.09 6.78 6.12 6.98 7.54 7.06
3 Available Potassium Kg/ha 121.36 102.35 113.46 102.39 135.73 138.62 160.48 151.60
4 Copper mg/kg 9.16 1.156 8.84 1.565 2.368 3.06 1.49 1.166
5 Iron mg/kg 16.59 4.86 18.52 8.08 3.98 8.58 6.30 3.82 6 Zinc mg/kg 5.98 2.32 41.06 0.584 3.96 14.32 0.604 1.26
7 Nickel* mg/kg 0.846 0.962 1.478 0.498 1.974 0.138 0.648 0.514
8 Available Sodium* Kg/ha 4.04 4.10 5.52 6.11 7.12 8.11 6.93 6.81 9 Lead* mg/kg 0.986 0.76 1.721 0.664 0.636 0.798 0.74 0.364
10 Cadmium* mg/kg 0.102 0.074 0.108 0.057 0.088 0.118 0.109 0.092
11 Chloride* mg/kg 10.216 7.768 5.115 5.108 7.764 12.980 9.890 7.789
12 Total Chromium* mg/kg BDL BDL BDL BDL BDL BDL BDL BDL 13 Water Holding
Capacity* % 31.382 26.896 27.03 27.72 30.21 22.688 28.907 24.04
14 Bulk Density* Gm/cm3
1.124 1.294 1.387 1.198 1.420 1.194 1.055 1.294
15 Sand* % 48 50 48 50 48 51 49 50
16 Silt* % 35 28 31 27 30 30 29 30
17 Clay % 17 22 21 23 22 19 22 20
BDL – Below Detective Limit, BDL (Total Chromium – 0.03 mg/kg)
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FEBRUARY 2018
Sl No
Characteristics Unit Results
S1
S2
S3
S4
S5
S6
S7
S8
1 Electrical Conductivity (1:2)
dS/m 0.386 0.352 0.254 0.238 0.198 0.326 0.398 0.294
2 pH (1:2) - 6.46 6.99 6.86 6.78 6.43 6.64 7.22 6.92
3 Available Potassium Kg/ha 118.6 99.66 109.58 102.39 129.5 128.14 154.59 143.61
4 Copper mg/kg 8.96 1.124 8.26 1.565 2.256 3.12 1.52 1.056 5 Iron mg/kg 15.89 4.28 18.23 8.08 3.42 8.32 5.90 4.02
6 Zinc mg/kg 5.42 2.13 40.56 0.584 3.38 13.98 0.594 1.10
7 Nickel* mg/kg 0.802 1.003 1.439 0.498 1.942 0.122 0.626 0.498 8 Available Sodium* Kg/ha 4.04 3.84 4.96 6.11 7.43 8.11 6.93 6.81
9 Lead* mg/kg 0.921 0.82 1.684 0.664 0.612 0.816 0.626 0.324
10 Cadmium* mg/kg 0.098 0.086 0.116 0.0574 0.096 0.126 0.096 0.106
11 Chloride* mg/kg 9.890 7.123 4.984 5.108 7.764 12.641 9.746 7.012
12 Total Chromium* mg/kg BDL BDL BDL BDL BDL BDL BDL BDL
13 Water Holding Capacity*
% 29.39 27.67 26.26 27.725 29.12 26.342 27.395 23.776
14 Bulk Density* Gm/cm3 1.104 1.274 1.286 1.198 1.420 1.205 1.059 1.296
15 Sand* % 49 48 45 50 49 50 48 49
16 Silt* % 32 30 32 27 29 30 30 29 17 Clay % 19 22 23 23 22 20 22 22
BDL – Below Detective Limit, BDL (Total Chromium – 0.03 mg/kg)
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MARCH 2018
Sl No
Characteristics Unit Results
S1 S2
S3
S4
S5
S6
S7
S8
1 Electrical Conductivity (1:2)
dS/m 0.416 0.389 0.278 0.249 0.196 0.342 0.463 0.386
2 pH (1:2) - 6.90 7.12 6.96 6.87 5.86 6.46 7.68 6.89
3 Available Potassium Kg/ha 123.2 108.6 115.17 104.59 138.6 140.92 164.47 154.59
4 Copper mg/kg 9.52 1.198 8.92 1.594 2.40 3.14 1.508 1.174 5 Iron mg/kg 17.96 4.78 18.76 9.06 4.14 9.66 6.60 3.92
6 Zinc mg/kg 6.24 2.26 41.36 0.592 3.94 14.44 0.618 1.13
7 Nickel* mg/kg 0.764 0.976 1.484 0.504 1.986 1.40 0.654 0.522 8 Available Sodium* Kg/ha 3.47 4.54 5.52 6.11 7.12 8.11 6.93 6.81
9 Lead* mg/kg 1.618 0.89 1.736 0.672 0.656 0.866 0.77 0.376
10 Cadmium* mg/kg 0.096 0.084 0.112 0.058 0.092 0.122 0.108 0.088
11 Chloride* mg/kg 10.49 7.85 5.25 5.20 7.85 13.10 10.50 7.85
12 Total Chromium* mg/kg BDL BDL BDL BDL BDL BDL BDL BDL
13 Water Holding Capacity*
% 32.53 27.27 29.38 28.37 29.97 23.16 29.62 25.71
14 Bulk Density* Gm/cm3 1.063 1.307 1.407 1.216 1.410 1.214 1.067 1.324
15 Sand* % 49.00 51 49 50.00 53.00 51.00 49.00 50
16 Silt* % 36.00 32 30 27.00 29.00 30.00 29.00 29 17 Clay % 15.00 17 21 23.00 18.00 19.00 22.00 21
BDL – Below Detective Limit, BDL (Total Chromium – 0.03 mg/kg)
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3.7.1 OBSERVATIONS
It has been observed that the pH of the soil quality ranged from 5.86 to 7.84 indicating
that the soil is usually moderately acidic to moderately alkaline in nature.
The Iron values ranged between 3.42 mg/kg to 18.23 mg/kg.
The Potassium values range between 99.66 kg/ha and 160.48 kg/ha. The potassium
levels recorded indicates that the Potassium concentration is ‘very less to less’.
The pH value of the soil is an important property; plants cannot grow in low and high
pH. Most of the essential nutrients like N, P, K, Ca, and Mg are available for plant at the
neutral pH except for Fe, Mn, and Al, which are available at low pH range.
Fig 3.7: Location of sampling stations
(Air, Noise, Soil and Ground Water Stations)
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Surface water sampling locations
Source: Google Earth
3.8 HYDROLOGY AND HYDROGEOLOGY
The district of Belagavi is located east of the Western Ghats and is situated in the north
western part of Karnataka state.Geographically The district lies between 15°00’ and 17°00’
north latitudes and between 74°00 and 75°30’ east longitudes. It covers an area of 13,444
Sq. Km. The entire district falls in the Krishna river basin. The river Krishna, along with its
tributaries Ghataprabha and Malaprabha are perennial and effluent in nature and flow in
easterly direction.
The district is underlain by gneisses, schist, limestone, sandstone, basalts, alluvium etc. of
Archaean to Recent age. Deccan basalts cover an area of 7,650 Sq.Kms. in the northern part
of the district and have a maximum thickness of around 256 m, which gradually thins out in
the southern direction.
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Ground water occurs both in weathered and fractured zones. Ground water occurs in all
weathered formations of the district under phreatic conditions and in fractured and jointed
formations under semi-confined conditions. The average thickness of these aquifers ranges
from 5 to 15m. In general, 60% area of the district is having the weathered thickness in the
range of 5 to 10 m. About 25% of the district area has weathered thickness in the range of
10 to 15m and 15% in the range of 15 to 20m.
3.9 ECOLOGY
Natural flora and fauna are important features of the environment. They are organized into
natural communities with mutual dependencies among their members and show various
responses and sensitivities to physical innocence.
Ecological survey of the study area was carried out by actual field visits of the study area to
observe the various species of flora and fauna. Personal enquiries/discussion with local
people and forest department officials was also conducted to get a fair idea of the existing
ecological status.
The flora and fauna existing in the study area is presented below.
3.9.1 ANTICIPATED IMPACTS
The impact can be considered insignificant as the region consists of only skeletal Vegetation
like grasses & thorny shrubs with no rare & endangered species. As the Project activity will
be limited only to the core zone and mitigative measures will be implemented to contain air
and noise pollution. There shall be no damage to the flora of the buffer zone.
The area is not a significant faunal habitat. No deforestation will take place in the Buffer
zone. Thus, the impact on fauna of the buffer zone will be minimal.
3.9.2 FLORA
There are no National Parks or Wildlife Sanctuaries in the 10 Km radius from the proposed
plant site. The Government forests are found in scattered patches mainly observed in
Central part of the District on hill slopes and depressions there are no reports of
endangered species or notified protected species. Wildlife species, common almost all over
rural India such are hare, jackals, monkeys, pigs, several species of birds and reptiles are
present. Land use pattern within the study zone is industrial oriented with rural village
settings. Floral composition in the study area is presented in the table 3.17 below.
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Table 3.16: Flora in the study area
Sl No Local Name Botanical Name Family
Trees
1 Ala Ficus bengalensis Moraceae
2 Ankole Alangiumlamarkii Cornaceae
3 Ari, Bauhinia recemosa Fabaceae
4 Anjan Hardwickia binata Fabaceae
5 Akash mallige Millingtonia hortensis Bignoniaceae
6 Bilpatri Aegle marmelos Rutaceae
7 Bela Feronia elephantum Rutaceae
8 Bilkumbi Albizia odoratissima Fabaceae
9 Banni Acacia suma Fabaceae
10 Bilijali Acacia leucophloea Fabaceae
11 Babul Acacia arabica Fabaceae
12 Hunse Tamarindus indica Fabaceae
13 Sandalwood Santalum album Santalaceae
14 Dindal Gardenia lucida Rubiaceae
15 Dandoshi Dalbergia paniculata Fabaceae
16 Gensinz Stereosperumum
xylocarpum
Bignoniaceae
17 Gorvi Ixora parviflora Rubiaceae
18 Ghatbor Zizyphus xylopyra Rhamnaceae
19 Godambekai Anacardium occidentale Anacardiaceae
20 Hirejali Acacia latronum Fabaceae
21 Hebbevu Ailanthus excelsa Simaroubaceae
22 Hanmanki· Flacourtia ramontchi Salicaceae
23 Honge Pongamia glabra Fabaceae
24 Kasod Cassia siamia Fabaceae
25 Khair Acacia catechu Fabaceae
26 Kalagonda Diospyros montana Ebenaceae
27 Kari Randia dumetorum Rubiaceae
28 Karihannu Canthium parviflorum Rubiaceae
29 Bevu Azadirachta indica Meliaceae
30 Karijaali Acacia nilotica Fabaceae
31 Gajaga Caesalptine bonduce Caesalpiniaceae
Shrub
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1 Bandaraki Dodonaea viscosa Fabaceae
2 Chaduranga Lantana camara Ebenaceae
3 Honnambri Cassia auriculata Rubiaceae
4 Henkal Gymonsporia montana Rubiaceae
5 Kalli Euphorbia tirukalli Euphorbiaceae
6 Lakki Vitex nigundo Lamiaceae
7 Menbandti Mundulia suberosa Fabaceae
8 Pargi Toddalia auriculata Rutaceae
9 Torani Zizyphus rugosa Rhamnaceae
10 Jaali Prosopis juliflora Fabaceae
Herbs and Climbers
1 Nachikemullu Mimosa pudica Fabaceae
2 Anantmullu Hemidesmus indicus Apocynaceae
3 Gulaganji Abrus precatorius Fabaceae
4 Mallige Jasminum sp. Oleaceae
5 Bondwell Litsea elliptica Lauraceae
6 Avarike Casssia tora Caesulpinaceae
Source: Literature Survey and sample verificaiton
3.9.3 FAUNA
Fauna observed in the region include domestic animals, reptiles and birds. No rare,
threatened, vulnerable and endangered animal species are found in the study area. The
composition of fauna in the study area is presented in the table 3.18 below.
Table 3.17: Fauna in the study area
Sl No Local Name Scientific Name WL(P)Act, Schedule
1 Barbet Megalaimidae Schedule- IV
2 Black drongo Dicrurus macrocercus Schedule- IV
3 Catte egret Bubulcus ibis Schedule- IV
4 Baya weaver bird Ploceus pillippinus Schedule- IV
5 King fisher Alcedines Schedule- IV
6 Sun bird Nectariniidae Schedule- IV
7 Yellow throated sparrow Petronia xanthocollis Schedule- IV
8 Cuckoo Cuculus laborous Schedule- IV
9 Red wattled lapwing Vanellus indicus Schedule- IV
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10 Parakeet Psittalula krameria Schedule- IV
11 Bulbul Hypsisptes amourotis Schedule- IV
12 House sparrow Passer domesticus Schedule- IV
13 Common Myna Arcidotheres tristis Schedule- IV
14 Pigeon Columbia livia Schedule- IV
15 Koel Eudynamys
scolopacea
Schedule- IV
16 Tailor Bird Orthomus sutorius Schedule- IV
Source: Literature Survey and sample verification
3.10 SOCIO-ECONOMIC ENVIRONMENT
The baseline data referring to the socio-economic environment is collected from secondary
sources such as census records, statistical hand book and relevant official records with the
government agencies and primary sources such as the socio-economic surveys conducted
by different Govt. & Non Govt. Agencies.
The growth of industrial sectors and infrastructure development in and around the
agricultural area i.e. villages and semi-urban settings and towns is bound to create certain
socio-economic impacts on the local populace. The impacts may be either positive or
negative depending on the nature of development. To assess such impact, it is necessary to
know the existing socio-economic order of the study area, which will be helpful in improving
the overall quality of life.
3.10.1 DEMOGRAPHIC STRUCTURE
Most of the population is found in the villages depend on the ground water and canal water
source for their domestic usage. There is no organized water supply or drainage system in
the localities. Agriculture and related activity is the main source of income for their lively
hood. Educational facilities are limited to primary and high school levels and there are no
facilities for higher education.
An official Census 2011 detail of Belagavi, it had population of 4,779,661 of which male and
female were 2,423,063 and 2,356,598 respectively. The distributions of population in the
study area as per the census record of the 2011 are presented as table 3.18 below.
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TABLE 3.18: DISTRIBUTION OF POPULATION
Description 2011
Actual Population 4,779,661
Male 2,423,063
Female 2,356,598
Population Growth 13.41%
Average Literacy 73.48
Male Literacy 82.20
Female Literacy 64.58
Total Child Population (0-6 Age) 626,269
Male Population (0-6 Age) 323,761
Female Population (0-6 Age) 302,508
Literates 3,052,032
Male Literates 1,725,548
Female Literates 1,326,484
Child Proportion (0-6 Age) 13.10%
Boys Proportion (0-6 Age) 13.36%
Girls Proportion (0-6 Age) 12.84%
Source: District census handbook
3.10.2 LITERACY LEVELS
The literacy level in the study area is as appended in table 3.19 below
Table 3.19: Distribution of literates and literacy levels in the study area for the year 2011
Particulars Belagavi
Total population 4,779,661
Total literate 3,052,032
Literate male 1,725,548
% of Male literate 82.2
Literate female 1,326,484
41.11
% of Female literate 64.58
Source: District census hand book
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3.10.3 SOCIAL INFRASTRUCTURE AVAILABLE
Infrastructure is the basic physical and organizational structures needed for the operation
of a society or enterprise or the services and facilities necessary for an economy to function.
The term typically refers to the technical structures that support a society, such as roads,
water supply, sewers, electrical grids, telecommunications and so forth and can be defined
as "the physical components of interrelated systems providing commodities and services
essential to enable, sustain or enhance societal living conditions.
Viewed functionally, infrastructure facilitates the production of goods and services, and also
the distribution of finished products to markets, as well as basic social services such as
schools and hospitals. For example, roads enable the transport of raw materials to a factory.
The list of hospitals & other infrastructural facilities available in the vicinity of the proposed
industry is tabulated in below table 3.20.
Table 3.20: List of infrastructural facilities in the surroundings
Sl
No
Hospital Distance from the
Industry
Direction w.r.t.
the industry
1 Dr Naik Hospital, Munoli 1.8 Km East
2 Navadagi hospital, Saundatti 8.7 Km South
3 Government Hospital, Bailahongal 18.2 Km South West
4 Shivaveerakshi Eye Hospital, Bailahongal 17 Km South West
5 Gadag Hospital, Bailahongal 20 Km South West
Note: All distances mentioned are aerial.
3.11 CONNECTIVITY
Connectivity to the project site is detailed in the following table 3.21. Google map showing
the same is appended subsequently in fig 3.9.
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Table 3.21: Connectivity from the project site
Sl
No
Road Distance from
the project site
(km)
Direction w.r.t.
project site
1 SH-45 0.3 North
2 SH-83 2.5 North West
3 Belagavi railway Station 63 West
4 Munoli Bus Stand 1.1 West
Note: All distances mentioned are aerial.
Fig- 3.8 Google Map Showing Connectivity to Project Site
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Figure 3.9: Google map showing surrounding water bodies
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Fig 3.10: GOOGLE MAP COVERING 1 KM AERIAL DISTANCE FROM THE PROJECT SITE
1 Km
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Fig 3.11: GOOGLE MAP COVERING 5 KM AERIAL DISTANCE FROM THE PROJECT SITE
5 Km
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Fig 3.12: GOOGLE MAP COVERING 10 KM AERIAL DISTANCE FROM THE PROJECT SITE
3.12 BASE MAPS OF ALL ENVIRONMENTAL COMPONENTS
The major environmental components in the surroundings along with the distance &
direction from the project site are tabulated in below table 3.22. The topo map of 10 km
radius is appended as Annexure - 5
Table 3.22: Existing land-use pattern
Sl
No
Particulars Details Distance From the
Project site (km)
Direction w.r.t
Project site
1 Agriculture Scattered - -
2 National park,
Forest
None - -
3 Water bodies Malapraba river 1.4 South West
10 km Km
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downstream of the
reservoir (Near factory
building)
Renuka sagar reservoirs 3.7 South West
4 Archaeological
Monuments
- - -
Note: All distances mentioned are aerial.
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CHAPTER 4
ANTICIPATED ENVIRONMENTAL IMPACTS &
MITIGATION MEASURES
4.0 DETAILS OF INVESTIGATED ENVIRONMENTAL IMPACTS DUE TO PROJECT LOCATION,
POSSIBLE ACCIDENTS, PROJECT DESIGN, PROJECT CONSTRUCTION, REGULAR
OPERATIONS, FINAL DECOMMISSIONING OR REHABILITATION OF COMPLETED PROJECT
4.1 ENVIRONMENTAL IMPACTS DUE TO PROJECT LOCATION, POSSIBLE ACCIDENTS,
PROJECT DESIGN
4.1.1 INTRODUCTION
Prediction of impacts is the most important component in the Environmental Impact
Assessment studies. Predictions are superimposed over the baseline (pre-project) status of
environmental quality to derive the ultimate (post-project) scenario of environmental
conditions. The prediction of impacts helps to minimize the adverse impacts on
environmental quality during pre and post project execution.
4.1.2 IMPACT DUE TO PROJECT LOCATION
Major environmental impacts due to project location are not anticipated because;
The proposed expansion of sugar plant is in the existing industry.
The project location is alienated for industrial use. The integrated sugar distillery and co
gen plant is located amidst of the agricultural lands. The location of the project site has
already been approved and Environmental clearance is obtained for the existing activity.
The location of the project is in the sugar cane growing belt of Karnataka. Therefore, the
availability of the raw material is assured. The farmers are benefitted by the industry as it
is supporting for systematic and scientific method of sugar cultivation.
With this expansion there is positive impact in terms of resource utilization to its full
potential.
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All environmental safeguards are in place and they are meeting the regulatory
requirement.
4.1.3 PROJECT DESIGN
The industry is designed with utmost consideration to the environment. The project is
designed to achieve maximum sugar recovery, minimizing the loss, optimal utilization of the
natural resources. A total area of 104.18 Acres i.e. 34.01 % of the total plot area is reserved
exclusively for green-belt/landscape development.
4.2 MEASURES FOR MINIMIZING & / OR OFFSETTING ADVERSE IMPACTS IDENTIFIED
The Environmental Impact Statement enumerates likely impacts due to the proposed
project on the six basic environmental parameters, which are listed below.
1. Air Environment
2. Noise Environment
3. Water Environment
4. Land Environment
5. Biological Environment
6. Socio-economic Environment
The impacts on the above parameters have been identified, analyzed and classified as
adverse, beneficial impacts and the impact matrix is presented later in the report.
4.2.1 AIR ENVIRONMENT
CONSTRUCTION PHASE
Construction phase impact is not foreseen as no additional building is proposed. The
existing equipments capacity will be optimized and some equipments will be added within
the process area. Therefore, the impacts during construction phase/equipment erection
phase are minimal and impact if any will be within the plant area and plant process area. All
necessary mitigative measures will be taken to control such impacts.
OPERATION PHASE
The main sources of air emission are from Boiler and DG sets.
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Gaseous emissions in the industry include boiler flue gases, fugitive emissions and D.G. set
emissions. Pollutants in the form of oxides of nitrogen, sulfur & SPM are expected from
boiler and generator.
The process of sugar unit requires generation of steam for which boilers are being used. The
project envisages use of boiler using bagasse and paddy husk and other agro waste as fuel.
The necessary pollution control precautions have been taken in the design of the boiler, i.e.
efficient furnace, air heater and multi cyclone dust collector. With this, the emission would
be very minimal.
Potential impact from the plant will be controlled by constant monitoring. Fugitive
emissions are originated mainly in bagasse yard and in roads due to vehicular movement.
The main air pollutants are suspended particulate matter, oxides of nitrogen & sulphur
dioxide from boiler flue gas and D.G sets.
There will not be addition of any new emission sources. Steam required for the expansion
will be met from the existing boilers. Therefore, there is no change in scenario as far as air
emissions are concerned.
Air Pollution Sources and control measures:
Stack
No
Stack attached to Stack height Emission Limits Air pollution
control measures Existing Proposed
1 100 TPH Boiler No change Common
chimney of
65m AGL
SPM
150
ESP
2 50 TPH Boiler No change ESP
3 44 TPH Boiler No change Common
chimney
of 58m AGL
Wet Scrubber
4 26 TPH Boiler No change Wet Scrubber
5 1165 KVA DG No change 30m AGL No2 &
PM
710 &
100
Acoustic
Enclosures
6 1010 KVA DG No change 30m AGL Acoustic
Enclosures
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4.2.1.1 AIR ENVIRONMENT MITIGATION MEASURES
Air quality management during operation phase
Environmental
impacts
Mitigation proposed
Boiler Stacks of adequate height are provided to all the boiler emission
sources. It is as per the KSPCB stipulation.
ESP of proven make is provided to reduce SPM in flue gas to the
permissible levels.
Online monitoring facilities is provided
Arrangements are made for periodical monitoring of stack emissions
Ladder, porthole, power supply points are provided to the boiler
chimney for manual monitoring.
DG sets, Provided the chimney as per the norms.
Provide the acoustics to control noise.
Periodic check and maintenance is provided.
Fugitive Emission Control Measures
The following measures are in place to prevent the fugitive dust emissions from the proposed project.
Fuel unloading areas are provided with dust suppression system.
All the conveyers are covered to prevent the fugitive dust.
The emission level will always be maintained below the stipulated standards. In the
event of failure of any pollution control system adopted by the unit, the respective unit
will not be restarted until the control system is rectified.
Fugitive emissions within the factory are prevented by good housekeeping.
Bagasse/pith spillage control
Tree plantation in 3 to 5 rows is developed all around the site
All internal roads are properly paved or tarred so as to avoid fugitive emissions. A tree
plantation in 2 to 3 rows is developed on both sides of the roads.
4.2.2 NOISE ENVIRONMENT
CONSTRUCTION /ERECTION PHASE
The noise due to this activity is localized within the erection area.
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OPERATION PHASE
The movement of vehicles carrying sugarcane to sugar plant and the finished product is the
main source of noise pollution. For existing DG sets necessary acoustics are provided. The
movement of vehicles carrying Raw materials and the finished product is the main source of
noise pollution. The noise due to release of steam pressure is another source and is
momentary and confined within the factory premises. The greenbelt in the premises is
acting as noise barrier. There will be no increase in noise level because of the expansion.
4.2.2.1 NOISE ENVIRONMENT MITIGATION MEASURES:
Equipments generating minimum noise and vibrations will be chosen.
Ear plugs and/or ear muffs will be provided to workers working near the noise
generating activities.
Vehicles and construction equipment with internal combustion engines will be provided
with silencers and mufflers in order to reduce noise levels.
Green-belt will be developed to attenuate noise impacts and to reduce noise pollution.
Noise levels are checked periodically using a Noise Pressure Level Meter.
4.2.3. WATER ENVIRONMENT
The existing and after expansion water consumption and waste water generation details for
3 units are given below;
Water available from Sugar cane:
Sugar and Co-generation Water Consumption and Effluent generation in cum/day
Sl
No
Particulars Water
Consumption
Effluent
generation
Disposal
A. River water
1 Domestic (Fresh water) 50
45
No. of qtrs-
110 &
Population-
500 No.s
Total 50 45
Septic tank &
by soak pit
B. Surplus Water from Cane
utilization
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2 Sugar Lab 15 15 Treated in
existing ETP
(Activated
Sludge
process).
3 Sugar Plant 75 75
4 Boiler make up & DM back wash
after Sugar condensate polishing
unit
(Fresh water-164
+ reuse- 209)=
374 cum/day
346
6 Cooling tower (Cogen) make up
after Sugar Condensate polishing
unit
760 50
Total 1059 486
NOTE: The treated sugar CPU remaining 661 cum/day is reused in distillery & Cooling tower
makeup. Therefore, the waste water generation and water use is within the stipulated limits
under the EP rules.
Table: - 2.8 After expansion water consumption & wastewater discharge-sugar unit, m3/d
Sugar and Co-generation Water Consumption and Effluent generation in cum/day
Sl
No
Particulars Water
Consumption
Effluent
generation
Disposal
A. River water
1 Domestic (Fresh water) 50
45
No. of qtrs-110 &
Population-500
No.s
Total 50 45
Septic tank & by
soak pit
B. Surplus Water from Cane
utilization
2 Sugar Lab 20 20 To be treated in
existing ETP
(Activated Sludge
process). We
have proposed to
Anaerobic
digester with
existing Activated
sludge process
3 Sugar Plant 200 200
4 Boiler make up & DM back wash
after Sugar condensate polishing
unit
580 500
6 Cooling tower (Cogen) make up
after Sugar Condensate polishing
unit
850 50
Total 1650 770
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NOTE: The treated sugar CPU remaining 661 cum/day is reused in distillery & Cooling tower
makeup. Therefore, the waste water generation and water use is within the stipulated limits
under the EP rules.
NOTE: The treated sugar factory effluent is reused in distillery & Cooling tower makeup.
Therefore, the waste water generation and water use is within the stipulated limits under
the EP rules.
The fresh water requirement of the industry is around 230 KLD including existing and
expansion project.
The total water demand will be met through Malaprabha River.
The condensate water is reused during the process. This includes Process Water,
Cooling Tower make up Soft water, DM Water for Boiler Feed & Domestic
requirement, etc.
The most significant problem is contamination of groundwater by the wastewater which
can leach out into the soil & pollute the groundwater. The other possibility of accidental
discharge of treated/untreated effluent to Malaprabha river which is 1.4 Km from the plant.
4.2.3.1 WATER ENVIRONMENT MITIGATION MEASURES
Sewage is treated in septic tank & soak pit
The effluent generated from the industry will be treated in existing effluent
treatment plant. The treated water is monitored on line by providing flow meter and
for monitoring the parameters pH, BOD, COD and SS.
The effluent generated is treated in the effluent treatment plant by primary,
secondary and tertiary treatment and reused for cooling tower make up, cane
washing etc.,
Only the excess treated effluent is applied on land for irrigation on the land owned
by the industry and on private lands with the consent of the farmers for irrigation.
There are no water bodies nearby except for Malaprabha River which is located 1.4
Kms from the nearest factory building. The treated effluent is collected in polishing
pond and regulated to the agricultural fields for irrigation. Hence there is no scope
of effluent discharge directly into water bodies.
For sugar plant, the fresh water requirement is minimal as the water in sugar cane is
collected in the form of condensates and used for various purposes.
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The waste water from the process is 72 Liters/ton restricted to less than 100
Liters/ton of cane crushed. Similarly, the cooling tower bleed will be 50 Liters/ton
restricted to less than 100 liters/ton of cane crushed as per the EP Rules.
Effluent treatment plant is provided for sugar plant effluent. The capacity of the ETP
is 800 KLD. This was built at the time of establishment of the plant during the year
1999. Over the years there was lot of initiatives by the industry to reduce the water
consumption by optimizing the recycle of condensate water. There by the effluent
quantity at present is 526 KLD. After expansion it will be 815 KLD. Therefore the
existing ETP is adequate to handle the effluent generated from sugar plant. The flow
sheet of the ETP is in the chapter 2 and fig 2.6.
4.2.4 LAND AND BIOLOGICAL ENVIRONMENT
There will not be any major impacts on land during the construction phase of the industry
as the proposed expansion will take place within the existing process area.
OPERATION PHASE ATTRIBUTES
Discharge of wastewater on land
Storage and disposal of solid wastes on land
Back wash from DM plant and Softener, Boiler blowdown will be neutralized in a
neutralization tank and will be mixed with cooling tower blow down and will be utilized
for greenbelt development, dust suppression and ash conditioning after ensuring
compliance with treated effluent quality as per MoEF / SPCB Standards. Due to the
extensive greenbelt development proposed the aesthetics of the land will improve.
4.2.4.1 LAND ENVIRONMENT MITIGATION MEASURES
The measures indicated below will be practiced in maintaining land and biological
environment:
The treated wastewater is re-used for process and excess is used for irrigation.
ETP Sludge is collected and used as manure.
Green belt is provided all round and within the plant which is taking care of noise, soil
erosion and fugitive emissions besides improving the aesthetics of the region
The domestic solid wastes are segregated at source, collected in bins and composted.
The press mud generated is used for composting with the distillery effluent.
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Mitigation measures for solid waste management
The solid wastes or by-products produced in sugar industry such as bagasse, press mud
and molasses are made use as valuable resources.
The domestic wastes are segregated at source, collected in bins and composted. The in-
organic solid waste will be sent for recycling.
Waste oil generated from the industry is collected in Sealed Carboys and it is being
collected in leak proof containers and disposed to KSPCB registered & authorized
reprocessors.
4.2.5 SOCIO-ECONOMIC ENVIRONMENT
The local people are benefited by way of generation of employment opportunities,
increased demand for local products and services. There is an overall improvement in the
income level of the local people. The project creates employment to 400 persons (direct)
and 800 persons (indirect). Priority is given to local people for employment of Unskilled and
semi-skilled workers.
The project proponent has already take-up welfare activities in the surrounding villages the
activities will further continue with Corporate Environmental Responsibility. As MoEF and
CC The project proponent intends to conduct regular health check-ups in the surrounding
villages. Therefore there will be a certain enhancement of educational and medical
standards of people in the study area. There will be generally positive and beneficial
impacts by the way of economic improvements, transportation, aesthetic environment and
business generation.
The Corporate Environmental Responsibility activity and fund allocation are as under. As per
the ToR the fund at least 2.5 % of the project cost is required to be earmarked. The cost of
expansion is Rs. 18.78 Crore. As per the MoEF & CC Office Memorandum F. No. 22-65/2017-
IA. III dated 1st May 2018 for brown field projects – Percentage of additional capital
investment towards CER is 1%. However, as per ToR 2.5 % (Rs. 50 Lakhs) is earmarked for
various activities mentioned below.
Sl No Activity Fund allocated
1 Infrastructure creation for drinking water
supply and sanitation to ---- village
20
2 Periodical health check up in the nearby
villages
5
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3 Conducting skill development trainings 5
4 Providing solar power in the nearby
villages
10
5 Awareness to local farmers to increase the
yield of crops and fodder
5
6 Rainwater harvesting in nearby schools 5
7 Plantation in the open barren government
lands in association with Revenue and
Forest Department
5
4.2.6 ODOR MANAGEMENT FOR SUGAR UNIT
SOURCES OF ODOR
Typical compounds generating odor in sugar industry are acetic acid, ethyl alcohol / butyl
alcohol, bacterial decomposition of organic matter (stale cane smell) & bacterial
decomposition of Sulphur compounds (H2S).
Causes of odor are stale cane, bad mill sanitation, bacterial growth in the interconnecting
pipes & unattended drains etc.
4.2.6.1 ODOR MITIGATION MEASURES
Better cane management to avoid staling of sugar
Use of mill sanitation bio-ciders to minimize the growth of aerobic / anaerobic micro–
organisms
Steaming of major pipelines
Proper cleaning of drains
Avoid stagnation of condensate and waste water.
Regular use of bleaching powder in the drains to avoid growth of Sulphur decomposing
micro-organisms to control H2S generation.
4.3 IRREVERSIBLE & IRRETRIEVABLE CONSTRAINTS OF ENVIRONMENTAL COMPONENTS
There are no irreversible or irretrievable constraints of the environmental components as
adequate care is taken to prevent any major impact on the environmental parameters. The
plant is in operation since 1999, with the present pollution control systems and reducing
the water consumption by implementation of various conservative measures no adverse
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impact is observed on the environment. In fact the environment and social status of the
people around is improved significantly.
4.4 ASSESSMENT OF SIGNIFICANCE OF IMPACTS (CRITERIA FOR DETERMINING
SIGNIFICANCE, ASSIGNING SIGNIFICANCE)
The significance of the impacts is identified in the previous sections for various
environmental parameters.
The by-products produced in sugar industry such as bagasse, press mud and molasses are
made use as valuable resources. The 19 years of operation has demonstrated that the
project is sustainable and has not created any adverse impact on land and ground water.
4.4.1 IMPACT MATRIX
Table 4.7 presents the impact matrix for the actions identified along with various
environmental parameters. A rating scale has been devised to give severity of impacts in the
following manner.
A : Strongly beneficial (positive) impact
B : Low beneficial impact
C : Strong adverse (negative) impact
D : Low adverse impact (localized in nature)
- : No conceivable impacts on environment
4.4.2 ENVIRONMENTAL IMPACT ASSESSMENT
The environmental impact assessment is detailed in table 4.1
Table 4.1: Environmental impact assessment
Particulars Details
Air Quality Management
Possible
Sources
Boilers, D.G. Sets, Transportation Vehicles etc.
Emissions and
Existing
Control
measures
Fugitive emissions within the factory are prevented by good house
keeping
Bagasse spillage is avoided and the floor is kept clean.
Tree plantation in 3 to 5 rows is developed all around the bagasse yard,
press mud yard and cane yard.
All internal roads are properly paved or tarred so as avoid fugitive
emissions. A tree plantation in 2 to 3 rows is developed on both sides
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of the roads.
Measures will be taken to maintain all the roads used for
transportation of sugar cane. Trees will also be planted on either side
of the road.
Stacks of adequate height Common chimney of 65m AGL for 2 boilers,
common chimney of 58m AGL for 2 boilers and common chimney of
30m AGL for 2 DG Sets are provided.
ESP of proven make is provided to the boilers to reduce SPM in flue gas
to the permissible levels.
Online monitoring facilities is provided
Arrangements are made for periodical monitoring of stack emissions
Ladder, porthole, power supply points are provided to the boiler
chimney for monitoring.
Monitoring Online Monitoring facility is provided.
Ambient air quality emissions are being monitored regularly to ensure
that ambient air quality standards are met.
Water Management
Management Fresh water requirement of the project is being met by Renuka
Reservoir.
Efforts are being made to conserve as much water as possible by
recycling and reuse.
The domestic sewage is being treated in septic tank and soak pit.
Effluent generated from the sugar plant is being treated in ETP.
Monitoring Waste water monitoring for quantity and quality
Ground water monitoring
Noise Management
Management Proper maintenance, oiling and greasing of machines at regular
intervals is adopted
PPEs like ear plugs and ear muffs are provided to the workers exposed
to high noise level.
Development of Green Belt
Regular monitoring of noise level.
Turbo Generator and D.G set is provided with acoustic enclosures to
control the noise level within the prescribed limit.
Monitoring Regular monitoring of noise levels. Corrective measures in concerned
areas to be adapted accordingly as and when required.
Solid Waste Management
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Management The solid wastes or by-products produced in sugar industry such as
bagasse, press mud and molasses are made use as valuable resources.
separate enclosure for the collected material in a secured manner.
Used oil & grease generated from plant machinery/Gear boxes are
hazardous wastes and is being disposed through KSPCB authorized
reprocessors.
Green belt Development/ Plantation
Management About 35.29 % of total project area has been developed under green
belt/plantation with diverse species.
All the barren areas are vegetated.
Native plant species is planted in consultation with local horticulturist.
Green belt development along with the road & plant boundary will
attenuate noise level arrest dust and improve the environment in
surrounding.
Odor Management
Management Odor is the primarily controlled at source by good operational
practices, including physical management control measures.
Better housekeeping is being maintained with good hygiene condition
by regular steaming of all equipment.
Table 4.2:- Impact matrix
Environmental parameter Proposed actions
Excavation Civil
works/ma
chineries
Fabrication
/Erection
Operation
phase
1.0 Air environment
Ambient air quality
Suspended particulates C C - D
Sulfur dioxide - - - D
Nitrogen oxides - - - D
Carbon monoxides - - - D
2.0 Water environment
Ground water
quality/availability - - - -
Surface water availability - - - D
Receiving water body quality - - - D
Drainage system - - - D
3.0 Solid & hazardous waste
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Land disposal - C - D
4.0 Noise
Ambient noise levels - C C D
5.0 Ecological parameters
Flora C C - D
Fauna - - - D
Aquatic ecology - - - -
6.0 Human settlement
Economic output - B B A
Employment opportunity - B A A
Occupational health - D D C
7.0 Aesthetics
Topography / skyline - - - -
Visual air quality - C - C
Visual water quality - - - -
A: Strongly beneficial (positive) impact, B: Low beneficial impact, C:Low adverse impact
(localized in nature), D:Strong adverse (negative) impact :No conceivable impacts on
environment
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CHAPTER 5
ANALYSIS OF ALTERNATIVES
(TECHNOLOGY & SITE)
M/s. Shree Renuka Sugars Limited is operating sugar, co-generation plant and Distillery. The
expansion of sugar plant is proposed in the existing premises. In the existing infrastructure
industry propose to add some new machineries/equipments and expand the capacity of
some equipments to meet the expansion capacity.
During the scoping there is no recommendation for review of process technology.
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CHAPTER 6
ENVIRONMENTAL MONITORING PROGRAM
6.0 TECHNICAL ASPECTS OF MONITORING THE EFFECTIVENESS OF MITIGATION MEASURES
(INCLUDING MEASUREMENT METHODOLOGIES, FREQUENCY, LOCATION, DATA ANALYSIS,
REPORTING SCHEDULES, EMERGENCY PROCEDURES, DETAILED BUDGET & PROCUREMENT
SCHEDULES)
6.1 MEASUREMENT METHODOLOGY
Online monitoring facilities are provided, photographs of the Online monitoring facilities is
provided in Chapter 2, Section 2.6.1.
Ambient air & noise monitoring, water, wastewater & soil quality is outsourced to NABET
accredited laboratory.
Environment Aspect Parameter Method
Ambient Air Quality PM10, PM2.5, SO2 &
NOx, CO, O3
PM10, PM2.5 : Gravimetric method
SO2 : Modified West and Gaeke
Method (IS : 5182, Part II)
NOx : Jacobs and Hochheiser Method (IS
5182 Part VI)
Water Quality pH, EC, Total
alkalinity, Chlorides,
Hardness, Ca, Mg,
TDS, DO, COD, BOD,
Sulphate, Phosphate,
Na, K, Cu, Fe, Total
coliform & E.coli
Physical, chemical & bacteriological as per
APHA and Manual Published by CPCB.
Noise Quality Noise levels in dB(A) IS: 9989-1981 (Reaffirmed 2001)
as adopted by CPCB.
Soil Quality Physical, Chemical
Characteristics, Soil
Texture
Lab standard operating procedures and
department of agriculture and cooperation
ministry of agriculture Govt of India, New
Delhi
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6.2 FREQUENCY, LOCATION, DATA ANALYSIS, REPORTING SCHEDULES
A comprehensive monitoring program is suggested in below table 6.1.
Table 6.1: Monitoring schedule for environmental parameters
Sl
No
Particulars
Monitoring
frequency
Duration of
monitoring
Important parameters
for monitoring
I Air quality
A Ambient air monitoring
1. Project premises Once in a
month
24 hourly
sample – 2
times a week
PM & SO2, NOx
2. Stack monitoring of
boilers
Once in a
month during
the season
Grab SPM
II Water and wastewater quality (to follow the uniform protocol on water quality
monitoring, MoEF Notification No. S O 2151 dated 17/6/2005)
B Water quality
i. Groundwater at two
locations (up-gradient
and down-gradient)
Twice a year –
pre and post
monsoon
Grab As per KSPCB stipulation.
C Wastewater quality
i. Low strength & high
strength wastewater
streams (raw &
treated)
Once in a
month
Grab As per KSPCB
requirements
ii. Online continuous
monitors
Online monitoring for
parameters prescribed by CPCB
viz Flow, pH, BOD, COD, SS.
Connected to CPCB &
KSPCB web portals.
III Soil quality
1. Within project
premises at one
location
Once in a year Composite
sample
To assess the soil quality
for agricultural
requirement.
2. Soil quality and crop
yield study by UAS,
Dharwad.
Twice a year Grab As per protocol of
agriculture practice.
IV Noise monitoring
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1. Project premises Once in a year
during the
season
Day and night As per KSPCB
requirements
V Hazardous waste monitoring
1. Hazardous waste
characterization
Annually - As per KSPCB stipulation.
6.3 BUDGET PROVISIONS FOR ENVIRONMENTAL MONITORING PROGRAM
Sl
No
Application Budget towards EMP, Rs in Lakhs
Already
implemented in
existing sugar
industry
Additional during
proposed
expansion of sugar
industry
1.0 Capital Investment
1.1 Air pollution control facilities (ESP,
Chimney, ESP and ash handling) 230 -
1.2 Waste water treatment facilities 500 60
1.3 Green belt 30 5
1.4 Laboratory and monitoring
facilities 10 -
Sub total 770 65
2.0 Recurring Cost of Operation and Maintenance
Air pollution control 100 -
Water pollution control 120 30
Monitoring cost 2.0 -
Sub total 222 30
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6.4 EMERGENCY PROCEDURES
Structure of Onsite Emergency Preparedness and Response
Plant Level Worker noticing
an emergency situation
Shift In-charge
1. If necessary, shutdown
the plant.
2. Contact the emergency
declarer
If emergency is off
site contact concerned
authority and
handover the charge
of emergency control
operations.
Govt. Authorities
Police
Fire
Accounting of personnel
All clear signal (when
emergency is over)
Incident/Emergency controller
Fire/Security
Team
Rescue/First
Aid Team
Declarer of
emergency
Raise alarm
Inform over phone
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6.4.1 EMERGENCY ORGANIZATION STRUCTURE
6.4.2 EMERGENCY COORDINATES
6.5 COMPLIANCES TO ENVIRONMENTAL STATUTES
This industry is law-abiding and the Environmental Statutes are proposed to be complied
with letter and spirit.
1. Carrying out “Environmental Audit Statement” of various environmental aspects, review
the environmental policies with the help of experts and make the up gradation/changes
accordingly.
2. Submission of the “Environmental Statement” to the State Pollution Control Board in
Form V under Rule 14 of the Environment (Protection) Second Amendment Rules 1992 of
the Environment (Protection) Act, 1986.
3. Renewal of Consent to Operate under the Water and Air Acts.
CONCERNED DEPARTMENTS
SECURITY
PERSONNEL
ESSENTIAL & SUPPORT SERVICES
FIRE FIGHTING RESCUE REHABILITATION & TRANSPORT
Site Controller & Chief Emergency Declarer (General Manager Manager)
Incident Controller/Alternative Emergency Declarer
(Administrator)
Maintenance Supervisors / Incident Emergency Declarer/Controller
Maintenance Supervisors / Alternative Emergency
Declarer
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4. Renewal of the Hazardous Waste Authorization under sub-rule 3 of the Hazardous Waste
(Management and Handling) Rules, 1989.
6.6 MONITORING OF COMPLIANCES TO STATUTORY CONDITIONS
Environmental clearance from KSPCB and SEAC is always accompanied by the specified terms
and conditions. Necessary measures are taken to comply with these conditions.
Environmental Cell and the associated staff monitor the compliances regularly.
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CHAPTER 7
ADDITIONAL STUDIES
7.0 PUBLIC CONSULTATION
The public hearing for the proposed expansion of sugar crushing from 7500 TCD to 10000
TCD is to be held at existing industry site of M/s Shree Renuka Sugars Limited at Survey.R.s
Mo. 367/1, Munoli Village, Saundatti Taluk and Belagavi District as per EIA notification No.
1533 of MoEF dated 14th September 2006. This is in line with the ToR issued by SEIAA.
7.1 RISK ASSESSMENT AND HAZARD ANALYSIS
7.1.1 INTRODUCTION
The emergency management plan is concerned with preventing hazards through good
design, operation maintenance and inspection. Though every care is taken at the design
stage itself, absolute safety is not achievable and therefore the essential aspect of
emergency management plan must include measures to mitigate the effects of such
eventualities. An important element of mitigation is emergency planning, i.e., recognizing
that accidents are possible, assessing the consequence procedures that would need to be
implemented in the event of an emergency.
The main objective of emergency management plan is to keep the organization in a state of
readiness to contain the extent of emergency and cascading effect of the original
emergency and bring the incident under control with priority to saving of life, preventing
further injury and loss of property and also to bring back the plant to normally and working
condition. Mobilize internal and external resources of man, materials and services required
to manage emergency.
Containing the hazards will require prompt action by operators and emergency staff using
firefighting equipment, emergency shutdown of plants etc. Minimizing the effects will
include rescue, first aid, evacuation, habituation and giving information promptly to
concerned people.
Emergency planning is just one aspect of safety and is not substitute for maintaining good
standard within plant operation. Before starting to prepare the EMP, it should be ensured
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that all the necessary standards and codes of safety including electrical, insurance etc., are
followed from the design stage itself in the industry.
For convenience of planning the emergencies are classified in to on-site and off-site
emergencies.
7.1.2 On-Site Emergency
It consists of those situations affecting one or more plants of the industrial facility and manageable by a planned resources of the industry itself.
7.1.3 Off-Site Emergency
It consists of more serious situations affecting several plants of the industry, even spreading outside and requiring outside assistance including state or national level resources mobilisation to manage them.
In Co-Gen sugar industries the eventualities are likely to cause emergency situation confined to the industry itself, and therefore, on-site emergency management plan is prepared for its implementation in Shree Renuka Sugars Ltd., Munoli.
7.2 RISK ASSESSMENT
To consolidate the on-site emergency plan, one needs to identify and assess the potential hazardous area and activity, in and around the co-generation plant. The areas of possible hazardous incident are given for follow up action:
a. Fire in Bagasse storage yard.
b. Short circuit and consequent fire accident.
c. Any likely sort of explosion in Boiler area
d. Puncture of Boiler tubes.
e. Possibility of any gas leakage.
f. Bursting of pipeline joints.
g. Malfunctioning of the Conveyor Protection System.
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Following is the brief description about the above causes:
A. FIRE IN BAGASSE STORAGE YARD
This may occur on account of external cause. The Bagasse may catch fire since it contains lot of fiber and it may spread slowly because of the high moisture content.
B. SHORT CIRCUIT AND CONSEQUENT FIRE ACCIDENT
The electrical short circuit may happen in any of the plant area due to poor insulation of the equipments.
C. ANY LIKELY SORT OF EXPLOSION IN BOILER AREA
The fuel, i.e., Bagasse, is burnt in the boiler furnace, at operating Platform. The furnace pressure is controlled by running forced draught fan in the upstream side and induced draught fans at the downstream side. Bagasse, on burning in the furnace, transforms into flue gas with high temperature, occupies more volume. The furnace volume is adequately designed to take care of this transformation. The FD & ID Fans in combination evacuate this flue gas pass through chimney.
Due to possible prolonged accumulation of soot in the furnace, improper combustion of fuel in the furnace, excessive dumping of fuel into the furnance, may lead to the excessive pressure in the furnace. This may occasionally result in explosion of furnace.
D. PUNCTURE OF BOILER TUBES
In boiler, due to burning of Bagasse, the heat generated is transferred from the flue gas to the tubes, which are arranged all around the furnace. These tubes are carrying the feed water, which gets heated up to its saturation temperature and starts generating steam. Due to the thermal convection current, the water flows across these tubes after absorbing the heat from its surroundings.
The steam generated in the boiler goes to the turbo-generator to drive the prime mover, i.e., the turbine. In this turbine, the steam is condensed and that condensate is returned back to the boiler again.
This process is repeated is repeated continuously. Due to this, the dissolved salts present initially in small amount in the water gets concentrated, which attains its threshold limit, over a period of time. This results in the scale formation in the tubes, which drastically reduces the heat transfer rate. This leads to the localized overheating of the tubes. This
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overheating makes the tube material soft and start bulging, eventually bursting of the tubes in such vulnerable places may occur.
E. POSSIBILITY OF ANY GAS LEAKAGE
In this plant, sources of occurrence of gas leakage are very limited. Hydrochloric Acid is used in water treatment plant. Sodium are in small quantity. These chemicals are stored in closed storage tanks. Leakage of gas from these equipments is avoided by providing effective gland and packings and also by good maintenance of equipments. In sugar and co-generation plant, toxicity level is very minimum.
F. BURSTING OF PIPELINE JOINTS
The water required for Boiler is pumped and transferred to the boiler by using high-pressure pumps. Also the high-pressure steam generated in the boiler is sent to the turbine through the pipeline. This pipeline will have flanged joints, with sandwich gaskets in between for better sealing. At times, due to water hammering this gasket fails and leads to bursting of the flange joint.
G. MALFUNCTIONING OF THE CONVEYOR PROTECTION SYSTEM
The Bagasse from the sugar plant is transported to Co-generation Boiler by a set of low speed belt conveyors. The remaining Bagasse, if any, is conveyed to the covered Bagasse storage yard by another set of low speed belt conveyors. There is also an arrangement in this system to back feed the Bagasse from the closed Bagasse storage yard to the sugar plant. There is a possibility of occurrence of any snapping of failure of interlocking or protective systems, which may lead to accidents.
Hence, a preliminary Safety Audit conducted by qualified technical personnel have studied the strengths and weakness of the possible occurrence of risk and accidental areas which are likely to be vulnerable which are as follows:
Possibilities of cascading effects of the probable original emergency.
Possibilities of collapse of tall structures and its possible original emergency.
Location of the incident in relation to build-up areas.
7.3 STRUCTURE OF EMERGENCY MANAGEMENT
In the event of disaster it is required to declare emergency, evacuate persons, arrange rescue and repair (hazard control) operations, medical attention to injured etc., to control
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the emergency situation. Officers of the factory have to be designated to be in charge of these operations. Other important aspect of EMP is to acquaint and train concerned persons in the factory and around about the likely hazards, and the measures in case of disaster so that the consequence of it is minimized.
7.3.1 EMERGENCY ORGANIZATION
An organization consisting of various officers of the factory as “Specified Members” is formed to manage the emergency situations. A senior officer of the factory is overall in charge of the emergency management and is designated as Emergency Declarer. He is assisted by Incident controller and Emergency Co-coordinators, who have the responsibility of Control of Incidence and Emergency Co-Ordination, respectively. Incidence control involve operations of prevention and control of damage to life and property during emergency situation and the emergency co-ordination involves the activity of facilitating the former.
Incident controller and emergency coordinators are in turn assisted by different teams to carry out specified tasks of the emergency management. The organization structure for the proposed Co-Gen sugar industry is given in Table-10.1.
7.3.2 EMERGENCY CONTROL ROOM (ECR)
It is expeditious and advantage to have one specified control spot for interactions and directions. The office room at Administration building is chosen as the ECR from where Emergency situation is controlled by emergency controller. This spot is safe and away from the likely spot of disaster but has easy access to all the plants of the factory. Senior staff and communication facilities are available in the administrative building. In case of hazard to administrative building, cane development office is identified as alternative location. The ECR is provided with communication facilities and information files required in control of emergency situation.
EMERGENCY ORGANIZATION (E.O)
No. Designation Person Alternate person
1 Declarer of Emergency General Manager
(power plant)
1. General Manager (Sugar plant)
2. Chief Engineer
2 Incidence Controller Chief Engineer (Sugar) Deputy chief Engineer (sugar)
2.1 Evacuation and Rescue Team
Boiler chief Engineer
Sr. Engineer (Sugar)
Deputy chief Engineer (Boiler)
Sr. Engineer (Boiler)
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2.2 Repair Team Maintenance Engineer Workshop Superintendent
2.3 Essential Service Team Chief Chemist (Sugar)
Sr. Engineer (Boiler)
Sr. Engineer (Turbine)
Deputy Chief Chemist (Sugar)
Sr. Engineer (Electrical)
Sr. Engineer (Instruments)
3.0 Emergency Co-coordinator
Chief Chemist WTP Laboratory In charge
3.1 Transportation Vehicle Team
Personal Manager
Vehicle Manager
3.2 Medical Services Team Safety Officer Safety Assistant
3.3 Security Security Officer Security Supervisor
3.4 Communication Public Relation Officer(PRO) Office
Office Manager.
LIST OF FACILITIES AT EMERGENCY CONTROL ROOM
i. P & T, Fax, Telephone and E-mail facilities for internal and external communications.
ii. Walkie – Talkie and Mobile Phones.
iii. Layout plan of factory and site with indication of vulnerable zones, location of safety
equipments and other resources, escape routes, workers roads, assembly points and
evacuation paths etc.
iv. List with addresses of first aiders, firefighting employees, trained safety persons, key
officers of the factory, statutory authorities, essential services and organizations.
v. Data sheet of chemicals
vi. Copy of EMP, list with addresses of emergency control team members and siren with
codes.
vii. Internal and external telephone directories.
viii. Emergency shutdown procedure for each plant.
Security Officer along with Emergency Co-coordinator is responsible to maintain the ECR along with the facilities indicated above
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7.3.3 IMPLEMENTS FOR REPAIR SAFETY GEARS
Rescue and control team have to work under hostile environment and therefore require different types of protective appliances and equipments. Further to manage the situation such as ambulance, fire brigade, and emergency vehicle, ladders etc. in addition to firefighting and first aid medical facilities. These facilities will be procured and kept at easily assessable locations. A list of safety equipments, protective appliances and other facilities needed for control of emergency is given below.
SAFETY IMPLEMENTS AND FACILITIES
1. COMMUNICATION SYSTEM
P & T, internal and external telephone, mobile telephone, Fax, E-mail, and Walkie – Talkie are available at ECR. Internal telephone, Walkie – Talkie and mobile phone are provided to all departments. Receptionist during day period and security officer during other period is available for management of above communications.
2. FIRE FIGHTING FACILITIES
i. FIRE HYDRANTS
Fire hydrant system with hose pipe of 7 kg/cm2 pressure with single hydrants are located at in bagasse yard, boiler house and sugar godown.
Water tank at elevated place : 60 m3 capacity
Water pump at 10 kg/cm2 pressure : 20 m3/hr
ii. FIRE EXTINGUISHERS
Fire extinguishers
Foam water : 2 Nos. each at main office and store.
CO2 type : 6 Nos. one each at departmental office.
DCP type : 8 Nos. in sugar plant, 8 in power plant.
Sand buckets.
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iii. FIRE PROTECTIVE APPLIANCES
Three sets of fire safety appliances each consisting of fire mask (6), face shield (6), fire gloves (12) fire helmet (12), safety belts (6), located at store, power plant office and sugar plant office respectively.
iv. FIRE BRIGADE:
Fire brigade facilities available at Mundargi and Gadag shall be utilized whenever need arises.
3. SAFETY EQUIPMENTS AND APPLIANCES
These equipment and facilities listed below are kept at administrative building/stores building and are under the control of emergency Co-ordinator
i. First AID medical units one unit of each department, 4 units at store and 4 units
at ECR
ii. Safety belts
iii. Ear muffs, Noise muffs, against dusts, Aprons against chemical spillage.
iv. Shock proof gloves and mats.
v. Leather / Aprons.
vi. Safety items of shoes, gum shoes, hand gloves, helmets, goggles.
vii. Safety ladder.
viii. Face masks & gas masks (against SO2 gas).
ix. Leather gloves.
x. Breathing apparatus.
xi. Stretchers and oxygen cylinder.
xii. Flame proof battery and lighting.
xiii. Ambulance at Munoli and Saundatti
xiv. Emergency lighting facilities,
xv. Air life line for working in vessels and tanks.
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4. EMERGENCY TRANSPORT VEHICLE
One vehicle along with driver is always made available at the factory premise for emergency needs.
5. AMBULANCE
Ambulance facilities are available at general hospitals of Munoli and Soundatti will be made whenever necessary.
7.3.4 ASSEMBLY POINTS
Assembly points are those locations where the persons not connected with emergency operations can await either for further instructions or for rescue, transportation and rehabilitation. These points are safe locations free from hazard and have easy access to other departments of the factory. Premises at the entrance of sugar plant and power plant are specified as assembly point for the employees working in the sugar plant and power plant respectively. Assembly points will be managed by security officers and are under the control of emergency Co-coordinator.
7.4 ACTION PLAN FOR CONTROL OF EMERGENCY
Various functions to be carried out for control of emergency are categorized and assigned to Emergency Controller, and to the members of Incident Control and Emergency Co-ordination.
7.4.1 IDENTIFICATION AND ASSESSMENT OF HAZARDS
The worker, who is first to notice the hazard will communicate the incident to the plant supervisor personally or through phone. The plant supervisor will come to the spot, assess the situation and communicate to Declarer of Emergency or his alternative, through walkie – talkie / phone / messenger. The supervisor assumes the responsibility to control the hazard till the arrival of Emergency Controller to the spot.
It is essential that the situation be identified at the earliest possible time and judged correctly and if necessary an emergency be declared. Under this plan, the G.M. Sugar plant (as alternate G.M. Power plant) is identified and nominated as “Declarer of Emergency” Immediately after the receipt of information, he shall move to the place of hazard/ calamity. He will assess the nature and magnitude of situation and if necessary decides to declare emergency and assumes the responsibility of emergency control.
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7.4.2 DECLARATION OF EMERGENCY
The Declarer of Emergency will decide to declare emergency in the particular plant or the entire plant. For the purpose of declaring emergency, the declare will arrange to sound the siren continuously for two minutes with intermittent low pitch at every half minutes. On hearing the coded sound, the workers in factory and around will be alerted for emergency situation and especially the members of emergency control teams will be in touch with emergency control room (ECR) for necessary direction. Workers of the plant which are not affected by the emergency can continue their normal work.
7.4.3 FUNCTIONS OF EMERGENCY MANAGEMENT PERSONNEL
A. FUNCTIONS OF DECLARER OF EMERGENCY
After receipt of message the Emergency Declarer will visit the spot assess the
situation of hazard and take over the management of emergency.
Declare emergency if the situation is of serious in nature by means of coded siren
and by public address system.
Interact with incidence controller and Emergency Co-coordinator and direct them to
proceed with the operations of emergency control.
Arrange to liaison with five brigade, medical assistance, mutual aid from nearby
factories and outside experts and if needed seek their services.
Monitor emergency control operation and give necessary guidance.
Nominate person to give information to media and families of team members and
affected persons.
Arrange to inform statutory authorities such as chief Inspector of factories
Karnataka State Pollution Control Board, Police authorities etc.
Give all clear signals through the coded siren, when the emergency situation has
been controlled and normally reached.
Make a detailed report.
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B. FUNCTIONS OF INCIDENCE CONTROL
i. INCIDENCE CONTROLLER:
Assemble the members of incident control team
Decide the course of action to be taken to control the particular type of emergency
and give direction to evacuation repair and essential services.
Arrange for appropriate safety equipment and necessary tools for the team
members.
Keeps in touch with the “Declarer of Emergency” and informed of the progress being
made.
After completely controlling the emergency keep inform the emergency declarer of
the same.
ii. EVACUATION TEAM:
Ensure that the evacuation paths are adequately lighted if the emergency situation
arises during night hours.
Evacuate the workers through the exit route to assembly point. Remove obstacles
inside plant for movement of control personnel and control machineries.
Organize for accounting of personnel and in case of any difference organise for
search and evacuation.
iii. REPAIR TEAM
Shutdown of power supply, boiler and other machineries in case required.
Segregate the affected area.
Remove dangerous material from work area to prevent any secondary disaster.
Fighting of the fire with fire extinguishers, fire hydrants and fire fighting equipments.
Attend hazard control operations such as prevention of leaks etc.
iv. ESSENTIAL SERVICE TEAM
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Maintain essential services like D.G sets, water, compressed air and power supply to
lighting and for essential needs.
Plan for alternative facilities in the event of power failure to maintain essential
services such as lighting telephone, water and other utilities.
Give necessary instructions to electricians and shift incharge regarding emergency
power supply, isolations of certain sections.
Ensure availability of adequate quantities of protective equipment and other
emergency service materials, spares etc.,
C. FUNCTIONS OF EMERGENCY CO-ORDINATION
i. EMERGENCY CO-COORDINATOR:
Assemble team members of emergency Co-ordination, plan the course of action
needed to assist the emergency control and direct the operations
Maintain liaison with Emergency Declarer and Incident Controller
Maintain necessary cash for rescue and emergency operations, and also maintain
the canteen facilities.
Assist Incident Controller in updating of EMP, training of personnel for emergency
operations, organizing mock drills and furnishing report to emergency declarer.
ii. TRANSPORTATION AND VEHICLE TEAM
Make available transport vehicles for emergency operations.
iii. MEDICAL ASSISTANCE TEAM:
Keep a list of medical aiders of the factory and seek their assistance. Maintain
adequate stock of first aid and medical emergency requirements. If necessary,
mobilize extra medical help from outside.
Ensure that all the personnel safety appliances and protective equipment’s are
available to the emergency activities.
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Arrange Medical treatment to the injured and if necessary shift the injured to near
by hospitals.
iv. SECURITY:
Receive and assemble the workers at the assembly point.
Along with relief team account the number of workers with respect to attendance
register.
Cordon off the hazard location. Control the public and traffic.
v. COMMUNICATION TEAM
Maintain liaison with hospital, fire brigade, police station etc., and seek their
assistance whenever needed.
Maintain liaison with neighboring industry and if required seek their mutual aid.
Persons treated for minor injuries are escorted to their home. After hospitalization
of injured persons the message should be sent to their relatives through messenger
who in turn will confirm the intimation to emergency Co-ordinator.
7.5 EMERGENCY SHUT DOWN OF PLANTS
The shutdown is required either to one or more plants and is decided by the Declarer of Emergency. Incidence may be confined to a particular plant such as milling unit, boiling unit or power plant. In such case stop steam, stop pumps and motor, release pressure from pressure equipments and switch off power to the plant. In case of major event to the entire plant stop main steam supply, switch off main power supply and release pressure from pressure equipments. D.G. Sets may be used for emergency power requirement and lighting.
7.6 EVACUATION OF PERSONNEL
All the employees are trained to understand emergency sirens and to leave the premise through specified exit routes and report to assembly point. The evacuation team and the respective plant managers are in charge of evacuation. Evacuation paths and assembly paths shall be displayed in plant for workers knowledge. Low and high pitch siren for one
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minutes is the respective plant is the indication for the workers evaluate the location. The team member of medical treatment shall attend the injured and give first aid.
7.7 ACCOUNTING OF PERSONNEL
The plant manager along with evacuation personnel is responsible for accounting personnel of the plant involved and of the rescue team. In the event any worker not accounted, the matter is reported to control room so that the necessary can be made for rescue team search and locate the missing personal. Accounting of personnel is again verified at the assembly point by the security officer. The attendance roll of the employees is available with the plant manager and the security officer.
7.8 INFORMATION TO THE RELATIVES OF AFFECTED PEOPLE
Persons with minor injuries who are given first aid and not requiring further medical care are taken to their home with an escort. In case of persons hospitalized, the message is immediately sent through messenger to their relatives. After giving the message, he had to confirm the same emergency coordinator.
7.9 MEDICAL TREATMENT
i. On intimation from Declarer of Emergency / Emergency Coordinator officer / (Medical
assistance team head) could arrange for necessary facility to render medical treatment
for the affected workers
ii. Send medical assistants to the where the evacuated worker are reporting .
iii. Ensure that those requiring medical assistance are segregated
iv. Arrange for ambulance and transportation for shifting the affected workers to the
hospital
v. Treat all who can be handled inside the factory premises.
vi. Inform outside hospitals about treatment of injured and seek their assistance. If
required arrange for hospitalization of injured persons.
Sufficient number of factory persons are trained in first aid and emergency medical service. Presence of adequate number of trained first aiders and other service is ensured in each shift
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7.10 SECURITY
i. Receive and assemble the evacuated workers at the designated assembly point
ii. Account for number of workers by keeping readily the figure of number of workers
made entry into the factory along with rescue and relief team.
iii. Organize for fire tenders and call for outside help
iv. Help the police to control the traffic and law and order just outside the factory
premises.
7.11 LAW AND ORDER
i. Control traffic and crowds of on- lookers just outside the factory premises and keep
the area clear
ii. Maintain law and order
iii. Cordon off the affected premises
iv. Keep liaison with the local police at Munoli and seek their assistance if needed to
maintain the law and order.
7.12 ALL CLEAR SIGNAL
Once the emergency is controlled the Declarer of Emergency assess the situation along with other team heads. If he is satisfied that normalcy is regained and no further hazards involved, he shall arrange all clear signal by giving one minute continuous siren at high pitch.
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TABLE –7.1 ADDRESSES OF AUTHORITIES AND SERVICES
Sl No
Authority Address Phone No’s
1 The Chief Inspector of Factories, Karnataka, Bangalore
Karmika Bhavan near ITI College, Banneragatta Road, Bangalore
080/2260106
080/2263712
2 The Chief Inspector of Boilers, Bangalore.
3 The Members Secretary, Karnataka State Pollution Control Board. Bangalore.
25, Public Utility Building, 6th, 7th and 8th floors, Mahatma Gandhi Road, Bangalore-560001
080/5588151
080/5588270
4
The Environmental Officer,
Karnataka State Pollution Control Board, Belagavi.
Auto Nagar,
Belagavi 0831/2454721
5 The Deputy Commissioner, Belagavi
D. C Compound, Belagavi 0831/2407200
6 The Superintendent of Police, Belagavi
Police H/Q, Belagavi 0831/2471301
7 Police Inspector
Saundatti
Munoli
Tq Soundatti
8
General Hospital,
Soundatti
Belagavi
Soundatti
9 The Inspector of Factories, Belagavi
Club Road,
Belagavi
10 Primary Health Center,
Monoli Monoli
11 Fire Station Officer,
Soundatti Soundatti
12 List of Adjacent Industries. Adjacent Distillery Industry
7.13 INTIMATION TO AUTHORITIES
Immediately after the incidence is brought into control, the personnel manager in Co-ordination with Declarer of Emergency will inform chief Inspector of Factories and Boiler Bangalore, Inspector of factories Belagavi, telephonically. A detailed report on the nature of emergency and its consequence will be sent to them within 24 hours of the incidence results in the pollution of environment, then the Karnataka State Pollution Control Board
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shall be kept informed. The list and addresses of important authorities including the above relevant to the Management of Emergency are given in Table-10.2.
7.14 RELIEF AND REHABILITATION
After emergency situation is over the prime responsibility of the Declarer of the Emergency is to interact with management and arrange for rehabilitation of those suffered physically and financially due to the hazards and ameliorative measures as necessary.
7.15 REVIEW OF INCIDENCE
After emergency situation is over, the Declarer of Emergency should appoint a expert committee of two to three members to,
i. Identify the causes lead to the emergency situation.
ii. Preventive measures to avoid recurrence of such situations in future.
iii. Identifying the areas of lapses in implementory emergency plan so that the same can be
improved in future.
iv. Recommendation for further strengthening of EMP
7.16 UPDATE OF EMERGENCY PLAN
The Declarer of Emergency shall arrange a meeting of all the members of the emergency organization once in six months to review EMP and also to ensure its effectiveness.
7.17 TRAINING AND REHEARSAL
Mock drills and training exercise will be conducted half yearly to acquaint all the employees of the factory to
i. Identify hazard
ii. Understand the siren for emergency declaration, evacuation and all clear messages.
iii. Conduct themselves in an orderly manner.
iv. To know the exit routes and assembly points in case of evacuation.
v. Render necessary help during the emergency.
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First aiders, firefighting personnel team members of emergency management are adequately trained. Rehearsal and mock drills are conducted for them once in six months. For training programs assistance, of District Fire Brigade Station, Central Labour Institution, etc., shall be utilized. Such training from external resources will be arrange once a year.
7.18 AIR POLLUTION DISPERSION MODELING STUDIES
7.18.1 INTRODUCTION
Atmospheric dispersion modeling is the mathematical simulation of how air pollutants
disperse in the ambient atmosphere. It is performed with computer programs that solve the
mathematical equations and algorithms which simulate the pollutant dispersion. The
dispersion models are used to estimate or to predict the downwind concentration of air
pollutants emitted from sources such as industrial plants and vehicular traffic. Such models
are important to governmental agencies tasked with protecting and managing the ambient
air quality. The models are typically employed to determine whether existing or proposed
new industrial facilities are or will be in compliance with the National Ambient Air Quality
Standards (NAAQS). The models also serve to assist in the design of effective control
strategies to reduce emissions of harmful air pollutants.
In the present study prediction of impacts on the air environment has been carried out
employing U.S. EPA AERMOD dispersion model, 1996 – 2015 Lakes Environmental Software,
Version 7.1.0 and designed for multiple sources for predicting the maximum ground level
concentration (GLC).
7.18.2 MODEL INPUT DATA
The major air emissions at the site of M/s Shree Renuka Sugars Limited (SRSL) are SPM, SO2
and NOx from existing and proposed boilers. The Proponents have proposed to install
electrostatic precipitator to the stack of the boiler to control the flue gas emissions. The site
specific and monitored details considered for input data for the software AERMOD view by
Lakes Environmental for prediction of impact on the air environment are given in the below.
TABLE 7.2: DATA CONSIDERED FOR CALCULATION OF GLC
Particulars Existing
Boiler 100 TPH
Stack height, m 65 AGL
Stack diameter, m 4.4
Flue gas temperature,K 428
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Gas exit velocity, m/s 8.22
PM10 29.49
SO2 3.1
NOx 5.86
CO (only for DG set)
METEOROLOGICAL DATA
Data recorded at the site for one year period (January 2017- December 2017) for wind
speed, direction, temperature etc. has been used for computations. In order to conduct a
refined air dispersion modeling short term air quality dispersion models, the site specific
hourly meteorological data measured at the site is pre-processed using U.S. EPA AERMET
program.
7.18.3 PRESENTATION OF RESULTS
The simulations were made to evaluate incremental short-term concentrations due to
proposed project.
In the short-term simulations, the incremental concentrations were estimated to obtain an
optimum description of variations in concentrations within study area of 10 km radius. The
predicted (maximum) concentration levels & the incremental concentrations at various
locations due to the existing and emerging scenario of sugar industry are tabulated in the
following tables.
TABLE 7.3: PREDICTED INCREMENTAL SHORT-TERM CONCENTRATIONS DUE TO THE
EXPANSION PROJECT
Time Maximum predicted concentrations, µg/m3 Direction and distance of occurrence
24 hour Annual 24 hour Annual
1ST
highest
values
98
percentile
1ST highest
values
98 percentile
Suspended
Particulate
Matter (PM10)
3.1533 0.5175 0.0234
0.15 KM –N
& 0.434 - S
0.65 KM - E
& 0.430 - W
0.56
KM -E
Sulfur di-oxide
(SO2) 4.560 0.6793 0.0284
0.4 KM - S Within the Site
boundary
0.5 KM
-E
Oxides of
Nitrogen (NOx) 5.4244 0.7943 0.0311
0.2 KM-N &
0.424 - S
0.62 KM
- E
1.145
KM - E
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FIG 7.0: SUSPENDED PARTICULATE MATTER ISOTHERM
I) 24HOURS-1ST HIGHEST VALUE
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II) 24HOURS-98 PERCENTILE
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(III) ANNUAL
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FIG 7.1: SULPHUR DI-OXIDE ISOTHERM
I) 24HOURS-1ST HIGHEST VALUE
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II) 24HOURS-98 PERCENTILE
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III) ANNUAL
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FIG 7.2: OXIDES OF NITROGEN (NOX) ISOTHERMS
I) 24HOURS-1ST HIGHEST VALUE
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II) 24 HOURS-98 PERCENTILE
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iii) ANNUAL
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7.18.4 COMMENTS
The maximum short-term incremental ground-level concentrations are superimposed on
the baseline data to get the likely resultant levels after the establishment of the expansion
project as tabulated below table 4.5.
TABLE 7.4: RESULTANT MAXIMUM 24 HOURLY CONCENTRATIONS
Pollutant Incremental
concentrations
µg/m3
Max. Baseline
concentrations
µg/m3
Resultant
concentrations
µg/m3
Limits as per MoEF,
µg/m3 for industrial
areas (24 hrs)
PROJECT SITE (A1)
PM10 3.1533 91.67 94.8233 100
SO2 4.560 4.95 9.51 80
NOx 5.4244 10.52 15.944 80
UJJANAKOPPA (A2)
PM10 3.1533 83.57 86.7233 100
SO2 4.560 4.80 9.36 60
NOx 5.4244 9.85 15.2744 80
MUNOLI (A3)
PM10 3.1533 90.12 93.2733 100
SO2 4.560 4.86 9.42 80
NOx 5.4244 10.63 16.054 80
NAVILUTEERTHA (A4)
PM10 3.1533 70.18 73.3333 100
SO2 4.560 4.80 9.36 80
NOx 5.4244 9.85 15.2744 80
JAKABAL (A5)
PM10 3.1533 85.74 88.8933 100
SO2 4.560 4.69 9.25 80
NOx 5.4244 10.35 15.7744 80
SHINDOGI (A6)
PM10 3.1533 79.50 82.6533 100
SO2 4.560 5.28 9.84 80
NOx 5.4244 10.22 15.6444 80
SHRIRANGAPURA (A7)
PM10 3.1533 78.10 81.2533 100
SO2 4.560 4.86 9.42 80
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NOx 5.4244 9.97 15.39 80
KARLAKATTI (A8)
PM10 3.1533 77.49 80.6433 100
SO2 4.560 4.88 9.44 80
NOx 5.4244 10.07 15.4944 80
According to MoEF air quality standards (as per the notification dated 16th November 2009
for industrial, residential & rural areas) 24 hourly, 8 hourly or 1 hourly monitored values, as
applicable, shall be complied with 98% of the time in a year; 2% of the time, they may
exceed the limits but not on two consecutive days of monitoring.
Therefore the 98% values are considered for estimation of the incremental concentration.
The above table indicates that the cumulative resultant ambient air quality after proposed
project operation will be within the ambient air quality limits specified by MoEF as per the
notification dated 16th November 2009 for industrial, residential & rural areas.
7.19 SOCIAL IMPACT ASSESSMENT, R&R ACTION PLANS
A. SOCIAL IMPACT ASSESSMENT
Social Impact Assessment is link to Socio – Economic Benefit to the people living around the
project. The present proposal is expansion of sugar unit. Therefore, the proposed project
will continue to benefit it the agriculturists in terms of utilization of their produce that is
sugarcane in the factory and in return they get treated water from sugar plant. The Industry
under the corporate social responsibility has undertaken various activities for the benefit of
the local people and will continue the same in the future also.
B. R&R ACTION PLANS
The existing land is sufficient for the expansion proposal also & therefore no re-settlement
& re-habilitation is envisaged.
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CHAPTER 8
PROJECT BENEFITS
8.0 IMPROVEMENTS IN THE PHYSICAL INFRASTRUCTURE
Due to the presence of Shree Renuka sugars Ltd, there are improvements in the region that
has taken place over the years since the commissioning of the plant. To name a few
infrastructural developments are road connectivity between the villages and to the
industry, green cover has increased, drinking water facilities have been created along with
sanitation etc.
8.1 SOCIAL INFRASTRUCTURE
The existing co-gen sugar industry is having a total of 400 direct employees including
Manager, office staff, skilled & unskilled workers and indirect employment of 800
employees towards transportation, vehicle maintenance, petty shops etc. Further, about
10,000 farming families are engaged in sugarcane cultivation and supply of the sugarcane to
the present industry. The proposed project will require additional manpower of 50 direct
and 200 indirect persons.
It will not disturb the existing pattern of social relations and democratic setup.
Society of farmers and the industry are symbiotically dependent. Industry gets raw material
from the farmers. Better and purer the raw material quality better the finished product
quality. Both of them can get better pricing.
The cycle of sowing, cutting, removing, next sowing and milling can be computerized. The
intermediate time-loss can be avoided. Early and timely cutting of cane will make the
farmer free to plant the next crop early. Industry also is benefited as it will get the
sugarcane without any hydrocarbon loss into the air. Recovery will be better. This in turn
will create more job opportunities both in the field as well as in the factory.
Firefighting tenders will be now more easily available.
In the study zone of 10 km radius, the purchasing power of people is very less. The
agricultural implements, agro-chemicals and vehicles will be in more demand and also
village grown milk products, vegetables and agricultural produce.
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8.2 EMPLOYMENT POTENTIAL & TANGIBLE BENEFITS
The Operating Sugar plant has employed about 400 persons and additional 50 Persons,
comprising skilled and semi-skilled will be required after expansion. SRSL will give
preference to the local people for employment. The following facilities will be provided to
the employees:
Regular Health checkups, Medi claim.
Transportation facilities
Housing facilities
Additionally, certain works like security will be outsourced on contract. Secondary
employment in the form of providing services to the employed manpower will also be
developed in the neighboring villages.
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CHAPTER 9
ENVIRONMENTAL MANAGEMENT PLAN
(EMP)
9.0 INTRODUCTION
The Environment Management Plan (EMP) is required to ensure sustainable development in
the area of the proposed project. Hence it needs to be an all encompassive plan for which
the industry, Government, regulating agencies like Pollution Control Board working in the
region and more importantly the population of the area need to extend their co-operation.
It has been evaluated that the surrounding area will not be affected significantly by the
proposed expansion project. Mitigation measures at the source level and an overall
Management Plan at the site level are elicited so as to improve the surrounding
environment.
The following mitigation measures are recommended in order to synchronize the economic
development of the project area with the environmental protection of the region. The
construction phase impacts are not significant, restricted to the plant area and not
envisaged on a larger scale. Also, since it is expansion / modification of process of existing
industry major impacts are not anticipated. In the operational phase the environmental
impacts are due to continuous operation of the project, hence, the emphasis in the
Environment Management Plan (EMP) is to minimize such impacts.
The emphasis on the EMP development is on the following:
Mitigation measures for each of the activities causing the environmental impact;
Monitoring plans for checking activities and environmental parameters and monitoring
responsibilities;
Role responsibilities and resource allocation for monitoring.
Following sections describes in brief the environment management plan proposed for
operation phases.
9.1 ENVIRONMENT COMPONENTS:
SRSL is aware that environmental management is not a job. The success lies if three
components are simultaneously present viz. (1) Management support, (2) Efficiency of the
environment management cell and (3) Acceptability of resulting environmental quality,
both by SPCB and by public. A structure of this plan and hierarchy of process flow for
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environmental management is prepared and enclosed. SRSL will adopt this structure and
hierarchy, which is akin to principles and practice.
i) Air Environment:-
The major source of Air Pollution is Boiler & diesel generator. The boilers have been
provided with ESP & adequate chimney height for control of Air Emissions. The DG set is
provided with chimney of adequate height as prescribed by KSPCB. The following measures
have been recommended.
a) Monitor the ambient air quality.
b) Monitor the work zone at various stations to satisfy the corporate requirements for
health and environment.
c) Maintain a record of running of DG (diesel generating) sets
d) Monitor the stacks or vents fitted to sections of raw materials, manufacturing area, DG,
boiler and power plants.
ii) Water Environment: -
Effluent treatment plant & septic tank
a) Keep record of input water every day for quantity and periodically for quality.
b) Measures are taken to segregate the sub-streams of effluent as per their source and
characterization viz., process water, boiler blow down and cooling water blow down.
c) Water conservation is accorded high priority in every section of the factory.
d) Effluents are treated in ETP.
e) Domestic sewage is being treated in septic tank and overflow from septic tank is being
treated in sugar plant ETP.
iii) Noise Environment:
a) Monitor the ambient noise level and work zone noise level to ensure conformance to
the stipulated norms.
b) Creation of awareness for noise attenuation and mitigation program
c) Monitor the ambient Odor level and work zone Odor level.
d) Creation of awareness for Odor attenuation and mitigation program
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iv) Odour Control
Sources of Odor
Typical compounds generating odor in sugar industry are acetic acid, ethyl alcohol / butyl
alcohol, organic matter (stale cane smell), Sulphur compounds (H2S).
Causes of odor are stale cane, bad mill sanitation, bacterial growth in the interconnecting
pipes & unattended drains etc.
Remedial Measures
Better cane management to avoid staling of sugar
Use of mill sanitation bio-ciders to minimize the growth of aerobic / anaerobic micro–
organisms
Steaming of major pipelines
Proper cleaning of drains
Regular use of bleaching powder in the drains to avoid growth of sulphur decomposing
micro-organisms to control H2S generation.
v) Green Environment:
Development of greenbelt in and around industrial activity is an effective way to check
pollutants and their dispersion in to surrounding areas. The degree of pollution attenuation
by a green belt depends on its height and width, foliage surface area, density, dry
deposition, velocity of pollutants and the average wind speed through the green belt. The
main objective of green belt around the factory is;
1. Mitigation of impacts due to fugitive emissions
2. Attenuation of noise levels
3. Ecological restoration
4. Improvement in aesthetic environment quality
5. Waste water treatment and reuse.
6. Soil erosion prevention
Keeping in view of the soil and water quality available in and around the project site and the
topography of land, following species are existing tree species within the industry premises.
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No Species Name English Name App no
of trees
Height
in m
Age of
the
tree
Canopy /Area
occupied acre
1 Salix triandra Almond 574 5.5 10 1.50
2 Azadirachta idica Neem 1670 6 12 2.00
3 Achras sapota Ckikoo 202 4.5 8 0.15
4 Mangifera indica Mango 190 5 10 0.25
5 Ficus Benghalensis Banayan 1354 8 10 4.00
6 Cocus Nucifera Coconut 270 6 10 3.00
7 Polyalthia Longifolia Ashoka 556 6 8 0.80
8 Caesalpinia
pulcherrima
Shankasur 1116 8 6 0.50
9 Ficus religiosa Peepal 1828 7.5 10 3.00
10 Leucaena
leucocephala
Ipil ipil 3245 6 12 2.00
11 Ficus infectoria Ficus infectoria) 76 6 3 0.10
12 Pthyllanthus embica Gooseberry 36 3 12 0.01
13 Syzygium cumini Jamun 52 4 8 0.04
14 Psidium guajava Guava 72 4 4 0.25
15 Thespesia populnea portia tree 34 3 2 0.12
16 Casuarina
equisitifolia
Casurina 545 7 5 2.00
17 Moringa oleifera Drumstick 16 4 4 0.02
18 Acacia mangium Acacia 334 4 8 1.40
19 Zizipus mauritiana Bor 14 5 12 0.01
20 Pithecolobium dulce Manila tamarind 18 3 4 0.05
21 Eantulum album (Shrigandha) 16 4 5 0.05
22 Pongemia pinnata Karanja 1235 3 5 1.80
23 Pomagrante Pomagrante
(Dhalimbe)
112 2.5 8 0.86
24 Cerry leaves (kari bevu) 162 2 8 0.01
25 Salix triandra Umbar 44 4 10 0.10
26 Citrus medica Lemon 44 2 5 0.01
27 Phyllanthus emblica Indian
gooseberry
154 2 4 0.10
28 Albizia lebbeck Rain trees 250 5 10 1.50
29 Eucalyptus globubus Eucalyptus 2567 8 12 2.20
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30 Carica papaya Papaya 48 4 2 0.01
31 Tamarindus indica Tamrind 64 3 6 0.88
32 Artocarpus
eterphyllus
Jackfruit 12 4 4 0.10
33 Mangolia champca Champak 10 4 6 0.01
34 Melia dubia Meliadubia
(Hebbevu)
122 5 6 0.90
35 Grevillea robusta Silver oak 80 5 10 1.30
36 Thevetia peruviana Yellow oleander 1970 3.5 6 0.80
37 Roystonea regia Royal Palm 414 3.5 6 1.40
38 Ficus elastica Rubber tree 6 5 10 0.60
39 Delonix regia Gulmohar 120 6 10 1.50
40 Anacardium
occidentale
cashew 20 2 2 0.10
41 Bougainvillea glabra bougainville 30 3 3 0.01
Criteria for Selection of Species for Green belt
1. Rapid growth and evergreen type of species.
2. Tolerance to water stress and extreme climatic conditions.
3. Difference in height and growth habits
4. Aesthetic and pleasing appearance
5. Large bio-mass to provide fodder and fuel
6. Ability to efficiently fixing carbon and nitrogen.
7. Improving waste land
8. To suit specific climate and soil characteristics.
9. Sustainability with minimum maintenance.
The salient features of green belt are as follows.
1. More than 30% of the total industrial land area is covered for greenery and green belt.
An average of about 3000 plants will be maintained per hectare of the greenery area.
2. 20 m width green belt is provided all along the border of the site
3. 10 m width green belt is provided all along the border of cane yard, coal yard, bagasse
yard, press-mud cum ash yard
4. Tree plantation is provided on both sides of interior roads in the premise.
5. Lawn with aesthetic plants in open space of buildings and other places
a) Special attention is planned to maintain green belt in and around the factory premises.
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b) Adequate provisions are made to facilitate adequate watering of all plants and lawns.
Special attention provided during summer to ensure that the green belt does not suffer
from water shortage.
c) No outside soil is brought for any building/ greenery developments.
vi) Work-zone Comfort Environment:
a) Monitor the work zone temperature levels and humidity.
b) Examine the health of workers and keep record.
vii) Socio- Economic Environment:
a) The operators and workers are trained in various aspects of ESH (Environment, Safety
and Health).
b) The managers and officers involved in Environment Management Cell shall undergo
refresher workshop and up gradation of information on various environmental issues.
c) The industry will help in promoting the activities related to environmental awareness in
nearby villages/neighbors.
d) The industry will help in promoting local people for livelihood commensurate with their
will, skill and abilities.
9.2 ENVIRONMENTAL MONITORING SCHEDULE:
Aappropriate monitoring is a technique of drawing a sample and deriving inferences from
the same for knowledge and improvements.
A scheme for monitoring is presented in chapter Six. The monitored data are compiled and
submitted to regulatory authorities as per the stipulations.
9.3 SCHEDULES:
There will be three facets to design and follow the schedules viz.: (A) for compliance of
responsibilities, (B) for day-to-day operation and management of ETP and (C) for routine
environmental monitoring, to assess the impact and take timely warning. The schedule:
i) Daily Compliance:
1. Take the meter readings - initial and final, for checking the water consumption.
2. Maintain the electricity consumption record for pollution control equipments.
3. To maintain log book for operation of effluent treatment plant viz, Physio chemical
treatment and composting as per CPCB protocols.
4. Monitor ambient air periodically as per Consent conditions.
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ii) Monthly Compliance:
1. Monitor the emission sources through the competent authority and submit the analysis
reports to the board.
2. Monitor ambient/work zone noise levels & ensure conformance to standards.
3. Periodical monitoring of compost quality and the outlet of digester.
iii) Quarterly Compliance: 1. Monitor the ambient air quality at upwind and downwind locations of the factory.
2. Review the Water Reuse performance.
iv) Yearly Compliance:
1. Carryout “Environmental Audit Statement” of various environmental aspects, review the
environmental policies with the help of experts and make the up-gradation /changes
accordingly.
2. Submit the “Environmental Statement” to the State Pollution Control Board in Form V
under Rule 14 of the Environment (Protection) Second Amendment Rules 1992 of the
Environment (Protection) Act, 1986.
3. Renew the Consent to Operate under the Water and Air Acts.
4. Renew the Hazardous Waste Authorization under sub-rule 3 of the Hazardous & other
Waste (Management and Handling) Rules,2016.
5. The management of SRSL periodically reviews the performance of EMP and the data
generated from monitoring.
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9.4 ENVIRONMENTAL MANAGEMENT PLAN (EMP)
The environmental management plan during occupancy phase is detailed in tables 10.2.
Operation of the facilities/utilities
Table 9.1: Environmental management plan during operation of the facilities/utilities
Sl
no
Environmental
components
Predicted
impacts
Probable source of
impact
Mitigation measures Remarks
1 Ambient air
quality
Minor negative
impact.
1. Flue gases from
boilers and diesel
generators
2.Fugitive emissions
due to bagasse, ash and
movement of vehicles
Gaseous emission in the industry is mainly flue gases
from boilers and diesel generators. Diesel generators
are used only during emergency requirement of power.
Other emissions include fugitive emissions due to
bagasse, ash and movement of vehicles.
The emissions from DG & boiler are let out through
stacks and control equipment for boiler. The details are
in chapter - 4.
DG sets is used
only during
power failure.
1 2 Noise Minor negative
impact near
noise
generation
sources inside
the premises.
Handling and
conveying of raw
materials and semi-
finished components
to different
operations.
Operation of DG set.
The conveying system is maintained by following
routine and periodic maintenance to reduce noise
generation in material handling.
DG set is provided with acoustic enclosure. They
are installed in dedicated utility area, where the
access is restricted. Also the use of PPE (ear plugs)
is mandatory in this area.
Green belt at the project boundary further act as
-
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noise barrier and help in attenuation of noise.
2 3 Water quality No significant
adverse impact.
Discharge of domestic
sewage and industrial
effluent.
The domestic sewage is being treated in septic tank &
overflow is connected to Sugar plant ETP.
Effluent generated from the sugar plant is being
treated in ETP.
Water
conservation
measures are
encouraged.
3 4 Land No negative
impact
Discharge of
wastewater.
Storage and disposal
of solid wastes.
The domestic sewage is being treated in septic tank &
soak pit.
Effluent generated from the sugar plant is being
treated in ETP.
The solid wastes or by-products produced in sugar
industry such as bagasse, press mud and molasses are
made use as valuable resources.
-
4 5 Odor Minor negative
impact.
Acetic acid, ethyl
alcohol / butyl alcohol,
organic matter (stale
cane smell), Sulphur
compounds (H2S)
Better cane management to avoid staling of sugar
Use of mill sanitation bio-ciders to minimize the
growth of aerobic / anaerobic micro–organisms
Steaming of major pipelines
Proper cleaning of drains
Regular use of bleaching powder in the drains to
avoid growth of sulphur decomposing micro-
organisms to control H2S generation.
-
5 6 Socio-
economic
Overall positive
impact
Employment
opportunities
Locally available manpower will be utilized to the
maximum possible extent.
-
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9.5. EMP IMPLEMENTATION SCHEDULE
Phased according to the priority, the implementation schedule is presented in the following
table 4.4.
Table 9.2:- Implementation schedule for EMP
Sl No Recommendations Requirement
1 Air pollution control measures Existing
2 Water pollution control measures Existing
3 Noise control measures Existing
4 Solid waste management Existing
5 Landscape development Existing & Stage-wise implementation
The responsibility of EMP implementation lies with M/s. Shree Renuka Sugars Limited & the
financial allocation/budgetary provisions for environmental management is detailed in table
4.5.
9.6 ENVIRONMENTAL POLICY
The Board of Directors of M/s Shree Renuka Sugars Limited., recognize the important
responsibility it has towards the environment, and is committed to:
Complying with all applicable environmental legislation.
Planned evaluation of compliance by external auditors and the implementation of
improvement programs.
Continuous improvement by following best practice guidance produced by
appropriate regulatory and advisory organizations and aim to get certified to ISO-
14001, the internationally recognized Environmental Management System standard.
Ensuring that all employees are aware of their duty to fellow employees, suppliers,
customers and those who live in the surrounding community, to act in an
environmentally responsible and safe manner.
Collecting, analyzing and publishing key environmental performance metrics to
enable the Group to continually review, assess and improve its environmental
performance.
Minimizing, where practicable, the Group’s impact on the local and global
environment arising from its operations and products, by:
Integrating environmental considerations into the development of any new products
and processes;
Achieving a reduction in emissions of greenhouse gases by using energy, raw
materials and natural resources efficiently;
Reducing the emissions of harmful substances and where practicable using
alternative environmentally safer substances in its manufacturing processes;
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Reducing waste generated by its operations through recycling programs and
minimizing the amount of waste sent to landfill.
Working with all the suppliers to minimize the impact of their products and
operations on the environment.
Benefit the farmers by supplying compost.
The Board delegates responsibility for oversight of environmental policy and
performance to the Director, Management and for local implementation of this
policy to the employees. This policy and its implementation will be reviewed on a
regular basis by the Board to ensure that it remains appropriate and relevant to the
organization. The Group is committed to providing the necessary support in order to
ensure that all sites can fulfill the requirements outlined in this policy.
This policy is communicated to everyone working for or on behalf of the Group. The
non-compliances communicated and will be brought to the notice of all the board of
directors during the board meeting.
9.7 DESCRIPTION OF THE ADMINISTRATIVE ASPECTS OF ENSURING THAT MITIGATIVE
MEASURES ARE IMPLEMENTED & THEIR EFFECTIVENESS MONITORED, AFTER APPROVAL,
IMPLEMENTATION AND DURING OPERATION
In order to maintain the environmental quality within the standards, regular monitoring
network to maintain environmental quality will be implemented.
9.8 ENVIRONMENT MANAGEMENT CELL
A separate Environment Management Cell is already in place as the project is expansion of
existing Sugar plant to monitor and control the environmental quality. Members of the
Environmental Cell are well qualified and experienced in the concerned field.
Services of reputed laboratory with NABL accreditation as well as that of a consultant of
repute would be hired for various monitoring & other environmental management needs of
the industry.
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CHAPTER 10
SUMMARY & CONCLUSION
10.0 OVERALL JUSTIFICATION FOR IMPLEMENTATION OF THE PROJECT
The Environmental Impact Assessment studies carried out for the proposed expansion
project of M/s. Shree Renuka Sugars Limited has been completed. The study conducted has
covered various facets of the proposed expansion project starting with the need for
expansion, its basic requirements like raw materials, water, availability of land,
manufacturing process etc.
In addition to this the metrological data and baseline environmental features have been
evaluated to understand the environmental setting of the project site. Also the ecological
features of the location including the flora & fauna, socio-economic environment, the
demographic structure have been evaluated.
Based on the above studies an Environmental Impact Statement has been prepared to
ascertain the possible impacts of the proposed expansion project on the environmental
parameters like air, water, land, biological and socio-economic environment. An impact
matrix has also been prepared based on the observations of the impacts on the
environment.
An Environmental Management Plan has been prepared covering the environmental aspect
and the management plan required to be adopted by the management during its
operational phase. An environmental monitoring plan is envisaged deciding frequency,
location, data analysis, reporting schedules.
Detailed risk assessment study is carried out to evaluate the risks involved due to storage of
various finished products and precautionary measures to be taken for
prevention/management of such risks.
The conclusions drawn from the above study relates to the fact that the proposed Expansion
Of Co-gen Sugar Industry Plant Capacity, from 7500 TCD to 10000 TCD undertaken by the
management of the industry has certain level or marginal impacts on the local
environmental setting, which will not affect the natural environmental setting of the study
zone either drastically or otherwise. However, certain beneficial impacts are anticipated in
terms of the employment opportunities created during the operation of the industry. Also,
there will be economic growth at the regional level including tangible benefits to the
farmers around the industry.
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The industry created an Environmental Management Cell to monitor and implement
programs to improve its environmental status from time to time and will adopt all such
technological advances to reduce the impact due to its operation on the environment.
To put it in a nut shell the management of M/s. Shree Renuka Sugars Limited., strongly
believes in the concept of sustainable development and understands the impacts of the
proposed industry on the environment from the Environmental Impact Assessment studies
conducted. It is committed to develop its industry without giving room for any adverse
impacts on the environment and also lays emphasis on the implementation of the
recommendations of the Environmental Management Plan in true spirits.
10.1 EXPLANATION OF HOW ADVERSE EFFECTS HAVE BEEN MITIGATED
The measures adopted to mitigate the impacts due to the proposed expansion are tabulated
in table 11.0 below.
Table 10.1:- Measures adopted to mitigate the impacts
No. Parameter Mitigation measures
1 1 Water pollution sources
Domestic sewage The domestic sewage is being treated in septic tank & soak pit
Industrial
wastewater
Effluent generated from the sugar plant is being treated in
ETP.
2 2 Air pollution sources
Boilers ESP with 65 m AGL Chimney
3 D.G. sets Stacks of adequate heights
3 4 Noise pollution
sources – DG sets
In-built acoustic enclosures.
4 5 Solid/Hazardous waste
Domestic garbage Organic portion is composted & in-organic portion is sent for
recycling.
Solid waste
The solid wastes or by-products produced in sugar industry
such as bagasse, press mud and molasses are used as valuable
resources.
Hazardous solid
waste
Used oil & grease generated from plant machinery/Gear
boxes are hazardous wastes being disposed through KSPCB
authorized reprocessors.
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CHAPTER 11
DISCLOSURE OF CONSULTANTS ENGAGED
11.0 THE NAMES OF THE CONSULTANTS ENGAGED WITH THEIR BRIEF RESUME & NATURE
OF CONSULTANCY RENDERED
Address: SAMRAKSHAN F- 4, I Floor, Swastik Manandi Arcade,
S C Road, Sheshadripuram,
Bangalore - 560 020.
Ph : 080-41466009
E mail id – [email protected], [email protected]
On the office memorandum of MOEF & CC no. F. No. J-l1013t7712004- lAll (l) Dated 2nd
December, 2009 regarding Accreditation of the EIA Consultants with Quality Council of India
(National Accreditation Board of Education and Training (NABET), the Honorable High Court
of Karnataka has been approached by Shri Nandakumar S and Hanumath Raj Urs. T.H in W.P
no. 12624-12625/2017 (GM-RES). The Honorable High Court has deferred the
implementation of impugned notification. Copy of the order high Court order dated 24-03-
2017 is enclosed.
11.1 INTRODUCTORY PROFILE
SAMRAKSHAN is a Bangalore, Karnataka based Environmental Engineering Consultancy
Company. SAMRAKSHAN is an off shoot of AQUATECH ENVIRO ENGINEERS, Bangalore. We
are leading solutions providers of B2B solutions in the field of Environment since two
decades. SAMRAKSHAN is a specialized solution providers, we serve varied industries like
Distillery, Sugar, Fertilizers, Pharmaceuticals, Power generation, Service industries, Common
waste disposal facilities etc.,
11.2 PROFESSIONAL SERVICES OFFERED:
We undertake works related to Pollution Control,
Environmental Impact Assessment studies
Preparation of Environmental Management plan
Design and execution of Effluent / wastewater and water treatment plants
Air pollution control and management
Solid and hazardous waste management
Due-diligence studies.
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Assists clients for implementation of conditions stipulated in the Environmental
Clearances, Consent to Establish and consent to operate issued by the Regulatory
agencies.
Assist clients in Environment related Project Management Consultancy.
Imparting training to the industries for Environment regulatory compliances.
Compliance report preparation.
We also undertake assisting clients in techno-legal issues before the Hon’ble High Court,
NGT and Supreme Court etc.,
KEY PERSONNEL OF THE ORGANISATION:
Name Qualifications Designation Experience
Mr. Nanda Kumar S
B E (Civil), PG
Diploma in
Ecology and
Environment, FIE
Chief Executive
Officer
37 Years at Karnataka State
Pollution Control Board
(Retired as CEO, KSPCB)
Dr. C T Puttaswamy
B E (Chem.,),
M Tech (Env.,),
Ph. D.,
Technical Advisor
20 Years’ experience in
industry, research and
development, environmental
consultancy and Teaching for
graduate and postgraduate
engineering courses.
Mr. Vasudevaiah
Technical Advisor
30 year experience in
chemical, water and Waste
Water, air samples analysis,
as senior Chemist in KSPCB
laboratory and retired from
Public Health Institute.
Mr. B Ramaiah
B E (Civil)
Technical Advisor
35 Years of service at
Karnataka State Pollution
Control Board (Retired as MS,
KSPCB)
Mr. G R Manjunath
B E (Mech.),
M Tech (Env.,)
Technical Advisor
16 years industrial and
environmental consultancy
Mr. Nandakishore
B E (Chem)
Technical Advisor
30 Years experience in
Pharmaceutical and related
industries.
Mr. Channakesava
B E (Env.,)
Sr. Manager -
Projects
15 Years in implementation
of Water, Wastewater
treatment plant from concept
to commissioning
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11.3 LABORATORY FOR ANALYSIS:
NAME OF LABORATORY SCOPE OF SERVICES ACCREDITATION STATUS
Nichrome Testing Laboratory
And Research Private
Limited,
No.170, Judges Bungalow
Road, Narayanpur, Dharwad-
580008, Karnataka, Ph.No.
0836 2771115 / 2778521
Fax: 0836 2770085
Monitoring and Analysis of:
1. Ambient Air Quality Monitoring
2. Ground and Surface Water Quality
Monitoring
3. Noise Level Monitoring and
4. Soil Quality Monitoring
Nichrome Testing
Laboratory And Research
Private Limited is a NABL
certified laboratory
Mr. Hanumanth Raj
Urs
M Sc (Env. Sce),
PGDIS
Sr. Manager -
Environment
12 Years experience in
environmental consultancy.
Mrs. Lakshmi L S
B E (Chem.,)
Chemical
Engineer
8 Years experience in
environmental consultancy.
Mrs. Rohini S
B E (Env.)
Environmental
Engineer
9 Years experience in
environmental consultancy.
Mr. Shreeshailacharya
Badiger
B E (Chem.,) Chemical
Engineer
7 Years experience in Pharma
production and consultancy.
Ms. Pooja M D
B E (Env.)
Environmental
Engineer
3 Years experience in
environmental consultancy
Mrs. Rachana J
B E (Env.)
Environmental
Engineer
1 Year experience in
environmental consultancy
Mr. Santhosh
M A (Economic)
Admin and
Logistic Manager
10 Years experience in
administration and logistics.
Mr. Suresh PUC Project Assistant 4 years experience