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VISAKA INDUSTRIES LIMITED - (PROPOSED PROJECT)
Location: Rachakpura Village, Shedriya Grampanchayat, Niwai Tehsil, Tonk District, Rajasthan.
PRODUCTION CAPACITY
Asbestos Cement Sheets - 2, 16,000 TPA
“NO VIOLATION”
FOR
ENVIRONMENT CLEARANCE
("A" of 4 (c) of Gazette Notification dated 14.06.2006 and its subsequent amendment dated
01.12.09 & 04.04.2011) { Asbestos milling and asbestos based products }
Study Period (Pre Monsoon) – March, April & May’ 2013
Proposed Project Cost: 56.62 Crores.
AUTHORIZED SIGNATORY
Mr. S.R.Warrier
Mobile No. 9959553719
ENKAY ENVIRO SERVICES PVT. LTD.
(An ISO 9001:2008 Certified Firm) (Serial no. 43 as per the List of Accredited EIA Consultant Organizations as on January 05, 2014)
Corporate Office: L-G-6, Corporate Park, Gopal Bari, Ajmer Road, Jaipur Phone: - 0141-2363996, 4023996, Fax:-5118996
Email- [email protected], Website: www.enkayenviro.com
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
1
FORM-1
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
2
APPENDIX I
(See Paragraph – 6)
FORM - 1
I Basic Information
S. No. Item : Details
1. Name of the Project/s : Visaka Industries Ltd., Proposed asbestos cement sheets
manufacturing project.
2. S. No. in the schedule : The proposed unit is categorized under 4 (c) 3 of Gazette
Notification dated Sep 14th, 2006 and subsequent
amendments on 01.12.09 and 04.04.2011 {Asbestos milling
and asbestos based products}. The same is categorized as
“A” category.
3. Proposed
capacity/area/
length/tonnage to be
handled /command
area/lease area
/number of wells to be
drilled
:
The unit is coming up at Rachakpura Village, Shedriya
Grampanchayat, Niwai Tehsil, Tonk District, Rajasthan State
Total area allotted is 22.5 Acres.
Proposed Capacity
Asbestos cement sheets: 2,16,000 TPA
4. New / Expansion /
Modernization
: This is a new unit.
5. Existing capacity/Area
etc.
: No
6. Category of project i.e.
'A' or 'B'
: A
7. Does it attract the
general condition? If
yes, please specify.
: No
8. Does it attract the
specific condition? If
yes, please specify.
: No
9. Location
Plot / Survey / Khasra
no.
: Visaka Industries Ltd.,
Rachakpura Village, Shedriya Grampanchayat,
Niwai Tehsil, Tonk District,
Rajasthan.
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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Village / Town : Rachakpura
Tehsil : Niwai
District : Tonk
State : Rajasthan
10. Nearest Railway
station/Airport along
with distance in KM.
: Railway Station: Siras Railway Station
Distance: 19.36 km towards south.
Airport: Jaipur Airport
Distance: 47.21 km towards NNW.
NH – 11 A: Distance: 7.27 km North.
Saidariya Khurd Town: Distance 1.0 Km South-West
11. Nearest Town, City,
District Headquarters
along with distance in
kms.
: Saidariya Khurd,1.0 km SW
12. Village Panchayat, Zilla
Parishad, Municipal
Corporation, Local
body (Complete postal
address with telephone
no. to be given)
: Gram Panchayat - Shedriya,
Tehsil- Niwai
Distt. – Tonk, Rajasthan.
13. Name of the applicant : Mr. S.R.Warrier
14. Registered address : Mr. S.R.Warrier
Visaka Towers,
69/3, S,P. ROAD,
Secunderabad – 500 003 AP
15. Address for correspondence:
Name : Mr. S.R.Warrier
(Assistant General Manager)
Designation (Owner/ Partner
/CEO)
: Assistant General Manager
Address : Visaka Towers”, 1-8-303/69/3
Sardar Patel Road, Secunderabad – 500 003,Andhra
Pradesh.
Pin Code : --
E-mail : [email protected]
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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Telephone no. : 9959553719
Fax No. : --
16. Details of alternative sites
examined, if any. Location of
these sites should be shown
on a Toposheet.
: No
17. Interlinked projects : No
18. Whether separate application
of interlinked project has
been submitted?
: No
19. If yes, date of submission : No
20. If no, reason : No
21. Whether the proposal
involves approval/Clearance
under: if yes, details of the
same and their status to be
given.
(a) The Forest
(Conservation) Act,
(1980)?
(b) The Wildlife (Protection)
Act, 1972?
(c) The C.R.Z. Notification,
1991?
: No
22. Whether there is any
Government Order/Policy
relevant/relating to the site:
: No
23. Forest land involved
(hectares)
: No
24. Whether there is any litigation
pending against the project
and/or land in which the
project is propose to be set
up?
(a) Name of the Court
(b) Case No.
: No litigation is pending in court of law to the best of our
knowledge.
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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(c) Orders/directions of the
court, if any and its
relevance with the
proposed project.
25. Expected cost of the project : The total project cost estimated is Rs 56.62 Crores
*Capacity corresponding to sectoral activity (such as production capacity for manufacturing, mining
lease area and production capacity for mineral production, area for mineral exploration, length for linear
transport infrastructure, generation capacity for power generation etc.,)
II Activity
1. Construction, operation or decommissioning of the Project involving actions,
which will cause physical changes in the locality (topography, land use, changes in
water bodies, etc.)
S.
No.
Information/Checklist
confirmation
Yes/
No
Details thereof (with approximate quantities
/rates, wherever possible) with source of
information data
1.1 Permanent or temporary
change on land use, land
cover or topography
including increase in
intensity of land use (with
respect to local land use
plan)
Yes Land use:
The proposed project is coming up in village
Rachakpura, Shedriya Grampanchayat, Niwai Tehsil,
Tonk District, Rajasthan. The land use of the site is
converted for industrial purpose. Thus, the proposed
project has impact on the land use of the site.
Land Cover: There will be scrapping of soil during
constructional activities which will be balanced within
the project site itself. The land cover will be changed
at local level and will have insignificant impact on the
study area.
Topography: The project is coming up on agricultural
land converted for industrial purpose. The topography
of the site is almost flat while during construction
further leveling will be required.
1.2 Clearance of existing
land, vegetation and
buildings?
Yes Vegetation:-
Currently, there is no significant vegetation at the site
except for few herbs and grasses such as, Calotropis
procera, Parthenium hysterophorus, Saccharum
munja, , Argemone maxicana, Cynodon dactylon,
Amaranthus spinosus, Dactyloctenium aegyptium and
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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Tribulus terrestris present at the site. Thus, no
physical changes is envisaged due to clearance of
locality will be insignificant
Buildings:-
There is no structure existing at the site.
1.3 Creation of new land
uses?
Yes The land use of the site has been changed from
agricultural use to industrial purpose. The land use
breakup of the site is given below:-
S. No.
Particulars Area (sq. m)
(%)
1. Plant area, office area 36421.6 40% 2. Road area 10015.94 11% 3. Green belt 30047.82 33% 4. Open area 14568.64 16%
Total 91054 100 %
1.4 Pre-construction
investigations e.g. bore
houses, soil testing?
No Soil testing will be carried out, as it is a pre-requisite
for assessing the soil characteristics for designing the
structure of the building. This will not cause any
changes in the physical environment.
1.5 Construction works? No The proposed unit will have concrete work for the
construction of work shed, waste storage room, raw
material storage room; D.G. set room, office, lab,
machine room, etc. within the project area. The
overall impact towards physical environment will be
insignificant.
1.6 Demolition works? No --
1.7 Temporary sites used for
construction works or
housing of construction
workers?
Yes There will be no temporary sites created as the labour
deployed will be local.
Temporary storage yard will be provided for the
storage of construction material.
Temporary sheds and hutments will be constructed
for watchman during the construction phase, which
will have localized and temporary impact on physical
environment.
1.8 Above ground buildings,
structures or earthworks
including linear structures,
cut and fill or excavations
Yes The road area will not require any excavation because
land is leveled.
Erection of building will change the view of the site.
The project will also involve excavation of soil during
foundation purposes. The excavated soil will be
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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utilized within the site by balancing with scrap and fill
operations.
1.9 Underground works
including mining or
tunneling?
No No
1.10 Reclamation works? No _
1.11 Dredging? No --
1.12 Offshore structures? No --
1.13 Production and
manufacturing
processes?
Yes The proposed unit will manufacture 2, 16,000 TPA of
Asbestos cement sheets.
The basic raw material required for the manufacturing
of asbestos cement sheets will be cement, fiber, fly
ash and pulp.
The complete process will be done through a closed
circle.
All pollution control measures will be inaugurated.
The proposed manufacturing process will not
contribute any significant changes in the physical
environment. The flow chart showing the complete
manufacturing process is given in Section-II of
EIA/EMP report.
1.14 Facilities for storage of
goods or materials?
Yes Construction Phase: Temporary storage yard will be
provided for the storage of construction material.
Storage yard will be covered from all the sides.
Operation Phase: During operation phase, the
asbestos fiber bags will be stored in storage area.
Other raw materials viz., cement, fly ash, and fibers
will be received in bags and stored in storage area
and will be transported through belt/conveyor/hand
trolley to plant from the storage area. Storage of the
raw materials will be done in their respective godowns
in the factory shed. Due to these facilities changes
towards physical environment will be insignificant.
1.15 Facilities for treatment or
disposal of solid waste or
liquid effluents?
Yes Construction phase:-
Solid waste:-
Construction waste will be generated, out of which:-
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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• Recyclable waste (metal) will be sold to the
vendors.
• The inert waste (brick, masonry, aggregates
concrete etc.) will be used for making of roads,
loading & unloading area.
Liquid effluents:-
Domestic waste water will be generated to the tune of
10.5 KLD. The same will be treated in STP.
Liquid effluents:-
During industrial process, water will be recycled and
reused again in the manufacturing process.
Waste water generated from the domestic purposes
will be to the tune of 10.5 KLD.
1.16 Facilities for long term
housing of operational
workers?
No There will be no provision made for workers within the
area; however labours employed will be from local
area.
1.17 New road, rail or sea
traffic during construction
or operation?
No --
1.18 New road, rail, air
waterborne or other
transport infrastructure
including new or altered
routes and stations, ports,
airports etc?
No The development in terms of infrastructure will be
very minimal and the impact related to the same will
be negligible.
1.19 Closure or diversion of
existing transport routes
or infrastructure leading to
changes in traffic
movements?
No --
1.20 New or diverted
transmission lines or
pipelines?
No --
1.21 Impoundment, damming,
culverting, realignment or
other changes to the
No --
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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hydrology of
watercourses or aquifers?
1.22 Stream crossings? No --
1.23 Abstraction or transfers of
water from ground or
surface waters?
Yes Daily fresh water demand for the proposed project is
around 240 KLD. The water demand will be met from
borewell. The application for NOC from CGWA has
been submitted.
1.24 Changes in water bodies
or the land surface
affecting drainage or run-
off?
No There will be no change in the surface run-off and
drainage of the area as the slope of the site will not be
altered. The project will involve construction of paved
areas and hence, quantity of run-off will increase due
to reduced infiltration. The runoff will be harvested
through well designed storm water pipe network of
rain water harvesting and will be used for recharge of
the aquifers.
1.25 Transport of personnel or
materials for construction,
operation or
decommissioning?
Yes The transportation of raw materials for construction,
operation and products to desired destination will be
carried out by trucks. Daily movement of local labours
will be there. The local employment will be preferred.
Thus, the impact will be negligible.
1.26 Long-term dismantling or
decommissioning or
restoration works?
No --
1.27 Ongoing activity during
decommissioning which
could have an impact on
the environment?
No --
1.28 Influx of people to an area
in either temporarily or
permanently?
Yes During construction phase there will be influx of semi-
skilled and unskilled labour from the nearby villages
and during operation phase there will be influx of staff
members from nearby villages.
1.29 Introduction of alien
species?
No --
1.30 Loss of native species or
genetic diversity?
No --
1.31 Any other actions? No --
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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2. Use of Natural resources for construction or operation of the Project (such as land,
water, materials or energy, especially any resources which are non-renewable or in
short supply):
Information/checklist
confirmation
Yes /
No
Details thereof (with approximate quantities /rates,
wherever possible) with source of information
data
2.1 Land especially
undeveloped or
agricultural land (ha)
Yes The proposed project will cover the maximum
Agriculture topography of 10 km of study area The
land use pattern is indicated in the previous section as
well as in prefeasibility report (Section–I and Section-
III).
2.2 Water (expected source &
competing users) unit:
KLD
Yes The daily fresh water requirement for the proposed
project is 240 KLD. Out of 240 KLD water, industrial
water demand is 225 KLD while 15 KLD water is
required for domestic purposes. During the industrial
process water will be used for slurry formation and
curing purposes. The application for NOC from
CGWA has been submitted
2.3 Minerals (MT) No --
2.4 Construction material –
stone, aggregates, sand /
soil (expected source –
MT)
Yes The site will have concrete work. The building
materials will be coarse aggregate, fine aggregate,
structural steel, bricks, etc. Quantity depends upon
the design criteria.
2.5 Forests and timber
(source – MT)
No --
2.6 Energy including
electricity and fuels
(source, competing users)
Unit: fuel (MT), energy
(MW)
Yes Energy: The total power demand for the proposed
unit will be 750 kVA, which will be supplied from
Rajasthan State Electricity Board.
Fuel: Two D.G. sets of 500 kVA each will be installed
for the complete power back up. The proposed project
area has continuous 24 hours power supply hence, no
diesel will be used during these hours. However, in
case of electricity cut there would be consumption of
around 40 l/hr of fuel per D.G. set.
2.7 Any other natural
resources (use
No --
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
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appropriate standard
units)
3. Use, storage, transport, handling or production of substances or materials, which
could be harmful to human health or the environment or raise concerns about
actual or perceived risks to human health.
S.
No.
Information/Checklist
confirmation
Yes
/
No
Details thereof (with approximate quantities/rates,
wherever possible) with source of information
data
3.1 Use of substances or
materials, which are
hazardous (as per MSIHC
rules) to human health or
the environment (flora,
fauna, and water
supplies)
Yes The proposed unit is an asbestos cement sheets
manufacturing unit. Asbestos will be used as raw
material, which is hazardous in nature. Asbestos may
cause serious health problems like Asbestosis to the
workers if not treated properly. Following measures
will be taken during work with asbestos fiber:
Closed loop manufacturing process
Automatic bag opening machine
Wear protective clothing and an approved respirator.
Use of vacuum cleaner to clean up the spills/fugitive
emissions.
Thus, asbestos fiber will not be harmful to human
health & environment.
3.2 Changes in occurrence of
disease or affect disease
vectors (e.g. insect or
water borne diseases)
No Proper sanitation facilities will be provided to avoid
insect and water borne disease.
3.3 Affect the welfare of
people e.g. by changing
living conditions?
Yes The proposed project would have positive impact on
the socio-economic status, thus contributing to the
growth of the nearby area.
Increased employment opportunities
Indirect employment: for truck drivers
Periodic medical check-up.
Wages will be provided as per norms.
Appropriate pollution control equipments will be
followed.
The proposed is a long-standing project thus, would
serve as a stable source of employment.
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3.4 Vulnerable groups of
people who could be
affected by the project
e.g. hospital patients,
children, the elderly etc.,
No --
3.5 Any other causes No --
4. Production of solid wastes during construction or operation or decommissioning
(MT/month)
S.No. Information/Checklist
confirmation
Yes
/
No
Details thereof (with approximate quantities/rates,
wherever possible) with source of information
data
4.1 Spoil, overburden or mine
wastes
No --
4.2 Municipal waste
(domestic and or
commercial wastes)
No --
4.3 Hazardous wastes (as per
Hazardous Waste
Management Rules)
Yes S.No. Waste Source Quantity MT
1. Empty Fibre
Bags (Category
15.1)
Auto Bag
Opening Device
(BOD)
0.080
2. Fibre Dust
(Category 15.3
From Dust
Collector
attached to ER
Mill & BOD
0.012
3. Cement & Fly
ash Dust
From Dust
Collector
attached to
Cement feeding
& FA feeding
point.
0.100
4. Process Sludge
(Category 15.1)
From Week-end
Tank
0.100
5. Hard Broken
Pieces
(Category 15.1)
Sheet damages
& rejects
9.000
4.4 Other industrial process
wastes.
Yes Sludge generated from the process will be about
0.209 MT, which will be Continuously recycled though
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the Wet Ball Mill in slurry forms.
4.5 Surplus product. No --
4.6 Sewage sludge or other
sludge from effluent
treatment.
No --
4.7 Construction or demolition
wastes.
No Demolition Wastes: There is no structure at the site;
hence no demolition waste will be generated.
Construction Waste: Construction waste will be
generated out of which recyclable waste (metal) will
be sold to the vendors. The inert waste (brick,
concrete, masonry, aggregates etc.) will be used for
making of driveway & pathway within the site.
4.8 Redundant machinery or
equipment.
No --
4.9 Contaminated soils or
other materials.
No --
4.10 Agricultural wastes. No --
4.11 Other solid wastes. Yes • Empty asbestos fiber bags will be kept in separate
area and send to the vendors.
• Fibre Dust will be periodically recycled after the
container containing water and placed beneath the
rotary valve of the Dust Collector is adequately
filled in.
• Broken pieces will be continuously recycled though
the wet ball mills in slurry form.
5. Release of pollutants or any hazardous, toxic or noxious substances to air (Kg/hr)
S.
No.
Information/Checklist
confirmation
Yes /
No
Details thereof (with approximate quantities/rates,
wherever possible) with source of information data
5.1 Emissions from
combustion of fossil fuels
from stationary or mobile
sources.
Yes In the proposed unit, emissions from combustion of
fossil fuels will be from D.G. set and transportation. To
control the emission of exhaust gas following
measures will be adopted :-
S.No Source Management
1. 2 D.G. sets
(500 kVA each)
The D.G. set will be provided
with adequate safe stack height
of 10 m above the roof of the
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D.G. house to regulate the
emission within the permissible
norms.
2. Transportation. Plantation will be done at the
periphery of the proposed
project and local drought
resistive plant will be planted.
33.50% area will be under
plantation. PUC checked
vehicles will be used.
5.2 Emissions from
production processes.
Yes The complete process will be carried out in a closed
loop. The fugitive sources of dust emission will be from
asbestos bag opening, raw material mixing, storage of
the raw material and area emission will be from main
cement silos & transfer lines. The fugitive areas
emissions will be routed through bag filters to control
the pollutants well within the norms. There will be
automatic bag opening devices for opening of
asbestos bags. Air separation unit will be used for
nitrogen.
5.3 Emissions from materials
handling including
storage or transport
Yes
The material handling including storage and
transportation will contribute to fugitive emissions. The
materials will be stored in a closed room to contain the
emission.
• The raw asbestos will be received in pressure
packed and sealed bags. It will be used in moist
form to avoid air borne. The asbestos bags will be
opened in a separate machine in which complete
bag will be fed into the machine and asbestos fiber
will be transferred to the process without any
contact with the workers and atmosphere.
• Cement will be received in bags & stored in the
cement silo, weighed in hopper by automatic
weighing scale and charge into cement conveyor.
• The processing of the asbestos will be done in a
Kollargang, which will be totally sealed and water
will be sprinkled immediately in the machine to
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detain any air borne asbestos fiber.
• There will be provision of dust collectors for
detaining any dust emanating in the process.
To control the fugitive emissions in proposed unit,
following measures will be adopted:-
• The entire process of asbestos cement sheets
will be in closed loop.
• Covered Conveyor belt system will be used for
the conveying of the materials. Hence, it will help
to avoid the dust emission from the process and
contact with workers.
• Storage and material handling areas will be
enclosed to prevent loose material from
becoming air borne.
• All equipments and valves will be maintained
properly.
• In plant training will be provided to the plant
personnel on operation and maintenance of dust
collectors, techniques of dust emission
measurements, particle size analysis etc.
• Storage of the raw materials will be done in their
respective godowns in the factory shed.
• Automatic bag opening devices will be installed.
• All transportation vehicles will be suitably
covered with tarpaulin & overloading of the
vehicles will be avoided.
• Cleaning all mud and dirt deposited on roads
from construction-related activities.
• 33.50% green area will be developed.
Ambient air quality and stack emissions will be
regularly monitored to ensure that ambient air quality
standards and suggested limits of the stack emission
loads are met honestly all the time.
5.4 Emissions from
construction activities
including plant and
Yes Fugitive dusts from various activities of construction
are expected, which will be temporary in nature.
The fugitive dust emission sources are:
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equipment 1.Construction operation
Construction operations are significant source of
dust emissions that may have a substantial
temporary impact on local air quality.
Particulate dust emissions from the construction are
a function of total land disturbed and the volume of
soil excavated.
The emission factor will be around 0.062
kg/sq.m./month.
2.Road Construction
Particulate dust emission from road construction
activities are function of the total land disturbed
during construction. The road constructed is used to
estimate the total area disturbed using conversion
factors for area disturbed/road constructed, as a
function of road type.
The emission factor will be around 0.027
kg/sq.m./month.
5.5 Dust or odours from
handling of materials
including construction
materials, sewage and
waste.
Yes Construction phase:-
During the construction of plant area/office area, dust
will be generated to the tune of 0.062 kg/sq.m./month.
During the construction of road, same will be
generated to the tune of 0.027 kg/sq.m./month.
Operation phase:-
During manufacturing process, fibre dust will be
generated to the tune of 0.012 MT.
Sludge generated from the process will be about 0.209
MT, which will be continuously recycled though the
Wet Ball Mill in slurry form.
In the proposed unit, during construction & operation
phase there will be no odour problem.
5.6 Emissions from
incineration of waste
No --
5.7 Emissions from burning
of waste in open air (e.g.
slash materials,
construction debris)
No --
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5.8 Emissions from any other
sources
No --
6. Generation of Noise and Vibration, and Emissions of Light and Heat:
S.
No.
Information/Checklist
confirmation
Yes/
No
Details thereof (with approximate quantities/rates,
wherever possible) with source of information
data
6.1 From operation of
equipment e.g. engines,
ventilation plant, crushers
Yes Major sources of noise pollution will be pumps,
machinery, D.G. sets, etc. Following measures will be
adopted to control the noise and vibration:-
• Foundations and structures will be designed to
minimize vibrations and noise.
• The insulation provided for prevention and loss of
heat and personal safety shall also act as noise
reducer.
• Necessary safety and personal protective
equipment such as ear plugs, ear muffs, helmet
etc. will be provided to the workers.
• Noise levels generated will be maintained to
comply with the Factories Act & Rules and will not
exceed 75 dB (A) at 1 m distance.
• Implementation of green belt (33.50%) within the
premises of plant will help to absorb the noise.
• The D.G. set used will be eco-friendly with
minimum noise.
• Proper lubrication and housekeeping will be
usually done to avoid excessive noise generation.
6.2 From industrial or similar
processes
Yes During industrial process pumps, motors & machinery
will be used. Same will be source of noise in the unit.
6.3 From construction and
demolition
Yes Noise will be generated from the operation of
machineries.
6.4 From blasting or piling No --
6.5 From construction or
operational traffic
Yes During the construction phase, noise will be
generated from movement of vehicles, earth work,
cement mixer, etc. The construction site will be
shielded to avoid the noise propagation and
transportation of the material & machineries will be
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18
done at the peak time of the day.
During operation phase, raw material and products
are transported at the peak time of the day.
PUC checked vehicle is used for transportation
purposes.
6.6 From lighting or cooling
systems
No --
6.7 From any other sources No --
7. Risks of contamination of land or water from releases of pollutants into the ground
or into sewers, surface waters, groundwater, coastal waters or the sea:
S.
No.
Information/Checklist
confirmation
Yes/
No
Details thereof (with approximate quantities/rates,
wherever possible) with source of information
data
7.1 From handling, storage,
use or spillage of
hazardous materials
No The chrysotile type asbestos fiber will be received in
pressure pack and sealed bags. It will be used in
moist form to avoid air borne of the fibers. It will be
imported from Brazil, Canada and Russia. The
asbestos bags will be opened in a separate machine
in which complete bag will be fed into the machine
and asbestos fiber will be transferred to the process
without any contact with the workers and atmosphere.
There will be facilities for the storage of raw material
as well as product.
7.2 From discharge of
sewage or other effluents
to water or the land
(expected mode and
place of discharge)
No There will be no industrial waste water generated from
the proposed unit; only domestic waste water (10.5
KLD) generated, which will be treated in STP.
7.3 By deposition of pollutants
emitted to air into the land
or into water
No The sources of air emission in the unit are both area
and point. The flue gas emitted from the main cement
silo, transfer line, asbestos bag opening, etc. will be
routed into the atmosphere, the dust deposited on
land and water in near areas will be polluted.
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19
Measures will be applied to control the emission of
pollutants.
1. Air
Bag filters (pulse jet) will be installed at fiber dust
collector, cement & fly ash dust collector and
pulverizor dust collector. The height and diameter of
the chimney will be selected in such a way that
chimney will have a velocity sufficient to avoid any
down wash and ensure proper dispersion. Thus will
not cause deposition on land or water body.
2. Water
Domestic waste water will be treated in STP.
3. Land
There will be hazardous waste generated in the form
of asbestos containing residues (category - 15.1 &
15.3). The waste generated will be basically from
rejected, cracked, broken sheets, dust from the bag
filters. However, these solid wastes will be Shredded ,
Periodically recycled through Wet Ball Mill in slurry
form. The same will be stored in the isolated area
and will be disposed off by pulverizing the same and
re-used in the process.
Sludge generated from the process will be about 0.209
MT, which will be Continuously recycled though the
Wet Ball Mill in slurry form.
7.4 From any other sources No --
7.5 Is there a risk of long term
build up of pollutants in
the environment from
these sources?
No
Adequate pollution control equipments will be
installed which will keep the emission within the level
as per the norms.
8. Risk of accidents during construction or operation of the Project, which could
affect human health or the environment
S.
No.
Information/Checklist
confirmation
Yes/
No
Details thereof (with approximate quantities/rates,
wherever possible) with source of information
data
8.1 From explosions, Yes For protection of the plant, following measures will be
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
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20
spillages, fires etc from
storage, handling, use or
production of hazardous
substances
adopted:-
• On-site emergency preparedness plan and Off-site
emergency preparedness plan has been prepared.
• All precautionary measures will be adopted and
use of protective footwear and helmet will be
mandatory.
• Fire extinguisher will be installed at strategic points
all over the premises, checked at regular intervals
and a record will be made and maintained.
• First aid facilities will be provided for the staff
personals.
• One vehicle will always be on standby for
immediate transport.
• The workers will be provided with the training for
the first aid measures in case of accident.
• The asbestos fiber will be received in pressure
packed and sealed bags.
• The fiber bags will be stacked on pallets and
carried in closed vehicles.
• The bags will contain warning label incorporating
the "A" symbol.
• Hooks and other sharp equipment will not be used
on bags or unit loads.
• A vacuum cleaner will be used for cleaning or
surfaces will be thoroughly wetted before
sweeping.
• All damaged bags will be repaired with adhesive
tape and if need be, placed in a second
impermeable bag, which will be sealed properly
and kept separately for use.
• All units having loose asbestos or other debris on
the bag will be cleaned as soon as possible by
vacuum cleaner.
• The storage area of asbestos fiber will bear the
Warning sign label.
• PPE’s (respirators, ear plug, noise muff and
PROJECT: VISAKA INDUSTRIES LTD FORM- 1
DOCUMENT NO: EESPL/VIL/002/358-EC/IND/2013
21
helmet) will be mandatory for the workers.
• However, to meet out the minor incidences and
accidents first aid measures will be provided at
site.
• Dust may create nuisance for the labours.
Therefore, bag house will be installed to control
the dust emission.
• Medical check-up of the workers will be done
periodically.
• The asbestos bags will be placed on pallets very
nearer to the feed chamber. The fiber bags will be
opened and emptied manually in hydro pulper.
• Exhaust ventilation with negative pressure will be
maintained within the enclosure.
• All spills from the broken fiber bags and on the
floor will be cleaned by vacuum hose. If the spill is
more personal protective item like protective
clothing and respirators will be used during
cleaning/ retrieving operation.
8.2 From any other causes No Good construction safety practices will be applied
such as precautionary measures, protective footwear,
helmet. First aid measures at site will be provided in
order to meet out minor incidences and accidents.
Bag house will be installed to control the dust
emission. Medical check-up will be carried out
periodically.
8.3 Could the project be
affected by natural
disasters causing
environmental damage
(e.g. floods, earthquakes,
landslides, cloudburst
etc)?
No --
9. Factors which should be considered (such as consequential development) which
could lead to environmental effects or the potential for cumulative impacts with
other existing or planned activities in the locality
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22
S.
No.
Information/Checklist
confirmation
Yes /
No
Details thereof (with approximate
quantities/rates, wherever possible) with
source of information data
9.1 Lead to development of
supporting cities, ancillary
development or
development stimulated
by the project which could
have impact on the
environment e.g.:
• Supporting
infrastructure (roads,
power supply, waste
or waste water
treatment, etc.)
• housing development
• extractive industries
• supply industries
• other
Yes The proposed project would lead to large scale,
long term stable employment opportunities leading
to standard of living and housing renovation and
development in the study area.
9.2 Lead to after use of the
site, which could have an
impact on environment
No --
9.3 Set a precedent for later
developments
No --
9.4 Have cumulative effects
due to proximity to other
existing or planned
projects with similar
effects
No --
II Environmental Sensitivity (within 15 km radius) –
S.
No.
Areas Name/
Identity
1 Areas protected under
international conventions,
national or local
None There are no archeological protected monuments
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23
legislation for their
ecological, landscape,
cultural or other related
value
2 Areas which are important
or sensitive for ecological
reasons - Wetlands,
watercourses or other
water bodies, coastal
zone, biospheres,
mountains, forests
None --
3 Areas used by protected,
important or sensitive
species of flora or fauna
for breeding, nesting,
foraging, resting, over
wintering, migration.
None --
4 Inland, coastal, marine or
underground waters
None --
5 State, National
boundaries
None --
6 Routes or facilities used
by the public for access to
recreation or other tourist,
pilgrim areas
Yes Railway Station: Siras Railway Station
Distance: 19.36 km towards south.
Airport: Jaipur Airport
Distance: 47.21 km towards NNW.
NH – 11 A: Distance: 7.27 km North.
Saidariya Khurd Town: Distance 1.0 Km South-
West
7 Defense installations None --
8 Densely populated or
built-up area
Yes Niwai
9 Areas occupied by
sensitive man-made land
uses (hospitals, schools,
places of worship,
community facilities)
Yes Hospitals, Educational institution facilities are as
follows in the study area :
Medical Facilities: PHC Mundiya 7.3 km W,
Aaganbadi Munidya 7.4 km W; Aaganbadi
Bhanwati 4.3 km SW; PHC Bhanwati 4.4 km SW;
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24
Aaganbadi Lalwari 3.2 km ESE; Upswastha
Kendra Lalwari 3.2 km ESE; Upswastha Kendra
Shedriya 1.8 km NW;
Educational Facilities: Jeevan Jyoti Madhyamik
Vidhyalya, Bhanwata 3.2 km SW; Rajkiya
Madhyamik Vidhyalya Mundiya 6.0 km SW;
Rajkiya Adarsh Uchh Prathmik Vidhyalya, Lalwari
3.5 km ESE, Rajkiya Uchh Prathmik Vidhyalya,
Shedriya 1.7 km NW ; Sandeep Convent School,
Mundiya 6.3 km SW ; Rajkiya Ucch Prathmik
Vidhyalya , Kishorpura 2.0 km NE
Religious places: Bhairon ji ka Baagh 1.6 km NE
Market Places: Unorganasied market place is in
Dahlod 3.4 km NE, Shedriya 2.0 km NW, but for
organized market place villagers commute to
Niwai.
10 Areas containing
important, high quality or
scarce resources (ground
water resources, surface
resources, forestry,
agriculture, fisheries,
tourism, minerals)
None --
11 Areas already subjected
to pollution or
environmental damage.
(those where existing
legal environmental
standards are
exceeded)
None --
12 Areas susceptible to
natural hazard which
could cause the project to
present environmental
problems (earthquakes,
None The area is falling in Zone- II, Low Damage Risk
Zone (MSK VI or less).
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25
subsidence, landslides,
erosion, flooding or
extreme or adverse
climatic conditions)
"I hereby given undertaking that the data and information given in the application and
enclosure are true to the best of my knowledge and belief and I am aware that if any part of
the data and information submitted is found to be false or misleading at any stage, the
project will be rejected and clearance give, if any to the project will be revoked at our risk
and cost.
Date:
Place:
Mr. S.R.Warrier
(Assistant General Manager)
Visaka Industries Ltd
Rachakpura Village,
Shedriya Grampanchayat, Niwai Tehsil,
Tonk District,
Rajasthan
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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SECTION- I
INTRODUCTION
INDEX
INTRODUCTION ...................................................................................................... 26
1.1 PREAMBLE ..................................................................................................... 27
1.2 GENERAL INFORMATION ON ASBESTOS INDUSTRIES ............................ 28
1.3 ENVIRONMENTAL CLEARANCE PROCESS ................................................ 28
1.4 TERMS OF REFERENCE ............................................................................... 30
1.5 GENERIC STRUCTURE OF ENVIRONMENTAL IMPACT ASSESSMENT ... 43
1.6 POST ENVIRONMENTAL CLEARNCE MONITOIRNG ................................. 44
1.7 IDENTIFICATION OF PROJECT PROPONENT ............................................ 44
1.8 BRIEF DESCRIPTION OF THE PROJECT ................................................... 44
1.9 LOCATION OF THE PROJECT ..................................................................... 44
1.10 ENVIRONMENTAL SETTING OF THE PROJECT SITE .............................. 47
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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INTRODUCTION 1.1 PREAMBLE
The word "Environment" is most commonly used describing "Natural" environment and
means the sum of all living and non-living things that surround an organism, or group of
organisms. Environment includes all elements, factors, and conditions that have some
impact on growth and development of certain organism. Environmental management is a
way to reach out for environmental conservation, which consolidates ecology, policy making,
planning and social development.
Environmental Impact Assessment (EIA) is a process of evaluating the likely environmental
impacts of a proposed project or development, taking into account inter-related socio-
economic, cultural and human-health impacts, both beneficial and adverse.
Environmental Impact Assessment (EIA) studies need a significant amount of primary and
secondary environmental data. Primary data are those collected in the field to define the
status of the environment (like air quality data, water quality data etc.). Secondary data are
those collected over the years that can be used to understand the existing environmental
scenario of the study area.
The eight steps of the EIA process are presented in brief below:
• Screening: First stage of EIA, which determines whether the proposed project,
requires an EIA and if it does, then the level of assessment required.
• Scoping: This stage identifies the key issues and impacts that should be further
investigated. This stage also defines the boundary and time limit of the study.
• Impact analysis: This stage of EIA identifies and predicts the likely environmental
and social impact of the proposed project and evaluates the significance.
• Mitigation: This step in EIA recommends the actions to reduce and avoid the
potential adverse environmental consequences of development activities.
• Reporting: This stage presents the result of EIA in a form of a report to the decision-
making body and other interested parties.
• Review of EIA: It examines the adequacy and effectiveness of the EIA report and
provides the information necessary for decision-making.
• Decision-making: It decides whether the project is rejected, approved or needs
further change.
• Post monitoring: This stage comes into play once the project is commissioned. It
checks to ensure that the impacts of the project do not exceed the legal standards
and implementation of the mitigation measures are in the manner as described in the
EIA report.
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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1.2 GENERAL INFORMATION ONASBESTOSINDUSTRIES
The word ‘asbestos' has been derived from the Greek word meaning "indestructible"or
"inextinguishable". The very meaning reflects the durability of thematerial. This property of
asbestos resists its erosion against dust and rain, andthus prompted civilization to use it
where durability is needed. There are a large number of asbestos products manufacturing
industries in India,both in large and medium scale sectors. These industries are spread over
in aboutfifteen major states. Nearly sixty units are in operation. However, significantamount
of small scale sector and unorganized sector are located around the majorurban centers. In
India, mostly asbestos are used in non-friable and cementations products.The major raw
materials which will be used in the manufacturing of asbestos cement sheets are ordinary
portland cement, fiber, fly ash and pulp.The Asbestos used by the proposed unit will be
Chrysotile (also known as white asbestos).Asbestos is used in the building industry because
of its inexpensive processing and its special chemical and physical properties which makes it
quite strong and durable. Asbestos is a fibrous silicate mineral that maintains chemical
resistance especially to alkalis, fire resistance, mechanical strength due to the fibers’ high
length to diameter ratio, flexibility, and good friction and wear characteristics. While used
separately in many successful applications, asbestos and cement are combined to form an
innovative new building material. The project is proposed for its advantages of Asbestos-
cement products such as its durability, fire resistance, and ease in processing; forming,
installing, and overall economic benefits and its use in a host of applications like Asbestos
cement roof, etc.
The asbestos cement sheet industry recorded a growth of 10 to 12% yearly in India. Experts
believe that the high growth rates clocked by the sector have been mainly possible due to
the sustained demand in the rural sector, which accounts for over 50% of the market for the
asbestos industry.
The proposed project aims to fill the gap between the demand and supply of Asbestos
cement sheetsin the region. The Asbestos cement industry has witnessed continuous
modernization and adoption of new technologies in recent years. Hence, the project is
proposed to be an automized unit to encompass all technical and social advantages in the
region and also contribute (though marginally) in the stabilization of its prices through
fulfilling required supply.
1.3 ENVIRONMENTAL CLEARANCE PROCESS
The proposed unit is categorized under 4 (c) 3 of Gazette Notification dated Sep 14th, 2006
and subsequent amendments on 01.12.09 and 04.04.2011 {Asbestos milling and
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
Document No.:EESPL/VIL/002/358-EC/IND/2013
asbestosbased products}. The same is categorized as “A” category. These stages in
sequential order are:-
1. Scoping
2. Public consultation
3. Appraisal
The flow chart depicting these stages to obtain the prior Environmental Clearance for the
existing project is as given below:--2006 is as under:-
Figure 1.1
Environment Clearance process chart
Project Concept
Form 1, pre-feasibility project report with proposed TOR to MoE&F (EAC)
Scoping by EAC (site visit by sub group of EAC, if necessary)
TOR approved by EAC EC- rejected by MoE&F on the recommendation of EAC
Draft EIA report to SPCB by project proponent
Public consultation process by SPCB
Summary EIA and Form 1 – display on the website by SPCB
Proceedings of public consultation
Appraisal and recommendation by
EAC
Display on the MoE&F website
Display at Panchayat, ZP, DM/DC/Dy. Com & on the SPCB website
To proponent for submission of final EIA report/Supplementary report to draft EIA
Approval by MoE&F
Rejected Approved Display on MoE&F website & project proponent website
Post EC monitoring
Submission of half yearly compliance report to MoE&F/RO-MoE&F Display of compliance report on
MoE&F website
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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1.4 TERMS OF REFERENCE
The application for the Terms of Reference ofVisaka Industries Ltd.– a proposed Asbestos
Cement Sheets manufacturing project to the tune of 2,16,000 TPA, has been submitted to
The Ministry of Environment & Forests on 20.7.2012. The5thReconstituted Expert Appraisal
Committee of Industrial projects considered the project during its meeting held on 31stJan
’2013. Based on the consideration of the documents and presentation, the Reconstituted
Expert Appraisal Committee ofMoE&F prescribed the Terms of Referencethe copy is
enclosed asAnnexure-I. The point raised in the TOR issued by MOE&F is attended as
under:-
TOR
Ref.
Points mentioned In TOR issued by
MoEF&CC
Implementation Plan/ Compliance
1. Executive summary of the project. A separate section of summary and
conclusion is given as Section- IX of
EIA/EMP report.
2. Photographs of the proposed plant area. The photographs of the proposed plant
area are enclosed as Annexure- II.
3. A line diagram/flow sheet for the process
and EMP.
The flow diagram of the manufacturing
process is given in Section- II, point
no.2.11 of EIA/EMP report.
4. The earlier questionnaire for industry
sector should be submitted while
submitting EIA/EMP.
The questionnaire for industry is
enclosed as Annexure- III.
5. Modern up-to-date asbestos plant with
automatic bag opening devices should be
installed.
The unit is proposing asbestos plant
with automatic bag opening devices.
The details of the same is given in
Section- II, point no.2.5.1 and 2.5.2
of EIA/EMP report
6. The safety measures adopted during
import and transport of asbestos from
Canada or any other country should be
installed.
The unit will take all safety measures
during import and transport of
asbestos from Russia and other
countries, the details of the same is
given in Section- II, point no. 2.5 of
EIA/EMP report.
7. Present land use of study area for 10 km
should be included. Detailed topographical
The detailed land use and land cover
map has been prepared using the
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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map indicating drainage pattern and other
features of the area should also be
included.
satellite imagery. The same is given in
section- III, point no. 3.3 of EIA/EMP
report.
The legible map of land use and land
cover is enclosed as Annexure- IV.
8. Proposal should be submitted to the
Ministry for environmental clearance only
after acquiring total land. Necessary
documents indicating acquisition of land
viz. allotment letter should be included.
The proposed project will come up in
land measuring 28 Acres. The unit has
acquired the land. The land
documents is enclosed as Annexure-
V.
9. High-resolution satellite image data having
1m-5m spatial resolution like quickbird,
Ikonos, IRS p-6 pan sharpened etc. for the
10 km radius area from proposed site
should be incorporated. The same should
be used for land used/land-cover mapping
of the area.
The land use/land cover map using the
high resolution satellite image is
enclosed as Annexure- IV.
10. Project site layout plan to scale using
AutoCAD, raw materials, fly ash and other
storage plans, bore well or water storage,
aquifers(within 1 km) dumping, waste
disposal, green areas, water bodies,
rivers/drainage passing through the project
site should be included.
The project site layout plan to scale
using auto cad showing all salient
features of the project is enclosed as
Annexure- VI.
11. For the project location within 10 km radius
of any major river, Flood Hazard Zonation
Mapping is required at 1:5000 to 1:10, 000
scale indicating the peak and lean river
discharge as well as flood occurrence
frequency.
There is no major perennial river in the
study area except for few scattered
water bodies. Thus, flood hazard is
least expected in the close proximity of
the project site. So far no such case is
reported in the study area.
12. Geo-technical data by a bore hole of upto
40 mts. in every one sq.km area such as
ground water level, SPTN values, soil
fineness, geology, shear wave velocity etc.
for liquefaction studies. This will help
making a future Seismic Hazard and
The proposed project is coming up in
Tonk district which is notified as zone-
II, low damage risk zone(MSK VI or
less) as per BMTPC (Building
materials and technology promotion
council), GOI. Thus, geo- technical
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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Earthquake Risk Management area. data study is not applicable for our
project.
13. Site specific micro meteorological data
including inversion height and mixing
height should be included.
The site specific metrological data has
been generated for summer season of
March to May’2013. The copy of the
same enclosed as Annexure-X. The
summary of the same is given below:-
Micro meteorological data for the study period at project site
Month Temperature (0C)
Relative Humidity (%)
Rainfall in mm
Wind Speed mph
Max Min Max Min Max Total Max Min
March - 2013 37.0 12.5 86.9 9.5 0 0 9.0 < 1.0
April - 2013 41.1 17.5 77.8 9.5 0 0 11.0 < 1.0
May - 2013 45.4 20.9 83.5 9.5 0 0 14.0 < 1.0
14. Details of the other industries located in 10
km radius should be included.
There are no major industries in study
area except for few brick kiln
industries.
15. One season baseline data on air, water,
soil and noise etc. should be included.
One season baseline data has been
generated. The copy of the same is
enclosed as Annexure- VII.
16.
A chapter on chemistry of Asbestos,
handling of asbestos material, precaution
proposed for the direct contact,
arrangements made for storage and
monitoring of asbestos fibers etc. other
details as per given below:
The details on chemistry of asbestos,
and other handling details are
elaborated in Section- II, point no.
2.2 of EIA/EMP report.
I. Size of silica sand, transportation,
storage, spillway of melt and
temperature management for float
glass and mirror industry along with
silicosis management and toxicity
studies and management for Ag etc.
Not Applicable.
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II. Source and location of Asbestos (GPS)
even if imported, size in F/ml, levels in
environment, Chemical composition of
raw material as specially amount of
Tremolite, Crocidolite, Amosite and
other amphiboles, Hexavalent chromium
in raw material especially in serpentine,
talc and chrysotile, Electron microscopy,
XRD and Raman Spectra studies.
The MSDS sheet of asbestos fibre is
enclosed as Annexure- VIII A.And the
test report for type of asbestos and its
composition by XRD analysis, SEM-
EDS and hexavalent chromium is
enclosed as Annexure- VIII B.
III. Health Management Plan for
Mesothalmia, Lung cancer and
Asbestosis related problems in
asbestos industries.
The health management plan is given
in Section- VI, point no. 6.9 of
EIA/EMP report.
17. Petrological and Chemical analysis and
other chemical properties of raw materials
used (with GPS location of source of raw
material) i.e. ores, minerals, rock, soil,
coal, iron, dolomite, quartz etc. using high
definition and precision instruments
mentioning their detection range and
methodology such Digital Analyzers, AAS
with Graphite furnace, ICPMS, MICRO-
WDXRF, EPMA, XRD, Nano studies or at
least as per 130-10500 and WHO norms.
These analyses should include trace
element and metal studies like Cr (vi) Ni,
Fe, AS, Pb, Zn, Hg, Se, S etc. Presence of
radioactive elements (U Th, etc.), if
applicable, should also be included.
Asbestos Fibre mineralogical &
Chemical (for heavy elements)
analysis report is enclosed as
Annexure- IX.
18. Petrography, grain size analysis and Major
element analysis of raw material and soil
from project site and raw material should
be done on the same parameters along
with analysis for SiO2,Al2O3, MgO, MnO,
K2O, CaO, FeO, Fe2O3 , P2O5 ,H2O, CO2
Asbestos Fibre mineralogical &
Chemical (for heavy elements)
analysis report is enclosed as
Annexure- IX.
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19. If these rocks, ores, raw material has trace
elements their petrography, ore
microscopy, XRD, elemental mapping
EPMA, XRF is required to quantify the
amount present in it and hence future risk
involved while using it and management
plan.
There are no trace elements in the raw
material as can be seen in enclosed
report asAnnexureVIII B&IX. Thus,
this point is not applicable on our
project.
20. Modes of transport of raw materials from
sources are to be shown. All the trucks for
raw material and finished product
transportation must be “Environmentally
compliant”.
Asbestos fiber (Chrysotile variety) is
imported from Russia, Brazil,Canada.It
is received in shrink or stretch-
wrapped HDPE woven bags. Fiber
bags are received tightly packed in
wooden pallets and transported in
closed containers. The bags bear the
warning symbol “a”.
After unloading containers are cleaned
using Vacuum cleaners. Palletized
fibre Bags are stacked inside closed
go-down.
21. Studies are also required for management
of muck disposal, slurry, sludge material
and solid waste generated if the raw
materials used has trace elements and a
management plan.
As such no solid waste for disposal is
envisaged from the proposed project.
The entire process is in closed loop
and solid waste generated in the
process is recycled back in to the
system.
The management plan for the same is
given in Section- IV, point no. 4.5.2
of EIA/EMP report.
22.
Air quality modeling for the Asbestos handling system. Ambient air quality
monitoring, modeling along with cumulative impact. Following are to be included as
an Annexure for the day (24 hrs) considered for maximum GLC:
I. Emissions (g/second) with and without
the air pollution control measures.
The details of the same is given in
Section- IV, point no. 4.3.2 of
EIA/EMP report
II. Meteorological inputs (wind speed,
m/s), wind direction, ambient air
The metrological input data for
modeling is enclosed as Annexure-X.
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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temperature, cloud cover, relative
humidity & mixing height) on hourly
basis.
III. Model input options for terrain, plume
rise, deposition etc.
The model input for terrain, plume rise,
deposition is enclosed as Annexure-
XI.
IV. Print-out of model input and output on
hourly and daily average basis.
Print- out of model input and output on
hourly basis is enclosed as Annexure-
XI.
V. A graph of daily averaged
concentration (MGLC scenario) with
downwind distance at every 500 m
interval covering the exact location of
GLC.
A graph of daily averaged
concentration (MGLC scenario) with
downwind distance at every 500 m
interval covering the exact location of
GLC is giveninAnnexure- XII.
VI. Details of air pollution control methods
used with percentage efficiency that
are used for emission rate estimation
with respect to each pollutant.
The details of the pollution control
equipment is given in Section- IV,
point no. 4.3.3 of EIA/EMP report.
VII. Applicable air quality standards as per
LULC covered in the study area and %
contribution of the proposed plant to
the applicable air quality standard. In
case of expansion project, the
contribution should be inclusive of both
existing and expanded capacity.
Ambient air quality has been done
according to the CPCB air quality
standards. All the parameters are
observed within the permissible limits.
Details of the ambient air quality are
given in Section-III of the EIA/ EMP
report.
VIII. No. I-VII are to be repeated for fugitive
emissions and any other source type
relevant and used for industry.
The fugitive emission due to
transportation is considered in air
quality modeling.The management of
the same is given in Section- IV,
point no. 4.3.2 of EIA/EMP report.
IX. Graphs of monthly average daily
concentration with down-wind distance.
The graph for different pollutants of
ambient air quality monitoring is
enclosed as Annexure- XII.
X. Specify when and where the ambient
air quality standards are exceeded
either due to the proposed plant alone
The detail of the incremental load due
to the proposed project is given in
Section IV.The table showing the
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or when the plant contribution is added
to the background air quality.
incremental concentration of pollutant
is given below:-
Pollutant Concentration (µµµµg/m3)
Baseline
(Max.) Incremental Resultant
Distance (km)
Direction
PM10
Project Site 39.3 2.9 42.2 -- --
Sedria 52.8 1.2 54 1.9 NW
DeholdkiDhani 42.5 3.5 46 2.7 NNE
Kishore PurakiDhani 41.6 1.7 43.3 1.6 NE
Lalwari 52.9 1.2 54.1 3.0 ESE
Shrisukhpur 41.2 3.5 44.7 1.0 SSE
Thunj(Radhagovindpura) 41.5 2.9 44.4 1.5 SSW
BhagatpurRampura 41.3 0.6 41.9 3.6 WNW
PM2.5
Project Site 20.3 1.9 22.2 -- --
Sedria 27.9 0.7 28.6 1.9 NW
DeholdkiDhani 21.6 1.9 23.5 2.7 NNE
Kishore PurakiDhani 21 0.8 21.8 1.6 NE
Lalwari 26.3 0.8 27.1 3.0 ESE
Shrisukhpur 21.6 2.6 24.2 1.0 SSE
Thunj(Radhagovindpura) 21.6 2.6 24.2 1.5 SSW
BhagatpurRampura 21.3 0.4 21.7 3.6 WNW
NOx
Project Site 12.6 4.3 16.9 -- --
Sedria 15.6 1 16.6 1.9 NW
DeholdkiDhani 13.2 3.5 16.7 2.7 NNE
Kishore PurakiDhani 13.2 2.6 15.8 1.6 NE
Lalwari 15.3 1.8 17.1 3.0 ESE
Shrisukhpur 13.2 3.5 16.7 1.0 SSE
Thunj(Radhagovindpura) 13.6 3.5 17.1 1.5 SSW BhagatpurRampura 14.5 0.1 14.6 3.6 WNW
CO
Project Site 123 2.8 126 -- --
Sedria 248 0.7 249 1.9 NW
DeholdkiDhani 215 1.7 217 2.7 NNE
Kishore PurakiDhani 215 1.2 216 1.6 NE
Lalwari 291 0.7 292 3.0 ESE
Shrisukhpur 182 2.8 185 1.0 SSE
Thunj(Radhagovindpura) 182 2.3 184 1.5 SSW
BhagatpurRampura 182 0.1 182 3.6 WNW
XI. Fugitive dust protection or dust
reduction technology for workers within
30 m of the plant active areas.
Fugitive dust protection or dust
reduction technologies for workers
within 30 m of the plant active areas
are addressed in Section-VI of the
EIAEMP report.
XII. Existing stack emission data and fibre
concentration in the work zone.
The unit is proposed unit. Thus, this is
not applicable on our project.
23. Sources of Secondary Emissions, Its
Control and Monitoring as per The CPCB
The source of air emission is given in
Section- IV, point no. 4.3, of
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Guidelines And Latest Notification Vide
G.S.R. 414(E) Dated 30Th May, 2008
should be included.
EIA/EMP report.
24. Chemical characterization of RSPM and
incorporation of RSPM data. Location of
one AAQMS in downwind direction.
The chemical characterization of
RSPM is given below:-
CHEMICAL CHARACTERIZATION ANALYSIS OF PM10
Location Name : Project Site Date of Sampling : 15.04.2013
S. No Characteristics Units Project Site
1. Respirable Particulate Matter (PM10) µg/m3 35.4
2. Calcium as Ca µg/m3 1.81
3. Magnesium as Mg µg/m3 0.23
4. Sodium as Na µg/m3 0.02
5. Potassium as K µg/m3 0.01
6. Chromium as Cr µg/m3 <0.01
7. Aluminum as Al µg/m3 <0.01
8. Lead as Pb µg/m3 <0.01
9. Zinc as Zn µg/m3 <0.01
10. Iron as Fe µg/m3 <0.01
11. Nickel as Ni µg/m3 <0.01
12. Barium as Ba µg/m3 <0.01
13. Cadmium as Cd µg/m3 < 0.01
14. Mercury as Hg µg/m3 <0.001
CHEMICAL CHARACTERIZATION ANALYSIS OF PM 10
S. No. Characteristics Units Values
1. Particulate Matter (PM10) (1264 m
3 sample Volume)
µg/m3 35.4
2. Silica µg/m3 <0.1
3.
POLY-AROMATIC HYDROCARBONS (PAH)
Compound (PAH) Minimum Detection Limit (ug/L)
Result (ug/L)
LC Column PAH (HC-ODC SIL-X eq
I Naphthalene 1.8 1.9
II Acenaphthalene 2.3 1.8
III Acenaphthene 1.8 1.9
IV Fluorene 0.21 <0.21
GC Column 3% OV-17 Chromosorb
A Anthracene (Group + Phenanthrene) 28.7 28.8
B Pyrene 3.4 3.4
C BenzoFluranthene 3.1 < 3.1
D Benao (a) pyrene 4.0 4.1
E Fluoranthene 3.0 < 3.0
F Chrysene 4.2 < 4.2
Note: Total PAH observed in the Air Volume are 41.9 µg/L which is represented by actual sample volume of 1224 m
3. The volume of total PAH PM10 works out <0.05 µg/m
3. The
above results interpreted in light of the AAQ standards, indicated that the Ambient Air quality of the sampling location was free of PAH contamination at the time of sampling.
25. Action plan to follow National Ambient Air
Quality Emission Standards issued by the
ministry vide G.S.R. No. 826(E) dated
Details regarding the same are given
inSection-IV of the EIA/EMP report.
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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16thNovember, 2009 should be included.
26. Action plan for rainwater harvesting
measures at plant site should be
submitted to harvest rainwater from the
roof tops 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.
Rainwater harvesting and ground water
recharge structures may also be
constructed outside the plant premises in
consultation with local Gram Panchayat
and Village Heads to augment the ground
water level. Incorporation of water
harvesting plan for the project is
necessary, if source of water is bore well.
Rain water harvesting is proposed at
the plant site. The details of the same
are given in Section- IV, Point no.
4.4.3 of EIA/EMP report.It is
estimated that the total volume of
water generated in project
premises from rooftop, road/paved
& open area in asingle storm on 40
mm peak rainfall intensity would
be- 410m3. Rainwater harvesting
structures are proposed in the
enterprises social commitments,
towards sustainable development
in due consultation with Gram
Panchayat, Shedriya and local
authorities for Government schools
and health centers.
27. Actual source and permission for the drawl
of water from bore well from the
SGWB/CGWA or concerned authority and
water balance data including quantity of
effluent generated, recycled and reused
and discharged is to be provided. Methods
adopted/to be adopted for the water
conservation should be included.
The unit has obtained NOC from
CGWA for ground water abstraction
vide letter no. CGWA/IND/Proj/2014-
1565, dated 3rd Sep 2014.The copy of
the same is enclosed asAnnexure-
XIV.
28. Ground water monitoring minimum at 8
locations should be included.
The ground water monitoring is given
in Section- III of EIA/EMP report.
29. Scheme for proper storage of Asbestos
fibres and disposal of solid/hazardous
waste should be included.
The details of proper storage of
asbestos fibre are given in Section- II,
point no. 2.3 of EIA/EMP report.
The management of hazardous waste
is given in Section- IV, point no. 4.5
of EIA/EMP report.
30. Presence of aquifer/aquifers within 1 km of The details of the Hydrogeology
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the project boundaries should be included.
Management plan for recharging the
aquifer should be submitted.
&Drainage are given in Section- III,
point no. 3.6.1 of EIA/EMP
report.The management plan for
recharging the ground water is given in
Section- IV, point no. 4.4.2 of
EIA/EMP report
31. Source of surface or ground water level,
site (GPS), cation, anion (ion
chromatograph), metal trace element (as
above) chemical analysis for water to be
used along with a Piper and Piper Duro-V
diagram. If surface water is used from
river, rainfall, discharge rate, quantity,
drainage and distance from project site
should also be included.
The source of water for the project is
ground water. The proposed project
will require 240 KLD fresh water. The
unit proposes to recharge the ground
water to the tune of 22373.52
m3/annum.The chemical analysis of
Ground water is given in Section- III,
point no. 3.6.4 of EIA/EMP report.
There is no major surface water in the
study area.
32. Ground water analysis with bore well data,
litho-logs, drawdown and recovery tests to
quantify the area and volume of aquifer
and its management should be included.
The report on ground water analysis
with bore well data and drawdown and
recovery test is enclosed as
Annexure- XV.
33. Ground water modeling showing the
pathways of the pollutants should be
included.
The proposed unit is zero discharge
unit. Thus, the chances of ground
water contamination are negligible.
34. Column leachate study for all types of
stockpiles or waste disposal sites, at 20o
C-50OC should be conducted and
included.
There is no chance of leachate in the
proposed project. The raw material will
be stored in dry form with in the closed
godown. Thecomplete process is in
closed system and no solid waste is
generated to be stored in stock piles.
35. All sampling for water have to be done
during the peak summer time (Sampling
number, dates and standard deviation
should be included.
The ground water monitoring is done
during March’2013 to April’2013. The
result of the same is given in Section-
III, point no. 3.6.4 of EIA/EMP report.
36. Incorporation of water harvesting plan for
the project is necessary, if source of water
is bore well should be ensured.
The detailed water harvesting plan is
given in Section- IV, point no. 4.4.5
of EIA/EMP report.
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37. Provision of traps and treatment plants are
to be made, if water is getting mixed with
oil, grease and cleaning agents should be
included.
The complete process is in closed
loop system with no waste water
discharge from the process. The
details of water balance and treatment
is given in Section –II, point no. 2.7
of EIA/EMP report.
38. If water is mixed with solid particulates,
proposal for sediment pond before further
transport should be included. The
sediment pond capacity should be 100
times the transport capacity.
Two number of recuperative tanks of
100 KL capacity each is proposed for
storing the re circulating water.
39. Wastewater characteristics (heavy metals,
anions and cations, trace metals, PAH)
from asbestos bearing effluent should be
included.
The complete process is in closed loop
system with no waste water discharge
from the process.
40. The pathways for pollution via seepages,
evaporation, residual remains are to be
studied for surface water (drainage, rivers,
ponds, and lakes), sub-surface and ground
water with a monitoring and management
plans should be included.
The proposed unit is a zero waste
water discharge unit.As such no solid
waste for disposal is generated.
The raw material is stored in dry form
with in the closed godown. The entire
process is in closed loop with solid
waste generated in the process is
recycled back in to the system. The
management plan for the same is
given in Section- IV, point no. 4.5 of
EIA/EMP report.
41. All stock piles should be on top of a stable
liner to avoid leaching of materials to
ground water.
Not Applicable. The details given in
above TOR point no. 40, 34 and 29.
42. The green belt should be around the
project boundary in 33% area and a
scheme for greening of the travelling roads
should also be incorporated. All
rooftops/terraces should have some green
cover.
The unit has proposed 33 % for green
belt for the proposed unit. The
detailed green development plan is
given in section- VIII, point no. 8.4 of
EIA/EMP report.
43. Disaster Management plans including risk The detailed disaster management
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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assessment and damage control needs to
be addressed and included.
plan is given in Section- VI of
EIA/EMP report.
44. Details regarding expected Occupational
and Safety Hazards. Protective measures
for Occupational Safety & Health Hazards
so that such exposure can be kept within
permissible exposure level so as to protect
health of workers. Health of the workers
with special reference to Occupational
Health. Plan of exposure specific health
status evaluation of workers; pre-
placement and periodical health status of
workers; plan of evaluation of health of
workers by pre-designed format, chest x-
ray, Audiometric, Spirometry Vision testing
(Far & near vision, colour vision and any
other ocular defect) ECG, during pre
placement and periodical examinations
and pan of monthly and yearly report of
the health status of workers with special
reference to Occupational Health & Safety.
The details regarding occupational
and safety hazards is given in
Section- VI of EIA/EMP report.
45. Detailed action plan for compliance of the
directions (including the recent
Kalyaneswari case) of the Hon’ble
Supreme Court of India regarding
occupational health & safety measures in
asbestos industries should be included.
The detailed action plan for
compliance of direction is given in
Section- VIII of EIA/EMP report.
46. Detailed description of the flora and fauna
(terrestrial and aquatic) should be given
with special reference to rare, endemic
and endangered species.
The detailed flora and fauna of the
study area is given in Section- III,
point no. 3.8 of EIA/EMP report.
47. Compliance to the recommendations
mentioned in the CREP guidelines should
be included.
No separate CREP recommendations
have been stipulated for Asbestos
plant. However allrequired
environmental management systems/
will be implemented to comply with
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MoEF / CPCB / RSPCB norms. All the
codes stipulated by BIS will be strictly
implemented
48. An action plan on entire operation should
be automatic and closed system for all
operations for fibre handling and
processing should be included.
The unit will install automatic and
closed system. The details of the
same are given in Section- II of
EIA/EMP report.
49. Details of arrangement for measurement
and monitoring of asbestos fibre (phase
contrast microscope) should be included.
The unit will install all the in house
monitoring equipments required for
asbestos monitoring. The details of the
same are given in Section- V of
EIA/EMP report.
50. Detailed Environment Management Plan
(EMP) with specific reference to details of
air pollution control system water and
waste water management, monitoring
frequency, responsibility and time bound
implementation plan for mitigation
measure should be provided.
The detailed environment
management plan is given Section-
VIII of EIA/EMP report.
51. EMP should include the concept of waste-
minimization, recycle/reuse/recovery
techniques, Energy conservation, and
natural resource conservation.
The detailed environment
management plan is given Section-
VIII of EIA/EMP report.
52. EMP should include a clear map for
plantation/greenbelt.
The green belt development program
is given in Section- VIII, point no. 8.4
of EIA/EMP report.The greenbelt
landscape plant layout is enclosed as
Annexure- XVIII.
53. Commitment that laboratory for monitoring
asbestos fibres will be established at the
site.
The unit will develop in house
laboratory for asbestos monitoring.
The details of the same are given in
Section – V of EIA/EMP report.
54. Public hearing issues raised and
commitments made by the project
proponent on the same should be included
separately in EIA/EMP report in the form of
Public hearing has been conducted as
per the EIA Notification 2006 and
amendment thereof. The issues raised
and a commitment made by the
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tabular chart with financial budget for
complying with the commitments made.
project proponent has been included in
the report.
55. At least 5% of the total cost of the project
should be earmarked towards the
Enterprise Social Commitment based on
Public Hearing issues and item wise
details along with time bound action plan
should be included. Socio-Economic
development activities need to be
elaborated upon.
A sum of Rs. 2,83,10,000/- equivalent
to 5% of the project cost is earmarked
towards the enterprises social
commitment. Public hearing has been
conducted. The details are given in
Section VI, point no. 6.9 of the EIA /
EMP report.
56. Any litigation pending against the project
and/or any direction /order passed by any
Court of Law against the project, if so,
details thereof should also be included.
No litigation is pending in court of law
to the best of our knowledge
1.5 GENERIC STRUCTURE OF ENVIRONMENTAL IMPACT ASSESSMENT
Environmental Impact Assessment (EIA) is a well planned process to predict the
environmental consequences of any kind of development, which is result of human activities
and to suggest appropriate measures in order to reduce adverse effects and also to
augment positive effects. The EIA procures a rational and ethical approach for sustainable
development.However,it is more scientific process because it not only tells the past, present
and the future consequences of going on development , but also predicts the future events
which likely to change due to some reasons.
In terms of the EIA notification of the MOE&F dated 14th September 2006 and subsequent
amendment on 01.12.09 and 04.04.2011, the generic structure of EIA documents shall be as
under:-
• Introduction
• Project Description
• Description of the Environment
• Anticipated Environmental Impact &Mitigation Measures
• Environmental Monitoring Program
• Additional Studies
• Project benefits
• Environment Management Plan
• Summary & Conclusion
• Disclosure of Consultant Engaged
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1.6POST ENVIRONMENTAL CLEARNCE MONITOIRNG
This is a new project; hence post-environmental clearance monitoring is not applicable.
Although, the project management will submit half-yearly compliance reports of the
stipulated prior environmental clearance terms and conditions on 1st June and 1st December
of each calendar year.
1.7 IDENTIFICATION OF PROJECT PROPONENT
Promoters of the proposed New Asbestos Cement Project are Visaka Industries Limited.
The Company is professionally managed under the leadership of Dr G.Vivekananda (who
holds an MBBS degree) who is the promoter and Vice Chairman. He has over 27 years of
experience in the Asbestos Cement Industry and 22 years in the Spinning Industry. He is
assisted by a competent team of professionals in the fields of Technical, Marketing, Finance
and Administration, with several years of experience in their respective fields.The company
was originally promoted in 1981 by Dr.G.Vivekananda, and Andhra Pradesh Industrial
Development Corporation (APIDC). APIDC has since disinvested its shareholding (26% of
original share capital) to the Dr.G.Vivekananda in the year 1990.
1.8 BRIEF DESCRIPTION OF THE PROJECT
The proposed project is an Asbestos cement sheets manufacturing Unit. The proposed
production capacity of the unit is 2, 16,000TPA. The total land area occupied by the unit is
28 Acres. The Unit is coming up at Rachakpura Village, Shedriya Grampanchayat, Niwai
Tehsil, Tonk District, Rajasthan State. The total project cost will be Rs. 56.62 Crores. The
unit has earmarked Rs. 50 Lakh for environment Management plan as capital investment
and Rs. 10 lakhs as recurring cost.
1.9 LOCATION OF THE PROJECT
The project will come at Rachakpura Village, Shedriya Grampanchayat, Niwai Tehsil, Tonk
District, Rajasthan.
The site falls in geological survey of India of toposheet No. 45N/14, 45N/15, 54B/2 & 54B/3.
The geographical location of the project is-
NW NE SE SW
Latitude 26o 26’ 04.82” N 26o 26’ 00.49” N 26o 25’ 51.55” N 26o 25’ 52.86” N
Longitude 76o 01’ 03.17” E 76o 01’ 13.38” E 76o 01’ 11.68” E 76o 01’ 00.39” E
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The plan clearly showing the project site and study area of 10 km radius is shown in Figure
1.2& Figure 1.3
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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Figure No. 1.2 Location Map
Project: Visaka Industries Ltd. SECTION-I INTRODUCTION
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Figure No. 1.3
Topographical map showing 10 km radius
*Source: G.T. Sheet of Survey of India
1.10 ENVIRONMENTAL SETTING OF THE PROJECT SITE
Sr. No. Particulars Details
1 Location
A Village Rachakpura
B Tehsil Niwai
C District Tonk
D State Rajasthan
E Latitude 26o 26’ 00.49” N
26o 26’ 00.49” N
26o 25’ 51.55” N
26o 25’ 52.86” N
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F Longitude 76o 01’ 03.17” E
76o 01’ 13.38” E
76o 01’ 11.68” E
76o 01’ 00.39” E
G Toposheet No. 45N/14, 45N/15, 54B/2 & 54B/3
H Total Plant Area 28 Acres
2 Land use at the
project area
Agricultural land converted for industrial purpose.
3 Nearest habitation Nearest habitation in SaidariyaKhurd1.0 km South-
West.
4 Nearest major town SaidariyaKhurd at a distance of 1.0 Km South-West
5 Nearest highway NH 11A at a distance of 7.27 km N connecting
Manoharpura to Kothum.
6 Nearest railway track
from Project site
9.03 km towards West
7 Nearest airport Jaipur airport at a distance of 47.21 km NNW
8 Nearest Railway
Station
Siras Railway Station at a distance of 19.36 km S.
9 Nearest tourist places Nil with in 10 km radius
10 Defence installations Nil with in 10 km radius
11 Archaeological
important
Nil with in 10 km radius
12 Reserved / Protected
forest / National
Parks / Wildlife
Sanctuary (from
Project Site)
Reserved Forest is at a distance of 5.21 km NE.
13 Nearest streams /
Rivers / water bodies
(from Project Site)
S.No Rivers Distance (km)
Direction
1. Dhilnadi 3.13 km SSW
13 Other Industries None within the study area.
14 Seismic zone The area is falling in Zone- II, Low Damage Risk
Zone (MSK VI or less).
*********
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SECTION-II
PROJECT DESCRIPTION
INDEX
PROJECT DESCRIPTION .................................................................................................. 50
2.1 INTRODUCTION ...................................................................................................... 50
2.2 GENERAL INFORMATION ON ASBESTOS ........................................................... 50
2.3 DESCRIPTION OF THE PROJECT ....................................................................... 53
2.4 PLANT LAYOUT ..................................................................................................... 53
2.5 RAW MATERIALS STORAGE AND QUANTITY ..................................................... 54
2.6 CAPACITY OF THE PROJECT ............................................................................... 56
2.7 WATER REQUIREMENT ........................................................................................ 56
2.8 POWER .................................................................................................................. 57
2.9 SCHEDULE OF APPROVAL AND IMPLEMENTATION .......................................... 58
2.10 MAN POWER .......................................................................................................... 58
2.11 MANUFACTURING PROCESS............................................................................... 58
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PROJECT DESCRIPTION
2.1 INTRODUCTION
The proposed unit is categorized under 4 (c) 3 of Gazette Notification dated Sep 14th, 2006
and subsequent amendment on 01.12.09 {Asbestos milling and asbestos based products}.
The same is categorized as “A” category.
Visaka Industries Ltd. has proposed to set up a manufacturing unit of 2,16,000 TPA capacity
of Asbestos Cement Sheets at Visaka Industries Ltd., Rachakpura Village, Shedriya
Grampanchayat, Niwai Tehsil, Tonk District, Rajasthan.
2.2 GENERAL INFORMATION ON ASBESTOS
A. ASBESTOS CLASSIFICATION
Asbestos is a naturally occurring hydrated mineral silicate that crystallizes in fibrous form.
Mineralogical asbestos can be classified into two major groups; the Serpentine and the
Amphibole. Both groups have different physico–chemical nature. Serpentine is curly and
stranded structure whereas amphiboles are straight and rod like structures (ATSDR).
� Serpentine – Chrysotile (White Asbestos) (90% of Chrysotile Asbestos used in
industry)
� Amphibole – Whose variety include Amosite (Brown Asbestos), Tremolite, Actinolite,
Anthophylite & Crocidolite (Blue Asbestos) (Crocidolite Asbestos is banned in India
causing maximum damage).
Figure- 2.1
Flow chart showing types of asbestos
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Asbestos fibers bear unique properties of a high tensile strength, resistance to heat and
many chemicals without having any detectable odor. Asbestos in air at work environment is
a major cause of adverse effects on health of industrial workers.
B. CHEMICAL STRUCTURE AND PROPERTIES
(I) Chemical Structure
� Serpentine
Chrysotile Mg3Si2O5 (OH)4
� Amphibole
Actinolite: (Ca, Fe) 2Mg5Si8O2 2 (OH)2
Amosite: Fe2Fe5Si8O22 (OH)2
Anthophyllite: Mg2Mg5Si8O22 (OH)2
Crocidolite: Na2Fe2+3Fe3+2Si8O22 (OH)2
Tremolite: Ca2Mg5Si8O22 (OH)2
(II) General Properties
Asbestos has got certain unique properties, which has led to its application in more than
3000 products. Its chief properties are:
• High Tensile strength
• High resistance to abrasion
• Resistance to corrosion
• Resistance to heat
• Non-combustibility
• Resistance to Alkali Attack
• Durability & Toughness
• Good Electrical Insulation Properties
• Chemical inertness
By virtue of the high tensile strength and bonding properties with cement, it is used in the
manufacture of Fibre Cement Products. It acts as the reinforcing medium in much the same
way as Steel in RCC. The said products are used in variety of applications. Nowadays Fibre
Cement sheets are used in place of GI sheets, tiles, and other roofing materials. Fibre
Cement Sheets are used extensively for roofing of factories, residential colonies, garages,
warehouses, railway platforms, low cost housing etc. Out of the above type of the asbestos,
the proposed plant will use only chrysotile type of asbestos. The properties of chrysotile are
as follows:-
Chemical and Physical Properties of Chrysotile
Chemical name
Chrysotile is listed on the Australian Inventory of Chemical Substances (AICS). CAS
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number 12001-29-5
EC number 650-013-00-6 RTECS
number GC2625000
Other names Trade names
Asbestos 7-45 Asbestos
Serpentine asbestos Avibest
White asbestos Avibest C
Calidria RG 100
Calidria RG 144
Calidria RG 600
Cassiar AK
K 6-30
NCI C61223A
5RO4
Molecular formula and Structure
Molecular formula: Mg3Si2O5 (OH)4
The crystal structure of chrysotile is layered or sheeted similarly to the kaolinite group. It is
based on an infinite silica sheet (Si2O5) in which all the silica tetrahedra point one way. On
one side of the sheet structure, and joining the silica tetrahedra, is a layer of brucite, Mg
(OH)2. The result is a layered structure.
Molecular Weight: - 283
Chemical Composition
Chemical analysis shows that chrysotile typically consists of the following range of major
constituents (%) (IPCS, 1986):
COMPONENT PERCENTAGE (%)
SiO2 38 – 42
MgO 38 - 42
N2O+ 11.5 – 13
Fe2O3 0 - 5
FeO 0 - 3
Al2O3 0 – 2
CaO 0– 2
Na2O 0- 1
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2.3 DESCRIPTION OF THE PROJECT
Visaka Industries Ltd. proposes to manufacture Asbestos Cement Sheet to the capacity of
2,16,000 TPA.
� The unit is coming up at Rachakpura Village, Shedriya Grampanchayat, Niwai Tehsil,
Tonk District, Rajasthan. The site falls in geological survey of India of Toposheet No.
45 N/14, 45 N/15, 54 B/2, 54B/3.
� The proposed project is a new unit proposes to manufacture Asbestos Cement Sheet
to the tune of 2, 16,000 TPA.
� The main plant and machinery includes conveyor mixer tanks, re-cupperater tanks,
sheet forming machine, atmospheric corrugating unit, cooling tower, shifting
machine.
� The processing of the asbestos will be done in a Kollargang (or Edge Runner Mill as
is popularly known), which will be totally sealed and water will be sprinkled
immediately in the machine to detain any air borne asbestos fiber.
� Automatic bag opening devices will be installed.
� The fugitive area emissions will be routed through vide bag filters to control the
pollutants well within the norms. There will be automatic bag opening devices for
opening of asbestos bags.
� There will be provision of dust collectors for detaining any dust emanating in the
process.
� The total land area occupied by the unit is 28 Acres.
� The capital cost for the proposed project is 56.62 Crores.
2.4 PLANT LAYOUT
The total plot area acquired by the unit is 28 Acres. The unit will consist of work shed,
godown, store room, parking area for vehicles as well as trucks, administrative block etc.
Plantation will be developed inside the unit in an area of 33%.
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2.5 RAW MATERIALS STORAGE AND QUANTITY
The company being already in the business of manufacturing asbestos cement products,
has established regular parties from whom the required raw materials, including asbestos
fibre, cement wood pulp etc. are sourced.
There are six types of asbestos: actinolite, amosite, anthophyllite, crocidolite, tremolite, and
chrysotile. Out the above all type the proposed project will use only chrysotile type of
asbestos due to the following benefits.
• The first five types are known as amphiboles. They are characterized by having very
strong and stiff fibers, which makes them a serious health hazard.
• Amphibolic asbestos fibers can penetrate body tissue, especially in the lungs, and
eventually cause tumors to develop.
• The sixth type of asbestos, chrysotile, is known as a serpentine. Its fibers are much
softer and more flexible than amphibolic asbestos, and they do less damage to body
tissue.
• Chrysotile is usually white, and is sometimes known as white asbestos, although it can
also be amber, gray, or greenish in color. Most chrysotile fibers are about 0.25-0.50 in
(6.4-12.7 mm) long and are usually added to concrete mixes to provide reinforcement.
Only about 8% of chrysotile fibers are long enough to be spun into fabric or rope.
• The other major raw materials used in the manufacturing of asbestos cement sheets are
Ordinary Portland Cement (OPC-33/43(/53) grade), fly ash and pulp.
• The quantity of raw material along with mass balance chart is given below:-
Table No. 2.3
Raw material requirement
S.No. Particulars Consumption Storage
TPA
1. Asbestos-(Chrysotile) 17992 (2 months)
2. Cement-OPC 90007 (750 MT)
3. Fly Ash 61689.6 (500 MT)
4. Pulp 1728 (50 MT)
Total 171416.6
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2.5.1 Asbestos fiber transportation, receiving & handling
• Asbestos Fiber transportation & Receipts- Asbestos fiber (Chrysotile variety) is
imported from Canada, Brazil, Zimbabwe, & Russia. It is received in shrink or stretch-
wrapped HDPE woven bags. Fiber bags are received tightly packed in wooden pallets
and transported in closed containers. The bags bear the warning symbol “a”. After
unloading containers are cleaned using Vacuum cleaners. Palletized fibre Bags are
stacked inside closed go-down.
• Fibre Handling & Storage- The bags are handled at site by means of fork lifts. Spillages
if any and container after unloading at site is cleaned using portable vacuum cleaner.
Where this is not practicable, wet mopping, collection & recycling method is adopted.
Torn bags received if any, is stitched and sealed with suitable adhesive tapes. Such
cleaning operation is undertaken by the operatives wearing protective clothing and
respiratory masks. The fibre bags are stacked in go-downs.
• Bag Opening & Fibre Milling- This operation is carried out under closed condition &
under negative pressure which is provided by Fibre Dust Collector, routed through Air
Wet Washer
• Empty Bags Generation handling- Recycled back to the process along with fibre after
shredding
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2.5.2 Scheme of proper storage of Asbestos Fibre
The Asbestos fibre is received in shrink or stretch wrapped HDP woven sacs. The fibre bags
are stacked on pallets and transported from the port in closed container. The bags contain
warning label incorporating the "a" symbol. Hooks and other sharp equipment are not used
on bags. Forklift are used for unloading and loading. Vacuum cleaner is used for cleaning.
Where this is not practicable, surface is thoroughly wetted before sweeping. Where the
wrapping of a bag is damaged and spillage of asbestos is likely, suitable adhesive tape is
used for repairing of damaged portion. Before storage all bags are carefully inspected for
cleanliness and for damage. All bags are stacked on pallets.
2.6 CAPACITY OF THE PROJECT
The proposed production capacity for Asbestos cement sheets is 2,16,000 TPA. The ISI
specification of the product is as follows:-
ISI Specification
ISI SPECIFICATION TECHNICAL DATA
Standard lengths in (Metres)
: 3.00, 2.75, 2.50, 2.25, 2.00, 1.75, 1.50
Tolerance (in mm)
+5 -10
+Free -0.5
+6 -2
+3 -5
+10 -5
+10 -5
Maximum unsupported overhang
: 300 mm
Thickness : 6 mm Maximum Purlin Spacing for roofing
: 1.4 M
Pitch : 146 mm Maximum Rail spacing for Vertical cladding
: 1.7 M
Depth : 48 mm Section modulus : ZB:75 cm3 ZT:85 cm3
Overall Width
: 1050 mm Moment of Rupture : 200 kg/cm2
Effective Width
: 1010 mm
2.7 WATER REQUIREMENT
The one time water demand of the proposed unit is 5402 KLD (Daily fresh water demand –
240 KLD and recycled water – 5167 KLD).
Out of the 5402 KL water 5382 KL water is required for industrial purpose, 15 KL is for
domestic purpose and 5 KL is for cooling purposes.
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Out of 240 KLD water, industrial water demand is 225 KLD while 15 KLD water is required
for domestic purposes. During the industrial process water will be used for slurry formation
and curing purposes.
The water demand will be met from Borewell. The unit has obtained CGWA approval for
withdrawing ground water.
The detail of water requirement and water balance are shows as under:-
Water Requirement
S.No. Particulars Water Requirement (KLD)
1. Domestic purpose 15
2. Industrial purpose 225
Total 240
WATER BALANCE
2.8 POWER
The power requirement for the proposed unit is 750 kVA. Two D.G. sets of 500 kVA each will
be installed for the complete power back up. The proposed project area has continuous 24
hours power supply hence, no diesel will be used during these hours. Thus, it is presumed
that there will be no electricity cut. However, in case of electricity cut there would be
Domestic 15 KLD
Green product 173 KLD carried
by product
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consumption of around 40 L/hr of fuel per D.G. set. Fuel required for the D.G. set will be in
the form of H.S.D. There will be facility for storage of fuel (HSD).
2.9 SCHEDULE OF APPROVAL AND IMPLEMENTATION
The proposed project has been planned for manufacturing asbestos cement sheet to the
tune of 2, 16,000 TPA. The entire development will take about 18 months for completion.
The plant will be fully operated after 3 years.
The construction activities will start after obtaining necessary approval from Ministry of
Environment and Forests and Rajasthan Pollution Control Board.
2.10 MAN POWER
In the full fledge process of the plant, the total employment will be around 521 employees.
EMPLOYMENT GENERATION MANPOWER
a) Managers/Supervisors 15
b) Staff 20
c) Workers –
i) Skilled
ii) Unskilled (contract)
iii) Contract Workers (Loading & Unloading)
51
141
(100
Total 327
2.11 MANUFACTURING PROCESS
The proposed unit will be manufacturing asbestos cement sheets to the tune of 2,16,000
TPA. The basic raw material required for the manufacturing of asbestos cement sheets will
be Ordinary Portland Cement (7417 TPM), fiber (1508 TPM), fly ash (4750 TPM), and pulp
(144 TPM). Complete processing will be done through a closed circuit. Nothing will be done
manually. The proposed unit will have the following manufacturing process:-
1. Raw material preparation
2. Slurry preparation section
3. Sheet forming machine
4. Process water recycle system
5. Conveyor system
6. Corrugating unit
7. Waste recycle section
8. Heating section
9. Destacker
10. Curing area
11. Storage area
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1. Raw Material Preparation
The basic raw material required for the process includes fiber, fly ash, pulp and cement.
Asbestos fiber of various grade packed in HDPE bags will be fed to bag opening machine,
where bag will be automatically cut and transferred to fiber mill. Requisite quantity of water
will be added by water dosing equipment. Thereafter, fiber will be transferred to fiber silo for
storage. The milled fiber will be transported to auto weighed, where requisite quantity per
batch will be weighed and kept ready for feeding to slurry preparation section.
Cement received in bulker will be transferred to storage silo through blower & some quantity
when received in HDPE bags will be transferred to storage silo through elevator system.
From silo, cement will be transferred to auto weighing system through screw conveyor,
where the required quantity per batch will be weighed and kept ready for feeding to slurry
preparation section.
2. Slurry Preparation Section (Hydropulper/Mixer)
The requisite quantity of water will be taken in the hydro-disintegrator according to the batch
size (controlled with Electrical Level Controllers). In which, already weighed asbestos fiber
will be transferred and mixed for preset time. After that the fibre slurry will be taken to the
Beater tank where pre weighed quantity of cement & fly ash which has already been
transformed into slurry in Mixer tank, will be pumped in & kept circulating to form RM slurry.
A pumping set will be installed for circulation and discharge of slurry. Slurry will be the
transferred to agitator tank.
3. Sheet Forming Machine (5 Vats)
The slurry lying in agitator tank will be fed to slurry dilution tank along with additional water.
The diluted slurry will be controlled by level controllers and pneumatic valves for supply to
VATS of sheets.
Each VAT will be cylindrical mould (Sieve cylinder) through which thin slurry will be filtered
and the layer formed on the outside of sieve will be transferred to a continuously running
synthetic felt. All the layers picked up from 5 to 7 vats as the case may be will be subjected
to vacuum system for controlling moisture in the final layer before it will be transferred to
sheet forming drum. The forming drum will be rotated by driving felt itself and it will be
loaded pneumatically to control final moisture in the sheet apart from compression of sheet
to desired density.
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4. Process Water Recycle System
The filtrate received from VAT machine will be collected in a pit and pumped to conical water
tanks for recycling the same to the machine. The water flows from first tank to the second
tank by overflow system and solid (i.e. cement and fiber) settle down in the first cone tank,
which will be used in slurry dilution tank. The clear water from the second curing tank will be
used for high pressure spray system for cleaning the felt & sieve cylinder and other process
cleaning operations and vacuum system.
5. Conveyor System
Conveyor system consists of two rubber belt (flat) conveyors installed just after the sheet
forming drum for transportation of green sheet upto corrugating unit.
First conveyor receives green sheet automatically cut from the drum. As the sheet moves on
the conveyor the sides will be trimmed by longitudinal cutters installed on both sides of the
first conveyor.
Second conveyor receives the sheet from first conveyor and positions the same in the
central line of corrugating unit.
6. Corrugating Unit
The unit consisting of traveling carriage system will be set of seamless steel bars for
corrugating the flat sheet on to the steel modules. The steel sheet mould will be packed up
from the carriage trolley by suction hoods and pushed on to the corrugators. It will be so
synchronized that the plain sheet, which travels from first conveyor to second conveyor duly
cut by cross cutters installed on carriage frame which cuts the front and rear edges of the
sheet to the required length, drops on to the steel mould from second conveyor. The sheet
will be than pressed simultaneously from outer corrugation to inner corrugation. Sheets will
be corrugated to size on automatic atmospheric corrugators. Such shaped wet sheet along
with the steel mould will be than transferred to the stapler for collection on another sheet
carrying trolley.
7. Waste Recycle Section
The side cutting of the green sheet and rejected sheets fall automatically on a running waste
conveyor which transports the same to waste dissolver unit.
The waste dissolver consists of cylindrical tank with turbo impeller, which cuts the waste in
water media and converts the waste into slurry. The slurry will be pumped to the agitator
tank, where it will be once again used for sheet forming.
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8. Closed Initial Curing Chamber
The sheet trolleys will be transported on rail tracks to an enclosed chamber and kept for 12
to 16 hours for hardening/setting. Thereafter the sheet trolleys (having sheets and steel
moulds stacked one over the other) will be transported to destacker machine. Some times
during winter season whenever the temperature dips, electrical heaters will be installed in
the enclosed chamber for accelerating the process of hardening/setting of sheets.
9. Destacker
This machine will be similar to the corrugating unit in operation and has two suction hoods –
one for sheet and the other for steel mould. Here the sheet and steel moulds will be
separated and stacked on the respective trolleys.
The sheet trolleys will be shunted to curing area for stacking under water spray system. The
mould trolleys will be recycled to the corrugating unit for reuse for the on-going production.
10. Curing Area
The curing area consists of platforms for stacking sheets and pipelines will be installed
overhead for periodic spray of water for curing, ensuring adequate humidity within the curing
section.
The water will be stored in underground reservoirs and will be pumped continuously to the
curing area and will be recycled. However, make up water requirement will be met from the
water supply source. The sheets are cured for 10 to 15 days
11. Storage Area
The cured sheets will be removed after curing is completed and stacked outside in the open
or the covered area for final inspection and dispatch.
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SECTION – III
DESCRIPTION OF THE ENVIRONMENT
INDEX
DESCRIPTION OF THE ENVIRONMENT .......................................................................... 62
3.1 GENERAL .................................................................................................................. 63
3.2 BASELINE DATA GENERATION ............................................................................... 63
3.3 LAND USE STUDIES ................................................................................................. 65
3.4 SOIL CHARACTERISTICS ......................................................................................... 70
3.5 AIR ENVIRONMENT .................................................................................................. 73
3.6 WATER ENVIRONMENT ........................................................................................... 80
3.7 NOISE ENVIRONMENT ............................................................................................. 85
3.8 BIOLOGICAL ENVIRONMENT .................................................................................. 88
3.9 SOCIO ECONOMIC ENVIRONMENT ...................................................................... 108
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DESCRIPTION OF THE ENVIRONMENT
3.1 GENERAL
The anthropogenic activities related to industrial sector cause impacts on environmental
components in and around the project site. However, the intensity of environmental
impacts vary from project to project, depending upon several factors like- Physical,
Chemical, & other etc., Involved in the project, processing capacity (scale / size of the
project), type and extent of pollution control measures, project location surrounding
geomorphology etc. To assess environmental impacts from proposed project (specific), it
is essential to monitor the environmental quality prevailing in the surrounding area prior
to implementation of the proposed project. The environmental status (baseline status)
within the study area is used for prediction of anticipated environmental impact
assessment study. The impacts from an existing industrial project on its surrounding
environment are due to the nature of pollutants, their quantities discharged to the
environment, existing environmental quality, assimilative capacity of the surrounding
environment and topography.
3.2 BASELINE DATA GENERATION
The baseline data generation for Visaka Industries Ltd. was collected for pre
monsoon season (March-May’2013). The same was agreed by honorable EAC
committee during our Terms of Reference presentation. The data of March-May 2013
is presented and interpreted in this chapter.
3.2.1 Monitoring methodology
• Air
Fine Particulate Samplers (FPS) has been used for PM2.5 Sampling. Respirable
Dust Samplers (RDS) with gaseous attachment have been used for PM10
Sampling. RDS with Gaseous attachment assembly is used for the collection of
gaseous pollutants such as SO2 & NOx.
• Meteorological Data
An auto weather monitoring station was installed during the study period to
record various meteorological parameters on hourly basis to understand the wind
pattern, Temperature variation, solar insulation and relative humidity variation
etc.
• Water
Ground Water samples were collected in Pre sterilized sampling containers.
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Chemical and Metal analysis was carried out as per standard methods for ground
water, Published by AWWA, APHA, etc.
• Noise
Instant sound level meter is used for the collection of data related to noise at an
interval of one hour per reading. Noise level test for 24 hours was conducted
during one week period at pre decided location. The details of the instrument
used for the sampling is mentioned in the separate annexure under the heading
of Details of instruments & Apparatus.
• Soil
Representative soil sample was collected from project site for analysis of
physico-chemical characteristics. Standard procedures, as per BIS / CPCB and
other published methods were followed for sampling and analysis.
3.2.2 Location of monitoring stations
Eight monitoring stations including the site were selected for monitoring of Ambient
Air, Water, Noise and Soil. The monitoring period was from March to May 2013. The
monitoring stations were selected on the basis of surface influence, demographic
influence and meteorological influence. The topographical map showing the
monitoring locations is given below in Figure No. 3.1. and the details of the
monitoring locations is given below in table no. 3.1
Table no. 3.1
Monitoring location
S. No.
Location Name Details Direction w.r.t
project Site Co-ordinates
1 Project Site At Site -- N-26025’52.4’’ E-76
001’03.4’’
2 Sedria Rajaram S/o Devlal NW N-26026’44.3’’ E-76
000’17.7’’
3 Dehold Ki Dhani Ajaykumar S/o Sreeramsevak
NNE N-26027’19.9’’ E-76
002’39.6’’
4 KishorePura Ki Dhani Mangilal Gujjar NE N-26
026’28.4’’ E-76
001’45.4’’
5 Lalwari Shankarlal Sharma S/o Harichandra ji
ESE N-26025’27.7’’ E-76
002’44.5’’
6 Shrisukhpur Madhan Jain S/o Kaluram
Ji SSE N-26
025’35.0’’ E-76
001’00.0’’
7 Thunj (Radhagovindpura)
Shivaji Lal SSW N-26025’14.8’’ E-76
000’07.1’’
8 Bhagatpur Rampura Mahendra kumar Jan S/o Nirmal Kumar Jai
WNW N-26025’09.2’’ E-75
058’56.5’’
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Figure No. 3.1
Topographical Map Showing Monitoring Locations
3.3 LAND USE STUDIES
3.3.1 Study Area
Visaka Industries Limited at Khasra No -: 265/1-4,266/2-5,285, Village-Rachakpura,
Tehsil – Niwai, Dist- Tonk, Rajasthan. This is an asbestos manufacturing unit project
and project will cover the maximum agriculture topography of 10 km of study area
and its co-ordinates spread 26° 25' 57.74" N latitude, 76° 01' 06.73" E longitude.
3.3.2 Introduction
Satellite design development and operations including data reception, processing,
interpretation, and utilization of satellite images. All these advancements have
widened the applicability of remotely sensed data in various areas, like forest cover,
agriculture type mapping, and their changes on a regional scale. If satellite data is
judiciously used along with the sufficient ground data, it is possible to carry out
detailed forest inventories, monitoring of land use, and vegetation cover at various
scales.
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Digital image processing and classification of the satellite imageries and analysis of
interpreted maps were carried out using ERADAS imagine 9.1
3.3.3 Source of information
The data in this work is collected from the following sources
1. Topographic data - From Survey of India Toposheet
2. Remotely Sensed Data --From IRS P6 – LISS IV Data
All the data used in this work have been supplied by National Remote Sensing
Centre, Hyderabad, India.
3.3.4 Study period
Study period of the proposed project is post season in the month of October –
December 2013.
3.3.5 Components
Following component observed in land use land cover classification;
• Built up: Settlement Urban/Rural, Civil Structures
• Agriculture: Crop land, Plantation, Fallow land, shifting cultivation.
• Forest: Forest plantation, all kind of forest.
• Grazing land
• Barren/ Uncultivable/Wasteland: Salt affected land, Sandy land, Scrub land,
Barren rocky, Rann.
• Wetland/ Water bodies: River, Stream, Canal, Lake, Pond, Reservoir, Coastal
Zone.
• Snow and Glacier: Seasonal and Permanent snow cover.
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3.3.6 Methodology
High resolution data (IRS-P6, LISS-IV) ordered from NRSC
Geometric corrections of IRS -P6, LISS-IV data using Survey of India toposheet at 1:50,000 scale
Identification and selection of study area
Land use Land cover classification by supervised classification method
Land use land cover classification by unsupervised classification
Extraction of Land use land cover classes using ERDAS/ Arc GIS + Thematic Maps
Accuracy Assessment
Final output generation
Ground Truthing
3.3.7 Objective
The objective of the present work is to prepare land use and land cover map using
hybrid digital classification technique. The land cover/ land use map will depict the
state of the land features and land use of the study area. In addition land cover/land
use thematic map will also be used in studying the proposed project. The land use/
land cover thematic map is also used for Drainage plan in Environmental Impact
Assessment report.
3.3.8 Data base
The details of the primary data in the form of digital data on LISS-IV for interpretation
and analysis are given in Table no. 3.2. The mask of the entire ropeway area
including the influence zone was generated from the IRS-P6 LISS-IV. For the
secondary data, Cartosat-1 was referred to for the preparation of drainage map.
Table No. 3.2
Database used for land use and land cover mapping
S. No. Satellite Sensor Date type & bands
1. IRS-P6 LISS-IV Digital (1,2,3)
2. Cartosat-I - Digital (1)
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3.3.9 Classification criteria
1. A land use and land cover classification system which can effectively employ orbital
and high-altitude remote sensor data should meet the following criteria (Anderson,
1971):
2. The minimum level of interpretation accuracy in the identification of land use and land
cover
3. Categories from remote sensor data should be at least 85 percent.
4. The accuracy of interpretation for the several categories should be about equal.
5. Repeatable or repetitive results should be obtainable from one interpreter to another
and from one time of sensing to another.
6. The classification system should be applicable over extensive areas.
7. The categorization should permit vegetation and other types of land cover to be used
as surrogates for activity.
8. The classification system should be suitable for use with remote sensor data
obtained at different times of the year.
9. Effective use of subcategories that can be obtained from ground surveys or from the
use of larger scale or enhanced remote sensor data should be possible.
10. Aggregation of categories must be possible.
11. Comparison with future land use data should be possible.
12. Multiple uses of land should be recognized when possible.
3.3.10 Classification scheme
Keeping in mind the objectives of preparation of environmental management plan
(EMP), action plan for LULC (Land use Land Cover), DEM (Digital Elevation Model),
Drainage plan, and classification scheme adopted for the preparation of land
use/land cover maps on 1:50,000 scales. Land use/ Land cover classification
standardized by NRSC/ISRO.
Sr. No. Description – I Description – II 1. Built-up Urban
Rural
Mining
2. Agriculture Crop land
Plantation
Fallow
Current Shifting Cultivation
3. Forest Evergreen/ Semi evergreen
Deciduous
Forest Plantation
Scrub Forest
Swamp/ Mangroves
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4. Grass/ Grazing Grass / Grazing
5. Barren/ Un-Culturable/ Waste Land
Salt affected Land
Gullied / Ravenous Land
Scrub Land
Sandy Area
Barren Rocky
Rann
6. Wetlands/ Water Bodies
Inland Wetland
Coastal Wetland
River / Stream / Canal
Water Bodies
7. Snow and Glacier Seasonal and Permanent Snow
3.3.11 Land use/ land cover area
The land use and land cover of the Proposed Visaka Industries Limited area includes
Settlement, road, railway track, agriculture fallow land, plantation, forest land, waste
land, river/streams, ponds etc. Total area of the buffer zone is 314.149 sq. km., major
part covered by agriculture fallow land 92.637%, Water bodies 3.507%, Rural/Urban
1.321%, Scrub Land 0.784%, Scrub Forest 0.638%, Major Roads 0.518%,
Lake/ponds 1.522%, Plantation 0.054%, Railway track 0.053%. Types of land use
and land cover and their geographic area are summarized in Table No. 3.3.
Table No. 3.3
Areas of the different categories of land use/ land cover classless.
Land Use/Land Cover Classification
Classes Area (sq.km.) Area (%)
Builtup- Rural/Urban 4.151 1.321347513
Builtup- Major Road 1.63 0.518862069
Builtup- Railway Track 0.167 0.053159488
Agriculture- Fallow 291.02 92.63757007
Agriculture- Plantation 0.172 0.054751089
Forest- Scrub Forest 2.005 0.638232176
Barren Land- Scrub Land 2.463 0.784022868
Water Bodies- Lake/Pond 1.522 0.484483478
Water Bodies- River/Stream 11.019 3.507571248
Total 314.149 100
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3.4 SOIL CHARACTERISTICS
3.4.1 Physiography
Tonk is situated on National Highway No. 12 at distance of 100 km from Jaipur. It is
located in northeastern part of the state between 75.19' & 76.16 East longitude and
25.41' and 26.24' North Latitude. The total area of the district is 7194 km. The district
mainly comprises a flat peneplain with thick alluvium cover. However the Rajkot
Baneta hills in the eastern part of Rajmahal- Toda Raisingh ridge in the southern part
of the district with isolated hills, Tordi and Chansen are the main hill ranges of district.
Banas is the only perennial river which flows through the district. The general
elevation of the plain ranges from 231 to 337 m above mean sea level and trends
from south-west to north-east.
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3.4.2 Soil Quality
The soil in the district varies from sandy loam to loam in Niwai block and parts of
Tonk block and from clay loam to loam in the remaining area. The National Council of
Applied Economic Research regards the district as having undifferentiated soil.
3.4.3 Geology
The district comprises Aravalli & Delhi Group of rocks. The Aravalli’s are represented
by the schists & gneisses and the Delhi is by grits, conglomerates & quartzites. Grits,
conglomerates and the schists and gneisses all have been considered to be of pre-
Aravalli age. The general trends of formations vary from N-S to NE-SW with steep
dips. The Aravallis and Delhis have been intruted by post Delhi granites, pegmatites
& basic dykes.
The grits & conglomerates are best exposed along the foot hills of Toda Raising-
Botunda ridge whereas the main hill ranges of Rajmahal, Toda Raisingh & Tordi-
Chansen etc. are composed of quartzites. Phyllites are exposed in the south-eastern
part of the district near Aligarh, Sop, etc. Rest of plain area is occupied by schists &
gneisses. The geological succession in Tonk district is given as below (after GSI).
Recent to Sub Recent Sand, alluvium etc
Delhi Supergroup Grits, conglomerates & quartzites.
Post- Aravalli Granite (intrusive)
Pre-Aravalli Schist, gneisses and
migmatites, phyllites, marble and quartzites.
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3.4.4 Data Generation
For studying soil quality of the region, samples were collected to assess the existing
soil conditions in and around the project area.
The sample was collected by ramming a core-cutter into the soil up to a depth of 90
cm. The present study on the soil quality establishes the baseline characteristics and
identifies the incremental concentrations if any, due to the proposed project. The
objective of the sampling is:
• To determine the baseline soil characteristics of the study area;
• To determine the impact of proposed activity on soil characteristics; and
• To determine the impact on soils more importantly from agricultural productivity
point of view.
The soil samples were collected from three different depths viz. 30 cm, 60 cm and 90
cm. The samples were then packed in polythene plastic bags and sealed. The
samples from three different depths were homogenized and then were analyzed.
3.4.5 Soil quality of study area
The soil study was carried out to analyze the soil characteristics of the study area.
For studying soil quality of the region 4 samples (including site) were collected,
description of the same as follows:
Table no. 3.4 Monitoring locations for soil quality testing
Location Code
Location Name Distance w.r.t Project Site
Direction w.r.t Project
Site
Co-ordinates
S-1 Project Site -- -- N-26025’51.1’’ E-76001’03.6’’
S-2 Kishorepura Ki Dhani
1.6 km NE N-26026’28.5’’ E-76001’47.2’’
S-3 Lalwari 3.05 km ESE N-26025’39.4’’ E-76001’58.6’’
S-4 Bhagatpur Rampura
3.6 KM N-26025’11.8’’ E-75059’07.3’’
Soil Quality
Four soil samples in 10 km radius project Area was collected and analyzed. The
analytical results are given in blow.
Table no. 3.5
Sample Code
Location Name Date of sampling
S-1 Project Site 30.05.2013
S-2 Kishorepura Ki Dhani 30.05.2013
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Soil Quality Analysis Results
S.No. Parameters Units S1 S2 S3 S4 1 Texture - Sandy Clay Sandy Clay Sandy Clay Sandy Clay
2.
Particle size Distributions
Sand % 42 38 40 36
Silt % 16 14 14 14
Clay % 42 48 46 50
3. Appearance -- Light Brown Color
Brown Color Brown Color Brown Color
4. Sodium as Na mg/100grm 1.56 1.39 1.36 1.52
5. pH (10% Slurry) - 7.23 7.25 7.23 7.26
6. Conductivity µmhos/cm 264 214 188 168
7. Bulk density gram/cc 1.36 1.28 1.02 0.98
8. Porosity % v/v 18 16 18 20
9. Total Organic Matter(TOC) % 0.72 0.88 0.92 0.90
10. Nitrogen as N mg/100grm 164 172 187 202
11. Potassium as K mg/100grm 86 102 89 105
12. Phosphorus as P mg/100grm 48 39 42 46
13. Zinc as Zn mg/kg 4.61 3.98 4.05 4.16
14. Cadmium as Cd mg/kg 0.01 0.01 0.01 0.02
15. Chlorides as Cl mg/100grm 0.98 0.84 0.92 0.79
16. Alkali Metals mg/kg 1.02 0.69 0.65 0.78
17. Permeability Cm/h 6.24 6.59 6.58 6.49
18. Water holding capacity % 16.28 18.98 20.52 21.54
19. Copper as Cu mg/kg 0.02 0.01 0.03 <0.01
20. Iron as Fe mg/kg 0.23 0.12 0.15 0.12
21. Lithium mg/kg 0.01 <0.01 <0.01 <0.01
22. Moisture Content % <1.00 <1.00 <1.00 <1.00
23. Boron as B mg/kg 0.08 0.26 0.08 0.12
3.4.6 Results & Conclusions
The soil analysis results are presented in Table 3.5 .The result obtained is compared with the
standard soil classification given Agriculture Soil Limits. It has been observed that the soils are
Sandy clay in texture and neutral in nature. The nutrient and organic matter contents are
medium and the soil is normally fertile.
3.5 AIR ENVIRONMENT
3.5.1 Climatology and Meteorology
Similar to most of the other cities in the state of Rajasthan, the town of Tonk
experiences harsh climatic conditions. Extreme conditions are prevalent in the town
throughout the year. Summers are very dry and temperatures soar during the peak
S-3 Lalwari 30.05.2013
S-4 Bhagatpur Rampura 30.05.2013
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summer months. Winters are dry as well and this season can be cold. The normal
annual rainfall (1901-70) of the district is 598mm whereas the average mean annual
rainfall (1979-2008) is 622mm. The summer season starts in the month of March and
the intensity of the heat increases till the month of June. The hottest month of the
year is May and temperatures can reach a maximum of around 45°C during this
time. The lowest temperatures that can be expected during the summer months are
around 26°C. The winter season is during the months between December and
February. The maximum temperature expected during the winter season is around
22°C. Temperatures reduce gradually from the month of July onwards.
3.5.2 Methodology
The methodology adopted for monitoring surface observations is as per the standard
norms laid down by Bureau of Indian Standards (IS: 8829) and India Meteorological
Department (IMD). Automatic Meteorological station has been installed near to the
proposed project site.
3.5.3 Meteorological data recorded at project site during the study period March to May
2013 (Pre Monsoon)
An auto weather monitoring station was installed during the study period to record
various meteorological parameters on hourly basis to understand the wind pattern,
Temperature variation, solar insulation and relative humidity variation etc.
Percentage frequencies of wind in 16 directions have been computed from the recorded
data during the Pre Monsoon study period. The pictorial representation of the summary
of the wind pattern is given blow of the study period.
Table no.3.6
Micro meteorological data for the study period at project site
Month Temperature (0C)
Relative Humidity (%)
Rainfall in mm
Wind Speed mph
Max Min Max Min Max Total Max Min
March - 2013 37.0 12.5 86.9 9.5 0 0 9.0 < 1.0
April - 2013 41.1 17.5 77.8 9.5 0 0 11.0 < 1.0
May - 2013 45.4 20.9 83.5 9.5 0 0 14.0 < 1.0
Wind pattern during the study period
The overall predominant wind direction on 24 hour basis was observed to be blowing
from NW to SE. Calm was observed to be 22.06%. The wind speed during this period
was observed to be 1.44 m/s.
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Table no.3.7 The Summary of the Wind Pattern is Given Below
S.No Wind Direction 0.5-2.1 Speed m/s
2.1-3.6 Speed m/s
3.6 - 5.7 Speed m/s
> = 5.7 Speed m/s
Total
1. N 103 55 10 1 169
2. NNE 110 56 3 0 169
3. NE 38 15 0 0 53
4. ENE 17 8 0 0 25
5. E 24 13 1 0 38
6. ESE 17 7 0 0 24
7. SE 14 3 0 0 17
8. SSE 36 14 3 0 53
9. S 25 12 0 0 37
10. SSW 48 11 0 0 59
11. SW 72 18 4 0 94
12. WSW 35 18 5 0 58
13. W 95 52 27 0 174
14. WNW 131 105 46 0 282
15. NW 110 64 16 0 190
16. NNW 150 104 24 0 278
Sub-Total 1025 139 1 1720 Calms 487
Missing/Incomplete 1 Total 2208
Figure no. 3.4
Wind rose 24hrs
3.5.4 Ambient Air Quality
The data was generated by Vison Labs, Hyderabad for March to May’2013 pre monsoon
season 2013, for ambient air quality status within 10 km radius of the site.
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The monitoring report is enclosed as Annexure- VII. Eight monitoring stations (including
project site) were installed at different locations during March to May’2013 to assess the
ambient air quality the summary of all the above location are given below Table no.3.11.
I. Methodology adopted for Air Quality Survey
� Selection of Sampling Locations
The baseline status of the air quality in the study area has been assessed through a
scientifically designed ambient air quality monitoring network. The design of monitoring
network in the air quality surveillance program has been based on the following
considerations:
• Meteorological conditions on synoptic scale;
• Topography of the study area;
• Representatives of regional background air quality for obtaining baseline status; and
• Representatives of likely impact areas.
Ambient Air Quality Monitoring (AAQM) stations were set up at eight locations with due
consideration to the above mentioned points. Table-3.8 gives the details of environmental
setting around each monitoring station and their distances with reference to the proposed
project.
Table No. 3.8 Location of air monitoring stations
S.No. Location Name Details Direction w.r.t
project Site Co-ordinates
1 Project Site At Site -- N-26025’52.4’’ E-76
001’03.4’’
2 Sedria Rajaram S/o NW N-26026’44.3’’ E-76
000’17.7’’
3 Dehold Ki Dhani Ajaykumar S/o Sreeramsevak
NNE N-26027’19.9’’ E-76
002’39.6’’
4 KishorePura Ki Mangilal NE N-26
026’28.4’’ E-76
001’45.4’’
5 Lalwari Shankarlal Sharma S/o
ESE N-26025’27.7’’ E-76
002’44.5’’
6 Shrisukhpur Madhan Jain
S/o Kaluram Ji SSE N-26
025’35.0’’ E-76
001’00.0’’
7 Thunj (Radhagovindpu
ra)
Shivaji Lal SSW N-26025’14.8’’ E-76
000’07.1’’
8 Bhagatpur Rampura
Mahendra kumar Jan S/o
WNW N-26025’09.2’’ E-75
058’56.5’’
Ambient air quality monitoring has been carried out with a frequency of two days per week at
eight locations covering one complete season except monsoon (CPCB guidelines). The
ambient air quality parameters along with their frequency of sampling are given in Table No.
3.10
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Table no. 3.9 Monitored Parameters and Frequency of Sampling
Parameters Sampling Frequency
Suspended Particulate Matter 24 hourly sample twice a week for a season except monsoon
Respirable Particulate Matter 24 hourly sample twice a week for a season except monsoon
Sulphur dioxide (SO2) 24 hourly sample twice a week for a season except monsoon
Oxides of Nitrogen (NOX) 24 hourly sample twice a week for a season except monsoon
II. Instruments used for sampling
Respirable Suspended Particulate Matter (RPM)/PM10 and gaseous pollutants like SO2,
NOx. And CO. APM 550 Fine Particle Sampler was used to monitor PM2.5.
III. Sampling and Analytical Techniques
PM2.5 and PM10 have been estimated by gravimetric method. Modified West and Gaeke
method (IS-5182 Part-II, 1969) has been adopted for estimation of SO2. Jacobs-
Hochheiser method (IS-5182 Part-IV, 1975) has been adopted for the estimation of NOx.
NDIR spectroscopy method will be adopted for carbon monoxide detection. The
techniques used for ambient air quality monitoring and its minimum detectable levels are
given in Table no. 3.10.
Table no. 3.10
Techniques Used for Ambient Air Quality Monitoring Sr. No.
Parameter Technique Technical Protocol Model no. Range and Sensitivity
1. Respirable Particulate Matter
Gravimetric method
IS- 5182(Part-IV) 1999 RDS- 9000 0.4 to 1.5 m
3/min
2. PM2.5 Gravimetric method
IS-5182 (Part-IV) 1999 APM 550 ±0.03 DGMm3
3. Sulphur Dioxide Modified West and Gaeke
method
IS-5182 (Part- II) 1969 -- --
4. Nitrogen Oxide Jacobs-Hochheiser
method
-- -- --
5. Carbon Monoxide NDIR spectroscopy
-- -- --
Filter Paper details
Apparatus Make Size Size Product Category no.
Filter Paper (PM10)
M/S Whatmann International Ltd.
203 x 254mm
GMF-S-10 Batch No-G015DO7
Filter Paper (PM2.5)
M/S Whatmann International Ltd.
47 mm Tuflon
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IV. Presentation of Results
The analysis results for the study period are presented in detail in Annexure- VII. Various
statistical parameters like 98th percentile, average, maximum and minimum values have
been computed from the observed raw data for all the AAQ monitoring stations. The
summary of these results for all the locations is presented in Table-3.11.These are
compared with the standards prescribed by Central Pollution Control Board (CPCB) for
rural and residential zone.
Table 3.11 Summary of ambient air monitoring for March to May’2013
Locations
Code
Location name
PM10 µµµµg/m3 PM2.5 µµµµg/m
3 SO2
µµµµg/m3
NOx
µµµµg/m3
CO
µµµµg/m
3
(Max.)
Max Min Avg. Max Min Avg. Max Min Avg. Max Min Avg.
A1 Project Site 39.3 30.6 34.9 20.3 14.2 17.2 5.1 4.1 4.5 12.6 11.2 11.8 123
A2 Sedria 52.8 43.2 48.5 27.9 19.3 24.2 6.7 4.4 5.4 15.6 12.5 14.3 248
A3 Dehold ki Dhani
42.5 34.3 38.2 21.6 17.3 19.4 5.3 4.4 4.8 13.2 12.3 12.8 215
A4 Kishore Pura ki Dhani
41.6 34.6 37.9 21 17.2 19.3 5.3 4.3 4.8 13.2 12.2 12.7 215
A5 Lalwari 52.9 43.2 48.2 26.3 20.4 23.7 6.8 4.6 5.7 15.3 13.5 14.4 291
A6 Shrisukhpur 41.2 33.6 37.0 21.6 15.6 18.3 5.2 4.2 4.7 13.2 12.2 12.7 182
A7 Thunj(Radhagovindpura)
41.5 34.5 38.2 21.6 17.3 19.3 5.1 4.3 4.7 13.6 12.4 12.8 182
A8 Bhagatpur Rampura
41.3 33.2 37.6 21.3 16.1 18.7 5.3 4.3 4.8 14.5 12.4 13.0 182
Table No. 3.11 (a) Chemical Characterization Analysis of PM10
Location Name : Project Site Date of Sampling : 15.04.2013 S.No Characteristics Units Project Site
1. Respirable Particulate Matter (PM10) µg/m3 35.4
2. Calcium as Ca µg/m3 1.81
3. Magnesium as Mg µg/m3 0.23
4. Sodium as Na µg/m3 0.02
5. Potassium as K µg/m3 0.01
6. Chromium as Cr µg/m3 <0.01
7. Aluminum as Al µg/m3 <0.01
8. Lead as Pb µg/m3 <0.01
9. Zinc as Zn µg/m3 <0.01
10. Iron as Fe µg/m3 <0.01
11. Nickel as Ni µg/m3 <0.01
12. Barium as Ba µg/m3 <0.01
13. Cadmium as Cd µg/m3 < 0.01
14. Mercury as Hg µg/m3 <0.001
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Table No. 3.11 (b)
Chemical Characterization Analysis of PM10
Location Name: Project Site
S.No. Characteristics Units Values
1. Particulate Matter (PM10)
(1264 m3 sample
Volume)
µg/m3 35.4
2. Silica µg/m3 <0.1
3.
POLY-AROMATIC HYDROCARBONS (PAH) Compound (PAH) Minimum Detection Limit (ug/L) Result (ug/L)
LC Column PAH (HC-ODC SIL-X eq I Naphthalene 1.8 1.9
II Acenaphthalene 2.3 1.8
III Acenaphthene 1.8 1.9
IV Fluorene 0.21 <0.21
GC Column 3% OV-17 Chromosorb A Anthracene (Group + Phenanthrene) 28.7 28.8
B Pyrene 3.4 3.4
C Benzo Fluranthene 3.1 < 3.1
D Benao (a) pyrene 4.0 4.1
E Fluoranthene 3.0 < 3.0
F Chrysene 4.2 < 4.2
Note: Total PAH observed in the Air Volume are 41.9 µg/L which is represented by actual sample volume of 1224 m
3. The volume of total PAH PM10 works out <0.05
µg/m3. The above results interpreted in light of the AAQ standards, indicated that the
Ambient Air quality of the sampling location was free of PAH contamination at the time of sampling.
V. Results of monitoring during March to May’2013
PM10: The maximum value for PM10 observed at Lalwari 52.9 µg/m3 and minimum
value for PM10 at Project Site 30.6 µg/m3. The 24 hours applicable limit for industrial,
Residential Rural and Other Areas is 100 µg/m3.
PM2.5: The maximum value for PM 2.5 observed at Sedria 27.9 µg/m3 and minimum
value for PM 2.5 at Project site 14.2 µg/m3. The 24 hours applicable limit for
industrial, Residential Rural and Other Areas is 60 µg/m3.
SO2: The maximum value for SO2 observed at Lalwari 6.8 µg/m3 and minimum value
for SO2 at Project site 4.2 µg/m3. The 24 hours applicable limit for industrial,
Residential Rural and Other Areas is 80 µg/m3.
NO2: The maximum value for NO2 observed at Sedria 15.6 µg/m3 and minimum value
for NO2 at Project site 12.2 µg/m3. The 24 hours applicable limit for industrial,
Residential Rural and Other Areas is 80 µg/m3.
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CO: The maximum value for CO observed at Lalwaria 291 µg/m3 and minimum value
for CO at Project site is 200 µg/m3. The 8 hours applicable limit for Industrial,
Residential Rural and other areas is 2000 µg/m3.
Results and Conclusions
The results of the monitored data indicate that the ambient air quality of the region in
general is conformity with respect to norms of National Ambient Air Quality standards
of CPCB, at all locations monitored.
3.6 WATER ENVIRONMENT
3.6.1 Hydrogeology & Drainage
In the studied area, the rainfall runoff is generated through various minor natural
drains. A seasonal river “Dhil” flows around 2 km. in south of proposed site from
West to South East. The area comprises of alluvial plain which is formed by the Dhil
river which is tributary of River Banas. The finished ground level gradient & storm
water runoff is towards South East. Rainfall plays a major role in groundwater
availability of region like Niwai as it is the major source available for groundwater
recharge. Ground water occurs mostly under phreatic conditions.
I. Aquifer Type
Ground water generally occurs under water table conditions where as in hard rock
and crystalline rocks, it is under slight pressure. Hard rock of Bhilwara Super Group
form main aquifers in the area comprising of mica schist and phyllite. These hard
rocks are covered by Quaternary fluvial and Aeolian deposits mainly composed of
sand, silt, clay, gravel and Kankar. The ground water occurs under unconfined to
semi-confined conditions & its occurrence and movement is mainly controlled by
weathered portion of hard rock and fractures. The dynamic water zone is 3 m, which
is controlled by hydraulic gradient, topography and aquifer characteristics.
II. Water Level Behavior, Water Level Fluctuation & Ground Water Flow
The water level in the study area varies from 8 m to 31 m below ground level in the
month of May‘2013, as per hydro geological investigation and the location of well
inventory in the study area. Average seasonal fluctuation of Niwai block is 3 m as per
CGWB district groundwater brochure. Groundwater flow direction in the investigated
area is towards South East Figure No. 3.5. The main sources of recharge in the
study area is rainfall, the other sources of recharge is return seepage from irrigation.
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Figure No. 3.5
Water level contour map showing flow direction
3.6.2 Water Quality
To assess the present ground water condition seven sampling location were selected for
ground water quality testing and one sampling location was finalized for surface water
sampling. The detail about the location is given in the Table 3.12. The detailed analysis
report is enclosed as Annexure-VII. The detailed analysis report of pre monsoon season
is enclosed as Annexure-VIII. The results are presented in Table No. 3.13.
The purpose of this study is to:
• Assess the water quality characteristics for critical parameters;
• Evaluate the impacts on agricultural productivity, habitat conditions, recreational
resources and aesthetics in the vicinity; and
• Predict the likely impacts on water quality due to the proposed project and related
activities.
3.6.3 Methodology
The monitoring location has been finalized considering following points:-
• Drainage pattern of the regional area;
• Location of residential areas representing different activities/likely impact areas;
Project: Visaka Industries Ltd. SECTION-III/Description of the Environment
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Enkay Enviro Services Pvt. Ltd., Jaipur 82
Ground water sources covering 10-km radial distance were examined for physico-chemical
parameters in order to assess the effect of industrial and other activities on the
hydrosphere resources. The samples were collected and analyzed as per the procedures
specified in 'Standard Methods for the Examination of Water and wastewater' published by
American Public Health Association (APHA).
3.6.4 Water Sampling Locations
Seven groundwater samples were collected as grab samples and were analyzed for
various parameters. The analyzed results were compared with the standards for drinking
water as per IS: 10500. The water sampling locations are listed below in Table 3.12.
Table 3.12 Water Quality Locations
Location Code
Location Name Details Direction w.r.t Project Site
Co-ordinates
GW-1 Sedria Near School ,Hand pump
Water NW N-26
026’28.5’’ E-76
000’13.7’’
GW-2 Dehold Ki Dhani Near Temple Hand pump
Water NNE N-26
027’23.1’’ E-76
002’47.6’’
GW-3 Kishorepura Ki Dhani
Near School, Hand pump Water
NE N-26026’20.7’’ E-76
001’51.9’’
GW-4 Lalwari Supply Water ESE N-26025’30.1’’ E-76
002’33.8’’
GW-5 Shrisukhpur Near Gram Panchayat Hand pump Water
SSE N-26025’47.6’’ E-76
001’06.5’’
GW-6 Thunj (Radhagovindpura)
Hand pump Water SSW N-26
025’13.8’’ E-76
000’15.1’’
GW-7 Bhagatpur Rampura
Near Gram Panchayat Hand pump
WNW N-26025’03.2’’ E-75
058’57.8’’
SW-1 Sedria Talab Water
Talab Water NW N-26
026’34.9’’ E-76
000’19.8’
Table 3.13 (a) Water quality of the study area
Sr.No. Parameter Requirement (Desirable
Limits)
Permissible Limits in the Absence of Alternate Source
Units
GW1
GW2
GW3
1 pH 6.5 – 8.5 NR - 7.14 7.17 7.24
2 Color (Hazen units)
< 5 < 25 Hazen <01 <01 <01
3 Taste Agreeable - - Agreeable Agreeable Agreeable
4 Odor Unobjec-tionable
- - Unobjec-tionable
Unobjec-tionable
Unobjec-tionable
5 Conductivity -- -- µS/cm 1986 1242 1466
6 Turbidity (NTU) < 5 < 10 NTU 1.30 1.50 1.30
7 Total Dissolve solids
< 500 < 2000 mg/L 1288 802 948
8 Total Hardness as CaCO3
< 300 < 600 mg/L 368 336 576
9 Total Alkalinity < 200 < 600 mg/L 440 360 300
10 Calcium as Ca < 75 < 200 mg/L 89.6 70.4 134.4
Project: Visaka Industries Ltd. SECTION-III/Description of the Environment
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11 Magnesium as Mg < 30 < 100 mg/L 34.5 38.4 57.6
12 Residual Chlorine < 0.2 - mg/L <0.02 <0.02 <0.02
13 Boron < 1 < 5 mg/L 0.005 0.002 0.008
14 Chloride as Cl < 250 < 1000 mg/L 340.8 134.9 255.6
15 Sulphate as SO4 < 200 < 400 mg/L 53.7 54.7 55.6
16 Fluorides as F- < 1.0 < 1.5 mg/L 1.16 1.12 1.16
17 Nitrates as NO3 < 45 < 100 mg/L 8.72 8.19 8.82
18 Phenolic Compounds
< 0.001 < 0.002 mg/L <0.001 <0.001 <0.001
19 Cyanide as CN < 0.05 NR mg/L <0.001 <0.001 <0.001
20 Anionic Detergents
< 0.2 < 1.0 mg/L <0.001 <0.001 <0.001
21 Mineral Oil < 0.01 < 0.03 mg/L <0.001 <0.001 <0.001
22 Cadmium as Cd < 0.01 NR mg/L 0.004 <0.001 <0.001
23 Arsenic as As < 0.01 NR mg/L <0.001 <0.001 <0.001
24 Copper as Cu < 0.05 < 1.5 mg/L 0.026 <0.001 0.002
25 Lead as Pb < 0.05 NR mg/L <0.001 <0.001 <0.001
26 Manganese as Mn < 0.1 < 0.3 mg/L 0.004 <0.001 <0.001
27 Iron as Fe < 0.3 < 1.0 mg/L 0.12 0.08 0.15
28 Chromium as Cr6+
< 0.05 NR mg/L <0.001 <0.001 <0.001
29 Zinc as Zn < 5 < 15 mg/L 0.032 0.0023 0.039
30 Aluminum as Al < 0.03 < 0.2 mg/L <0.001 <0.001 <0.001
31 Mercury as Hg < 0.001 NR mg/L <0.0002 <0.0002 <0.0002
32 Selenium as Se < 0.01 NR mg/L < 0.001 < 0.001 < 0.001
33 E-coli(Nos/100 ml) Absent - - Absent Absent Absent
34 Coliform Organisms/100mL
< 10 -- MPN/ 100 ml
Nil Nil Nil
Table 3.13 (b)
Water quality of the study area Sr.No. Parameter Requireme
nt (Desirable
Limits)
Permissible Limits in
the Absence of Alternate Source
Units
GW4
GW5
GW6
GW7
1 pH 6.5 – 8.5 NR - 7.19 7.08 7.15 7.19
2 Color (Hazen units)
< 5 < 25 Hazen
<01 <01 <01 <01
3 Taste Agreeable - - Agreeable
Agreeable Agreeable Agreeable
4 Odor Unobjec-tionable
- - Unobjec-
tionable
Unobjec-tionable
Unobjec-tionable
Unobjec-
tionable
5 Conductivity -- -- µS/cm
1058 1458 926 4156
6 Turbidity (NTU) < 5 < 10 NTU 1.50 1.60 1.50 1.20
7 Total Dissolve solids
< 500 < 2000 mg/L 684 942 598 2696
8 Total Hardness as CaCO3
< 300 < 600 mg/L 264 576 368 1120
9 Total Alkalinity < 200 < 600 mg/L 320 400 280 520
10 Calcium as Ca < 75 < 200 mg/L 54.4 121.6 83.2 227.2
11 Magnesium as Mg < 30 < 100 mg/L 30.7 65.2 38.4 132.7
12 Residual Chlorine < 0.2 - mg/L <0.02 <0.02 <0.02 <0.02
13 Boron < 1 < 5 mg/L <0.001 0.006 <0.001 0.031
14 Chloride as Cl < 250 < 1000 mg/L 113.6 156.2 99.4 1008.2
Project: Visaka Industries Ltd. SECTION-III/Description of the Environment
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15 Sulphate as SO4 < 200 < 400 mg/L 38.4 65.2 31.6 116.1
16 Fluorides as F- < 1.0 < 1.5 mg/L 0.96 1.23 0.68 1.98
17 Nitrates as NO3 < 45 < 100 mg/L 6.09 6.64 5.64 10.15
8 Phenolic Compounds
< 0.001 < 0.002 mg/L <0.001 <0.001 <0.001 <0.001
19 Cyanide as CN < 0.05 NR mg/L <0.001 <0.001 <0.001 <0.001
20 Anionic Detergents < 0.2 < 1.0 mg/L <0.001 <0.001 <0.001 <0.001
21 Mineral Oil < 0.01 < 0.03 mg/L <0.001 <0.001 <0.001 <0.001
22 Cadmium as Cd < 0.01 NR mg/L <0.001 <0.001 <0.001 <0.001
23 Arsenic as As < 0.01 NR mg/L <0.001 <0.001 <0.001 0.006
24 Copper as Cu < 0.05 < 1.5 mg/L <0.001 0.005 <0.001 0.052
25 Lead as Pb < 0.05 NR mg/L <0.001 <0.001 <0.001 0.002
26 Manganese as Mn < 0.1 < 0.3 mg/L <0.001 <0.001 <0.001 0.009
27 Iron as Fe < 0.3 < 1.0 mg/L 0.06 0.11 0.06 0.23
28 Chromium as Cr6+ < 0.05 NR mg/L <0.001 <0.001 <0.001 <0.001
29 Zinc as Zn < 5 < 15 mg/L 0.009 0.009 0.004 0.59
30 Aluminum as Al < 0.03 < 0.2 mg/L <0.001 <0.001 <0.001 0.001
31 Mercury as Hg < 0.001 NR mg/L <0.0002 <0.0002 <0.0002 <0.0002
32 Selenium as Se < 0.01 NR mg/L < 0.001 < 0.001 < 0.001 < 0.001
33 E-coli(Nos/100 ml) Absent - - Absent Absent Absent Absent
34 Coliform Organisms/100mL
<10 -- MPN/ 100 ml
Nil Nil Nil Nil
Table No. 3.13 (c)
Surface Water Analysis Results
Sample code .NO Location Name Date of sampling
SW-1 Sedria Talab Water 30.05.2013
S. No. Parameter Limits (Class C) Units SW1 1 pH 6.5 – 8.5 - 7.23
2 Color (Hazen units) < 300 Hazen 36
3 Taste -- - Agreeable
4 Odor -- - Unobjectionable
5 Conductivity -- µS/cm 730
6 Turbidity (NTU) -- NTU 26.6
7 Total Dissolve solids < 1500 mg/L 468
8 Total Hardness as CaCO3 -- mg/L 96
9 Total Alkalinity -- mg/L 220
10 Calcium as Ca -- mg/L 22.4
11 Magnesium as Mg -- mg/L 9.6
12 Residual Chlorine -- mg/L <0.02
13 Boron -- mg/L 0.005
14 Chloride as Cl < 600 mg/L 78.1
15 Sulphate as SO4 < 400 mg/L 24.9
16 Fluorides as F- < 1.5 mg/L 0.59
17 Nitrates as NO3 < 50 mg/L 5.14
18 Phenolic Compounds < 0.005 mg/L <0.001
19 Cyanide as CN < 0.05 mg/L 0.004
20 Anionic Detergents < 1 mg/L 0.026
21 Mineral Oil -- mg/L <0.001
22 Cadmium as Cd < 0.01 mg/L 0.002
23 Arsenic as As < 0.2 mg/L <0.001
24 Copper as Cu < 1.5 mg/L 0.03
Project: Visaka Industries Ltd. SECTION-III/Description of the Environment
Document No.: EESPL/VIL/002/358-EC/IND./2013
Enkay Enviro Services Pvt. Ltd., Jaipur 85
Results & Conclusions
Eight groundwater and one surface water samples were collected as grab samples
and were analyzed for various parameters. The result indicates that the ground water
quality values at location G7 (Bhagatpur Rampura) is much higher (TDS, Total
Hardness, Total Alkalinity, Total Calcium, Total Magnesium and fluorides) with
respect to other locations. The surface water results are more or less within the
permissible limit except for the BOD and COD parameter, which are slightly higher
than the permissible limit.
3.7 NOISE ENVIRONMENT
The physical description of sound concerns its loudness as a function of frequency.
Noise in general is sound, which is composed of many frequency components of various
types of loudness distributed over the audible frequency range. The most common and
universally accepted scale is the A weighted scale, which is measured as dB (A). This is
more suitable for audible range of 20 to 20,000 Hz. The scale has been designed to
weigh various components of noise according to the response of human ear. The
environmental impact of noise can have several effects varying from Noise Induced
Hearing Loss (NIHL) to annoyance depending on loudness of noise.
The main objective of noise monitoring in the study area is to establish the baseline noise
levels and assess the impact of the total noise expected to be generated during the
project operations around the project site. The statistical analysis is done for measured
noise levels at seven locations in the study area. The parameters are analyzed for Leqday
and Leqnight. The statistical analysis results are given below:
25 Lead as Pb < 0.1 mg/L <0.001
26 Manganese as Mn -- mg/L <0.001
27 Iron as Fe < 50 mg/L 0.21
28 Chromium as Cr6+
< 0.05 mg/L <0.001
29 Zinc as Zn < 15 mg/L 0.39
30 Aluminum as Al -- mg/L <0.001
31 Mercury as Hg -- mg/L <0.0002
32 Selenium as Se < 0.05 mg/L < 0.001
33 Dissolved Oxygen >4 mg/L 3.2
34 Biochemical Oxygen Demand ( 5 days at 20
0 C)
< 3 mg/L 15
35 Chemical Oxygen Demand -- mg/L 48
36 E-coli(Nos/100 ml) -- - Absent
37 Coliform Organisms < 5000 MPN/100 ml 4652
Project: Visaka Industries Ltd. SECTION-III/Description of the Environment
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3.7.1 Identification of Sampling Locations
A preliminary reconnaissance survey has been undertaken to identify the major noise
generating sources in the area. Noise at different noise generating sources has been
identified based on the residential, industrial and commercial activities in the area.
The noise monitoring has been conducted for determination of noise levels at seven
locations in pre-monsoon in the study area. The noise levels at each location were
recorded for 24-hrs. The environment setting of each noise monitoring location is given in
Table-3.14.
Table 3.14 Location of monitoring station of ambient noise levels in the study area
Location Code
Location Name Direction w.r.t Plant Site (km)
N-1 Project Site --
N-2 Sedria 1.9
N-3 Dehold Ki Dhani 2.7
N-4 KishorePura Ki Dhani 1.6
N-5 Lalwari 3.05
N-6 Shrisukhpur 1.06
N-7 Thunj (Radhagovindpura) 1.5
N-8 Bhagatpur Rampura 3.6
3.7.2 Method of Monitoring
Sound Pressure Levels (SPL) measurements were recorded at six locations. The readings
were taken for every hour for 24-hrs. The day noise levels have been monitored during 6
am to 10 pm and night noise levels during 10 pm to 6 am at all the locations covered in the
study area.
Measured noise level displayed as a function of time provides a useful scheme for
describing the acoustical climate of a community. Noise levels recorded at each station are
computed for equivalent noise levels. Equivalent noise level is a single number descriptor
for describing time varying noise levels.
3.7.3 Presentation of Results
The statistical analysis is done for measured noise levels at eight locations in the study
area. The parameters are analyzed for Lday, Lnight, and Ldn. The statistical analysis results
are given in Table-3.15
Table-3.15
Ambient Noise Levels in The Study Area [dB(A)] during March to May 2013
Location code
Location Name Direction w.r.t Plant Site (km)
Date of sampling
N1 Project Site -- 08.04.2013
N2 Sedria 1.9 10.04.2013
N3 Dehold Ki Dhani 2.7 12.04.2013
N4 Kishore Pura Ki Dhani 1.6 15.04.2013
N5 Lalwari 3.05 17.04.2013
N6 Shrisukhpur 1.06 19.04.2013
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N7 Thunj (Radhagovindpura) 1.5 22.04.2013
N8 Bhagatpur Rampura 3.6 24.04.2013
Values are in db(A)
3.7.4 Observation of Results
a) Day Time Noise Levels (Leqday)
Study Area
The daytime (Leqday) noise levels are observed to be in the range of 50.8 – 46.4
dB (A) which are within the prescribed limit of 55 dB (A).
b) Night time Noise Levels (Leqnight)
Study Area
The nighttime (Leqnight) Noise levels are observed to be in the range of 43.6 –
38.0 dB (A) Which are within the prescribed limit of 45 dB (A)
Time N1 N2 N3 N4 N5 N6 N7 N8 DAY TIME
7 AM 42.6 44.8 40.3 41.6 45.8 42.5 47.2 43.1
8 AM 45.8 46.5 43.6 42.2 47.2 45.8 49.5 48.5
9 AM 47.5 48.3 46.2 47.8 49.5 48.8 51.6 49.8
10 AM 48.3 50.4 47.8 49.7 50.4 49.5 53.8 50.6
11 AM 49.8 51.3 49.2 48.3 48.2 50.3 50.4 48.5
12 NOON 47.2 50.2 46.3 45.6 46.5 46.6 49.5 47.2
13 PM 46.5 48.3 45.8 47.8 45.9 48.8 48.6 48.3
14 PM 48.3 49.6 46.9 48.4 47.3 49.2 49.9 46.8
15 PM 46.2 47.8 47.3 49.9 46.5 47.3 50.4 47.7
16 PM 47.8 48.6 48.2 48.3 45.9 48.1 51.2 48.9
17 PM 49.5 50.7 48.9 50.4 48.5 49.2 53.5 49.8
18 PM 48.3 51.2 46.2 49.9 46.2 47.6 52.4 48.2
19 PM 46.8 49.5 44.6 46.3 44.8 46.5 51.2 46.7
20 PM 45.2 47.3 43.8 45.8 43.4 44.3 49.8 43.6
21 PM 43.3 45.2 39.5 42.6 41.2 42.8 46.7 42.2
NIGHT TIME
22 PM 42.8 43.5 39.8 40.5 39.5 40.5 45.8 40.8
23 PM 41.6 42.8 38.4 37.2 38.5 39.8 44.3 39.2
24 MN 40.9 40.6 37.6 36.8 38.9 40.4 42.8 38.4
1 AM 39.2 41.3 38.8 36.2 37.4 39.5 41.6 37.1
2 AM 38.5 39.5 37.2 35.7 36.2 38.2 40.3 36.2
3 AM 39.6 40.2 36.4 36.6 38.0 37.1 41.5 36.9
4 AM 37.4 41.6 36.9 37.4 39.8 38.5 42.6 38.2
5 AM 40.3 42.4 37.2 38.1 40.3 39.5 44.5 39.2
6 AM 41.5 43.1 39.5 40.5 42.9 41.2 45.8 41.3
Maximum 49.8 51.3 49.2 50.4 50.4 50.3 53.8 50.6
Minimum 37.4 39.5 36.4 35.7 36.2 37.1 40.3 36.2 Day
equivalent 47.3 49.1 46.4 47.7 47.0 47.1 50.8 47.3
Night equivalent
40.5 41.9 38.1 38.0 39.5 39.6 43.6 38.9
Project: Visaka Industries Ltd. SECTION-III/Description of the Environment
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3.8 BIOLOGICAL ENVIRONMENT
Documentation of biological components in a project area and its immediate
surroundings is imperative in the case of any developmental project, to ensure that
the ecological setup of the area does not degrade and in effect is improved. For
understanding the impact of a proposed project, it is better to prioritize the
conservation issues, in terms of flora and fauna, in addition to other base line
parameters. Biodiversity study of the proposed project ‘Visaka Industries’ was
carried out to understand the status of predominant floral and faunal groups i.e.
trees, shrubs, herbs, grasses, herpeto-fauna, avifauna and mammals. To collect data
and information on specific components of the ecological system and pertinent
issues widely used standard scientific methods were adopted. Rapid field surveys
were undertaken during Oct-Nov 2013 for collecting relevant data.
The objectives of the present study were as follows:
• To identify the floral and faunal diversity,
• To assess nature and distribution of the vegetation in the area,
• To identify the endangered species of flora and fauna, if any
• Discussion with local people so as to elicit information about local plants,
animals and their uses; Gathering data for ethno biology.
• To prepare conservation plan for Schedule I fauna , if any
a. Methodology
Extensive literature review was carried out to indentify the representative
spectrum of threatened species, population and ecological communities listed by
IUCN, WCMC, ZSI, BSI and Indian wild Life Protection act, 1972 (IWPA 1972).
Biodiversity study of the proposed project of Visaka Industries Ltd., coming up at
village Rachakpura, Shedriya Grampanchayat, Tehsil Niwai Dist. Tonk
Rajasthan, was carried out to understand the status of predominant floral and
faunal groups i.e. trees, shrubs, herbs, grasses, herpetofauna, avifauna and
mammals.
Table 3.16
Methods used for study of flora & fauna
Taxa Sampling Methods Plants Quadrate sampling and enumeration
Butterflies Transect, Visual encounter survey
Amphibians Visual encounter survey (search)
Reptiles Visual encounter survey (search)
Birds Point count, opportunistic observation
Mammals Tracks and signs, and visual encounter survey
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Fauna:
i. Avifauna
Species search and census: Standard methods were followed to survey the avifauna.
Point count method was followed for counting the birds. Opportunistic surveys were
also carried out with respect to avifaunal checklist. Identification by calls was also
made for species which were not directly encountered or were hidden in the
vegetation or canopy. Secondary data collected from the literature was also included
in the present given list.
ii. Herpetofauna
Amphibians and reptiles recorded during area searches were identified by visual
characteristics. Aquatic searches involved examining each type of aquatic habitat.
iii. Mammals
Presence of mammals was documented by using both direct sightings and indirect
evidences i.e. animal burrows/holes, scats, pellets, droppings and tracks
Opportunistic sightings were also included. Circular Plots were used to search
indirect evidences.
Floristic studies were conducted during March-May 2013 to know the presence of
any endangered/threatened/endemic plant species study area of the existing industry
(10-km radius).
The data collected in the field was analyzed for secondary parameters such as
density, frequency and abundance following standard phyto-sociological methods.
Shannon-Wiener diversity index (Shannon and Wiener, 1963) was calculated for all
life forms as follows:
Table 3.17
Estimation of phyto-sociological parameters
1 Frequency (%) = (No. of quadrats of occurrence of the species X 100) / Total No. of quadrats sampled
2 Abundance = Total No. of individuals of the species / No. of quadrats of Occurrence
3 *Density = Total No. of individuals of the species / Total No. of quadrats sampled
4 Relative Frequency = (Frequency of the given species X 100) / Sum of all frequencies
5 Relative Density = (Density of the given species X 100) / Sum of all densities
6 Relative Abundance = (Abundance of species X 100) / Sum of all abundances 7 Basal Area = (GBH)2 / 4Π
8 Dominance = Total Basal Area / Total area sampled 9 Relative Dominance = (Dominance of given species X 100) / Dominance of all
species
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10 Important Value Index (I.V.I.) = Relative Density + Relative Frequency + Relative Dominance
Note: *Density refers to the number of individuals per unit area of a site.
STATISTICAL ANALYSIS
Shannon-Wiener diversity index (Shannon and Wiener, 1963) was calculated for all
life forms following:
Shannon- Wiener Information Function: D = -Σ pi ln pi
Where: i = an index for the number of species sampled, pi = ni/N =percentage of
species i in the entire sample (N) of individuals, and ln = natural log. Multiply the
percentage (or proportion) of each species in the sample times the natural log of that
same value, sum the products across all species, and then multiply by minus 1.
Forest blocks within 10 km radius
S. No. Name of Forest Block Direction Distance 1. Open Mixed Jungle North-East 5.0 km
BIODIVERSITY PROFILE OF THE CORE ZONE (PROJECT SITE: 91054 Sq.m
/9.10 ha)
Vegetation Survey:
List of the plants recorded from the core zone (project site) is given below (table no.
3.19):
Table No. 3.18
Plants recorded in the proposed project area: Visaka Industries Ltd.
Trees
No tree species observed during the site visit
Shrubs 1 Aak Calotropis gigantea Apocynaceae (Sub.
family Asclepiadaceae)
Agriculture
2 Vilayati Babool
Prosopis juliflora Fabaceae (Sub. family Mimosoideae)
Agriculture
4 Jharberi Zizyphus nummularia Rhamnaceae Agriculture
5 Behaya Ipomoea carnea Convolvulaceae Agriculture
Herb & Grasses
S. No. Vernacular
Name Scientific name Family
Habitat
1 Bui Aerva tomentosa Amaranthaceae
2 Jangali Cholai
Amaranthus spinosus Amaranthaceae Scrubland
3 Pili Kantili Argemone mexicana Papaveraceae
Scrubland/ Agriculture
4 Doob Cynodon dactylon Poaceae Desert/ Scrubland/ Agriculture
5 Unthkanta Echinops echinatus Asteraceae Scrubland/ Agriculture
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6 Badi Dudhi Euphorbia hirta Euphorbiaceae Desert/ Scrubland/ Agriculture
7 Jangi Gobi/ Van gobi
Launaea procumbens Asteraceae Scrubland/ Agriculture
8 Gajar Ghas Parthenium hysterophorus
Asteraceae Desert/ Scrubland/ Agriculture
9 Kantkeri Solanum xanthocarpum
Solanaceae Desert/ Scrubland/ Agriculture
10 Sarphonk Tephrosia purpurea Fabaceae Desert/ Scrubland/ Agriculture
11 Gokhru Tribulus terrestris Zygophyllaceae Desert/ Scrubland/ Agriculture
12 Barahmasi Tridax procumbens Asteraceae Scrubland/ Agriculture
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3
BU
FF
ER
ZO
NE
(i.
e.
10 k
m r
ad
ius f
rom
th
e p
eri
ph
ery
of
the p
roje
ct
sit
e)
Veg
eta
tio
n s
urv
ey:
1.
Tre
e s
pecie
s:
Tab
le N
o.
3.1
9
Imp
ort
an
t V
alu
e In
de
x (
IVI)
of
tree s
pe
cie
s in
th
e B
uff
er
zo
ne o
f stu
dy a
rea
Lif
e F
orm
: T
ree
(100x 1
00
m.)
V
ern
acu
lar
na
me
S
cie
nti
fic N
am
e
To
tal N
o o
f q
uad
rate
stu
die
d
#
@
F (
%)
D
A
RF
R
D
RA
IV
I
Ronjh
A
cacia
le
ucoph
ole
a
70
27
31
38.6
0.4
4
1.1
5
9.0
6.5
4.0
19.5
Bab
oo
l A
cacia
nilo
tica
70
34
56
48.6
0.8
0
1.6
5
11.3
11.8
5.7
28.8
Kum
ttha
Acacia
se
neg
al
70
12
19
17.1
0.2
7
1.5
8
4.0
4.0
5.5
13.5
Bae
l A
eg
le m
arm
elo
s
70
8
9
11.4
0.1
3
1.1
3
2.7
1.9
3.9
8.5
Siris
A
lbiz
ia lebb
eck
70
12
14
17.1
0.2
0
1.1
7
4.0
2.9
4.1
11.0
Neem
A
zadir
achta
ind
ica
70
29
39
41.4
0.5
6
1.3
4
9.7
8.2
4.7
22.6
Dhak
Bute
a m
onosp
erm
a
70
30
45
42.9
0.6
4
1.5
0
10.0
9.5
5.2
24.7
lasod
a
Cord
ia d
ichoto
ma
70
5
6
7.1
0.0
9
1.2
0
1.7
1.3
4.2
7.1
Shesh
am
D
alb
erg
ia s
issoo
70
24
47
34.3
0.6
7
1.9
6
8.0
9.9
6.8
24.7
Kun
ali/
khairi
Dic
hro
sta
chys c
inere
a
70
3
5
4.3
0.0
7
1.6
7
1.0
1.1
5.8
7.9
Safe
da
E
ucaly
ptu
s g
lob
olu
s
70
12
29
17.1
0.4
1
2.4
2
4.0
6.1
8.4
18.5
Sub
abu
l Leucae
na leucoceph
ala
70
11
19
15.7
0.2
7
1.7
3
3.7
4.0
6.0
13.7
Kankera
M
ayte
nus e
marg
inata
70
19
31
27.1
0.4
4
1.6
3
6.3
6.5
5.7
18.5
Khajo
or
Pho
en
ix s
ylv
estr
is
70
15
25
21.4
0.3
6
1.6
7
5.0
5.3
5.8
16.1
Kara
nj
Pon
gam
ia p
innata
70
13
21
18.6
0.3
0
1.6
2
4.3
4.4
5.6
14.4
Kheja
ri
Pro
sop
is c
inera
ria
70
24
42
34.3
0.6
0
1.7
5
8.0
8.8
6.1
22.9
Rohid
a
Tecom
ella
un
dula
ta
70
5
9
7.1
0.1
3
1.8
0
1.7
1.9
6.3
9.8
Ber
Ziz
iph
us m
auritian
a
70
17
29
24.3
0.4
1
1.7
1
5.7
6.1
6.0
17.7
428.6
6.8
0
28.6
5
100.0
100.0
100.0
300.0
#: T
ota
l n
o o
f qu
adra
te in w
hic
h s
pecie
s o
ccurr
ed,
@:
Tota
l no.
of
ind
ivid
ua
ls, F
: F
requency (
%),
D: D
ensity,
A:
Abu
nda
nce, R
F:
Re
lative F
requ
ency,
RD
: R
ela
tive D
ensity, R
A:
Rela
tive A
bund
ance, IV
I: I
mport
ant V
alu
e I
nd
ex S
han
non W
ien
er
Div
ers
ity I
nd
ex (
H’)
fo
r tr
ees w
as o
bserv
ed
: 2.8
Pro
ject:
Vis
ak
a In
du
str
ies
Ltd
.
SE
CT
ION
-III
/De
scri
pti
on
of
the E
nvir
on
men
t
Do
cu
men
t N
o.:
EE
SP
L/V
IL/0
02/3
58-E
C/IN
D./2
013
En
ka
y E
nvir
o S
erv
ice
s P
vt.
Ltd
., J
aip
ur
9
4
The h
ighest
IVI
for
trees a
t stu
dy a
rea w
as r
ecord
ed f
or
Acacia
nilo
tica (
28.8
), P
rosopis
cin
era
ria (
55.5
), B
ute
a m
onosperm
a (
24.7
)
and D
alb
erg
ia s
issoo (
24.7
) w
ith I
VI
valu
es in p
are
nth
esis
.
Fig
ure
No
. 3.6
C
om
mo
n t
ree s
pecie
s o
bserv
ed
in
th
e s
tud
y a
rea
Pro
ject:
Vis
ak
a In
du
str
ies
Ltd
.
SE
CT
ION
-III
/De
scri
pti
on
of
the E
nvir
on
men
t
Do
cu
men
t N
o.:
EE
SP
L/V
IL/0
02/3
58-E
C/IN
D./2
013
En
ka
y E
nvir
o S
erv
ice
s P
vt.
Ltd
., J
aip
ur
9
5
Tab
le 3
.20
Imp
ort
an
t V
alu
e In
de
x (
IVI)
of
sh
rub
sp
ecie
s in
th
e b
uff
er
zo
ne o
f stu
dy a
rea
en
tifi
c N
am
e
To
tal N
o o
f q
uad
rate
stu
die
d
#
@
F (
%)
D
A
RF
R
D
RA
IV
I
Adh
ato
da v
asic
a
70
17
36
24.2
9
0.5
1
2.1
2
3.8
2
4.1
8
4.7
2
12.7
2
Calo
trop
is g
igante
a
70
33
39
47.1
4
0.5
6
1.1
8
7.4
2
4.5
3
2.6
3
14.5
8
Capp
aris d
ecid
ua
70
7
12
10.0
0
0.1
7
1.7
1
1.5
7
1.3
9
3.8
2
6.7
8
Carissa c
ong
esta
70
11
23
15.7
1
0.3
3
2.0
9
2.4
7
2.6
7
4.6
6
9.8
0
Cassia
auricula
ta
70
36
81
51.4
3
1.1
6
2.2
5
8.0
9
9.4
1
5.0
1
22.5
1
Cle
roden
dru
m v
iscosu
m
70
13
24
18.5
7
0.3
4
1.8
5
2.9
2
2.7
9
4.1
1
9.8
2
Datu
ra s
tra
mon
ium
70
23
35
32.8
6
0.5
0
1.5
2
5.1
7
4.0
7
3.3
9
12.6
2
Dodo
nae
a v
iscosa
70
5
17
7.1
4
0.2
4
3.4
0
1.1
2
1.9
7
7.5
7
10.6
7
Gre
wia
tenax
70
16
21
22.8
6
0.3
0
1.3
1
3.6
0
2.4
4
2.9
2
8.9
6
Indig
ofe
ra o
blo
ng
ifo
lia
70
12
25
17.1
4
0.3
6
2.0
8
2.7
0
2.9
0
4.6
4
10.2
4
Ipom
oea c
arn
ea
70
28
72
40.0
0
1.0
3
2.5
7
6.2
9
8.3
6
5.7
3
20.3
8
Pro
sop
is ju
liflo
ra
70
52
115
74.2
9
1.6
4
2.2
1
11.6
9
13.3
6
4.9
3
29.9
7
Law
son
ia inerm
is
70
12
21
17.1
4
0.3
0
1.7
5
2.7
0
2.4
4
3.9
0
9.0
3
Mim
osa h
am
ata
70
27
39
38.5
7
0.5
6
1.4
4
6.0
7
4.5
3
3.2
2
13.8
1
Neriu
m o
lea
nder
70
19
42
27.1
4
0.6
0
2.2
1
4.2
7
4.8
8
4.9
2
14.0
7
Lanta
na c
am
ara
70
12
25
17.1
4
0.3
6
2.0
8
2.7
0
2.9
0
4.6
4
10.2
4
Opuntia d
ille
nii
70
3
10
4.2
9
0.1
4
3.3
3
0.6
7
1.1
6
7.4
2
9.2
6
Securi
neg
a v
irosa
70
7
17
10.0
0
0.2
4
2.4
3
1.5
7
1.9
7
5.4
1
8.9
6
Sesba
nia
sesban
70
28
38
40.0
0
0.5
4
1.3
6
6.2
9
4.4
1
3.0
2
13.7
3
Thevetia p
eru
via
na
70
24
41
34.2
9
0.5
9
1.7
1
5.3
9
4.7
6
3.8
0
13.9
6
Ziz
yph
us n
um
mula
ria
70
31
57
44.2
9
0.8
1
1.8
4
6.9
7
6.6
2
4.1
0
17.6
8
Ric
inus c
om
munis
70
29
71
41.4
3
1.0
1
2.4
5
6.5
2
8.2
5
5.4
5
20.2
2
635.7
1
12.3
0
44.9
0
100.0
100.0
100.0
300.0
#: T
ota
l n
o o
f qu
adra
te in w
hic
h s
pecie
s o
ccurr
ed,
@:
Tota
l no.
of
ind
ivid
ua
ls, F
: F
requency (
%),
D: D
ensity,
A:
Abu
nda
nce, R
F:
Rela
tive F
reque
ncy, R
D: R
ela
tive D
ensity, R
A:
Rela
tive A
bund
ance,
IVI:
Im
port
an
t V
alu
e Ind
ex S
han
no
n W
ien
er
Div
ers
ity I
nd
ex
(H’)
fo
r sh
rub
s w
as o
bse
rved
1.7
3
The h
ighest
IVI
for
shru
b a
t stu
dy a
rea w
as r
ecord
ed f
or
Pro
sopis
julif
lora
(29.9
7),
Cassia
auricula
ta (
22.5
1),
Ipom
oea c
arn
ea
(20.3
8)
and R
icin
us c
om
munis
(20.2
2),
follo
wed b
y Z
izyphus n
um
mula
ria (
17.6
8)
with I
VI valu
es in p
are
nth
esis
.
Pro
ject:
Vis
ak
a In
du
str
ies
Ltd
.
SE
CT
ION
-III
/De
scri
pti
on
of
the E
nvir
on
men
t
Do
cu
men
t N
o.:
EE
SP
L/V
IL/0
02/3
58-E
C/IN
D./2
013
En
ka
y E
nvir
o S
erv
ice
s P
vt.
Ltd
., J
aip
ur
9
6
Fig
ure
No
. 3.7
C
om
mo
n s
hru
b &
herb
sp
ecie
s o
bserv
ed
in
th
e s
tud
y a
rea
Pro
ject:
Vis
ak
a In
du
str
ies
Ltd
.
SE
CT
ION
-III
/De
scri
pti
on
of
the E
nvir
on
men
t
Do
cu
men
t N
o.:
EE
SP
L/V
IL/0
02/3
58-E
C/IN
D./2
013
En
ka
y E
nvir
o S
erv
ice
s P
vt.
Ltd
., J
aip
ur
9
7
T
ab
le N
o.
3.2
1
mp
ort
an
t V
alu
e In
dex
(IV
I) o
f h
erb
sp
ec
ies i
n t
he b
uff
er
zo
ne o
f stu
dy a
rea
Lif
e F
orm
: H
erb
(5x
5m
.)
Vern
acu
lar
na
me
Scie
nti
fic N
am
e
To
tal N
o
of
qu
ad
rate
stu
die
d
#
@
F (
%)
D
A
RF
R
D
RA
IV
I
Bui
Aerv
a to
men
tosa
14
9
31
64.2
9
2.2
1
3.4
4
7.5
0
6.7
1
5.0
2
19.2
3
Janga
li C
ho
lai
Am
ara
nth
us s
pin
osus
14
3
17
21.4
3
1.2
1
5.6
7
2.5
0
3.6
8
8.2
6
14.4
4
Pili
Ka
ntili
Arg
em
on
e m
exic
ana
14
7
23
50.0
0
1.6
4
3.2
9
5.8
3
4.9
8
4.7
9
15.6
0
Aak
Calo
trop
is p
rosera
14
11
17
78.5
7
1.2
1
1.5
5
9.1
7
3.6
8
2.2
5
15.1
0
San
ay
Cassia
occid
enta
lis
14
3
7
21.4
3
0.5
0
2.3
3
2.5
0
1.5
2
3.4
0
7.4
2
Tum
ba
Citru
llus c
olo
cynth
is
14
4
6
28.5
7
0.4
3
1.5
0
3.3
3
1.3
0
2.1
9
6.8
2
Pill
i K
antili
Arg
em
on
e m
exic
ana
14
10
51
71.4
3
3.6
4
5.1
0
8.3
3
11.0
4
7.4
3
26.8
0
Doob
C
ynodo
n d
acty
lon
14
5
39
35.7
1
2.7
9
7.8
0
4.1
7
8.4
4
11.3
7
23.9
8
Unth
kanta
E
chin
ops e
ch
inatu
s
14
10
43
71.4
3
3.0
7
4.3
0
8.3
3
9.3
1
6.2
7
23.9
1
Bad
i D
udh
i E
up
horb
ia h
irta
14
8
29
57.1
4
2.0
7
3.6
3
6.6
7
6.2
8
5.2
8
18.2
3
Bekara
In
dig
ofe
ra c
ord
ifolia
14
6
37
42.8
6
2.6
4
6.1
7
5.0
0
8.0
1
8.9
9
22.0
0
Van g
ob
i Laun
aea
pro
cum
be
ns
14
8
41
57.1
4
2.9
3
5.1
3
6.6
7
8.8
7
7.4
7
23.0
1
Gaja
r G
has
Part
heniu
m h
yste
roph
oru
s
14
3
17
21.4
3
1.2
1
5.6
7
2.5
0
3.6
8
8.2
6
14.4
4
Kantk
eri
S
ola
num
xan
thocarp
um
14
9
19
64.2
9
1.3
6
2.1
1
7.5
0
4.1
1
3.0
8
14.6
9
Sarp
honk
Tephro
sia
purp
ure
a
14
11
34
78.5
7
2.4
3
3.0
9
9.1
7
7.3
6
4.5
0
21.0
3
Gokhru
T
ribulu
s terr
estr
is
14
7
27
50.0
0
1.9
3
3.8
6
5.8
3
5.8
4
5.6
2
17.3
0
Bara
hm
asi
Tridax p
rocu
mbe
ns
14
6
24
42.8
6
1.7
1
4.0
0
5.0
0
5.1
9
5.8
3
16.0
2
857.1
4
33.0
0
68.6
2
100.0
0
100.0
0
100.0
0
300.0
0
#: T
ota
l n
o o
f qu
adra
te in w
hic
h s
pecie
s o
ccurr
ed,
@:
Tota
l no.
of
ind
ivid
ua
ls, F
: F
requency (
%),
D: D
ensity,
A:
Abu
nda
nce, R
F:
Re
lative F
requ
ency,
RD
: R
ela
tive D
ensity, R
A:
Rela
tive A
bund
ance, IV
I: I
mport
ant V
alu
e I
nd
ex S
han
no
n W
ien
er
Div
ers
ity In
de
x (
H’)
fo
r h
erb
was o
bserv
ed
2.7
The h
ighest
IVI
for
herb
at
stu
dy a
rea w
as r
ecord
ed f
or
Arg
em
one m
exic
ana (
26.8
0),
Cynodon d
acty
lon (
23.9
8),
Echin
ops
echin
atu
s (
23.9
1),
Launaea p
rocum
bens (
23.0
1),
follo
wed b
y I
ndig
ofe
ra c
ord
ifolia
(22.0
) w
ith I
VI
valu
es in p
are
nth
esis
.
Pro
ject:
Vis
ak
a In
du
str
ies
Ltd
.
SE
CT
ION
-III
/De
scri
pti
on
of
the E
nvir
on
men
t
Do
cu
men
t N
o.:
EE
SP
L/V
IL/0
02/3
58-E
C/IN
D./2
013
En
ka
y E
nvir
o S
erv
ice
s P
vt.
Ltd
., J
aip
ur
9
8
Fig
ure
No
. 3.8
C
om
mo
n h
erb
s o
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1. Flora:
Table No. 3.22
List of tree species recorded in the Buffer Zone
Trees S.No. Vernacular Name Scientific name Family Habitat
1. Ronjh Acacia leucopholea Fabaceae (Mimosoideae) Forest/Agriculture
2. Babool Acacia nilotica Fabaceae (Mimosoideae) Forest/Agriculture
3. Kumttha Acacia senegal Fabaceae (Mimosoideae) Forest
4. Siris Albizia lebbeck Mimosaceae Forest/Agriculture/ Sub Urban
5. Neem Azadirachta indica Meliaceae Agriculture/Sub Urban
6. Kachnar Bauhinia purpurea Leguminosae Agriculture/Sub Urban
7. Dhak Butea monosperma Fabaceae (Papilionaceae) Forest/Agriculture
8. Amaltash Cassia fistula Caesalpiniaceae Agriculture/Sub Urban
9. lasoda Cordia dichotoma Boraginaceae Agriculture/Sub Urban
10. Shesham Dalbergia sissoo Fabaceae (Papilionaceae) Agriculture/Sub Urban
11. Gulmohar Delonix regia Caesalpiniaceae Agriculture/Sub Urban
12. Kunali/khairi Dichrostachys cinerea Mimosaceae Forest
13. Pangri,dadak Erythrina indica Fabaceae (Papilionoideae) Forest/Agriculture
14. Safeda/ Sugandhapatra Eucalyptus globolus Myrtaceae Agriculture/Sub Urban
15. Bargad Ficus benghalensis Moraceae Agriculture/Sub Urban
16. Pipal Ficus religiosa Moraceae Agriculture/Sub Urban
17. Subabul Leucaena leucocephala Fabaceae (Mimosoideae) Forest/Agriculture 18. Kankera Maytenus emarginata Celastraceae Forest/Agriculture
19. Shahtoot Morus alba Moraceae Forest/Agriculture
20. Khajoor Phoenix sylvestris Arecaceae (Palmae) Forest/Agriculture
21. Jangle Jalebi Pithecellobium dulce Fabaceae Forest/Agriculture
22. Karanj Pongamia pinnata Fabaceae (Papilionaceae) Forest/Agriculture
23. Khejari Prosopis cineraria Mimosaceae Agriculture/Sub Urban
24. Jamun Syzygium cumini Myrtaceae Agriculture/Sub Urban
25. Imli Tamarindus indica Fabaceae (Leguminosae) Agriculture/Sub Urban
26. Rohida Tecomella undulata Bignoniaceae Forest/Agriculture
27. Sagon Tectona grandis Lamiaceae Forest
28. Indrajau/ Dudhi Wrightia tinctoria Apocynaceae Forest
29. Ber Ziziphus mauritiana Rhamnaceae Forest/Agriculture/Sub Urban
Table No. 3.23
List of shrub, herb and grass species recorded in the buffer zone
SHRUB
S.No. Vernacular Name Scientific name Family 1 Aak Calotropis procera Asclepiadaceae
2 Aakra Calotropis gigantea Asclepiadaceae
3 Arandi Ricinus communis Euphorbiaceae
4 Behaya Ipomoea carnea Convolvulaceae
5 Champa Plumeria alba Apocynaceae
6 Dandathor Euphorbia caducifolia Euphorbiaceae
7 Dhatura Datura stramonium Solanaceae
8 Foog Calligonum polygonoides Polygonaceae
9 Jharberi Ziziphus nummularia Rhamnaceae
10 Kair Capparis decidua Capparaceae
11 Kaner Nerium oleander Apocynaceae
12 Khimp Leptadenia pyrotechnica Asclepiadaceae
13 Nag phani Opuntia elatior Cactaceae
14 Raimuniya Lantana camara Verbenaceae
15 Sanay Cassia auriculata Fabaceae
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16 Vilayati babool Prosopis juliflora Mimosaceae
HERBS
1 Bui Aerva tomentosa Amaranthaceae
2 Pili Kantili Argemone mexicana Papaveraceae
3 Kala bhangra Anisomeles indica Lamiaceae
4 Jangli chaulai Amaranthus spinosus Amaranthaceae
5 Latjira Achyranthes aspera subsp. argentea Amaranthaceae
6 Latjira Achyranthes aspera subsp. porphyristachya
Amaranthaceae
7 Muktajhuri Acalypha indica Euphorbiaceae
8 Punarnava Boerhavia diffusa Nyctaginaceae
9 Purple-Leaf Button Weed Borreria ocymoides Rubiaceae
10 Survali Celosia argentea Amaranthaceae
11 chitraa Citrullus colocynthis Cucurbitaceae
12 Jakhiya, Safed hulhul Cleome gynandra Cleomaceae
13 Kankus Commelina forskalei Commelinaceae
14 Ban Tulsi Croton bonplandianum Euphorbiaceae
15 Kachari Cucumis melo ssp. agrestis Cucurbitaceae
16 Dhatura Datura metel Solanaceae
17 Latmahuria Digera muricata Amaranthaceae
18 Motha Cyperus rotundus Cyperaceae
19 Unthkanta Echinops echinatus Asteraceae
20 Oldman'S Cap Polycarpaea corymbosa Caryophyllaceae
21 Gulpankhi Polygala erioptera Polygalaceae
22 Laptuna Setaria verticillata Poaceae (Gramineae)
23 Baraira (bala) Sida acuta Malvaceae
24 Khareti Sida rhombifolia Malvaceae
25 Asiatic witchweed Striga asiatica Scrophulariaceae
26 Marigold Tagetes minuta Asteraceae
27 Yellow Bell Tecoma gaudichaudi Bignoniaceae
28 Sarphonk Tephrosia purpurea Fabaceae (Papilionaceae)
29 Sarapunkha Tephrosia villosa Fabaceae (Papilionaceae)
30 Peeli Kaner Thevetia peruviana Apocynaceae
31 Ashvagandha Withania somnifera Solanaceae
32 Badi Dudhi Euphorbia hirta Euphorbiaceae
33 Sunflower Helianthus annus Asteraceae
34 Gokhru Indigofera cordifolia Fabaceae (Papilionaceae)
35 Nili Indigofera linnaei Fabaceae (Papilionaceae)
36 -- Ipomoea pes-tigridis Convolvulaceae
37 Raimuniya Lantana camera Verbenaceae
38 Tikiokra Melochia corchorifolia Sterculiaceae
39 jharasi Mollugo pentaphylla Molluginaceae
40 Shankhapushpi Evolvulus alsinoides Convolvulaceae
41 -- Fimbristylis falcata Cyperaceae
42 Dudhi Sonchus oleraceus Asteraceae
43 Damanpaper Oldenlandia corymbosa Rubiaceae
44 Gajar Ghas Parthenium hysterophorus Asteraceae (Compositae)
45 Bada gokhru Pedalium murex Pedaliacae
46 Bilari Mukia maderaspatana Cucurbitaceae
47 Ashwagandha Withania somnifera Solanaceae
Grass
1 Jhuhi ghas Alysicarpus monilifer Fabaceae (Papilionaceae)
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2 Bristle grass Aristida adscensionis Poaceae (Gramineae)
3 Doob ghas Cynodon dactylon Poaceae (Gramineae)
4 Sheda Grass Dichanthium annulatum Poaceae (Gramineae)
5 Makra Dactyloctenium aegyptium Poaceae (Gramineae)
6 Panghas Eragrostis japonica Poaceae (Gramineae)
FAUNA:
BIODIVERSITY PROFILE OF THE BUFFER ZONE
(10 km radius from the Periphery of the project site)
AVIFAUNA
Totally 31 species of the birds belonging to 22 families were recorded from the buffer
zone of the study area. Dominant family was Columbidae and Sturnidae with 3
species each and Laughing dove, Brahminy starling as the dominant species. A
Schedule I species, Pavo cristatus (Indian peafowl) was reported from the buffer
zone located close vicinity of the human habitation / villages. For the same,
conservation plan is given at the end of this chapter. All the bird species reported
from the study area enlisted in the following table:
Table No. 3.24
List of Avifauna observed in the buffer zone
S.No. Common Name Scientific name Family Status (IWPA 1972)
1. Shikra Accipiter badius Accipitridae Schedule IV
2. Spot-billed duck Anas poecilorhyncha Anatidae Schedule IV
3. Cattle egret Bubulcus ibis Ardeidae Schedule IV
4. Little Egret Egretta garzetta Ardeidae Schedule IV
5. Red-wattled lapwing Vanellus cinereus Charadriidae No mention
6. Rock Pigeon Columba livia Columbidae Schedule IV
7. Laughing dove Streptopelia senegalensis
Columbidae Schedule IV
8. Eurasian Collared dove Streptopelia decaocto Columbidae Schedule IV
9. House crow Corvus splendens Corvidae Schedule V
10. Black drongo Dicrurus macrocercus Dicruridae Schedule IV
11. White-throated Kingfisher Halcyon smyrnensis Halcyonidae Schedule IV
12. Wire-tailed swallow Hirundo smithii Hirundinidae No mention
13. Wire-tailed Swallow Hirundo smithii Hirundinidae Schedule IV
14. Southern Grey Shrike Lanius meridionalis Laniidae Schedule IV
15. Jungle Babbler Turdoides striata Leiothrichidae Schedule IV
16. Green bee-eater Merops orientalis Meropidae No mention
17. Blue-tailed Bee-eater Merops philippinus Meropidae Schedule IV
18. White Wagtail Motacilla alba Motacillidae Schedule IV
19. Indian Cormorant Phalacrocorax fuscicollis
Phalacrocoracidae Schedule IV
20. Grey francolin Francolinus pondicerianus
Phasianidae Schedule IV
21. Indian peafowl Pavo cristatus Phasianidae Schedule I 22. Baya weaver Ploceus philippinus Ploceidae Schedule IV
23. Rose-ringed Parakeet Psittacula krameri Psittaculidae Schedule IV
24. Red-vented bulbul Pycnonotus cafer Pycnonotidae Schedule IV
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25. White-breasted Waterhen Amaurornis phoenicurus Rallidae Schedule IV
26. Common Coot Fulica atra Rallidae Schedule IV
27. Black winged stilt Himantopus himantopus Recurvirostridae Schedule IV
28. Brahminy starling Sturnus pagodarum Sturnidae Schedule IV
29. Common myna Acridotheres tristis Sturnidae Schedule IV
30. Bank myna Acridotheres ginginianus
Sturnidae Schedule IV
31. Common hoopoe Upupa epops Upupidae No mention
Figure 3.9
Common birds recorded in the study area
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Figure No.3.10 Common birds recorded in the study area
Figure No. 3.11 Common water Birds observed in the study area
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Table No. 3.25
List of mammalian species recorded in Buffer Zone (31398 ha) S.
No. Vernacular Name Scientific Name Family Status
(IWPA) Occurrence
Common Rare Very Rare 1 Mongoose Herpestes
edwardsi Herpestidae II *
2 Five stripped palm squirrel
Funambulus pennantii
Sciuridae IV *
3 Common House rat
Rattus rattus Muridae V *
4 Grey Musk Shrew Suncus murinus Soricidae -- *
5 Indian Hare Lepus nigricollis Leporidae IV *
6 Indian field mouse Mus booduga Muridae V *
7 Common Fox Vulpes bengalensis
Canidae II *
8 Nilgai Boselaphus tragocamelus
Bovidae III *
Table No. 3.26
List of amphibian species recorded in Buffer Zone (31398 ha)
S. No. Vernacular Name Scientific Name Family Status (IWPA) 1 Indian Bullfrog Hoplobatrachus tigerinus Ranidae No mention
2 Indian skipper frog Euphlyctis cyanophlyctis Dicroglossidae No mention
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Table No. 3.27
List of reptiles recorded in Buffer Zone (31398 ha) S.No. Vernacular
Name Scientific Name Family Status
(IWPA) Occurrence
Common Rare Very Rare 1 Common
House Gecko Hemidactylus frenatus
Gekkonidae No mention *
2 Oriental Garden Lizard
Calotes versicolor Agamidae No mention *
3 Yellow-Bellied House Gecko
Hemidactylus flaviviridis
Agamidae No mention *
4 Indian sand boa
Eryx johnii Boidae Schedule IV *
5 Common Rat Snake
Ptyas mucosus Colubridae Schedule II *
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Table No. 3.28
Butterflies recorded in Buffer Zone (31398 ha) S. No. Species Scientific Name Family Occurrence
Common Rare Very Rare
1 Common Rose Atrophaneura aristolochiae Papilionidae *
2 Crimson Rose Pachliopta hector Papilionidae *
3 Lime Butterfly Papilio polymnestor Papilionidae *
4 Plain Orange Tip Colitis eucharis Pieridae *
5 Yellow Orange Tip Lxias pyrene Pieridae *
6 Yellow Pansy Junonia hierta Nymphalidae *
7 Blue Pansy Junonia orithya Nymphalidae *
8 Plain Tiger Danaus chrysippus Nymphalidae *
9 Common Grass Yellow
Eurema hecabe Pieridae *
A total of 09 species of butterflies were recorded during the field survey. The
dominant family was Nymphalidae with 03 species with plain tiger as the dominant
species.
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3.9 SOCIO ECONOMIC ENVIRONMENT
3.9.1 Methodology
a) Objectives
The broad objectives of the socio-economic impact assessment are:
1. To study the socio-economic status of the people living in the study area.
2. To assess the impact on socio-economic environment due to the project
concerned.
3. To evaluate the community development measures proposed to be taken up by
the Project Proponent, if any.
4. To suggest community development measures that needs to be taken for the study
area with stakeholder engagement.
5. The studies carried out are descriptive and exploratory in nature.
b) Collection of data
The information analyzed for the project has been collected from various secondary
sources, which has been supported by the extensive site visits and field observations.
Secondary: Review of secondary data viz. Primary Census Abstract- Census of India
2011, and latest available district statistical Hand Books with respect to population and
occupational structure. Various research papers of the concerned area.
Primary: A social survey for examination of the respective site and specific region in
reference to its general character. Primary data collected by Semi-structured
Interviews / discussions etc. in sample villages and households. Site visits and
observations of the socio economic environment.
c) Sampling method
The studies are conducted and inferences are drawn on the basis of observation and
field survey. The sample of (15) people were interviewed through Semi-structured
Interviews and selected, on the basis of non probability random sampling and
convenience sampling with access to the nearest habitation to the extent possible.
3.9.2 Demographic environment
a. Habitation
The study area comprises of, 56 village human settlement. The total area of the
study area is 314.0 Sq. km. The population of the Tonk thereby recording a
percentage decadal growth rate of 17.33% for the decade 2001 – 2011. The
demographic study area is as following tables:
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b. Population
The total number of households is 10,365 with an average household size of 5
people. There are 58,341 people in the study area as per Census of India,
2011.
Population of the study area (10.0 k.m.):-
S. No. Name Households Total Population Total Males Total Females 1 Agarpura 73 348 195 153
2 Ahmadnagar 52 323 174 149
3 Ajeetpura 119 663 353 310
4 Anatpura 141 786 424 362
5 Bahadurpura 39 231 116 115
6 Banshipura 138 633 300 333
7 Bhagatrampura 56 303 168 135
8 Bhagwanpura 56 370 197 173
9 Bhairupura 105 580 283 297
10 Bhanwata 286 1580 789 791
11 Bhanwati 157 934 481 453
12 Bharthala 410 2150 1112 1038
13 Bhurtiya 163 971 486 485
14 Chainpura 285 1777 922 855
15 Dahlod 295 1766 910 856
16 Dayalpura 46 279 142 137
17 Devpura 94 428 214 214
18 Ganeshpura @ Hathathali 184 973 527 446
19 Gangapura 164 781 405 376
20 Gopalpura 190 1051 542 509
21 Gordhanpura 129 799 408 391
22 Gunsi 291 1690 884 806
23 Harbhanwata 183 1147 588 559
24 Haripura 196 903 489 414
25 Jaisinghpura 149 997 494 503
26 Janwali 253 1341 701 640
27 Jasodanandan Pura @ Thuni 86 550 285 265
28 Jhanpari 61 427 217 210
29 Jhilai 1037 5758 2963 2795
30 Jugalpura Kalan 146 885 470 415
31 Kairod 149 753 405 348
32 Kareda Bujurg 458 2610 1347 1263
33 Kayamnagar @ Basri 90 523 281 242
34 Khajpura 131 767 394 373
35 Kishorpura 99 616 329 287
36 Kurawada 132 921 475 446
37 Lalwari 676 3534 1839 1695
38 Luhara 334 1898 998 900
39 Lunera 81 649 339 310
40 Mahadeo Pura 36 243 138 105
41 Mothooka 44 259 146 113
42 Mundiya Khurd 98 505 253 252
43 Niwai (M) Urban ward 282 1453 824 629
44 Rachakpura 11 59 29 30
45 Radha -Govindpura 63 280 142 138
46 Ramsagar 103 525 299 226
47 Shedriya 225 1468 767 701
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48 Sangrampura 59 429 216 213
49 Sanwariya 513 2762 1392 1370
50 Shri Gopalpura 50 362 184 178
51 Shri Sooratpura 93 419 223 196
52 Shyopura 53 314 163 151
53 Sirohi 789 4112 2101 2011
54 Soorat Rampura 91 685 359 326
55 Surajpura (Abad) 53 294 152 142
56 Vijai Govindpura 68 477 245 232
Total 10365 58341 30279 28062 *Census of India, 2011
b. Gender Ratio
Out of the total population, in the study area of 10.0 k.m. constitutes 51.90% of males
and 48.10% of females. The gender ratio in study area is 926 much lower against the
Jaipur district gender ratio (949) as per the Census of India 2011 and (936) 2001.
c. Literacy Rate
The Average literacy of 10.0 k.m. of the study area is 51.60%. The Male literacy with
respect to male population is 65.74% and the Female literacy with respect to female
population is 36.35%. The literacy gap is high and the female literacy is low in the
study area as per the Census of India, 2011.
Literacy Profile:-
S. No. Name Total Literates Male Literates Female Literates 1 Agarpura 173 131 42
2 Ahmadnagar 190 120 70
3 Ajeetpura 341 229 112
4 Anatpura 370 253 117
5 Bahadurpura 102 64 38
6 Banshipura 305 194 111
7 Bhagatrampura 187 126 61
8 Bhagwanpura 193 136 57
9 Bhairupura 230 153 77
10 Bhanwata 664 456 208
11 Bhanwati 495 332 163
12 Bharthala 1046 708 338
13 Bhurtiya 612 379 233
14 Chainpura 1096 727 369
15 Dahlod 863 589 274
16 Dayalpura 140 89 51
17 Devpura 162 116 46
18 Ganeshpura @ Hathathali 416 273 143
19 Gangapura 356 239 117
20 Gopalpura 499 351 148
21 Gordhanpura 427 286 141
22 Gunsi 986 643 343
23 Harbhanwata 524 373 151
24 Haripura 473 329 144
25 Jaisinghpura 537 315 222
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26 Janwali 669 456 213
27 Jasodanandan Pura @ Thuni 289 188 101
28 Jhanpari 207 140 67
29 Jhilai 3445 2132 1313
30 Jugalpura Kalan 453 301 152
31 Kairod 270 219 51
32 Kareda Bujurg 1647 1030 617
33 Kayamnagar @ Basri 185 149 36
34 Khajpura 323 224 99
35 Kishorpura 400 230 170
36 Kurawada 364 267 97
37 Lalwari 1448 958 490
38 Luhara 1077 724 353
39 Lunera 231 166 65
40 Mahadeo Pura 99 71 28
41 Mothooka 130 101 29
42 Mundiya Khurd 228 156 72
43 Niwai (M) Urban ward 1030 637 393
44 Rachakpura 29 16 13
45 Radha Govindpura 161 114 47
46 Ramsagar 234 188 46
47 Shedriya 694 491 203
48 Sangrampura 258 154 104
49 Sanwariya 1409 908 501
50 Shri Gopalpura 196 125 71
51 Shri Sooratpura 200 143 57
52 Shyopura 138 99 39
53 Sirohi 2115 1384 731
54 Soorat Rampura 384 259 125
55 Surajpura (Abad) 169 104 65
56 Vijai Govindpura 233 158 75
Total 30102 19903 10199 Census of India, 2011
d. Occupational structure
The work participation rate is 47.22% of the study area. The non working population
is 52.78% constituting male workers to be 25.74% and females with 27.04%
population. The main workers in the study area are 33.68% constituting 21.51%
males and 12.17% females. The marginal workers constitute 13.54%, among which
the males constitute 4.64% and female workers constitute 8.90%.
Occupation Profile
Name Main Workers Marginal Workers Non workers
Total Males Fem Total Males Fem Total Males Fem Agarpura 128 86 42 16 0 16 204 109 95
Ahmadnagar 74 68 6 80 11 69 169 95 74
Ajeetpura 319 169 150 8 7 1 336 177 159
Anatpura 328 188 140 43 18 25 415 218 197
Bahadurpura 84 49 35 29 15 14 118 52 66
Banshipura 234 114 120 22 9 13 377 177 200
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Bhagatrampura 186 98 88 0 0 0 117 70 47
Bhagwanpura 199 104 95 3 1 2 168 92 76
Bhairupura 353 166 187 14 2 12 213 115 98
Bhanwata 616 368 248 431 147 284 533 274 259
Bhanwati 222 182 40 298 92 206 414 207 207
Bharthala 652 471 181 414 74 340 1084 567 517
Bhurtiya 350 228 122 31 29 2 590 229 361
Chainpura 512 307 205 175 102 73 1090 513 577
Dahlod 556 372 184 368 104 264 842 434 408
Dayalpura 73 68 5 67 0 67 139 74 65
Devpura 244 108 136 22 10 12 162 96 66
Ganeshpura @ Hathathali 350 243 107 225 41 184 398 243 155
Gangapura 59 56 3 295 140 155 427 209 218
Gopalpura 30 23 7 613 301 312 408 218 190
Gordhanpura 308 175 133 58 35 23 433 198 235
Gunsi 674 404 270 79 21 58 937 459 478
Harbhanwata 416 251 165 170 36 134 561 301 260
Haripura 215 205 10 56 48 8 632 236 396
Jaisinghpura 310 172 138 189 52 137 498 270 228
Janwali 622 346 276 30 9 21 689 346 343
Jasodanandan Pura @ Thuni 224 105 119 14 9 5 312 171 141
Jhanpari 42 40 2 177 71 106 208 106 102
Jhilai 1912 1400 512 498 111 387 3348 1452 1896
Jugalpura Kalan 361 197 164 8 2 6 516 271 245
Kairod 315 160 155 107 52 55 331 193 138
Kareda Bujurg 968 622 346 173 51 122 1469 674 795
Kayamnagar @ Basri 240 117 123 14 10 4 269 154 115
Khajpura 115 109 6 349 121 228 303 164 139
Kishorpura 123 100 23 189 59 130 304 170 134
Kurawada 231 209 22 294 46 248 396 220 176
Lalwari 748 677 71 305 176 129 2481 986 1495
Luhara 654 394 260 164 84 80 1080 520 560
Lunera 314 170 144 13 1 12 322 168 154
Mahadeo Pura 65 39 26 53 23 30 125 76 49
Mothooka 66 65 1 129 50 79 64 31 33
Mundiya Khurd 259 126 133 5 2 3 241 125 116
Niwai (M) Urban ward 375 322 53 41 23 18 1037 479 558
Rachakpura 25 17 8 5 0 5 29 12 17
Radha Govindpura 63 61 2 110 23 87 107 58 49
Ramsagar 252 133 119 2 2 0 271 164 107
Shedriya 455 266 189 305 112 193 708 389 319
Sangrampura 201 96 105 21 15 6 207 105 102
Sanwariya 1298 723 575 258 70 188 1206 599 607
Shri Gopalpura 149 91 58 20 5 15 193 88 105
Shri Sooratpura 126 99 27 85 4 81 208 120 88
Shyopura 102 72 30 20 4 16 192 87 105
Sirohi 1405 851 554 688 222 466 2019 1028 991
Soorat Rampura 282 137 145 21 10 11 382 212 170
Surajpura (Abad) 25 20 5 95 49 46 174 83 91
Vijai Govindpura 145 114 31 1 1 0 331 130 201
Total 19654 12553 7101 7900 2712 5188 30787 15014 15773 *As per Census of India, 2011
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3.9.3 Social infrastructure available
The proposed project is located in the village Rachakpura with its Head Quarter in
the Gram Panchayat, Shedriya.
• Medical Facilities: PHC Mundiya 7.3 km W, Aaganbadi Munidya 7.4 km W;
Aaganbadi Bhanwati 4.3 km SW; PHC Bhanwati 4.4 km SW; Aaganbadi Lalwari 3.2
km ESE; Upswastha Kendra Lalwari 3.2 km ESE; Upswastha Kendra Shedriya 1.8
km NW;
• Gram Panchayat H.Q., Shedriya 1.6 km NW
• Educational Facilities: Jeevan Jyoti Madhyamik Vidhyalya, Bhanwata 3.2 km SW;
Rajkiya Madhyamik Vidhyalya Mundiya 6.0 km SW; Rajkiya Adarsh Uchh Prathmik
Vidhyalya, Lalwari 3.5 km ESE, Rajkiya Uchh
Prathmik Vidhyalya, Shedriya 1.7 km NW ;
Sandeep Convent School, Mundiya 6.3 km
SW ; Rajkiya Ucch Prathmik Vidhyalya ,
Kishorpura 2.0 km NE
• Religious places: Bhairon ji ka Baagh 1.6 km
NE
• Market Places: Unorganasied market place is
in Dahlod 3.4 km NE, Shedriya 2.0 km NW,
but for organized market place villagers
commute to Niwai.
• Others : Bharat Nirman Rajiv Gandhi Seva
Kendra, Dahlod,
Approach Road: The main road towards
Site location is permanent, painted, and
cemented. The internal roads of the
villages are semi-permanent and
temporary (Kutcha). The major modes of
transport which travel in the main roads
are Private, Tractors, Scooters, Motor
Cycles but the internal roads are kutcha
largely with Cycles, Carts & tractors. The
ladies generally take a walk when they
commute whereas the men travel cycles /
motorbikes.
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3.9.4 Socio economic observations
There various panchayats in the
study area includes Shedriya,
Dahlod, Lalwari & Shri Rampura.
All the above gets the source of
potable drinking water from the
Besalpur pipeline.
Housing
The habitation of Rachakpura is almost
negligible as compared to the nearby
villages in the study area with only 4
houses as per the site visit observations
whereas 11 households as per the
Population Census Abstract, Census of
India (2011). The village has large size
of land holdings in the revenue records
therefore it exists as a separate village
in the records with its Gram panchayat
h.q. at Shedriya.
Housing Pattern
The major houses were permanent with
semi-permanent sheds in the study area.
The Uninhabited Houses in the vicinity were
due to movement to Niwai and nearby towns
and cities in search of work. The internal
housing structure was nucleated with
chaotic agglomeration, a strong internal
differentiation of the separated quarters for
various castes in a village.
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Religion, Caste & Festivals
Predominant castes in village Lalwari (3.0
km ESE) is of Rajput, Brahmin, Dhobi, Jat.
In Rachakpura the 4 houses during survey,
belonged to Raigar community.
Bhairon-ji-ka-baag (1.60 km NE) is an
(oran) sacred area distinctively known for
the temple of Lord Bhairon and for the
Palaash trees found, only in the area. The
Palaash trees make the area look
distinctively beautiful and sacred.
In the 10.0 km of the study area there is large no. of Gurjars’ making the regional area
politically sensitive of Gurjar community. The community has recently been involved in the
agitations for reservation quota of Gurjars.
In Conversation with Pushpa devi
(Kishorpura) about the whether the folkways
are followed by men. The 65 year old
residents, exclaimed that as per the Gurjar
tradition, only those men shall keep
moustaches, had their fathers expire.
However this custom is not followed
anymore as they (whose fathers expire),
don’t like to keep moustaches. When asked
as the women in the region given a right to
decide to unfollow any custom she is not
comfortable, Smt. Pushpa devi refused
sadly.
Employment & Occupation
The local villagers practice more of agriculture (Gehu, Makka, Jwar, Bajra) and the skilled
workers and head loading labour move to Niwai. The educated youth of the villages find
services & job works in Niwai.
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Education Primary Education is available in the study area. For higher education students move to Niwai or Jaipur city.
Infrastructural facilities in the Rajkiya Adarsh Uchh Prathmik Vidhyalya, Lalwari 3.5 km ESE, there were bathrooms available (separate for boys and girls) in the school but the water supply was unavailable in bathrooms. Children fill water from the school borewell tap and carry the buckets to flush the toilets.
The educational level in the region is moderate. The female literacy is low as per the survey and the Census of India 2011. The young children mainly girls are increasingly sent to school. The students smilingly told that there is increasing number of young girls regularly coming to the school but the boys are not seriously studying as indicated by their low-attendance. Outdoor games are the ways of amusement adopted by majority children in Lalwari as compared to the urban youth involved with Television and indoor activities.
Rajkiya Uchh Prathmik Vidhyalya, Kishorpura. Up-swasth Kendra, Lalwari
• Hygiene, Drinking water & Sanitation Access to potable drinking water is drawn from Hand pumps. The major sources of water supply are mix of bore wells with more effluent classes in the village and Tap- water, Wells, Tanks, and Tankers. The source of potable drinking water now is from the Besalpur pipeline.
• Health There are presently only primary health facilities near the proposed site area. A multi specialty hospital is in Niwai (over 10.0 km from the proposed site area). Hence with the coming up of the proposed unit there shall be provision of critical medical facilities (like a Government hospital) with the ICU room within 5.0 km of the proposed unit. The weakness in women was observed mainly due to malnutrition. The Aanganbadi, Kishorpura workers train toddlers, provide daycare for infants and their mothers. Major health problems with mothers and children below 5 years are malnutrition (Kuposhan) as told by the active Aaganabadi workers Smt. Jyoti. Major bottlenecks in the study area:
• Malnutrition Camps for Mother and Child in the study area including drops / supplements are required in the region.
• Rain water harvesting structure is required to make the schools and health centers self sustainable with the water supply for drinking and bathrooms.
• Lack of sources of income and employment, make the region dependent on rain-fed agriculture. The sources of irrigation are insufficient to manage under-employment.
• A Multi-specialty hospital for critical illness and emergency should be in the vicinity of 5.0 km of the proposed site region.
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SECTION – IV
ANTICIPATED ENVIRONMENTAL IMPACTS & ENVIRONMENT
MANAGEMENT MEASURES
INDEX
ANTICIPATED ENVIRONMENTAL IMPACTS & ENVIRONMENT MANAGEMENT
MEASURES ........................................................................................................................... 118
4.1 GENERAL ..................................................................................................................... 118
4.2 LAND ENVIRONMENT ................................................................................................ 118
4.3 AIR ENVIRONMENT .................................................................................................... 119
4.4 WATER ENVIRONMENT ............................................................................................. 129
4.5 SOLID WASTE ............................................................................................................. 132
4.6 NOISE POLLUTION ..................................................................................................... 133
4.7 BIOLOGICAL ENVIRONMENT .................................................................................... 134
4.8 SOCIAL IMPACT ASSESSMENT ................................................................................ 139
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ANTICIPATED ENVIRONMENTAL IMPACTS & ENVIRONMENT
MANAGEMENT MEASURES
4.1 GENERAL
Various operations involved in proposed asbestos cement sheet manufacturing plant
have been studied before implementation of project to identify, predict and evaluate
impacts on various environmental components. This will help to avoid, minimize and
mitigate the pollution, which will be generated from the proposed project.
1. LAND ENVIRONMENT
2. WATER ENVIRONMENT
3. AIR ENVIRONMENT
4. NOISE ENVIRONMENT
5. SOLID WASTE
6. BIOLOGICAL ENVIRONMENT
7. SOCIO-ECONOMIC ENVIRONMENT
4.2 LAND ENVIRONMENT
4.2.1 Impact and Management
There are many changes after establishment of a new unit on a vacant land. The
new construction poses impacts on surrounding environment and surrounding land
use directly or indirectly. The possible impacts on topography and geology of the
area will occur due to land grading, scraping, filling, excavation of earthworks for
making water reservoir/piling activities, making roads; work shed related civil
construction activities. Following are the measures to minimize the impacts on land
environment:-
• After construction, land use will be consistent with the local land use plan.
• The site is not falling in the way of any stream. After construction, there will be no
changes in the topography as the drainage of the site and the nearby area will
not be changed during construction phase.
• The surrounding area is undeveloped.
• There is no restricted area within the study area.
• 33% of the total plot area will be under dense plantation.
• Traffic load will be increased but approach roads are sufficient to support the
extra traffic load. However, proponent will co-operate with Govt. time to time in
strengthening of approach roads.
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4.3 AIR ENVIRONMENT
Prediction of impacts is the most important component in the environmental impact
assessment studies. Several scientific techniques and methodologies are available to
predict impacts of developmental activities on physico, ecological and socioeconomic
environments. Such 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 identify the
environmental management plan required to be executed during and after
commissioning the proposed project to minimize the adverse impacts on
environmental quality. The details of the emission during construction phase and
operation phase is given below:-
4.3.1 Impact on Air Environment
A. During Construction Phase
Construction activities have the potential to generate a substantial amount of air
pollution. Construction activities that contribute to air pollution include - land clearing,
operation of diesel engines, burning, and working with toxic materials. Diesel is also
responsible for emission of carbon monoxide, hydrocarbons, nitrogen oxides and
carbon dioxide. Noxious vapors from oils, glues, thinners paints, treated woods,
plastics, cleaners and other hazardous chemicals that are widely used on
construction sites, also contribute to air pollution. The dust generation during
construction will be suppressed through intensive water spraying. The proper
maintenance of equipment and transport vehicles will reduce generation of gases.
During construction phase fugitive dust emission sources will be as under:
I. Construction Operation:
Fugitive dust emission is the main pollution, generated from the construction
activities.
Construction site generate high levels of dust (typically from concrete, cement,
wood, stone, silica). Construction dust is classified as PM10 - particulate matter
less than 10 microns in diameter, invisible to the naked eye. However, the impact
on the air quality during construction phase will be localized, temporary and
reversible in nature. Particulate dust emissions from the construction are a
function of total land disturbed and the volume of soil excavated. The ratio of PM2.5
to PM10 is assumed to be 0.20.
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The emission factors vary from approximately 0.019 tons PM10/acre-month for initial
emissions estimate. The construction will take 18 months for completion. Thus,
emission will be 1.06 kg PM10 per day.
II. Particulate Emission from Transportation:
When a vehicle travel on the road, particulate emissions occur due to direct
emissions from vehicles in the form of exhaust. The level of the emission
depends upon the condition of the road (paved/unpaved) and condition of
vehicles. PM dust emissions from road construction activities are a function of
acres disturbed during construction. As most of the vehicle used in plant are
trucks and heavy vehicle which are diesel vehicles. Diesel engines breathe only
air, blow by gases from the crankcase (consisting primarily of air and HC) are
rather low. Due to its low volatility, evaporative emissions from the fuel tank can
also be ignored. The low concentration of CO and un-burnt Hydro Carbons in the
diesel exhaust are compensated by high concentration of NOx.
B. During Operation Phase
1. Process Emissions
The operational activities are usually expected to have long-term impacts on air
quality. Major sources of air pollutants are process vents and handling of raw
materials in process. The other air pollutant is asbestos fibre, which arises from
Asbestos related activity. The major sources of emission from the proposed activity
are
1. Fibre Handling Area - Total dust with fibre content
2. Cement handling Area - Total dust or suspended particulate matter
3. Fly Ash handling Area - Total dust or suspended particulate matter.
4. Standby Power Supply System - DG sets - Suspended Particulate matter, SO2
and NOx.
4.3.2 AIR MODELING
Impact on Air Quality
The impact on air quality is assessed based on emissions of the proposed activities
in the plant. Suspended Particulate Matter (SPM), PM2.5, PM10, Asbestos fibre, NOx
and CO will be the important pollutants emitting from the point sources.
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Prediction of impacts on air environment has been carried out employing mathematical
model based on a steady state Gaussian plume dispersion model designed for multiple
point sources for short term. In the present case, AERMOD version 7.1 developed by
United States Environmental Protection Agency [USEPA] dispersion model based on
steady state Gaussian plume dispersion, designed for multiple point sources for short
term has been used for simulations from point and line sources.
Model Input Data
I. Point Sources:
For the modeling purpose, all pollutants as described above are considered. The
details of stack emissions envisaged from the project are given in Table-4.1 (a).
Table No. 4.1 (a)
Stack emission details
S.
No. Parameters Units Asbestos
Fibre Dust Collector System Stack
Cement Dust
Collector System Stack
Fly ash Dust
Collector System Stack
Pulverizer Dust
Collector System Stack
D.G. Set Stack
(2 nos of 500 kVA)
1 Stack Height m 18 18 18 18 10
2 Top diameter of flue m. 0.4 0.3 0.3 0.3 0.2
3 Flue gas velocity m/sec 14 12 15 12 15
4 Exit Flue gas temperature
oK 313 313 313 313 473
5 Flow Rate m3/hr 6000 2500 6000 3000 1700
6 Emission rate
A
Particulate matter (SPM) emission rate
mg/Nm3 < 2 < 50 < 50 < 50
< 50
B PM2.5 emission rate g/sec - 0.034 0.0424 0.034 0.053
C PM10 emission rate g/sec - 0.021 0.0265 0.021 0.035
E NOx g/sec - - - - 0.182
F CO g/sec - - - - 0.12
G Asbestos Fibre Dust Fibre/cm3 < 2 (0.00007
g/s)
- - - -
Particulars PM10 PM2.5 Quantity, TPA 2,16,000 Operational hours per day 24 Capacity of each truck 20 T Total number of trucks per day 30 - 50 Length per trip, km 10 10 USEPA Emission Equation, lb/VMT [[(k) x [(sL/2)^0.65] x [(W/3)^1.5]] - C]((1-
(p/1460)) Emission, kg/VKmT 0.0432 0.0063
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II. Line Source:
Trucks are used for transporting raw material to the plant and finished goods to end
use. The main pollutants emitting from these source are PM10, PM2.5, NOx and CO
which are considered in the present modeling.
Haulage Emissions (Paved) – Transport of Raw Materials and Finished Goods to end
use
Presentation of Results
In the present case, model simulations have been carried out for the study period. The
Ground level concentrations are computed for 24-hr average. Maximum Ground level
concentrations of PM10, PM2.5, NOx, CO and Asbestos Fibre for study period were 5.2
µg/m3, 3.3 µg/m3, 7.6 µg/m3, 5 µg/m3 and 0.002 µg/m3 respectively for the given
meteorological and topographical conditions. The obtained GLC’s are well within the
stipulated CPCB standards. The incremental ground level concentrations for PM10,
PM2.5, NOx, CO and Asbestos Fibre are given in Table-4.1 (b).
Table No. 4.1 (b)
Predicted 24-Hourly Short Term Maximum Incremental Ground Level Concentrations
Pollutant Maximum Incremental
Concentration (µµµµg/m3) Distance coordinates
(x , y) in m Towards Direction
PM10 5.2 (500 , 1000) NE PM2.5 3.3 (500 , 1000) NE NOx 7.6 (0 , - 500) W CO 5 (0 , - 500) W Asbestos Fibre
0.002 (0.000032 fibre/cm3 < 0.1
fibre/cm3)
(500 , 1000) NE
Resultant Concentrations after Implementation of the project
The maximum incremental GLCs due to the proposed project for PM10, PM 2.5, NOx and CO are
superimposed on the maximum baseline concentrations recorded during the study period. The
cumulative concentrations (baseline+incremental) after implementation of the project on the
nearby habitation are tabulated below in Table-4.1 (c). The predicted ground level
concentration isopleths for various parameters during study period are given in Figure- 4.1
to 4.5.
Emission rate, g/sec/m 0.000036 0.00000523
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Table No. 4.1 (c)
Details of incremental concentration of pollutants on sensitive locations like
habitations
Pollutant Concentration (µµµµg/m3)
Baseline
(Max.) Incremental Resultant Distance (km) Direction
PM10
Project Site 39.3 2.9 42.2 -- --
Sedria 52.8 1.2 54 1.9 NW
Dehold ki Dhani 42.5 3.5 46 2.7 NNE
Kishore Pura ki Dhani
41.6 1.7 43.3
1.6 NE
Lalwari 52.9 1.2 54.1 3.0 ESE
Shrisukhpur 41.2 3.5 44.7 1.0 SSE
Thunj(Radhagovindpura)
41.5 2.9 44.4
1.5 SSW
Bhagatpur Rampura
41.3 0.6 41.9
3.6 WNW
PM2.5
Project Site 20.3 1.9 22.2 -- --
Sedria 27.9 0.7 28.6 1.9 NW
Dehold ki Dhani 21.6 1.9 23.5 2.7 NNE
Kishore Pura ki Dhani
21 0.8 21.8
1.6 NE
Lalwari 26.3 0.8 27.1 3.0 ESE
Shrisukhpur 21.6 2.6 24.2 1.0 SSE
Thunj(Radhagovindpura)
21.6 2.6 24.2
1.5 SSW
Bhagatpur Rampura
21.3 0.4 21.7
3.6 WNW
NOx
Project Site 12.6 4.3 16.9 -- --
Sedria 15.6 1 16.6 1.9 NW
Dehold ki Dhani 13.2 3.5 16.7 2.7 NNE
Kishore Pura ki Dhani
13.2 2.6 15.8
1.6 NE
Lalwari 15.3 1.8 17.1 3.0 ESE
Shrisukhpur 13.2 3.5 16.7 1.0 SSE
Thunj(Radhagovindpura)
13.6 3.5 17.1
1.5 SSW
Bhagatpur Rampura
14.5 0.1 14.6
3.6 WNW
CO
Project Site 123 2.8 126 -- --
Sedria 248 0.7 249 1.9 NW
Dehold ki Dhani 215 1.7 217 2.7 NNE
Kishore Pura ki Dhani
215 1.2 216
1.6 NE
Lalwari 291 0.7 292 3.0 ESE
Shrisukhpur 182 2.8 185 1.0 SSE
Thunj(Radhagovindpura)
182 2.3 184
1.5 SSW
Bhagatpur Rampura
182 0.1 182
3.6 WNW
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The predictions indicate that the resultant of PM2.5, PM10, NOx, CO and Asbestos Fibre
concentrations are likely to be well within the prescribed limits.
Figure No. 4.1
Isopleths showing maximum incremental ground level concentrations of PM10
Figure No. 4.1
Isopleths showing maximum incremental ground level concentrations of PM2.5
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Figure No. 4.3
Isopleths showing maximum incremental ground level concentrations of NOx
Figure No. 4.4
Isopleths showing maximum incremental ground level concentrations of CO
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Figure No. 4.5
Isopleths showing maximum incremental ground level concentrations of asbestos
fiber
4.3.4 Management
I. During Construction Phase
The impacts of the construction phase will be temporary and localized phenomena
except the permanent change in local landscape and land use pattern at the project
site.
• Dust pollution can be minimized at the source by water spraying and
maintenance of road.
• Construction material will be stored in temporary storage yard.
• The excavated materials will be place only on the designated disposal areas.
• The construction area will be shielded with the help of tarpaulin from all the four
sides to contain the air emissions within the premises.
• Dust or dusty material will not be swept without effectively treating it with water or
other substances in order to minimize its dust emission.
• Suitable covered skips and enclosed chats or other suitable measures will be
provided in order to minimize dust emission to the atmosphere when materials &
waste will be removed from the premises.
• Parking lot and paved road will be constructed first.
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• Upwind portion of the project will be constructed first.
• During high wind condition, construction activities will be restricted, so that
minimum flow of dust particle takes place.
• The first and most important step towards emission control for the large in-use
fleet of vehicles is the formulation of an inspection and maintenance system. It is
possible to reduce 30-40% pollution loads generated by vehicles through proper
periodical inspections and maintenance of vehicles.
• All transportation vehicles will be suitably covered with tarpaulin & overloading of
the vehicles will be avoided.
• PUC certified vehicles will be used to avoid the exhaust emission.
II. During Operation Phase
During operation phase, the impacts on the various environmental attributes should
be mitigated using appropriate pollution control equipment. The Environment
Management Plan prepared for the proposed project aims at minimizing the pollution
at source.
Air Pollution Management
The proposed mitigative measures for the plant are:
• Automatic bag open device followed by shredder is proposed for fibre handling and
pneumatic bulk handling system for cement and fly ash. The design of the bag open
device is given below:-
• High efficiency pulsejet type bag filters will be installed for fibre circuit, cement and fly
ash circuit and solid waste management device-pulveriser, bin filter for cement silo
and fly ash silo to limit the particulate matter concentrations below the standards;
• Provision of adequate height stack for wider dispersion of emissions;
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• In the event of failure of any pollution control system, the unit will put off the operation
immediately and will not be restarted until the control system is rectified to achieve
the desired efficiency;
• Water spraying will be practiced frequently at all dust generating areas;
• All the internal roads are connected to reduce the fugitive dust due to vehicular
movement; and
• Improving the Greenbelt around the plant to arrest the fugitive emissions.
• Asbestos fiber (Chrysotile variety) will be imported from Canada, Brazil, Zimbabwe,
Russia and Greece. It is received in shrink or stretch wrapped HDPE woven bags.
Fiber bags are received tightly packed in wooden pallets and transported in closed
containers. The bags wear warning symbol “a”.
• The bags are handled at site by means of forklifts. Spillages if any and container after
unloading at site is cleaned using portable vacuum cleaner. Where this is not
practicable, wet mopping, collection & recycling method is adopted.
• The fibre bags will be stacked in godowns.
• Trucks after unloading will be subjected to thorough cleaning by vacuum cleaner.
• Sheet cutting operation will be carried out with the cutters operating under a steady
stream of water jet which will be recycled.
• The washing waste water is collected and periodically recycled to the process. This
technique of dust suppression has been proven to be very effective.
• Portable vacuum cleaner will be used for the cleaning of godowns and raw material
section.
• The filing and finishing operation of moulded asbestos cement goods will be carried
out in wet stage.
• Wet mopping /collection/Recycling method wherever applicable is adopted for the
spillage cleaning at raw material section.
Fugitive Emission Management • Management performance assessment to include a health and safety component which
includes asbestosis prevention.
• Utilization of appropriate and correct airborne dust sampling equipment and procedures.
• Prompt utilization of the respirable dust measurements as an indicator for the need for dust control.
• Use of approved /reputable laboratories for parameter analysis
• Measures to ensure correct statistical analysis and interpretation of homogeneous exposure group data
• Main and auxiliary ventilation air reduces dust by dilution and by displacement. The basic principle behind dilution ventilation is to provide more air and thus dilute the dust concentration. Most of the time, the dust concentration is reduced roughly in proportion to increased airflow.
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• The basic principle behind displacement ventilation is to use the airflow in a way that confines the dust source and keeps it downwind from employees.
4.4 WATER ENVIRONMENT
4.4.1 Impact
I. During Construction Phase
• Sewage will be the only source of water pollution.
• Un-captured run off from the site.
II. During Operation Phase:-
A. Waste water from industrial process
• No process waste water will be discharged and zero discharge will be adopted and entire
process waste water will be reused / recycled in the manufacturing process.
B. Domestic waste water
• The Domestic wastewater from plant will be treated in Sewage treatment plant.
4.4.2 Management
• The construction site will be provided with sufficient and suitable toilet facilities for
workers to allow proper standards of hygiene. These facilities should preferably be
connected to a septic tank and maintained to ensure minimum environmental impact.
• Measures will be implemented to prevent seepage of liquid materials into ground where
it could contaminate groundwater;
• Ensure prompt cleaning up of accidental spillages
• Measures will be followed to prevent the contamination of hydrological features by
diesel, grease, oil, etc. derived from the working area.
• The machinery / equipment will be maintained in a good operating condition;
• Specially designated areas will be created for vehicle maintenance;
• Accidental spillages will be cleaned up promptly.
• Curing water will be sprayed and after liberal curing, all concrete structures will be
covered with gunny bags this will conserves water
• Provisions will be made to ensure the construction vehicles stick to the access track to
prevent mud & dirt being deposited on roads
• Fence will be constructed around the site to trap sediments whilst allowing the water to
flow through.
• All mud & dirt deposited on the roads from the construction activities will be cleaned.
• Adopting good construction and engineering practices will help in mitigating the water
pollution.
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• The process waste water will be collected periodically and recycled to process after
sedimentation process, along with mud.
4.4.3 Rain Water Harvesting Scheme
For good design of rainwater harvesting, following points are to be kept under consideration: (a) Ideal location with good ground slope. (b) The location has adequate subsurface permeability of the aquifer to accommodate maximum recharge of rainwater through injection well. (c) Rate of filtration should exceed average rainfall intensity. (d) Clogging of filtration media should be cleaned periodically. (e) Ground water pollution does not take place
I. ROOFTOP RAIN WATER HARVESTING
Total rooftop area of proposed project is 10788 m2 that may be connected through pipes and drains to Rainwater harvesting structures which has storage chamber and the percolation pits as per sites having rooms for recharge in resonance with average rainfall, catchment area and peak rainfall intensity. Looking in to the average rainfall in this region, roof top area of the building, rain water harvesting structures are designed in such a way that even at peak rainfall intensity of 40 mm/day, water does not spill over & the entire rainwater falling over the total area goes in to the ground water body. Following dimensional parameters are considered for design of Rainwater harvesting system in the proposed project premises.
� Total Rooftop area = 10788 m2 � Average rainfall = 548 mm = 0.548 m � Catchment factor for Roof top = 0.85 (as per C.G.W.A) � Total volume of water to be captured = 10788 x 0.548 x 0.85 = 5025.05 m3 � The dimension of the structures to be designed for 40 mm/hour peak rainfall
intensity. � Considering 15 minutes of peak rainfall, runoff volume in a single storm should
be: 10788 m2 x 0.85 x 0.04 m/4 = 91.69 m3.
II. ROAD/PAVED AREA STORM WATER RUNOFF HARVESTING
In road storm water harvesting system, drains may be made on both the sides of roads with iron net filter of 2 mm opening at every 20 m. Rainwater falling on the road/paved area is carried through these drains to rainwater harvesting structure and allow to infiltered in groundwater regime. This will improve groundwater quality as well as quantity in and around the project premises. Following dimensional parameters are considered for design of road storm water harvesting system in the proposed project premises.
� Total Road/paved area = 27250 m2 � Average rainfall = 548 mm = 0.548 m � Catchment factor for Road/paved area = 0.75 (as per C.G.W.B.) � Total volume of water to be captured by road/paved area = 27250 x 0.548 x
0.75 m3 = 11199.75 m3/annum � The dimension of the structures to be designed for 40 mm/hour peak rainfall
intensity. Considering 15 minutes of peak rainfall, runoff volume in a single storm should be: 27250 m2 x 0.75 x 0.04 m/4 = 204.37 m3.
III. OPEN AREA RAINWATER HARVESTING
The total open area of proposed project is 74802 m2 which may be connected through drains to rainwater harvesting structures which has storage chamber and the percolation pits as per sites having rooms for recharge in resonance with average rainfall, catchment area and peak rainfall intensity.Following dimensional parameters
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are considered for design of open area rainwater harvesting system in the proposed project premises.
� Total open area = 74802 m2 � Average rainfall = 548 mm = 0.48 m � Catchment factor for open area = 0.15 (as per C.G.W.A) � Total volume of water to be captured = 74802 x 0.548 x 0.15 = 6148.72 m3 � The dimension of the structures to be designed for 40 mm/hour peak rainfall
intensity. Considering 15 minutes of peak rainfall, runoff volume in a single storm should be: 74802 m2 x 0.15 x 0.04 m/4 = 112.20 m3.
IV. DESIGN OF RAINWATER HARVESTING STRUCTURE
The total volume of water generated in project premises from rooftop, road/paved & open area in a single storm on 40 mm peak rainfall intensity would be = 91.69 m3 + 204.37 m3 + 112.20 m3 = 408.26 m3 ≈ 410 m3 It is revealed from recharge test that the aquifer would very well accept water of the order of 50.16 m3/day @ 2.09 m3/hour continuously in long term through vadose zone. Considering the space availability, the individual design is made for accumulation of 27 m3 of water i.e. 9 m3 of water in Desilting/settlement tank (1 m water column above dead storage x 3 m length x 3 m width), 9 m3 in the filtration tank (1 m water column above filtration media x 3 m length x 3 m width) and about 9 m3 in the process of infiltration through filtration media of recharge shaft. Hence, the dimensional parameters of Desilting/Settlement chamber would be 3 m (length) x 3 m (width) x 1.30 m (depth). In Desilting chamber, 0.30 m depth below outflow is kept for silt deposition. The filtration tank dimension would be 3 m (length) x 3 m (width) x 3 m (depth) with 0.15 m dia injection well of 60 m depth depending upon the formation for recharge in shallow aquifer through vadose zone. Each structure will be capable of handling rainwater volume @ 27 m3/day and such 15 structures will accommodate up to total rainfall volume of 405 m3 in any rainfall event at peak rainfall occurrence. The Map showing locations of proposed rainwater harvesting (RWH) structures
in plant premises
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4.5 SOLID WASTE
4.5.1 During Construction Phase
• Construction waste likely to be generated during the site formation works include waste
wood from concrete form work; spent concrete; waste steel rebars from concrete
reinforcement activities; and material and equipment wrappings.;
• Municipal wastes generated by site workers.
4.5.2 During Operation Phase
The solid waste generated is basically discarded fibre cement products, residue containing
fibre and dust from dust collectors which are pulverized, bagged and then taken back to the
Mixer for use in the manufacturing process.
A. Hazardous Waste: following category waste will be generated during operation
phase
Hazardous Waste Category
Empty Fibre Bags – From Bag
Opening Device (BOD)
15.1
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Fibre Dust – From Dust
Collector at ER Mill & BOD
15.3
Process Sludge – From
Week-End Tank
15.1
Hard Broken Pieces – From
Damages/Rejects
15.1
Table 4.2 Solid waste and its management
S.No. Waste Source Quantity MT
Management
1. Empty Fibre Bags
(Category 15.1)
Auto Bag
Opening Device
(BOD)
0.080 Shredded in the Shredder unit
attached to the BOD in a
closed loop & collected thro
cyclone collector, thro screw
conveyor to the Edge Runner
Mill (ERM).
2. Fibre Dust
(Category 15.3
From Dust
Collector
attached to ER
Mill & BOD
0.012 Periodically recycled after the
container containing water &
placed beneath the rotary
valve of the dust collector gets
filled up.
3. Cement & Fly ash
Dust
From Dust
Collector
attached to
Cement feeding
& FA feeding
point.
0.100 Periodically recycled after the
container placed beneath the
rotary valve of the Dust
Collector gets filled up.
4. Process Sludge
(Category 15.1)
From Week-end
Tank
0.100 Continuously recycled through
Wet Ball Mill in slurry form.
5. Hard Broken
Pieces
(Category 15.1)
Sheet damages &
rejects
9.000 Continuously recycled through
Wet Ball Mill in slurry form.
4.6 NOISE POLLUTION
4.6.1 During Construction Phase
Major sources of noise pollution are vehicular traffic, heavy moving machinery etc.
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4.6.2 During Operation Phase
Major sources of noise pollution will be
• Operational machineries
• Pumps
• D.G. set
• Transportation
4.6.3 Management
I. During Construction Phase
• Complete construction work especially heavy work will be done during day time.
• Vehicular movement carrying raw materials will be avoided during night time.
• The vehicles will be regularly maintained and optimum use of the same will be made.
• Adequate PPE’s (ear plugs, ear muffs, helmet, mask etc) will be provided to the
workers.
• PUC certified vehicles will be used.
II. During operation phase
• All possible measures will be taken to minimize the noise.
• Foundations and structures will be designed to minimize vibrations and noise.
• Regular equipment maintenance and better work habits will be adopted.
• Necessary safety and personal protective equipment such as ear plugs, ear muffs,
helmet etc will be provided to the workers.
• Noise levels generated will be maintained to comply with the Factories Act & Rules and
will not exceed 75 dB (A) at 1 m distance.
• Implementation of green belt within the premises of plant will absorb the noise. Thus will
help to control the noise pollution.
• Proper lubrication and housekeeping will be usually done to avoid excessive noise
generation.
• Supervisor will be responsible to control the noise by maintaining conditions of
machineries and silencers.
• 33% of the total plot area will be under greenbelt.
4.7 BIOLOGICAL ENVIRONMENT
4.7.1 Impact during Construction:
Site has undergone with the construction phase and subsequent vegetation clearance. The
adjacent spaces of the site possess common floral species; it indicates that, the site would
have only same vegetation, which has been already cleared.
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4.7.2 Impact during Operational phase:
I. Loss of Natural Vegetation and Threatened Species
Particular Description Nature Operational activities would result in a negative direct impact
on the natural vegetation of the project site. Impact Magnitude Low Extent: The extent of the impact is local due to local and common
species observed in the area. Duration The duration would be short-term as the ecology of the area
would be affected to the least until the project is decommissioned.
Intensity The intensity is Medium as vegetation may still be impacted from operational activities.
Likelihood It is likely that this impact would occur. Impact Significance (Pre-Mitigation) MODERATE (-VE) Degree of Confidence The degree of confidence is high.
Impact Characteristics: Impacts on Flora and Fauna
Pre- and Post-Mitigation Significance: Impact on Fauna
Summary Construction Operation Phase Significance (Pre-mitigation)
Residual Impact Significance
Project Aspect/ activity
NA
Damage to natural vegetation through off-road movement of vehicles and maintenance activities.
Construction NA NA
NA
Disturbance to fauna associated with the operation of the plant and movement of vehicles.
Operation
Mammals MINOR (-VE) MINOR (-VE)
Reptiles MINOR (-VE) MINOR (-VE)
Amphibians MINOR (-VE) MINOR (-VE)
Impact Type Direct Direct Avifauna MINOR (-VE) MINOR (-VE)
NA
(i) On-site vegetation (ii) Fauna on the project site.
4.7.3 Mitigation
A total of 30047 sq. m (33%) area will be under greenbelt/plantation which will help in
minimizing the impacts. Total 1200 trees will be planted for the green belt development. The
same is detailed as under:
Green Belt Development
Plant species act as bio-monitoring agent to monitor the air environment as well as to keep
and maintain the project environ healthy. Trees have substantial inter-specific as well as
intra-specific variation in air pollution tolerance. Green Belt development / tree plantation in
organized manner is already done through development of 33% green belt in the existing
project site.
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Now it was suggested to plant more trees (approx 1200 nos. of Local trees species like:
Butea monosperma, Cassia fistula, Delbergia sissoo, Delonix regia, Polyalthia longifolia) in
the project site and nearby villages, to reduce the impact of expansion activities in the
surroundings of the existing project site. The above mentioned plants are suitable for green
belt development have characteristics like, fast growing, thick canopy cover, perennial and
evergreen large leaf area, naturally growing, efficient in absorbing pollutants without major
effects on natural growth.
Species Suggested for Plantation
Species have been suggested by considering various biological and environmental role of
the various plant species like Dust Control, Noise Control, Absorptions of Gases, Drought
resistance, Fire Resistance etc. Some flowering herbs and subs have been suggested to
enhance aesthetic beauty of the project site area.
Table No. 4.3
Recommended Plant species for Plantation
Plant Spices Common Name Ecological and Environmental Performances of Plant Species
Trees
Annona squamosa Amrud DC, DR, SR, FR
Azardirachta indica Neem DC, NC, AG, DR, FR.
Cassia fistula Amaltas DC, DR, FR.
Delbergia sissoo Shesham DC, DR, FR.
Delonix regia Gulmohar DC.
Polyalthia longifolia Ashoka DC, NC, AG.
Source: Anon 2007, Saxena 1991, Anon 2006, Hocking, 1993. DC- Dust Control, NC - Noise Control, AG – Absorptions of Gases, DR - Drought resistance, SR - Salinity resistance, FR - Fire Resistance
Shrubs
Croton oblongifolius Croton To enhance aesthetic beauty / DC*
Tabernaemontana divaricata Chandni To enhance aesthetic beauty / DC*
Withania somnifera Ashwagandh To enhance aesthetic beauty / DC*
Herbs
Tagetese minuta Genda To enhance aesthetic beauty/ DC*
Chrysanthamum Crown Daisy To enhance aesthetic beauty/ DC*
Rosa indica Rose To enhance aesthetic beauty/ DC*
*Source: phytoremediation of particulate matter from ambient environment through dust capturing plant species, CPCB 2007.
Green belt development plan budget A capital cost provision of Rs. 2, 25,000 has been kept for development of greenbelt as given in Table no. 4.4 below The budget includes cost of digging of pits, fertilizers, saplings and maintenance for 3 years.
Table No. 4.4
Green belt development plan budget
Activity Sub Activity Unit
Physical Target Total
2014-15 2015-16 2016-17
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Green Belt development plan
Selection of Species
Year √ √ √
Plantation Number 400 400 400 1200
Financial Target
2014-15 2015-16 2016-17
Capital cost (In lacs.) 75,000 75,000 75,000 2,25000 Recurring 15,000
4.7.4 Conservation Plan for Pavo Cristatus (Indian Peafowl)
Peacock or Indian peafowl (Pavo cristatus) is a familiar and universally known large pheasant. It is a National Bird of India, belongs to Schedule I of the Wildlife (Protection) Act 1972 was reported from the some villages of the study area. The male has a spectacular glossy green long tail feathers that may be more than 60 percent of the bird’s total body length. These feathers have blue, golden green and copper colored ocelli (eyes). The long tail feathers are used for mating rituals like courtship displays. The feathers are arched into a magnificent fan shaped form across the back of the bird and almost touching the found on both sides. Females do not have these graceful tail feathers. They have the fan like crest with whitish face and throat, chestnut brown crown and hind neck, metallic green upper breast and mantle, white belly and brown back rump and tail. Their primaries are dark brown. Study Approach Buffer zone of the study area has been reported as a habitat of Schedule I species Pavo cristatus commonly known as peacock, more effort was made to assess their status in term of movements and habitat use in and around the study area. At first, a detailed biological survey of the core zone and buffer zone (10 km radius from periphery of the Industry) was carried out to understand the status distribution of the species in the study area. Also, questionnaire survey was carried out to understand the recent status of peacock sightings and their movements. Overall, 15 people from seven villages were interviewed randomly. The conclusion of the survey discussed the potential sightings & habitat use, and movement and food habits of peacock in the study area. Habitat Use No any peacock was sighted in the core zone. All the direct sightings of the peacock were located near the human dominated and forest areas. This species is well adapted to natural village environment setting. According to the villagers, peacock is present in both, village and forest areas. Day time they temporarily move towards the surrounding agriculture areas for feeding while during night time roosts on the trees present in the village. Food Habits Peafowls are omnivores, eating plant parts, flower petals, seed heads, insects and other arthropods, reptiles and amphibians. In the study area, dense tree canopy cover supports good insect diversity which is very common food for peafowl.
Threats in the Study Area
In the study area, all the villages surveyed are against hunting or poaching of the people.
Buffer Zone as a Peacock Habitat - Conclusion
Present survey of the peafowl in the buffer zone of the project site cleared that; peafowl is
using both, village adjacent habitats and forest habitats of the buffer zone. However, the
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following points can give an insight on the overall status of peafowl in the study area and
thereby plan for better management strategies related to proposed project activities.
People of the surveyed villages were well aware of the habits and habitats of peafowl in the
study area. Moreover, local people are against hunting and poaching of the Peacocks. In the
buffer zone, peafowl uses agriculture (adjacent to village) and forest habitats as a feeding
and breeding ground. Some of the peacocks are taking shelter in the village adjacent
habitats while some prefer to rocky forest hills. It clearly indicates that, peafowl normally
uses human associated and forest habitats.
From above study, it has been visualized that, the proposed project will not have any
significant impact on peacock in terms of their normal movements and other activities.
However, it is necessity to take some management options like habitat improvement in the
villages located in the vicinity of the project site. So, habitat improvement programme
(plantation of local plant species) will be undertaken indifferent villages located in the close
vicinity of the project area. Under this programme saplings will be distributed in the nearby
villages with the consultation of the local forest department.
Habitat Improvement Programme and Awareness
Habitat improvement programme will be undertaken through plantation of suitable tree
species. Saplings of Madhuca indica (Mahua), Mangifera indica (Aam), Tamarindus indica
(Emli), Tectona grandis (Sagaon), Terminalia arjuna (Arjun), Butea monosperma (Dhak),
Aegle marmelos (Bel), Moringa oleifera (Sehjan) will be distributed in the nearest five
villages (as per year wise schedule). Species recommended by local forest department will
also be added in the present plantation programme.
In consultation of the forest department, following Conservation Measures will be adapted for
Peacock conservation:
• Habitat improvement programme in the different villages will be undertaken in the
buffer zone area for shelter and roosting of peacocks. This will be achieved by
plantation of locally adapted species near villages in buffer area.
• School level awareness programmes will be conducted for conservation of peacocks
by organizing competitions during “Wildlife Week” and “Van Mahotsav” celebrations.
For above mentioned activities, proponent has proposed a sum of Rs. 1,00,000/- for the
“Peacock” conservation plan under the following heads up to three years in consultation of
local forest department.
Table No. 4.5
Expenditure Budget for Five Years for Peacock Conservation
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S. No Activity 1st
year 2nd
year 3rd
year 4th
year 5th
year Budget (INR)
1 Plantation- approximately 200 saplings/year for five years (@ Rs. 50/- per saplings)
Amount Rs. 10000/- 10000/- 10000/- 10000/-
10000/- 50,000/-
Villages Lalwari Thuni Bhaironji
Ka Bag Dehlod Ki Dhani
Bhagatrampura
2 Awareness programme for “Peacock” conservation will be scheduled in a year in five schools every year.
Amount Rs. 10,000 10,000 10,000 10,000 10,000 50,000/-
Schools of Jhanpari Bhanwata Sedria Agarpura Shrisurapura
Total Budget Rs. 1,00,000/-
(One Lakh Rupees)
All above activities will be carried out with the consultation of local forest department and
Gram panchayat of respective villages.
A. Plantation- approximately 200 tree/year plants of local plant species for five
years.
Plants species / verities will be suggested by the local forest department and plant
saplings will be distributed in project villages as per the above mentioned schedule
(year wise). Once the plantation will be
B. Awareness programme for “Peacock” conservation will be scheduled in a year
in five (nearest to project site) schools every year.
During awareness programme following activities will be arranged at the various
village level schools as mentioned above (year wise),
• “Essay writing on Peacock”
• “Drawing competition (Peacock picture)
Further Suggestions/recommendations:
� To carry annual census research projects to ecology and habitat use by peacock.
� By making provision of veterinary care and cages for injured or sick deformed birds.
4.8 SOCIAL IMPACT ASSESSMENT
Socio Economic
Issues
Details of Impact due to the proposed
project
Mitigation measures
The core zone
habitation
No habitation in the core zone. Hence Zero (0)
Loss of habitation.
--
The buffer zone
habitation
The habitation in the study area is scattered
from the location of the site proposed.
The nearest habitation in Shedriya 1.6 km
NW. The habitation comprises of agriculture
The proposed project is a
completely automated wet
asbestos process. Air quality
management shall be required :
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workers. The predominanat wind direction is
largely from NW towards South East , and in
this direction the habitation of the following
villages are :
Nearest Habitation SE H/H Population
Agarpura (4.5 km SE) 73 348
Lalwari (3.0 km ESE) 676 3534
Sangarampura (4.0 km
SSE) 59 429
• Water spraying for suppression
of air borne asbestos crystolite
and
• Development of green belt will
be done.
• Periodic maintenance and
emission check of vehicles shall
be ensured to restrict air
pollution.
Public health & safety plan is
given below :
Public Health & Safety Plan :
Observation by
supervisor and
Gram Panchayat
Shedriya, of any
symptoms will
be reported at
the earliest.
Development of any symptoms amongst the local
residents and employees will be monitored, such as
• shortness of breath
• coughing
• painful breathing
• chest pain
• difficulty to perform physical tasks
• loss of weight
• headache
• pain in the bones or
Any movement requiring medical attention.
Qualified Oncologist and /or Pathologist /Physician
will conduct exams to determine the cause of the
symptoms.
In consultation with local
authorities and Gram
Panchayat, Shedriya, for the
development of the primary
health centre, Shedriya by
Contributing for a Multi-
specialty hospital for
critical illness and
emergency along-with a
Medical Ambulance for the
study area.
Regular Health camps shall
be organized to trace any
indication of Asbestosis/ lung
Cancer and will be kept
under surveillance
immediate action will be
taken.
Regular
Diagnosis in
the study area :
Diagnosis by a qualified Oncologist and /or
Pathologist will be done in every quarter (3 months),
for every batch of 20 workers and mainly in three
villages in the wind direction viz. Agarpura, Lalwari,
Sangarampura.
Adequate monitoring of Asbestos Fibre in air, will be
done at regular intervals to check the effectiveness
of the automated plant & machinery.
A regular urinalysis, x-rays,
or a bronchoscopy (a test
that detects asbestos fibers
within lungs), and
determines the extent of the
damage done by asbestos
exposure, will be done in
every 3 months mainly in
three villages in the wind
direction viz. Agarpura,
Lalwari, Sangarampura.
Safeguards
during
transportation
enroute the
buffer zone.
The raw material will be procured and handled by
BOD (bag opening devices) and the finished
asbestos sheets will be automated to be sealed
with 0.2 mm thick polythene sheeting & taping it
with duct tape. This will nullify the amount of dust
The associated risks
during transportation and
manual handling will not be
applicable. The proposed
project is a capital-
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even during transportation. Hence the Manual
handling will not be done in any stage of the
production process. In case of breakage of any
asbestos cement sheets, adequate air quality
equipments will be installed. Also a spray with a
poly vinyl solution (PVA) or with water will be done.
intensive unit hence any
Man- Machine relationship
will be kept to the optimum
level of machine operation.
Research on
Vaccination is
being
followed.
The indicators of mesothalmia will be periodically
checked as they are swelling, anemia, nausea,
constipation, fever or sweating at nights and loss in
weight, in addition to the breathing symptoms will be
monitored of every worker public at large.
Immediate cure and treatment shall follow.
A vaccine developed at the Erasmus Medical
Research Centre in Rotterdam has shown early
promise in its first clinical trials.
Researchers at Erasmus say the vaccine brings
about an anti-tumor reponse, Dr Joachim Aerts a
pulmonary physician says "We hope to further
develop our methods so it will be possible to
increase survival in patients with Mesothalmia and
eventually vaccinate persons who have been in
contact with asbestos to prevent them from getting
asbestos related diseases".
The findings have been published online ahead of
print publication in the American Thoracic Society's
American Journal of Respiratory and Critical Care
Medicine.
Research done by Bob Tolley Asbestos Charity
Awareness on indicators of
mesotheolima shall be
given to the public at large.
Awareness camp shall
provide demonstration and
action plan.
The use of asbestos has
been prohibited in most
developed countries, but
the time between asbestos
exposure and diagnosis of
mesothalmia can be up to
50 years.
Large scale,
long term and
stable
employment
Large scale, long term and stable job
opportunities to locals.
Direct Employment
Employment Generation Manpower
a) Managers/Supervisors 15
b) Staff 14
c) Workers –
i) Skilled
ii) Unskilled
iii) Contract Workers
(Loading &
Unloading)
51
141
300
Total 521
No. of employees in the first year of
production and on achievement of installed
capacity will be same.
Increased Job opportunities to local people.
Training shall be given to local
residents. Skill enhancement
training shall be given to village
workers both on-the-job training
and off-the-job training. It is a long
standing project; therefore there
will be avenues for long term and
stable jobs.
Workers health & safety plan is
given below :
• Helmets, Face masks (P1 or P2
respirator/ ventilator), Heavy
duty gloves, Disposable ear
muffs and goggles will be
provided to the workers.
• Most importantly disposable
coveralls will be provided to
avoid any particles of asbestos
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on clothing or skin.
Workers Health & Safety Plan :
Conservancy /
Shower rooms
for workers.
Adequate shower rooms will be constructed.
Workers will have to take a shower anytime
during the day and before leaving for home.
The proposed project aims to put 492 workers.
(There shall be provided, a minimum of 5 toilets
for every 100 workers.)
To avoid any particles of asbestos left on the
workers clothing or skin, as it could be easily
inhaled while breathing in, when the job is
complete and the measure is to prevent any
traces of lung cancer.
Washing face and hands in
every 1-2 hours will be taught
as a good habit.
Safeguards All protective and safety gears will be provided
and regular training will be given on the
importance and use of the safeguards.
Helmets, Face masks (P1 or P2 respirator/
ventilator), Heavy duty gloves, Disposable ear
muffs and goggles will be provided to the
workers. Most importantly disposable coveralls
will be provided to avoid any particles of
asbestos on clothing or skin.
Training on laying out the
disposable coveralls, (the
polythene drop cloths) on the
ground, covering everything
on the surface. Asbestos will
stick to anything and bury
itself in material fibers.
Physical
Exertion of
musculo-
skeletel
movement.
The physical exertion such as excessive lifting,
climbing or digging with heavy objects will be
not be done in the proposed project as it is a
completely automated wet asbestos process.
Also work motion study will be done and the
following ways methods will be adopted :
a.) Use of relief workers
b.) Assign extra workers
c.) minimize overexertion
d.) Scheduling of jobs
The associated risks of
manual handling will not be
applicable
Medical
Appliances &
Arrangements
Equipped First aid Boxes or cupboards will be
at the disposal and accessibility of the workers.
Conveyance arrangements
to hospitals or dispensaries
from the proposed project
site, will be readily made in
unfortunate circumstances
if any worker, suffer bodily
injury or becomes ill during
the working hours.
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Insurance
(medical +
hospitalization
+ liability)
A provision liability and hospitalization
insurance will be made for each worker.
Medical Insurance and Life
Insurance shall be provided
to the plant workers.
Indirect
employment :
1. Transportation and warehousing in the region
would eventually be needed more therefore
truckers and jobs in logistical activities will increase
around the Gram Panchayat, Shedriya. Asbestos
cement sheets available will provide agency
employment in the value chain analysis, which will
add place utility and retail in the domestic market.
3. The increased employment through,
warehousing, and logistics management will
provide indirect agency employment.
A high importance & high
positive impact.
Many local people are
expected to gain
opportunities in various
sectors, through the
proposed project.
Development
of allied
business
activities.
Encourage the trade in the local market and in turn
will help in the development of the area. This would
create indigenous technologies for sustainable
development.
A low positive Impact.
Mechanical
and Atomized
handling of
Raw material
and Finished
products.
The raw material will be handled by BOD (bag
opening devices) and the finished asbestos
sheets will be automated to be sealed with 0.2
mm thick polythene sheeting & taping it with duct
tape. Hence the Manual handling will not be done
in any stage of the production process. In case of
breakage of any asbestos cement sheets,
adequate air quality equipments will be installed.
Also a spray with a poly vinyl solution (PVA) or
with water will be done. This will lessen the
amount of dust created.
The associated risks of
manual handling will not be
applicable;
Local /
Regional
Growth
The industrial activities and associated activities in
the Asbestos plant bearing areas bring about
gains in gross domestic product, i.e. there is
though a minor contribution by the proposed
project but will add to the gains in G.D.P.
A moderate importance as
the proposed production
capacity is a minor
contribution to regional and
national targets.
To meet the
demand and
supply gap in
the region.
As per the future outlook of Indian bureau of
mines: The resources of crystolite variety of
asbestos are very much limited in India. So, the
internal demand for asbestos in the country
cannot be met from indigenous production and
manufacturing.
A long term stable impact.
Hence, to meet the demand
effectively, the proposed
plant encompasses all
technical and social
advantages to marginally
bridge the demand supply
gap of Asbestos cements
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sheets in the region.
Additional gains
in Government
Revenue
Generation.
Indirectly, the proposed project will contribute the
Government by paying different taxes (sales tax,
excise duty, etc) from time to time, which forms a
part of the revenue and thus, will help in the
growth and development in the area.
A moderate positive impact.
The proposed project will
contribute through various
direct, indirect taxes and
duties like corporate tax,
sales tax, excise duty, etc.
These form a part of the
revenue and thus, will be
put in public expenditure.
Asbestos
Cement sheets
solutions
The Asbestos Cement sheets will fulfill its end-use
in Asbestos cement roof demanded in the local
region.
A low positive Impact.
Enterprises
social
commitment
benefits
The proposed plant impact will be welfare oriented
and aims to create sustainable development by
allocating welfare funds in the following sectors :-
� Permanent structures / facility development like
rainwater harvesting structures in government
institutions.
� Contribution towards a Multi-specialty hospital
for critical illness and emergency in the
development of the primary health centre, Gram
Panchayat, Shedriya
� Malnutrition Camps for Mother and Child in the
study area including drops / supplements.
� Skill development and earning sources for
youth.
The major positive impact of
the social development will
aim to strengthen social
inclusion by ensuring that
both poor and excluded
groups and intended
beneficiaries are included in
the benefit stream and in
access to opportunities
created by the project.
Quality
management
System
The proposed unit of Visaka Industries Ltd. aims to
have a well equipped, sophisticated, most modern
process control laboratory for chemical analysis
and mechanical testing for its proposed unit. The
laboratory will assists in keeping a tab on both
inputs and finished products. The quality control
activities in the proposed unit aims to begin right at
the procurement level itself and run through the
entire process concluding with the product specific
rigorous testing in the in house laboratory.
Visaka Industries Ltd., aims
for customer satisfaction
and maintaining quality
assurance system.
Quality Products
to the society
Visaka Industries Ltd., aims to get recognized by
Bureau of Indian Standards for fulfilling the best
quality of Asbestos Cement Sheets with the ISI
mark to meet all quality parameters and fitness for
use.
Visaka Industries Ltd. will
ensure fitness of its
products for use and
believes that by producing
quality products the
enterprise is fulfilling its
foremost social
commitment.
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Human Rights It is clearly stated in as per the Human Rights, that
the obligation of States is to promote universal
respect for, and observance of, culture & religion.
The proposed project will follow universal respect
for, and observance and protection of, human
rights and fundamental freedoms for all.
The proposed project will
promote neither selective, nor
relative, but universal respect
through contribution in
various festivities, equal
observance and protection
among employees and
societies at large in all
activities.
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SECTION – V
ENVIRONMENTAL MONITORING PROGRAMME
INDEX
ENVIRONMENTAL MONITORING PROGRAMME .......................................................... 146
5.1 INTRODUCTION ..................................................................................................... 146
5.2 ENVIRONMENTAL MONITORING AND REPORTING PROCEDURE ................... 146
5.3 ENVIRONMENTAL MONITORING CELL ............................................................... 147
5.4 MONITORING METHODS ..................................................................................... 149
5.5 REPORTING SCHEDULES OF THE MONITORING DATA ................................... 150
5.6 INFRASTRUCTURE FOR ENVIRONMENTAL MONITORING ............................... 150
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ENVIRONMENTAL MONITORING PROGRAMME
5.1 INTRODUCTION
Regular monitoring of environmental parameters is of immense importance to assess the
status of environment during project operation. With the knowledge of baseline conditions,
the monitoring programme will serve as an indicator for any deterioration in environmental
conditions due to operation of the project, to enable taking up suitable mitigatory steps in
time to safeguard the environment. Monitoring is as important as that of control of pollution
since the efficiency of control measures can only be determined by monitoring.
Usually, as in the case of the study, an impact assessment study is carried over short period
of time and the data cannot bring out all variations induced by the natural or human
activities. Therefore, regular monitoring programme of the environmental parameters is
essential to take into account the changes in the environmental quality.
5.2 ENVIRONMENTAL MONITORING AND REPORTING PROCEDURE
Monitoring will confirm that commitments are being met. This may take the form of direct
measurement and recording of quantitative information, such as amounts and
concentrations of discharges, emissions and wastes, for measurement against corporate or
statutory standards, consent limits or targets. It may also require measurement of ambient
environmental quality in the vicinity of a site using ecological/biological, physical and
chemical indicators. Monitoring may include socio-economic interaction, through local liaison
activities or even assessment of complaints.
The preventive approach to management may also require monitoring of process inputs, for
example, type and method used, resource consumption, equipment and pollution control
performance etc.
The key aims of monitoring are, first, to ensure that results/conditions are as forecast during
the planning stage, and where they are not, to pinpoint the cause and implement action to
remedy the situation. A second objective is to verify the evaluations made during the
planning process, in particular with risk and impact assessments and standard & target
setting and to measure operational and process efficiency. Monitoring will also be required to
meet compliance with statutory and corporate requirements. Finally, monitoring results
provide the basis for auditing.
5.2.1 Objectives of Monitoring
The objectives of monitoring are to:
• Verify effectiveness of planning decisions;
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• Measure effectiveness of operational procedures;
• Conform statutory and corporate compliance; and
• Identify unexpected changes.
5.3 ENVIRONMENTAL MONITORING CELL
A centralized environmental monitoring cell will be established for monitoring of important
and crucial environmental parameters which are of immense importance to assess the
status of environment during operation of plant. With the knowledge of baseline conditions,
the monitoring program can serve as an indicator for any deterioration in environmental
conditions due to operation of the plant, and helps in planning suitable mitigatory steps that
could be taken in time to safeguard the environment. Monitoring is as important as that of
control of pollution since the efficiency of control measures can only be determined by
monitoring. The following routine monitoring program will be implemented under the post-
project monitoring as per CPCB guidelines.
Environmental monitoring schedules are prepared covering various phases of project
advancement, such as constructional phase and regular operational phase.
5.3.1 Monitoring Schedule during Constructional Phase
The proposed project envisages setting up of Asbestos cement sheets manufacturing unit.
The construction or preoperational activities require mobilisation of construction material and
equipment. During construction phase the main source will be fugitive emission from
transportation of construction material and etc. As such monitoring is not required during
construction phase.
5.3.2 Monitoring Schedule during Operational Phase
Dust measurement / monitoring is done at work zone as per the guidelines of Rajasthan
Pollution Control Board and Central Pollution Control Board. Samples will be collected
periodically and measured. During operational stage, asbestos fibres, cement particles and
agglomerates of particles and fibres may be emitted from both point sources and fugitive
emissions. Along with the above, D.G. sets are also a potential source of emission.
Following attributes which merit regular monitoring based on the environmental setting and
nature of project activities are listed below:
• Source emissions and ambient air quality;
• Groundwater Levels and ground water quality;
• Water and wastewater quality (water quality, effluent & sewage quality etc);
• Soil quality;
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• Noise levels (equipment and machinery noise levels, occupational exposures and
ambient noise levels);
• Ecological preservation and afforestation.
The following routine monitoring programme as detailed in as under will be implemented at
site. Besides to this monitoring, the compliances to all environmental clearance conditions
and regular permits from SPCB/MoEF will be monitored and reported periodically.
Table No. 5.1
Ambient air monitoring program
SAMPLING LOCATION
1 Fibre Godown (P) 1 No. – Monthly once
2 Fibre bag feeding to BOD (P) 1 No. – Monthly once
3 Sheet cutting (P) 1 No. – Monthly once
4 Moulded goods finishing (P) 1 No. – Monthly once
5 Waste recycling ( Wet Ball Mill) (P) 1 No. – Monthly once
6 RM Section (S) 1 No. – Once in 6 month
7 Ambient location 1 No. – Once in 6 month
8 Loading Platform 1 No. – Once in 6 month
Note : (P) – Personal Sample, Sampler is attached to the operative
(S) – Static, Sampler is kept fixed in one location.
SAMPLING/COUNTING METHOD
Name of Sampler Personal Sampler
Make / Model of Sampler Envirotech, APM 800
Flow Rate / Sample dur’n 1 LPM / 1 Hr
Filter Paper Details Millipore, 0.8 u
Sample/Counting ref spec RTM1, IS 11450 – ’86
Fibre counting instrument ‘Carl Geiss’ Trinocular research microscope for bright field
phase contrast application, Model :AXIOS KOP40, Obj Mag
10x
Counting Method Membrane Filter Method
Max Permissible Value 0.1 fibre / cc
Table No. 5.2
Stack emission monitoring program
SAMPLER DETAILS
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Name of Sampler Stack Monitoring Kit
Make / Model of Sampler Envirotech, APM 810 Filters used Cellulose thimble, Glass thimble LIMITING VALUES
Fibre stack – SPM 2 mg/NM3
– Fib count 0.2 fib/cc
Cement Stack – SPM 115 mg/NM3
Fly ash Stack – SPM 115 mg/NM3
DG Set – SPM 115 mg/NM3
– SO2 800 mg/NM3
– NOx N.S.
Sampling Frequency Once in a month for each stack
5.4 MONITORING METHODS
5.4.1 Air Quality Monitoring
I. Workspace Monitoring
The concentration of air borne pollutants in the workspace/work zone environment will be
monitored periodically. If concentrations higher than threshold limit values are observed, the
source of fugitive emissions will be identified and necessary measures taken. If the levels
are high, suitable measures as detailed in EMP will be initiated.
II. Ambient Air Quality Monitoring
The ground level concentrations of PM10, PM2.5, SO2, NOX, cement particles, asbestos fibres
and agglomerates of particles and fibres in the ambient air will be monitored at regular
intervals. Any abnormal rise will be investigated to identify the causes and appropriate action
will be initiated. The ambient air quality data should be transferred and processed in a
centralised computer facility equipped with required software. Trend and statistical analysis
should be done.
5.4.2 Water and Wastewater Quality Monitoring
To ensure a strict control over the water consumption, flow meters will be installed for all
major inlets. All leakages and excess will be identified and rectified. In addition, periodic
water audits will be conducted to explore further possibilities for water conservation.
Methods prescribed in "Standard Methods for Examination of Water and Wastewater"
prepared and published jointly by American Public Health Association (APHA), American
Water Works Association (AWWA) are recommended.
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I. Monitoring of Wastewater Streams
All the wastewater streams in the project area will be regularly analysed for flow rate and
physical and chemical characteristics. Such analysis is carried out for wastewater at the
source of generation, at the point of entry into the wastewater treatment plant and at the
point of final discharge. These data will be properly documented and compared against the
design values for any necessary corrective action.
II. Monitoring of Groundwater
The monitoring of groundwater is the most important tool to test the efficiency of plant
performance. It is suggested to collect water samples and analyse. Records of analysis will
be maintained.
5.4.3 Noise Levels
Noise levels will be monitored in the plant area. The frequency will be once in a month in the
work zone. Similarly, ambient noise levels near habitations will also be monitored once in
three months. Audiometric tests should be conducted periodically for the employees working
close to the high noise sources especially D.G. Set operations in this case.
5.5 REPORTING SCHEDULES OF THE MONITORING DATA
It is proposed that voluntary reporting of environmental performance with reference to the
EMP should be undertaken.
The environmental monitoring cell will co-ordinate all monitoring programmes at site and
data thus generated will be regularly furnished to the State regulatory agencies.
The frequency of reporting will be on six monthly bases to the local state RSPCB officials
and to Regional office of MoE&F. The Environmental Audit reports will be prepared for the
entire year of operations and will be regularly submitted to regulatory authorities.
5.6 INFRASTRUCTURE FOR ENVIRONMENTAL MONITORING
Name of Equipment Purpose
High volume sampler Stack monitoring
Fine dust samplers / Respirable dust samplers
(Proposed)
AAQ monitoring
Online HF monitor AAQ monitoring (Installed)
Sound level meter Noise levels
Phase contrast microscope
UV – Spectro photo meter Chemical analysis
Micro-balance Chemical analysis
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Name of Equipment Purpose
High volume sampler Stack monitoring
Oven Heating
Thermometer / Dry & wet bulb Temperature / relative humidity
pH meter pH analysis
DO analyzer DO analysis
Pipette box Chemical analysis
Titration set up Chemical analysis
Relevant Chemicals Chemical analysis
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SECTION-VI
ADDITIONAL STUDIES
INDEX
ADDITIONAL STUDIES ......................................................................................................... 153
6.1 PUBLIC HEARING ...................................................................................................... 153
6.2 RISK ASSESSMENT .................................................................................................. 154
6.3 HAZARD IDENTIFICATION ........................................................................................ 154
6.4 HAZARD ASSESSMENT AND EVALUATION ............................................................ 155
6.5 RISK ASSESSMENT SUMMARY .............................................................................. 156
6.6 TYPE OF ACCIDENTS .............................................................................................. 156
6.7 RISK ASSESSMENT .................................................................................................. 157
6.8 DISASTER MANAGEMENT PLAN ........................................................................... 159
6.9 OCCUPATIONAL HEALTH AND SAFETY ............................................................... 166
6.10 CORPORATE SOCIAL RESPONSIBILITY ............................................................ 173
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ADDITIONAL STUDIES 6.1 PUBLIC HEARING
The Public hearing was conducted on 24.7.2014 at 01:00 PM under the Additional Deputy
Commissioner (ADC-Tonk) Mr. P.S. Naga and The Regional Officer, Rajasthan Pollution
Control Board, Kishangarh Mr. Mr. V.S. Sankhala.
As per the Gazette Notification dated 14th Sept’ 2006 by MoE&F and subsequently
amendment on 1st Dec’ 2009, the concerned industry had applied to RPCB for public
hearing. Hereinafter, the District Collector Tonk fixed the date of public hearing on
24.07.2014.
The public notice for the same was published in “DNA India” and “Dainik Bhaskar” on
21.06.2014. In the public hearing some points were raised by the public and
response/commitment were given by project proponent and towards the side of project
consultants is depicted as below:-
S. No. Issues raised Response
1.
Shri Bajrang Lal Bairwa, Surpanch
• He said that the villagers will get
employment due to the proposed
project.
In response to the same, Mr. Jawahar
Rawatani (Unit representative), said that
we will start the project with the support
of villagers only. There are several unit
of visaka industries and everywhere we
are working with the support with
villagers or local people.
We will provide training and
employment to local people.
We will also help in improving the
education facilities.
2. Shri Mangilal Gurjar, Sedaria
• He said that the unit should do
development in the village and
provide employment to the local
villagers.
• The unit should train the local
people.
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6.2 RISK ASSESSMENT
6.2.1 Introduction
Hazard analysis involves the identification and quantification of the various hazards (unsafe
conditions) that exist in the proposed plant. On the other hand, risk analysis deals with the
recognition and computation of risks, the equipment in the plant and personnel are prone to,
due to accidents resulting from the hazards present in the plant. Risk analysis follows an
extensive hazard analysis. It involves the identification and assessment of risks the
neighboring populations are exposed to as a result of hazards present. This requires a
thorough knowledge of failure probability, credible accident scenario, vulnerability of
population etc. Much of this information is difficult to get or generate. Consequently, the risk
analysis is often confined to maximum credible accident studies. In the sections below, the
identification of various hazards, probable risks in the proposed plant, maximum credible
accident analysis, consequence analysis are addressed which gives a broad identification of
risks involved in the plant.
6.2.2 Approach to the Study
Risk involves the occurrence or potential occurrence of some accidents consisting of an event
or sequence of events. The risk assessment study covers the following:
• Identification of potential hazard areas;
• Identification of representative failure cases;
• Visualization of the resulting scenarios in terms of fire (thermal radiation) and
explosion;
• Assess the overall damage potential of the identified hazardous events and the
impact zones from the accidental scenarios;
• Assess the overall suitability of the site from hazard minimization and disaster
mitigation point of view;
• Furnish specific recommendations on the minimization of the worst accident
possibilities; and
• Preparation of broad Disaster Management Plan (DMP), On-site and Off-site
Emergency Plan, which includes Occupational and Health Safety Plan.
6.3 HAZARD IDENTIFICATION
Identification of hazards in the proposed plant is of primary significance in the analysis,
quantification and cost effective control of accidents involving chemicals and process. A
classical definition of hazard states that hazard is in fact the characteristic of
system/plant/process that presents potential for an accident. Hence, all the components of a
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system/plant/process need to be thoroughly examined to assess their potential for initiating or
propagating an unplanned event /sequence of events, which can be termed as an accident.
The following two methods for hazard identification have been employed in the study:
• Identification of major hazardous units based on Manufacture, Storage and Import
of Hazardous Chemicals Rules, 1989 of Government of India (GOI Rules, 1989);
and
• Identification of hazardous units and segments of plants and storage units based on
relative ranking technique, viz. Fire-Explosion and Toxicity Index (FE&TI).
6.4 HAZARD ASSESSMENT AND EVALUATION
6.4.1 Methodology
An assessment of the conceptual design is conducted for the purpose of identifying and
examining hazards related to feed stock materials, major process components, utility and
support systems, environmental factors, proposed operations, facilities, and safeguards.
6.4.2 Preliminary Hazard Analysis (PHA)
A preliminary hazard analysis is carried out initially to identify the major hazards associated with
storages and the processes of the plant. This is followed by consequence analysis to quantify
these hazards. Finally, the vulnerable zones are plotted for which risk reducing measures are
deduced and implemented.
6.4.3 Fire Explosion and Toxicity Index (FE&TI) Approach
Fire, Explosion and Toxicity Indexing (FE & TI) is a rapid ranking method for identifying the
degree of hazard. The application of FE & TI would help to make a quick assessment of the
nature and quantification of the hazard in these areas. However, this does not provide precise
information.
The degree of hazard potential is identified based on the numerical value of F&EI as per the
criteria given below:
F&EI Range Degree of Hazard
0-60 Light
61-96 Moderate
97-127 Intermediate
128-158 Heavy
159-up Severe
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By comparing the indices F&EI and TI, the unit in question is classified into one of the following
three categories established for the purpose Table No. 7.1.
Table No. 6.1
Fire Explosion and Toxicity Index
Category Fire and Explosion Index (F&EI) Toxicity Index (TI)
I F&EI < 65 TI < 6
II 65 < or = F&EI < 95 6 < or = TI < 10
III F&EI > or = 95 TI > or = 10
6.5 RISK ASSESSMENT SUMMARY
The preliminary risk assessment has been completed for the proposed plant and associated
facilities and the broad conclusions are as follows:
• There will be no significant community impacts or environmental damage
consequences; and
• The hazardous event scenarios and risks in general at this facility can be adequately
managed to acceptable levels by performing the recommended safety studies as part of
detailed design, applying recommended control strategies and implementing a Safety
Management System.
6.6 TYPE OF ACCIDENTS
A. Erection / Commissioning
During erection stage, most of the accidents occur due to;
• Human errors (unsafe acts and unsafe conditions)
• Improper laying of cables
• Improper Housekeeping (keeping combustible material near welding / gas cutting
operations)
• Material handling
• Handling of tools
• Working at heights/elevated levels
• Material handling with equipments like crane, hydraulic pay loaders, JCB, Proclain
• Earth moving and filling
• Unsafe electrical practices
B. Process Operations
The excessive pressure may lead to serious injuries at the site.
• Malfunctioning of equipment
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• Power failures
• Failure to take corrective steps in time.
• Failure of utilities
• System failure
• Ageing of erection equipments
• Improper communication
C. Storage and Transfer Operations
• Accidents due to mechanical failure and external impacts.
• Static electricity
• Thunder and lightning
• On the job
6.7 RISK ASSESSMENT
Risk will be assessed by:-
• Identification of potential hazard areas;
• Identification of representative failure cases;
• Visualization of the resulting scenarios in terms of fire (thermal radiation) and explosion;
• Assess the overall damage potential of the identified hazardous events and the impact
zones from the accidental scenarios;
• Assess the overall suitability of the site from hazard minimization and disaster mitigation
point of view;
• Furnish specific recommendations on the minimization of the worst accident possibilities;
and
• Preparation of broad Disaster Management Plan (DMP), On-site and Off-site Emergency
Plan, which includes Occupational Health and Safety Plan.
• Identifying potential risks to local people and local resources in the event of an
emergency.
6.7.1 Risk Prevention Techniques
• Education and awareness
• Best practices Risk Based Maintenance Planning
• Hazard identification
• Quantitative Hazard Assessment
• Probabilistic Hazard Assessment
• Risk Quantification
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• Risk evaluation
• Setting up risk acceptance criteria
• Risk comparison
• Maintenance planning
I. Engineering and administrative measures
� Personal sampling will be carried out at these places to monitor work zone
fibre concentration levels. The workers working in these areas will be provided
with Nose masks made of cotton clothing material.
� A regular system of inspection, examination and maintenance is necessary for all
machinery and equipment of the plant. The bag opening devices will be checked
regularly for any leakages.
� Any leakage from closed loop will be regularly checked and the in case of any
leakge the plant will shut down and the emergency plan will taken up.
� There is a never-ending need for good housekeeping. Falls and stumbles caused
by obstructed floors or implements and tools left lying carelessly can cause injury
in themselves but can also throw a person against hot or molten material.
II. Industrial hygiene
� Good general ventilation throughout the plant and local exhaust ventilation (LEV)
wherever substantial quantities of dust and fumes will be generated or gas may
escape are necessary, together with the highest possible standards of cleanliness
and housekeeping.
� With a view to improving the work environment, induced ventilation will be installed
to supply cool air.
III. Personal protective equipment
� All parts of the body are at risk in most operations, but the type of protective wear
required will vary according to the location.
� Those working at slurry mixing tank and raw material handling area will need
nose mask, gloves to prevent the direct contact with asbestos dust.
� Safety boots, safety glasses and helmets are imperative in almost all occupations
and gloves are widely necessary.
� Strict supervision and continuous propaganda are necessary to ensure that
personal protective equipment is worn and correctly maintained.
IV. Medical supervision
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A. Pre-employment Surveillance
• Pulmonary Function Test (Spirometry – FVC & FEV1)
• Complete Physical Examination
• Blood Test
• Urine Test
• Chest X ray
B. Periodical Medical Surveillance
Pulmonary Function Test (– FVC & FEV1) ……………………..Once in a year
Complete Physical Examination…………………………………..Once in a year
Blood Test …………………………………………………………..Once in a year
Urine Test……………………………………………………………Once in a year
Chest X ray ………………………………………………………….Once in 3 years
C. At Cessation – Medical Surveillance
* Pulmonary Function
Test ( FVC & FEV1) }
* Complete Physical }
Examination } within 5 years
* Blood Test } after cessation
* Urine Test }
* Chest X ray }
6.8 DISASTER MANAGEMENT PLAN
Rapid development has posed wide-ranging hazards threatening safety and health of
people. Accidents may adversely affect the environment and the people living in the vicinity.
These accidents can be minimized to a great extent by proper procedures, handling and
training but it may be difficult to reach zero risk or absolute safety level. Whenever such
incidents do occur in order to prevent loss of lives and damage to property, it becomes
necessary to take immediate steps to control the situation. This can be achieved through a
planned advance preparation to face such a situation with respect to both on site and off site
emergencies.
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A Vulnerable Areas
Maximum Credible Areas (MCA) of consequence that could be needing consideration in
disaster management plan are work shed, machinery storage and feed areas of raw
materials, area of DG Sets, loading/unloading areas of materials/sheets, atmospheric
corrugators, run out conveyors and de-stacker’s (if any).
Analysis of Vulnerable Areas
From the analysis of the above zones the action suggested are discussed as below:
• All storage of raw materials & feed areas will be demarcated & placed in conformity to
the safety act & its prescription to prevent any hazards.
• The people involved in such work places will be protected with all BIS certified Personal
Protective Equipments and given adequate training on safe operation and disaster
control, if arises.
• Only trained personnel will be allowed to work at risky areas under strict supervision
• Provision of protective gear, masks, hand gloves etc. will be provided to all employees
in the raw materials feed areas.
• Good Ventilation and cleaning the above areas in multitude times of working hours.
• Occupational Health hazard survey will be undertaken for all employees from the
beginning of their employment.
B On- Site Emergency Plan
An On-site Emergency is caused by an accident that takes place in a hazardous installation
and the effects are confined to the factory premises involving the people working in the
factory. On-site Emergency Plan is dealing with eventualities, and it is the responsibility of
the Occupier, to prepare/implement necessary measures to contain the severity of cause of
disaster to the bare minimum.
The preparation of an On-site Emergency Plan, furnishing relevant information to the District
Administration Authority for the preparation of the Off-site Emergency plan are statutory
responsibilities of the Occupier of every industry and other units
a) Objectives
Maximize the resource utilization and combined efforts towards emergency operations. It
broadly covers the following:-
1. To safeguard the personal located in the premises.
2. To localize the emergency and if possible eliminate it.
3. To minimize the effects of accidents on people, property and environment.
4. To take remedial measures in the quickest possible time to contain the incident and
control it with minimum damage.
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5. To mobilize the internal resources and utilize them in the most effective way.
6. To minimize the damage in other sections.
7. To keep the required emergency equipment in stock at right places and ensure that
they are in working condition.
8. To keep the concerned personnel fully trained in the use of emergency equipment.
9. To mobilize transport and medical treatment of the injured.
b) Basic Contents of Disaster management Plan (DMP)
Basically, the Disaster Management Plan (DMP) contains the following aspects:
• Location of the site
• Brief Description of unit
• Details of major potential hazards
• Identification of specific type of Disasters
• Action Plan – Specific responsibilities
• Declaration of Emergency/Emergency Action Plan
• Evacuation and Assembly points
• Evaluation of Implementation system
c) Purpose & Scope:-
The principal aim of DMP of integrated steel unit is prevention of identified major hazards.
These hazards occur only due to exposure of individuals employed in the raw material feed
areas of the unit.
It is totally committed to “TOTAL CONSISTENT QUALITY ASSURANCE” from conception
stage to enable its objective of prevention can nurse ample opportunities to nurture and
realize in practice.
Second control strategy adopted could be reducing potential by way of minimizing the
handling of such materials manually by individuals both in process and storage within the
purview of continuous operation.
Thirdly adopted control measure could be well structured and well rehearsed, resources. On
site plan which could intercept any such occurrence with speed and rectify by ensuring
Safety of worker, equipment, public and ultimately the environment as a matter of priority.
General details like location, project layout, neighboring entities and the assistance they can
render etc., are also provided.
The important elements considered in this plan are:-
• Statutory requirements
• Emergency organization
• Roles and Responsibilities
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• Communications during emergency
• Emergency shutdown & control of situation
• Rescue & Rehabilitation
• Emergency facilities
• Important Information
The primary purpose of the on-site emergency plan or DMP is to control and contain the
incident and so to prevent if from spreading. It is not possible to cover every eventuality in
the plan and the successful handling of the emergency will depend on appropriate action
and decisions being taken on the spot.
d) Preventive measures and Plans:-
In DMP it clearly specifies the actions to be taken in case of such incident, including its
prevention, corrective action so as to mitigate such occurrence by the proponent. Practice &
Procedures with respect to the operational hazards, equipment failure, Human safety,
Malfunctioning of Safety interlocks. Natural disasters relevant to unit and its different section
of operation will be formulated and a detailed elaborate disaster management action plan will
be prepared and made available to all concerned persons to take care of the following
aspects.
• Industry will install an emergency alarm for immediate information
• A suitable location inside the unit will be demarcated for Emergency Control Center &
Assembly Point.
• Intercom will be provided to all departments for easy and immediate means of
communication.
• At sensitive fire prone areas Fire alarm and Fire hydrant lines will be provided along with
specified categories of Fire Extinguishers.
• Workers will be trained regularly to use Personal Protective Equipment and proper tools
at work place.
• Mock drill will be conducted at regular interval to evaluate the effectiveness of the
emergency preparedness plan
• First Aid Centre and First Aid Boxes will be made available at various sensitive points to
meet the requirement.
• Personal will be appointed and responsibilities will be assigned.
• Color-coding will be followed as per the statutory requirements.
• All heavy moving machineries, Cranes and belt conveyors will be properly maintained
and protected and valid license will be obtained before their usage
• All applicable Indian Laws, Rules and regulations for which company subscribes shall be
strictly followed under a Senior qualified Environment & Safety personal.
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e) Structure of Emergency Management
1. Noticing the accidents
2. Informing declarer of emergency
3. Declaration of emergency
4. Functions of declarer
5. Interaction with outside agencies
The emergency control center will be sited in an area of minimum risk. Suitable location from
where clear view of the unit is possible.
f) Infrastructure at Emergency Control Centre
Emergency control centers will therefore contain the following:-
• An adequate number of external telephones; if possible, one will accept only outgoing
calls, in order to bypass jammed switchboards during an emergency.
• An adequate number of internal telephones
g) Emergency Action Plan for Fire
The UNIT shall be protected against fire hazard. A comprehensive fire detection and
protection system is envisaged for the complete unit. This system shall generally
conform to the recommendations of TAC (INDIA)/ IS: 3034 and NFPA- 850.
1. Disconnect the affected areas electric supply.
2. Fire detection systems will be installed to detect any possibilities of fire. Detection and
communication process will be implemented which will inform the occurrence of fire
outbreak and triggers counteraction towards extinguishing the fire. Adequate
inspection, testing, and maintenance of fire suppression systems and containment
structures will be done regularly.
3. Water can’t be used as a fire extinguisher for fire and any kind of hazard in electrical
panel and equipments. Therefore, dry chemical extinguishers and CO2 will be used.
Beside of it following measures will also be applied :-
a. A thick coating of an insulating material (rubber) will be done on the surrounding of
the transformer.
b. For better electrical safety, transformer will be placed in separate switchgear rooms
for better electrical safety.
c. Fire protection barriers (walls) will be there to separate these areas to prevent
adjacent equipment from becoming involved in a fire or damaged by debris thrown
from any explosion.
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d. Machines will not be placed in nearby zone of these areas.
4. Periodic condition assessments in addition to routine inspection, testing, and
maintenance will be done.
5. Access to these areas will be limited only to those having official business in the area.
Proximity of the public to transformers will be restricted
6. Training will be provided to the workers and only trained employees will be allowed to
work at risky areas under strict supervision.
7. Knowledge of alarm system will be given to every worker.
8. All employees will be made aware of the safety and health hazards, which can occur
in the industry.
9. All precautionary measures will be adopted and use of protective footwear and helmet
will be mandatory.
10. Provision of protective gear, masks, hand gloves etc. will be provided to all
employees.
h) Emergency Action Plan for Electric Shock Casualties:
Rescue and First Aid
• Do first aid quickly and without fuss and panic
• Switch off the supply if this can be done at once.
• If not possible use a dry stick, dry cloth or other non-conductor to separate the
victim from electrical contact.
• The rescuer must avoid receiving shock himself by wearing gloves or using a
jacket to pull the victim.
• Always keep in mind that delays in rescue and resuscitation may be fatal. Every
sound counts.
First Information
The first person who observes/identifies the emergencies shall inform by shouting
and by telephone to the Shift In-Charge and fire station about the hazard. The Shift
In-Charge will inform to Works Incident Controller, Chief Incident Controller and also
concerned HODs who shall communicate it to all key officers about the emergency.
Declaration of Emergency
The first person who detects the emergency shall inform by shouting or by telephone
to the Shift In-Charge /Unit Controller. Shift In-Charge i.e. Incident Controller will
inform to Works Incident Controller i.e. Head of O&M and Fire Station, Security
Control Room and concerned HODs. Works Incident Controller shall communicate
Chief Incident Controller and to all concerned about the emergencies. The Chief
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Incident Controller taking into account of the severity of the situation shall declare
Emergency.
Emergency Alarm
Emergency shall be declared by Emergency alarm, which shall be sounded by Fire
Station on receipt of orders from Shift In-Charge /Works Incident Controller.
Evacuation
In an emergency it almost certainly is necessary to evacuate personnel from affected
areas and as precautionary measure to evacuate non-essential workers. In the first
instance from areas likely to be affected will be evacuated immediately. The
evacuation will be effected on getting necessary message from WIC. On evacuation
employees shall assemble at Assembly Points.
Mock Drills
It is imperative that the procedures laid in this plan are put to the test by conducting
Mock Drills. The mock drills will be carried out by the step as stated below.
First Step Test the effectiveness of communication system
Second Step Test the speed of mobilization of the unit emergency teams.
Third Step Test the effectiveness of search, rescue and treatment of casualties.
Fourth Step Test Emergency isolation and shut down and remedial measures taken
on the system.
Fifth Step Conduct a full rehearsal of all the actions to be taken during an
emergency.
The Disaster Management Plan will be periodically revised based on experience
gained from the mock drills.
There are two types of mock drills recommended in Disaster Management Plan – Full
Mock Drill (to be conducted at least once in 6 months) and Disaster Management
Efficacy Drill (to be conducted at least once in 3 months).
Full Mock Drill
This shall be conducted with Unit Head as Vice President (Operation); Head of O&M
as General Manager; Heads of Operation, Maintenance, Medical, Personnel,
Security, Auto Base and Materials as Members and Head of Safety as Convener and
it shall test the following:
• Functioning of Emergency Control Center, very specifically availability of all
facilities etc as mentioned in the Plan and its functional healthiness.
• To evaluate communication of the Disaster Plan to all segments of employees, to
familiarize them about their responsibilities in case of any disaster including
evaluation of behavior of employees and others.
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• To ensure that all facilities as required under the plan from within or from nearby
industries / aid center under mutual assistance scheme or otherwise are
available.
• To ensure that the necessities under material assistance scheme is properly
documented and the concerned employees are fully aware in this regard.
• To ensure that employees are fully aware to fight any emergency like any
leakages, fire fighting other such cause.
6.9 OCCUPATIONAL HEALTH AND SAFETY
All precautionary methods are adopted by the company to reduce the risk of exposure of
employees to occupational safety and health hazards. Pre & postmedical check-up are
carried out regularly and will be done regularly after the said expansion. All the employees
are regularly examined and the medical records are maintained for each employee.
Pulmonary function test and periodical medical checkup are done once in every year.
The raw material asbestos used in the plant is hazardous in nature, thus all the workers in
the industry are well informed on the hazard associated with the asbestos. Moreover, copies
of material safety data sheets for asbestos are kept with the unit and are available for the
employee review. For the safety of the workers, personnel protective appliances like hand
gloves, goggles, aprons etc are provided. Nose masks are provided at places, where there is
possibility of dust generation and asbestos fibre processing area. Ear muffs are provided to
the workers exposed to the noisy sources. Adequate facilities for drinking water and toilets
are provided to the employees. Proper ventilation system is provided in the process area.
Table 6.2
Action plan for health and safety of workers
S.No. Health and Safety Issues
Health and Safety plan Remarks
1. Handling Asbestos
containing bags
The fiber bags will be slit open in
closed automatic bag opening
device. The empty bags will be
lifted by a hooking device
attached within the bag opening
device and carried to the
attached bag shredder unit and
the fiber after passing through
the lump breaker will be collected
in the attached blender where
some water will be added to
The proposed project
will not generate
emissions and maintain
the ambient air quality.
Adequate air quality
equipments will be
installed.
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maintain the process in wet
condition.
Helmets, Face masks (P1 or P2
respirator/ ventilator), Heavy duty
gloves, Disposable ear muffs and
goggles will be provided to the
workers. Most importantly
disposable coveralls will be
provided to avoid any particles of
asbestos on clothing or skin. etc.
2. Avoiding the
prolonged exposure
and chances of
carrying the
asbestos particles
on the workers
clothing or skin.
Adequate shower rooms will be
constructed. Workers will have to;
take a shower anytime during the
day and before leaving for home.
The proposed project aims to put
81 workers. (There shall be
provided, a minimum of 5 toilets
for every 100 workers.)
To avoid any particles of asbestos
left on the workers clothing or skin,
as it could be easily inhaled while
breathing in, when the job is
complete and the measure is to
prevent any traces of lung cancer.
Washing face and hands
in every 1-2 hours will be
taught as a good habit.
3. Risk hazards To prevent any risk all protective
and safety gears will be provided
and regular training will be given
on the importance and use of the
safeguards. Helmets, Face masks
(P1 or P2 respirator/ ventilator),
Heavy duty gloves, Disposable ear
muffs and goggles will be provided
to the workers. Most importantly
disposable coveralls will be
provided to avoid any particles of
asbestos on clothing or skin.
Training on laying out
the disposable coveralls,
(the polythene drop
cloths) on the ground,
covering everything on
the surface. Asbestos
will stick to anything and
bury itself in material
fibers.
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4. Regular Diagnosis
and health checkup
Diagnosis by a qualified
Oncologist and /or Pathologist will
be done in every quarter (3
months), for every batch of 20
workers.
Adequate monitoring of Asbestos
Fibre in air will be done at regular
intervals to check the
effectiveness of the automated
plant & machinery.
A regular urinalysis, x-
rays, or a bronchoscopy
(a test that detects
asbestos fibers within
lungs), and determines
the extent of the damage
done by asbestos
exposure, will be done in
every 3 months.
6. Observation by
supervisor of any
symptoms, will be
reported.
Development of any symptoms
amongst the employees will be
monitored, such as :
• Shortness of breath
• Coughing
• Painful breathing
• Chest pain
• Difficulty to perform
physical tasks
• Loss of weight
• Headache
• Pain in the bones or
Any movement requiring medical
attention. Qualified Oncologist
and /or Pathologist /Physician will
conduct exams to determine the
cause of the symptoms.
Any indication of
Asbestosis/ lung Cancer
will be kept under
surveillance immediate
action will be taken.
7. Physical Exertion of
musculoskeletal
movement.
The physical exertion such as
excessive lifting, climbing or
digging with heavy objects will be
not be done in the proposed
project as it is a completely
automated wet asbestos process.
Also work motion study will be
done and the following ways
methods will be adopted :
The associated risks of
manual handling will not
be applicable
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a.) Use of relief workers
b.) Assign extra workers
c.) minimize overexertion
d.) Scheduling of jobs
8. Medical Appliances
& Arrangements
Equipped First aid Boxes or
cupboards will be at the disposal
and accessibility of the workers.
Conveyance
arrangements to
hospitals or
dispensaries from the
proposed project site,
will be readily made in
unfortunate
circumstances if any
worker, suffer bodily
injury or becomes ill
during the working
hours.
9. Insurance (medical
+ hospitalization +
liability)
A provision liability and
hospitalization insurance will be
made for each worker.
Medical Insurance and
Life Insurance shall be
provided to the plant
workers.
6.9.1 Measures for the abatement of occupational hazards (exposure to dust)
Occupational hazards due to Asbestos Cement Corrugated Sheet & Accessories - Plant
does not pose a major danger to the surrounding environment in general, but it has impact
on the health of the workers who are in the exposure of asbestos fibre dust generated during
fibre handling or related process operations for a long term. The following precautionary
measures have been adopted for the safety at work place keeping in view day-to-day
occupational hazards encountered.
I. Occupational Safety
• All working places will have safe means of access, safe working platform and
exit. Persons working in hazardous dust prone area will be provided with dust
mask.
• All personnel safety equipment, like, respirator, gloves, helmet, goggles &
earmuffs will be stored in assigned places & will be easily accessible.
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II. Occupational Health Hazard
• The fully automatic bag opening device with bag shredder completely avoids manual
handling of either loose fibre or fibre bag. The shredded particles of the woven sack will
be utilized in the process. The whole bag opening and shredding operations are
enclosed and are maintained under negative pressure with the help of bag filters and a
centrifugal fan. The bag filter collections are conveyed back into the storage chest with
the help of Air Lock rotary valves and screw conveyor.
• All the leaking points will be closed properly and periodically the chest will be carried to
avoid any spillage of fibre. The surface of screw conveyor and bucket elevators will
also be connected to dust collector.
• Regular vacuum cleaning will be carried out at all the fibre handling section.
6.9.2 Preventive methods adopted to minimize occupational health disorder
a) Use of personal protective equipment
SAFETY MEASURES PERSONAL PROTECTIVE EQUIPMENTS
Regular Process Area
Fibre bag feeding to BOD & BOD V – 20 – W Masks
Name – Nose mask, cup design with
exhalation valve as per IS : 9473 – ‘02
Inhalable dust - <100 µm
Thoracic dust – 2.5 to 30 µm
Respirable dust – 0.3 to 2.5 µm
Sheet cutting operation
Moulded goods finishing area
Wet Ball Mill (Waste recycling)
Maintenance Activity
Bag filter cleaning 3M – 9004 IN
Up to 0.1 µm BOD Cleaning
General (shop floor)
For nuisance/inert dust Cloth nose mask without filter
b) Work Zone Air Monitoring – All the potentially fibre dust exposure zone are connected
to Bag Filter type dust collectors & air wet washer. Besides these pollution control
measures, every month we are carrying out work zone air monitoring by carrying out
personal & static air sampling at different locations within the plant premises & finding
out the fibre concentration level in the air by Membrane Filter method using phase
contrast microscopy which is specified in the Indian Standards also. It is periodically
being verified by an external agency, M/S JR Labs, Hyderabad who are rated by IOM,
WHO
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6.9.3 Employer commitment to an asbestos prevention programme
The following needs to be in place for an effective programme:-
� An executive designated with programme oversight
� Designated person(s) to co-ordinate programme implementation
� A silicosis prevention task team/committee (depending on size of the company and existing
structures)
� Appropriate resources made available to facilitate the implementation of company strategy
to deal with silicosis
� A reporting mechanism to indicate progress on silicosis prevention. To include key indicators
from occupational hygiene and occupational medicine
� Management performance assessment to include a health and safety component which
includes silicosis prevention
� Key employer/company documents, e.g. annual reports to safety bulletins to include
information on silicosis prevention
� An employer programme to include progress monitoring of the Silicosis Prevention
Programme. Any dust control initiatives identified by this project to be evaluated for
relevance and implemented if appropriate.
6.9.4 Administrative controls and work practices including the correct use of appropriate
respiratory protection to minimise dust exposures
Work practices are procedures prepared by employers and must be followed by employers
and employees to control hazards in the workplace.
1. Written procedures for dust control These need to be sufficiently detailed to provide the information required by those
people and their supervisors who install, operate, monitor and maintain the dust control measures including suppliers. They need to allow the design intention, as identified in the risk assessment, to be applied in a practical way. The written procedures for dust control must specify the control measures. They will need to include the following:- � An outline description of the plant or processes identified in the risk assessment
as sources of airborne dust � Details of the equipment provided in connection with each of these sources to
prevent or minimise dust being produced or becoming airborne � Details of any equipment provided to remove dust from the air before it reaches a
workplace the design and minimum operating criteria for such equipment, including as appropriate, quality of water, water flow rates and pressures, pick sharpness, etc.
� The design and minimum required ventilation flow rates � The systems of work to be adopted to eliminate or reduce the need for workers to
go into hazardous areas close to downstream of dust sources � Arrangements for supervision and maintenance of control measures � The respiratory protective equipment (RPE) to be provided (such as disposable
dust masks) and rules about when it needs to be used to best effect, while taking account of risks to health and safety from other hazards which may be made
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worse by the use of RPE arrangements for ensuring the correct use/wearing of RPE
2. Respiratory protection
The protection of individual workers by respiratory protection should be the last resort, but such measures may be implemented as a temporary measure. It is important that employees are involved in the selection of the type of respirator to be utilized. It is no good having state-of-the-art respirators available if employees do not utilize them correctly. Where RPE is utilized as a means of exposure control, cognizance must be taken of the following (as a minimum):- � RPE must comply with national standards. � RPE must be appropriate for the task being performed and the environment
where the task will be performed. � RPE must be comfortable to wear and accepted by the employees required to
utilize it. � Appropriate training, awareness, maintenance and issuing facilities and
procedures must be implemented. � Special preventive measures such as the provision of airline supplied respirators
may be required for high-risk areas, e.g. abrasive blasting. 3. Hygiene facilities
To ensure that the duration of dust exposure does not extend beyond the work shift and to provide added protection to employees and their families, special attention should be given to workers personal hygiene. An employer must provide and ensure that workers use the washing facilities. Work clothes should not be cleaned by blowing with compressed air or shaking as this creates additional dust exposure. An employer should ensure that there are:- � Adequate hand washing facilities � Showers for each sex supplied with hot and cold water. Clean individual towels, body
soap, and other appropriate cleaning agents � Clean change areas with separate storage facilities for protective work clothing and
equipment and for street/personal clothes that prevent cross-contamination � Procedures for handling dusty work clothes.
6.9.5 Periodic medical surveillance of employees exposed to airborne crystalline silica
dust
A medical surveillance programme includes medical and work history tracking,
regular physical examinations, chest x-rays and lung function tests. Participating
in a medical surveillance programme can help in the early detection of silicosis
and associated diseases.
� The medical surveillance required is stipulated in the regulations for silica dust
exposure and for coal dust exposure under the Mines Act.
� An employer must establish and maintain a system of medical surveillance for all
employees in any working environment where exposure to crystalline silica occurs in
excess of 10% of the OEL for crystalline silica.
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6.10 CORPORATE SOCIAL RESPONSIBILITY
The proposed project social responsibility will aim to strengthen social inclusion by ensuring
that both the excluded groups and intended beneficiaries are included in the benefit stream
and in access to opportunities created by the project.
S. No.
Activities Capital Cost % Average (3 years) annual
N.P.
1st Year
2nd Year
3rd Year
1. Installation of Rainwater Harvesting Structures in
government institutions: Upswastha Kendra
Lalwari 3.2 km ESE; Rajkiya Adarsh Uchh
Prathmik Vidhyalya, Lalwari 3.5 km ESE & Facility
development of sanitation fittings connecting the
proposed rain water storage tank with the
bathrooms washing & flushing.
45.0
16.0 5.1 --
2. In consultation with local authorities and Gram
Panchayat, Shedriya, for the development of the
primary health centre, Shedriya by Contributing for
a Multi-specialty hospital for critical illness and
emergency along-with a Medical Ambulance for
the study area.
75.0 22.0 8.0 0.5%
3. Health Camps proposed in the study area:
1. Yearly Camp for Mother and Child in the study
area for awareness on malnutrition including
drops / supplements.
2. Awareness on indicators of esotheolima shall
be given to the public at large in the study area
mainly Agarpura (4.5 km SE), Lalwari (3.0 km
ESE), Sangrampura (4.0 km SSE). Camps shall
provide demonstration and action plan on
prevention, symptoms & cure.
8.0 7.0 7.0 0.3%
4. Skill development and earning sources for youth
both On-the-Job training of local skilled workers &
Off-the-Job training of the unskilled local non
workers for income generating activity.
5.0 5.0 5.0 0.2%
5. Regular Health Check up camps shall be
organized mainly in three villages in the wind
35.0 20.0 20.0 1%
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direction viz. Agarpura(4.5 km SE), Lalwari (3.0 km
ESE), Sangrampura (4.0 km SSE) and in the study
area for :To trace any indication of Asbestosis/
lung Cancer and will be kept under surveillance
and immediate action will be taken.Regular
urinalysis, x-rays, and a bronchoscopy (a test that
detects asbestos fibers within lungs, and also
determines the extent of the damage done by
asbestos exposure), will be done in every 6
months.
Total 168.0 70.0 45.1 2%
Capital Cost: Rupees 2, 83, 10,000/- as capital cost
Recurring Cost: As per the Companies Act 2013 (2% of Average Annual Net profits of the
first three years of operation).
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SECTION-VII
PROJECT BENEFITS
INDEX
PROJECT BENEFITS ........................................................................................................... 176
7.1 INTRODUCTION ........................................................................................................ 176
7.2 IMPROVEMENTS IN THE PHYSICAL INFRASTRUCTURE .................................... 176
7.3 IMPROVEMENTS IN THE SOCIAL INFRASTRUCTURE ........................................ 176
7.4 EMPLOYMENT POTENTIAL ..................................................................................... 176
7.5 OTHER TANGIBLE BENEFITS ................................................................................. 176
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PROJECT BENEFITS
7.1 INTRODUCTION
Asbestos Cement Fiber Sheet (CFS) is an oligopoly market.CFS being predominantly a rural
product has its fortunes closely linked with the rural economy. CFS industry is cyclical in
nature with March and June quarters are the best quarters for the industry historically.
Cement is the major input for asbestos Cement Fiber Sheet manufacturers. India and China,
are expected to record the fastest growth in demand for roofing and facades due growth in
population and urbanization on one hand and improved standard of living on the other is
already generating demand for housing, including affordable housing. Additionally, in India,
demand for roofing and facades is also felt in the industrial building segment including
factory buildings, airport terminals, hangars, inland container depots, logistics parks, special
economic zones and export processing zones, warehousing and food processing. Asbestos
mining is totally banned in India and many other countries leading to very few supplier of the
raw material Chrysotile and is 100% imported.
7.2 IMPROVEMENTS IN THE PHYSICAL INFRASTRUCTURE
The proposed Visaka Industries Ltd., an Asbestos Cement Fiber Sheet manufacturing unit
will have numerous induced impacts such as rainwater harvesting, sewage treatment plant,
various environment control equipments.
7.3 IMPROVEMENTS IN THE SOCIAL INFRASTRUCTURE
The social infrastructure will develop with the positive externalities like permanent structures
and facilities for government schools, promotion of education, facilities for drinking water,
adoption of health facilities for critical illness and emergency; Skill development and earning
sources for youth will be improved with the induced enterprises social commitment.
7.4 EMPLOYMENT POTENTIAL SKILLED, SEMI-SKILLED AND UNSKILLED
The proposed project will provide direct employment to skilled workforce and indirect
employment (transport, services deliveries etc.) to semi-skilled and unskilled workers. The
employment will be for long term, large scale and stable opportunities will be created by the
proposed unit in Tonk.
7.5 OTHER TANGIBLE BENEFITS
The other tangible benefits includes demonstrating process and system cost savings,
compliant inspections and customer audits, faster product approvals and manufacturing
throughput, less rejected material, reduced nonconformance issues, and more efficient
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continuous improvement and project implementation. Intangible benefits include improved
staff morale, faster, more accurate transparent decision making, less employee turnover,
increased staff accountability, and an enhanced culture of quality throughout the
organization.
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SECTION-VIII
ENVIRONMENTAL MANAGEMENT PLAN
INDEX
ENVIRONMENTAL MANAGEMENT PLAN ........................................................................... 178
8.1 INTRODUCTION ............................................................................................................ 179
8.2 ENVIRONMENT MANAGEMENT DEPARTMENT ......................................................... 179
8.3 ENVIRONMENTAL ACTION PROGRAMME .................................................................. 182
8.4 ACTION PLAN FOR COMPLIANCE OF THE DIRECTIONS OF THE HON’BLE
SUPREME COURT OF INDIA ........................................................................................ 188
8.5 GREEN BELT DEVELOPMENT .................................................................................... 189
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ENVIRONMENTAL MANAGEMENT PLAN
8.1 INTRODUCTION
The Environmental Management Plan (EMP) is a site specific plan developed to ensure that the
project is implemented in an environmental sustainable manner where all contractors and
subcontractors, including consultants, understand the potential environmental risks arising from
the proposed project and take appropriate actions to properly manage that risk. EMP also
ensures that the project implementation is carried out in accordance with the design by taking
appropriate mitigative actions to reduce adverse environmental impacts during its life cycle. The
plan outlines existing and potential problems that may adversely impact the environment and
recommends corrective measures where required. Also, the plan outlines roles and
responsibility of the key personnel and contractors who are charged with the responsibility to
manage the proposed plant.
The EMP is:
• Prepared in accordance with rules and requirements of the MoE&F and the State Pollution
Control Board;
• To ensure that the component of facility are operated in accordance with the design;
• A process that confirms proper operation through supervision and monitoring;
• A system that addresses public complaints during construction and operation of the facility;
and
• A plan that ensures remedial measures is implemented immediately.
8.2 ENVIRONMENT MANAGEMENT DEPARTMENT
8.2.1 Environmental department policies
The unit will ensure the following activity
a. Commitment & Policy
The proposed project management will strive to provide and implement the Environmental
Management Plan that incorporates all issues related to air, land and water.
b. Planning
This includes identification of environmental impacts, legal requirements and setting
environmental objectives. The various potential impacts are discussed under Section IV of the
EIA Report.
c. Implementation: This comprises of resources available to the proponents, accountability of
contractors, training of operational staff associated with environmental control facilities and
documentation of measures to be taken.
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d. Measurement & Evaluation: This includes monitoring, corrective actions, and record
keeping.
8.2.2 Environmental department structure
i. Environment management cell
• Organizational set-up
• linkage with other associated departments,
• reporting schedule to the regulating authorities
ii. Laboratory facility (in house / certified lab)
• Sampling,
• technique,
• analysis/monitoring practice followed,
• monitoring equipment/instrument available and
• schedule of monitoring.
iii. Library
• Books on environment & monitoring
• Records/drawing
• Collection of standards/norms/guidelines/notification etc.
iv. Safety, health, fire services and security
• For the supervisors and workers
v. Training facility
• For the supervisors and workers
vi. Maintenance
Response time for emergency maintenance, spare availability and routine programme of
maintenance
• Disaster Management Plan (DMP)
• On-site Emergency Management Plan
• Risk Assessment (RA)
• Environmental Audit (EA)
vii. Monitoring data
• Ambient air quality with meteorological data/information
• Ambient noise level
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• Receiving water quality up-stream and down-stream of treated wastewater disposal point
(if any / applicable)
• Ground water quality in and around factory
• Storm water disposal facility inside & outside the factory
viii. Greenbelt development
• Plants selection
• Green belt covered area
• Future plan, if any
ix. Waste Management
• recovery,
• recycle and
• reuse
x. Performance study of waste management
• Identification of shortcomings
• Finding out proper remedial measures
• Implementation time frame
xi. Material balance
• Sulphur present in feedstock - distribution & recovery of sulphur
• Catalyst disposal
• Fluoride present in rock phosphate - its distribution and recovery/disposal
• Specific consumption of raw material per MT of product
• Design
• Actual
• Reason for difference
xii. Identification of hazardous installations
• list with details of hazardous installations
• measures, in case of unforeseen release of pollutants
• Was there any episode discharge of pollutants in past?
• experience
• remedial measures
• strategy to be adopted based on experience
xiii. Prepare an environment check list to review environmental safeguard
• House keeping
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• Complaints
� Complaints received, if any
� Accident occurred in last two years
• Compliance of standards
� Copy of water consent
� Copy of air consent
� Copy of authorization of hazardous wastes
• Comply with the standards, stipulations, guidelines etc.
• If not, indicate deviations with reasons for the same
• Find difficulty in complying with the conditions of consent letters.
8.3 ENVIRONMENTAL ACTION PROGRAMME
“Visaka Industries Ltd.” management is quite conscious of its responsibility for maintaining
clean and a healthy environment. The management is also keen to modify and make more
efficient measures towards suppression of pollution sources. Lot of adequate funds for pollution
control measures are provided as a part of overall project financing to ensure the availability of
proper treatment facilities before the commissioning of the unit. The overall investment in the
project will be Rs. 56.62 Crores and about Rs. 50 lakh for the environment protection program
as capital investment and Rs. 10 lakh as recurring cost.
Table 8.1
Environmental Pollution control cost
The Environment Management Plan (EMP) includes all the mitigatory measures proposed under
each significant environmental attribute. For each potential negative impact identified,
S.No. Particulars Capital cost
In Lakhs
Recurring cost
in Rs.
1. Air Pollution Control 25 5
2. Water Pollution Control 5 1.50
3. Noise Pollution Control 5 0.50
4. Environment Monitoring and Management 8 1.0
5. Occupational Health 4.5 1.50
6. Green Belt 2.5 0.50
Total 50 10
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recommendations will be presented for avoidance, minimization or mitigation of impacts along
with costs associated with potential mitigation. Further, a suitable green belt development plan for
the project site will be included in the EMP report.
The EMP will address the following:
• Identify and summarize all anticipated significant adverse environmental impacts:
• Identify and summarize all mitigation measures, including the type of impact to which it relates
and the conditions under which it is required;
• Define a set of policies and objectives for environmental performance and continual
enhancement of performance;
• Wastewater and produced water handling, treatment and disposal;
• Solid and hazardous waste handling and disposal;
• Green belt development plan;
• Recommend monitoring and reporting procedures including the parameters to monitored,
methods to be used, sampling locations, frequency of measurements, detection limits and
definition of thresholds that will signal the need for corrective actions;
• Recommend capacity development and training requirements for implementation of EMP; and
• Recommend an organizational structure for effective implementation of the EMP;
An environmental monitoring and management plan has been developed for the sensitive
elements of the environment that may require monitoring during construction and production
phase of the proposed project. Recommendations have been made on the institutional
arrangements that will be necessary to ensure effective monitoring and management.
A detailed management and monitoring program has been developed to reduce the effects of
potential negative environmental impacts.
The EMP also reflects statutory requirements, M/s.VISAKA INDUSTRIES LIMITED own corporate
operational guidelines. Cognizance will also be taken of all the applicable standards and
guidelines (amongst others) in the preparation of the EMP.
The proposed Environment Management plan for the unit is summarized in the below table:
Table 8.2
Environment Management plan
Particulars Mitigation Measures
Air Environment
During construction
• Dust pollution can be minimized at the source by water
spraying and maintenance of road.
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phase • Construction material will be stored in temporary storage
yard.
• The excavated materials will be place only on the
designated disposal areas.
• The construction area will be shielded with the help of
tarpaulin from all the four sides to contain the air
emissions within the premises.
• Dust or dusty material will not be swept without effectively
treating it with water or other substances in order to
minimize its dust emission.
• Suitable covered skips and enclosed chats or other
suitable measures will be provided in order to minimize
dust emission to the atmosphere when materials & waste
will be removed from the premises.
• Parking lot and paved road will be constructed first.
• Upwind portion of the project will be constructed first.
• During high wind condition, construction activities will be
restricted, so that minimum flow of dust particle takes
place.
• The first and most important step towards emission
control for the large in-use fleet of vehicles is the
formulation of an inspection and maintenance system. It
is possible to reduce 30-40% pollution loads generated by
vehicles through proper periodical inspections and
maintenance of vehicles.
• All transportation vehicles will be suitably covered with
tarpaulin & overloading of the vehicles will be avoided.
• PUC certified vehicles will be used to avoid the exhaust
emission.
During operation phase • Automatic bag open device followed by shredder is
proposed for fibre handling and pneumatic bulk handling
system for cement and fly ash.
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• High efficiency pulsejet type bag filters will be installed for
fibre circuit, cement and fly ash circuit and solid waste
management device-pulveriser, bin filter for cement silo
and fly ash silo to limit the particulate matter
concentrations below the standards;
• Provision of adequate height stack for wider dispersion of
emissions;
• In the event of failure of any pollution control system, the
unit will put off the operation immediately and will not be
restarted until the control system is rectified to achieve the
desired efficiency;
• Water spraying will be practiced frequently at all dust
generating areas;
• All the internal roads are connected to reduce the fugitive
dust due to vehicular movement; and
• Improving the Greenbelt around the plant to arrest the
fugitive emissions.
• Asbestos fiber (Chrysotile variety) will be imported from
Canada, Brazil, Zimbabwe, Russia and Greece. It is
received in shrink or stretch wrapped HDPE woven bags.
Fiber bags are received tightly packed in wooden pallets
and transported in closed containers. The bags wear
warning symbol “a”.
• The bags are handled at site by means of forklifts.
Spillages if any and container after unloading at site is
cleaned using portable vacuum cleaner. Where this is not
practicable, wet mopping, collection & recycling method is
adopted.
• The fibre bags will be stacked in godowns.
• Trucks after unloading will be subjected to thorough
cleaning by vacuum cleaner.
• Sheet cutting operation will be carried out with the cutters
operating under a steady stream of water jet which will be
recycled.
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• The washing waste water is collected and periodically
recycled to the process. This technique of dust
suppression has been proven to be very effective.
• Portable vacuum cleaner will be used for the cleaning of
godowns and raw material section.
• The filing and finishing operation of moulded asbestos
cement goods will be carried out in wet stage.
• Wet mopping /collection/Recycling method wherever
applicable is adopted for the spillage cleaning at raw
material section.
• To control the fugitive emission from Cement Feeding
section and fly ash feeding section the unit proposes to
provided with identical Bag filter (with auto cleaning
system) type provided with stacks of adequate height.
• Compliance with the total dust emission limit of 50
mg/Nm3 for Fly ash & Cement feeding section.
• All the internal roads are already made pucca to reduce
the fugitive dust emission due to the vehicular movement.
Water Environment
• The process waste water will be collected periodically
and recycled to process after sedimentation process,
along with mud.
• No process water will be discharged and zero discharge
will be adopted and entire process effluent will be reused
/ recycled in the manufacturing process.
• The domestic wastewater will be treated in Sewage
treatment plant
• No waste is disposed either in liquid or solid form and
there is no possibility of leaching. The small amount of
waste water generated is recycled back into the process
itself.
• There is no possibility of oil and grease getting mixed
with water in the process. There is no effluent discharged
in to the soil. Therefore there is no possibility of pollution
and contamination into the ground and ground water.
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Solid Waste
• Entire solid waste generated including process, sheet
cuttings, rejects, dust from bag filters will be recycled and
reused in the manufacturing process.
• The cut and damaged fibre bags will be immediately
repaired with adhesive tape to ensure no spillages.
Noise Pollution
• All possible measures will be taken to minimize the noise.
• Foundations and structures will be designed to minimize
vibrations and noise.
• Regular equipment maintenance and better work habits
will be adopted.
• Necessary safety and personal protective equipment such
as ear plugs, ear muffs, helmet etc will be provided to the
workers.
• Noise levels generated will be maintained to comply with
the Factories Act & Rules and will not exceed 75 dB (A) at
1 m distance.
• Implementation of green belt within the premises of plant
will absorb the noise. Thus will help to control the noise
pollution.
• Proper lubrication and housekeeping will be usually done
to avoid excessive noise generation.
• Supervisor will be responsible to control the noise by
maintaining conditions of machineries and silencers.
• 33% of the total plot area will be under greenbelt.
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8.4 ACTION PLAN FOR COMPLIANCE OF THE DIRECTIONS OF THE HON’BLE SUPREME
COURT OF INDIA
S.No. Supreme Court Directions Compliance Status
1 To maintain and keep maintaining the health
record of every worker up to a minimum period
of 40 years from the beginning of the
employment or 15 years after retirement or
cessation of the employment whichever is later.
The unit will maintain the health
records of the workers from the
beginning of the employment.
Development of any symptoms
amongst the employees will be
monitored, such as :
• Shortness of breath
• Coughing
• Painful breathing
• Chest pain
• Difficulty to perform physical
tasks
• Loss of weight
• Headache
• Pain in the bones or
Any movement requiring medical
attention. Qualified Oncologist and
/or Pathologist /Physician will conduct
exams to determine the cause of the
symptoms.
2 The Membrane Filter Test to detect asbestos
fibre should be adopted by all the factories or
establishments at par with the Metalliferrous
Mines Regulations, 1961 and Vienna
Convention and Rules issued thereunder.
It is already proposed in environment
monitoring program and will be
complied as per regulatory
requirement
3 All the factories whether covered by the
Employees State Insurance Act or Workmen's
Compensation Act or otherwise are directed to
compulsorily insure health coverage to every
worker.
All the workers will be covered with
health insurance.
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4 The Union and the State Governments are
directed to review the standards of permissible
exposure limit value of fibre/cc in tune with the
international standards reducing the
permissible content as prayed in the writ
petition referred to at the beginning. The review
shall be continued after every 10 years and
also as when the I.L.O. gives directions in this
behalf consistent with its recommendations or
any Conventions.
The air pollution measurement in
relation to fibre/cc will be monitored
regularly and the reports will be
submitted to the state pollution
control board.
8.5 GREEN BELT DEVELOPMENT
Plant species act as bio-monitoring agent to monitor the air environment as well as to keep and
maintain the project environ healthy. Trees have substantial inter-specific as well as intra-
specific variation in air pollution tolerance. Green Belt development / tree plantation in organized
manner is already done through development of 33% green belt in the existing project site.
Now it was suggested to plant more trees (approx 1200 nos. of Local trees species like: Butea
monosperma, Cassia fistula, Delbergia sissoo, Delonix regia, Polyalthia longifolia) in the project
site and nearby villages, to reduce the impact of expansion activities in the surroundings of the
existing project site. The above mentioned plants are suitable for green belt development have
characteristics like, fast growing, thick canopy cover, perennial and evergreen large leaf area,
naturally growing, efficient in absorbing pollutants without major effects on natural growth.
Species Suggested for Plantation
Species have been suggested by considering various biological and environmental role of the
various plant species like Dust Control, Noise Control, Absorptions of Gases, Drought
resistance, Fire Resistance etc. Some flowering herbs and subs have been suggested to
enhance aesthetic beauty of the project site area.
Table 8.3
Recommended Plant species for Plantation
Plant Spices Common Name Ecological and Environmental Performances of Plant Species
Trees
Annona squamosa Amrud DC, DR, SR, FR Azardirachta indica Neem DC, NC, AG, DR, FR.
Cassia fistula Amaltas DC, DR, FR. Delbergia sissoo Shesham DC, DR, FR.
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Polyalthia longifolia Ashoka DC, NC, AG.
Source: Anon 2007, Saxena 1991, Anon 2006, Hocking, 1993. DC- Dust Control, NC - Noise Control, AG – Absorptions of Gases, DR - Drought resistance, SR - Salinity resistance, FR - Fire Resistance
Shrubs
Croton oblongifolius Croton To enhance aesthetic beauty / DC* Tabernaemontana divaricata Chandni To enhance aesthetic beauty / DC*
Withania somnifera Ashwagandh To enhance aesthetic beauty / DC* Herbs
Tagetese minuta Genda To enhance aesthetic beauty/ DC* Chrysanthamum Crown Daisy To enhance aesthetic beauty/ DC*
Rosa indica Rose To enhance aesthetic beauty/ DC*
*Source: phytoremediation of particulate matter from ambient environment through dust capturing plant species, CPCB 2007.
Green belt development plan budget
A capital cost provision of Rs. 2, 25,000 has been kept for development of greenbelt as given in
Table below The budget includes cost of digging of pits, fertilizers, saplings and maintenance
for 3 years.
Activity Sub
Activity
Unit
Physical Target Total
2014-15 2015-16 2016-17
Green Belt
development plan
Selection
of Species
Year √ √ √
Plantation Number 400 400 400 1200
Financial Target
2014-15 2015-16 2016-17
Capital cost (In lacs.) 75,000 75,000 75,000 2,25000
Recurring 15,000
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SECTION – IX
SUMMARY AND CONCLUSION
INDEX
SUMMARY AND CONCLUSION .......................................................................................... 191
9.1 INTRODUCTION ......................................................................................................... 192
9.2 DESCRIPTION OF THE PROJECT ........................................................................... 194
9.3 ENVIRONMENTAL MONITORING ............................................................................ 196
9.4 ANTICIPATED ENVIRONMENTAL IMPACTS & MITIGATION MEASURES ........... 197
9.5 ENVIRONMENTAL MONITORING PROGRAMME ................................................... 200
9.6 PROJECT BENEFITS ................................................................................................. 202
9.7 ENVIRONMENT MANAGEMENT PLAN DURING OPERATION PHASE ................. 203
9.8 CONCLUSIONS .......................................................................................................... 207
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SUMMARY AND CONCLUSION
9.1 INTRODUCTION
Visaka Industries Limited is a proposed Asbestos cement sheets manufacturing project
coming at Rachakpura Village, Shedriya Grampanchayat, Niwai Tehsil, Tonk District,
Rajasthan. The proposed unit is categorized under 4 (c) 3 of Gazette Notification dated Sep
14th, 2006 and subsequent amendments on 01.12.09 and 04.04.2011 {Asbestos milling and
asbestos based products}. The same is categorized as “A” category.
The total land area acquired by unit is 28.0 Acres. M/S Visaka Industries Limited (VIL) has
proposed to set up the unit, manufacturing Asbestos Corrugated sheets with a capacity
216,000 MT Per Annum (TPA).The estimated cost of the proposed project is 56.62 crores
The details of environmental setting are given below. The map showing the project site and
10 km study area is shown in Figure-9.1.
Table – 9.1
Details of Environmental Setting
Sr. No.
Particulars Details
1 Location
A Village Rachakpura
B Tehsil Niwai
C District Tonk
D State Rajasthan
E Latitude 26o 26’ 04.82” N 26o 26’ 00.49” N 26o 25’ 51.55” N 26o 25’ 52.86” N
F Longitude 76o 01’ 03.17” E 76o 01’ 13.38” E 76o 01’ 11.68” E 76o 01’ 00.39” E
G Toposheet No. 45N/14, 45N/15, 54B/2 & 54B/3.
H Total Plant Area
28.0 Acres
2 Land use at the project area
S. No.
Particulars Area (sq. m)
(%)
1. Plant area, office area 36421.6 40 2. Road area 10015.94 11 3. Green belt 30047.82 33 4. Open area 14568.64 16
Total 91054 100
3 Nearest habitation
Saidaria Khurd at a distance of 1.0 km towards SW.
4 Nearest major town
Saidaria Khurd at a distance of 1.0 km towards SW.
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5 Nearest highway
NH 11A at a distance of 7.27 km N connecting Manoharpura to
Kothum.
6 Nearest Railway Station
Siras Railway Station
Distance: 19.36 km towards south.
7 Nearest airport
Jaipur Airport
Distance: 47.21 km towards NNW.
8 Nearest tourist places
Nil with in 10 km radius
9 Defence installations
Nil with in 10 km radius
10 Archaeological important
Nil with in 10 km radius
11 Ecological
sensitive
zones
None within study area
12 Reserved / Protected forest / National Parks / Wildlife Sanctuary (from Project Site)
• Baragaon Reserved Forest at a distance of 5.21 km towards NE.
13 Nearest streams / Rivers / water bodies (from Project Site)
• Dhil Nadi at a distance of 3.13 km towards SSW
14 Other Industries
None
15 Seismic zone The area is falling in Zone- II, Low Damage Risk Zone (MSK VI or
less).
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Figure 9.1 Map showing the project site and 10 km study area
9.2 DESCRIPTION OF THE PROJECT
The salient features of the proposed plant are given below:
Table no. 9.2 Salient Features of Proposed Plant
S.No. Particulars Details 1. Project Name Visaka Industries Limited
2. Location Rachakpura Village, Shedriya Grampanchayat,
Niwai Tehsil, Tonk District, Rajasthan.
3. Production & its Capacity Asbestos Cement Sheet to the tune of 2, 16,000
TPA.
4. Land requirement 28.0 Acres
5. Source of power JVVNL, Jaipur
6. Water Requirement 240 KLD (225 KLD industrial water demand &15
KLD Domestic water demand.
7. Source of Water Borewell
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8. Manpower 521 persons
9. Wastewater generation • Industry waste water - No waste water is
generated from the industrial process.
• Domestic waste water - About 10.5 KLD of
waste water will be generated from domestic
activities
10. Solid waste generation
S.No. Waste Source Quantity MT
Management
1. Empty Fibre Bags
(Category 15.1)
Auto Bag
Opening Device
(BOD)
0.080 Shredded in the Shredder unit
attached to the BOD in a
closed loop & collected thro
cyclone collector, thro screw
conveyor to the Edge Runner
Mill (ERM).
2. Fibre Dust
(Category 15.3
From Dust
Collector
attached to ER
Mill & BOD
0.012 Periodically recycled after the
container containing water &
placed beneath the rotary
valve of the dust collector gets
filled up.
3. Cement & Fly ash
Dust
From Dust
Collector
attached to
Cement feeding
& FA feeding
point.
0.100 Periodically recycled after the
container placed beneath the
rotary valve of the Dust
Collector gets filled up.
4. Process Sludge
(Category 15.1)
From Week-end
Tank
0.100 Continuously recycled through
Wet Ball Mill in slurry form.
5. Hard Broken
Pieces
(Category 15.1)
Sheet damages &
rejects
9.000 Continuously recycled through
Wet Ball Mill in slurry form.
11. Project Cost 56.62 Crores
12. EMP costs 50 Lacs (Capital cost)
10 Lacs (Recurring cost)
13. Cost towards CSR activities Capital cost-2, 83, 10,000/-
Recurring cost: As per the Companies Act 2013
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9.3 ENVIRONMENTAL MONITORING
For monitoring of the environmental parameters like meteorology, air, water, soil and noise
quality, the monitoring stations have been established at different locations in and around
the project area. The base line data has been collected in the pre monsoon season from
March, April & May’2013.
Meteorology
The recorded meteorological data for the study period at project site is presented below:
Table No. 9.3
Micro meteorological data for the study period at project site
Month Temperature (0C) Relative Humidity (%) Rainfall in mm Wind Speed mph
Max Min Max Min Max Total Max Min
March - 2013 37.0 12.5 86.9 9.5 0 0 9.0 < 1.0
April - 2013 41.1 17.5 77.8 9.5 0 0 11.0 < 1.0
May - 2013 45.4 20.9 83.5 9.5 0 0 14.0 < 1.0
Ambient Air Quality
Ambient air quality monitoring has been carried out with a frequency of two days per week at
eight locations. The summary of these results for all the locations is presented below. These
are compared with the standards prescribed by Central Pollution Control Board (CPCB) for
rural and residential zone.
Table 9.4
Summary of ambient air monitoring for March- May2013
Location
s
Code
Location
Name
PM10 µg/m3 PM2.5 µg/m3 SO2
µg/m3
NOx
µg/m3
CO
µg/
m3
(Max.)
Max Min Avg Max Min Avg. Max Mi
n
Avg Max Min Avg
A1 Project Site 39.3 30.6 34.9 20.3 14.2 17.2 5.1 4.1 4.5 12.6 11.2 11.8 123
A2 Sedria 52.8 43.2 48.5 27.9 19.3 24.2 6.7 4.4 5.4
15.6 12.5 14.3 248
A3 Dehold ki Dhani
42.5 34.3 38.2 21.6 17.3 19.4 5.3 4.4 4.8 13.2 12.3 12.8 215
A4 Kishore Pura ki Dhani
41.6 34.6 37.9 21 17.2 19.3 5.3 4.3 4.8 13.2 12.2 12.7 215
A5 Lalwari 52.9 43.2 48.2 26.3 20.4 23.7 6.8 4.6 5.7 15.3 13.5 14.4 291
A6 Shrisukhpur 41.2 33.6 37.0 21.6 15.6 18.3 5.2 4.2 4.7 13.2 12.2 12.7 182
A7 Thunj(Radhagovindpura)
41.5 34.5 38.2 21.6 17.3 19.3 5.1 4.3 4.7 13.6 12.4 12.8 182
A8 Bhagatpur Rampura
41.3 33.2 37.6 21.3 16.1 18.7 5.3 4.3 4.8 14.5 12.4 13.0 182
Note: All values are represented in µµµµg/m3
All values were found to be well within the latest national standards.
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Ground water quality
Eight groundwater and one surface water samples were collected as grab samples and were
analyzed for various parameters. The result indicates that the ground water quality values at
location G7 (Bhagatpur Rampura) is much higher (TDS, Total Hardness, Total Alkalinity, Total
Calcium, Total Magnesium and fluorides) with respect to other locations. The surface water
results are more or less within the permissible limit except for the BOD and COD parameter,
which are slightly higher than the permissible limit.
Noise Quality
The noise monitoring has been conducted for determination of noise levels at eight locations
covering 10 km study area. The noise levels at each location were recorded for 24-hrs. The
results obtained were compared with the national standards and were found to be within limits.
Ecology
The project site is not surrounded by the urban environment and does not hold any critical
habitat/ecosystem as well as any threatened floral or faunal species. So project site will not
have any adverse impact on the environment.
Socio-Economic Aspects
The study area comprises 56 villages human settlement, with a total population of 58341.
The total number of households is 10365 with an average household size of 5 people.
Hence, it is interpreted there are less of joint family systems in the study area. The gender
ratio in study area is 926 is lower against the district Jaipur ratio (949). The Average effective
literacy of 10 km of the study area is 51.60%.
The work participation rate is 47.22% of the study area. The non working population is
52.78%. Proposed areas of social commitments are in the following areas: Promotion of
education, Water & conservation, Health and medical.
9.4 ANTICIPATED ENVIRONMENTAL IMPACTS AND MITIGATION MEASURES
The summary of anticipated adverse environmental impacts due to the proposed project and
mitigation measures are given below.
9.4.1 Air Environment
The major sources of emission from the proposed activity are
1. Fibre Handling Area - Total dust with fibre content
2. Cement handling Area - Total dust or suspended particulate matter
3. Fly Ash handling Area - Total dust or suspended particulate matter.
4. Standby Power Supply System - DG sets - Suspended Particulate matter, SO2
and NOx.
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The impact on air quality is assessed based on emissions of the proposed activities in the
plant. Suspended Particulate Matter (SPM), PM2.5, PM10, Asbestos fibre, NOx and CO will be
the important pollutants emitting from the point sources.
Prediction of impacts on air environment has been carried out employing mathematical model
based on a steady state Gaussian plume dispersion model designed for multiple point sources
for short term. In the present case, AERMOD version 7.1 developed by United States
Environmental Protection Agency [USEPA] dispersion model based on steady state Gaussian
plume dispersion, designed for multiple point sources for short term has been used for
simulations from point and line sources.
Model Input Data
In the present case, model simulations have been carried out for the study period. The Ground
level concentrations are computed for 24-hr average. Maximum Ground level concentrations
of PM10, PM2.5, NOx, CO and Asbestos Fibre for study period were 5.2 µg/m3, 3.3 µg/m3,
7.6 µg/m3, 5 µg/m3 and 0.002 µg/m3 respectively for the given meteorological and
topographical conditions. The obtained GLC’s are well within the stipulated CPCB standards.
The incremental ground level concentrations for PM10, PM2.5, NOx, CO and Asbestos Fibre are
given in Table-9.4
Table No. 9.5
Predicted 24-Hourly Short Term Maximum Incremental Ground Level Concentrations
Pollutant Maximum Incremental
Concentration (µµµµg/m3) Distance coordinates (x , y) in m
Towards Direction
PM10 5.2 (500 , 1000) NE PM2.5 3.3 (500 , 1000) NE NOx 7.6 (0 , - 500) W CO 5 (0 , - 500) W Asbestos Fibre
0.002 (0.000032 fibre/cm3 < 0.1
fibre/cm3)
(500 , 1000) NE
9.4.2 Water Environment
• Waste water from industrial process
No process waste water will be discharged and zero discharge will be adopted and entire
process waste water will be reused / recycled in the manufacturing process.
• Domestic waste water from the different sections of building
About 10.5 KLD of waste water will be generated from domestic activities which will be
treated in Sewage treatment plant.
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9.4.3 Noise Environment
• D.G. set is proposed to be housed in an inbuilt acoustic enclosure. The acoustic enclosure
will be designed for minimum 25dB (A) insertion loss for meeting the ambient noise
standards, whichever is on the higher side.
• Necessary safety and personal protective equipment such as ear plugs, ear muffs, helmet
etc will be provided to the workers.
• Noise levels generated will be maintained to comply with the Factories Act & Rules and will
not exceed 75 dB (A) at 1 m distance.
9.4.4 Socio-Economic Environment
The requirement of unskilled manpower will be met from nearby villages during construction
and operational phase through training and development. The project will also help in
generation of the indirect employment apart from direct employment. This will be a positive
socio-economic development for the region. There will be a general upliftment of standard of
living in the region.
9.4.5 Solid Waste
The anticipated quantities of some major solid hazardous waste is given below in table
Table No. 9.6
The anticipated quantities of solid waste are as follows
Hazardous Waste Category
Empty Fibre Bags – From Bag
Opening Device (BOD)
15.1
Fibre Dust – From Dust
Collector at ER Mill & BOD
15.3
Process Sludge – From
Week-End Tank
15.1
Hard Broken Pieces – From
Damages/Rejects
15.1
S.No. Waste Source Quantity
MT Management
1. Empty Fibre Bags
(Category 15.1)
Auto Bag
Opening Device
(BOD)
0.080 Shredded in the Shredder unit
attached to the BOD in a
closed loop & collected thro
cyclone collector, thro screw
conveyor to the Edge Runner
Mill (ERM).
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2. Fibre Dust
(Category 15.3
From Dust
Collector
attached to ER
Mill & BOD
0.012 Periodically recycled after the
container containing water &
placed beneath the rotary
valve of the dust collector gets
filled up.
3. Cement & Fly ash
Dust
From Dust
Collector
attached to
Cement feeding
& FA feeding
point.
0.100 Periodically recycled after the
container placed beneath the
rotary valve of the Dust
Collector gets filled up.
4. Process Sludge
(Category 15.1)
From Week-end
Tank
0.100 Continuously recycled through
Wet Ball Mill in slurry form.
5. Hard Broken
Pieces
(Category 15.1)
Sheet damages &
rejects
9.000 Continuously recycled through
Wet Ball Mill in slurry form.
9.5 ENVIRONMENTAL MONITORING PROGRAMME
Environmental Monitoring Cell
A centralized environmental monitoring cell will be established for monitoring of important
and crucial environmental parameters which are of immense importance to assess the
status of environment during mine operation.
The following routine monitoring programme as detailed in as under shall be implemented at
site. Besides to this monitoring, the compliances to all environmental clearance conditions
and regular permits from RPCB/MoEF shall be monitored and reported periodically.
Table 9.7
Environmental Monitoring Programme S.
No. Potential Impact
Action to be Followed
Parameters for Monitoring
Frequency of Monitoring
Location
1 Air Emissions Ambient air quality within the premises of the proposed unit and nearby habitations to be monitored.
PM10, PM2.5, SO2, NOx and CO.
As per CPCB/ RPCB requirement or on weekly basis whichever is earlier
At least two locations inside premises; Three locations outside
Exhaust from vehicles to be minimized by use of fuel efficient
Vehicle logs to be maintained
-
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S. No.
Potential Impact
Action to be Followed
Parameters for Monitoring
Frequency of Monitoring
Location
vehicles and well maintained vehicles having PUC certificate.
Measuring onsite data of Meteorology
Wind speed, direction, temp., relative humidity and rainfall.
Continuous monitoring using on-line weather station during operation phase
Onsite at one location
Vehicle trips to be minimized to the extent possible
Vehicle logs Daily records Main gate
2 Noise Noise generated from various plant operations, vehicular to be optimized and monitored
Spot Noise Level recording; Leq(night), Leq(day), Leq(dn)
Periodic during operation phase
Noise measurements at five locations
Generation of vehicular noise
Maintain records of vehicles
Periodic during operation phase
-
3 Wastewater Discharge
No untreated discharge to be made to surface water, groundwater or soil.
No discharge hoses in vicinity of watercourses.
Periodic during operation phase
-
Take care in disposal of wastewater generated such that soil and groundwater resources are protected
Discharge norms for effluents shall be maintained
Periodic during operation phase
-
Compliance of treated wastewater usage/discharge to standards
pH, TSS, TDS, BOD, COD & Temperature
Periodic during operation phase
One location (Treated Wastewater)
Compliance of treated sewage to standards
Comprehensive as per GSR 422(E)
Once in a season
One location (Treated sewage)
4 Drainage and effluent Management
Ensure drainage system and specific design measures are working effectively. Design to incorporate existing drainage pattern and avoid disturbing the same.
Visual inspection of drainage and records thereof
Periodic during operation phase
-
5 Water Quality and Water Levels
Monitoring used water quality & groundwater quality and levels
Comprehensive monitoring as per IS 10500 Groundwater level bgl
Periodic during operation phase
Three locations
surrounding project site
6 Energy Usage Energy usage for air- Energy audit Annual audits -
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S. No.
Potential Impact
Action to be Followed
Parameters for Monitoring
Frequency of Monitoring
Location
conditioning and other activities to be minimized Conduct annual energy audit for the buildings
report and periodic checks during operational phase
8 Emergency preparedness, such as fire fighting
Fire protection and safety measures to take care of fire and explosion hazards, to be assessed and steps taken for their prevention.
Mock drill records, on site emergency plan, evacuation plan
Periodic during operation phase
9 Maintenance of flora and fauna
Vegetation, greenbelt / green cover development
No. of plants, species
Periodic during operation phase
-
10 Waste Management
Implement waste management plan that identifies and characterizes every waste arising associated with proposed activities and which identifies the procedures for collection, handling & disposal of each waste arising.
Records of solid waste generation, treatment and disposal
Periodic during operation phase
11 Soil quality Maintenance of good soil quality
Physico-chemical parameters and metals.
Periodical monitoring
Plantation areas
12 Health Employees and migrant labour health check ups
All relevant parameters including HIV
Regular check ups
-
9.6 PROJECT BENEFITS
The product has following advantages:
• It is used in variety of applications.
• It is light in weight, thus reducing the cost of trusses and woodwork and easy to
install.
• It does not deteriorate with weather and will last indefinitely. On the other hand,
strength of
• Fibre Cement materials increases due to ageing.
• It is comparatively cooler.
• It could be fixed easily and has an attractive appearance.
• It is comparatively maintenance free.
• It is much cheaper than similar roofing materials.
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• It does not pose health hazard.
9.7 ENVIRONMENT MANAGEMENT PLAN DURING OPERATION PHASE
Environmental Management Plan (EMP) aims at the preservation of ecological system by
considering in-built pollution abatement facilities at the proposed site. Some of the major
criteria governing the environmental measures will be adopted, and the same is described in
ensuring paragraphs.
9.7.1 Air Pollution Management
Fugitive and stack emissions from the proposed plant will contribute to increase in
concentrations of SO2 and NOx pollutants. The mitigative measures suggested to control the
impact on air environment are:
• The unit will take all possible measures to control the emissions from all sources.
• The list of pollution control equipment along with approximate financial requirements is
given below in table:-
• Adequate stack height as per CPCB emission regulations for proper dispersion of
pollutants into the atmosphere.
• Adequate stack height as per CPCB emission regulations for D.G Set
• Green belt development will be done to attenuate the pollution. Only local species will be
planted. It will cover 33.00% area of the proposed plant.
• Ambient air quality and stack emissions should be regularly monitored (as per
CPCB/SPCB) to ensure that ambient air quality standards and suggested limits of the
stack emission loads are met honestly all the time. And also to check the efficiency of Air
Pollution Control Equipments.
• All the internal roads will be black topped to prevent fugitive emissions.
• PUC certified vehicles shall be used for transportation of raw material/products.
• To check the functioning of pollution control equipment the unit will prepare environment
monitoring schedule during operation. In case of value found above the statuary limit the
plant will be shut down immediately and the environment cell of the unit will be informed
for further action.
• Raw material will be kept in storage yard and base of storage yard will have impermeable
base surfaces, usually constituted from the material being stored. Other raw materials will
be stored under cover sheds.
• Local exhaust ventilation will be provided to vent out the emissions to suitable arrestment
plant to meet the emission limit.
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• Indore air monitoring will be done to check the exposure level of the worker for periodical
basis. (at least once in six months)
9.7.2 Water Pollution Management
• The construction site will be provided with sufficient and suitable toilet facilities for
workers to allow proper standards of hygiene. These facilities should preferably be
connected to a septic tank and maintained to ensure minimum environmental impact.
• Measures will be implemented to prevent seepage of liquid materials into ground where
it could contaminate groundwater;
• Ensure prompt cleaning up of accidental spillages
• Measures will be followed to prevent the contamination of hydrological features by
diesel, grease, oil, etc. derived from the working area.
• The machinery / equipment will be maintained in a good operating condition;
• Specially designated areas will be created for vehicle maintenance;
• Accidental spillages will be cleaned up promptly.
• Curing water will be sprayed and after liberal curing, all concrete structures will be
covered with gunny bags this will conserves water
• Provisions will be made to ensure the construction vehicles stick to the access track to
prevent mud & dirt being deposited on roads
• Fence will be constructed around the site to trap sediments whilst allowing the water to
flow through.
• All mud & dirt deposited on the roads from the construction activities will be cleaned.
• Adopting good construction and engineering practices will help in mitigating the water
pollution.
• The process waste water will be collected periodically and recycled to process after
sedimentation process, along with mud.
9.7.3 Noise Pollution Management
• All possible measures will be taken to minimize the noise.
• The insulation provided for prevention and loss of heat and personnel safety shall also
act as noise reducer.
• Foundations and structures will be designed to minimize vibrations and noise.
• Regular equipment maintenance and better work habits will be adopted.
• D.G. set is proposed to be housed in an inbuilt acoustic enclosure. The acoustic
enclosure will be designed for minimum 25dB (A) insertion loss for meeting the ambient
noise standards, whichever is on the higher side.
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9.7.4 Solid Waste Management
S.No. Waste Management
1. Empty Fibre Bags
(Category 15.1)
Shredded in the Shredder unit attached to the BOD in a
closed loop & collected thro cyclone collector, thro
screw conveyor to the Edge Runner Mill (ERM).
2. Fibre Dust
(Category 15.3
Periodically recycled after the container containing
water & placed beneath the rotary valve of the dust
collector gets filled up.
3. Cement & Fly ash Dust Periodically recycled after the container placed beneath
the rotary valve of the Dust Collector gets filled up.
4. Process Sludge
(Category 15.1)
Continuously recycled through Wet Ball Mill in slurry
form.
5. Hard Broken Pieces
(Category 15.1)
Continuously recycled through Wet Ball Mill in slurry
form.
9.7.6 Socio-Economic Aspect
• Zero (0) Loss of habitation.
• Public Health & Safety Plan is proposed for upliftments of health facilities and
awareness on Asbestos manufacturing.
• Large scale, long term and stable job opportunities to local villagers directly through
On-the-job training and off-the-job training to enhance local skills.
• Rise in indirect avenues for employment opportunities.
• Direct & indirect infrastructural development of the study area with the enterprises’
social commitments rendered in the study area.
• The proposed project will follow universal respect for, and observance and protection of,
human rights.
The following CSR activities have been proposed for the people of the study area:
S. No.
Activities Capital Cost % Average (3 years) annual
N.P.
1st Year
2nd Year
3rd Year
1. Installation of Rainwater Harvesting Structures in
government institutions: Upswastha Kendra
Lalwari 3.2 km ESE; Rajkiya Adarsh Uchh
Prathmik Vidhyalya, Lalwari 3.5 km ESE & Facility
45.0
16.0 5.1 --
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development of sanitation fittings connecting the
proposed rain water storage tank with the
bathrooms washing & flushing.
2. In consultation with local authorities and Gram
Panchayat, Shedriya, for the development of the
primary health centre, Shedriya by Contributing for
a Multi-specialty hospital for critical illness and
emergency along-with a Medical Ambulance for
the study area.
75.0 22.0 8.0 0.5%
3. Health Camps proposed in the study area:
1. Yearly Camp for Mother and Child in the study
area for awareness on malnutrition including
drops / supplements.
2. Awareness on indicators of esotheolima shall
be given to the public at large in the study area
mainly Agarpura (4.5 km SE), Lalwari (3.0 km
ESE), Sangrampura (4.0 km SSE). Camps shall
provide demonstration and action plan on
prevention, symptoms & cure.
8.0 7.0 7.0 0.3%
4. Skill development and earning sources for youth
both On-the-Job training of local skilled workers &
Off-the-Job training of the unskilled local non
workers for income generating activity.
5.0 5.0 5.0 0.2%
5. Regular Health Check up camps shall be
organized mainly in three villages in the wind
direction viz. Agarpura(4.5 km SE), Lalwari (3.0 km
ESE), Sangrampura (4.0 km SSE) and in the study
area for :To trace any indication of Asbestosis/
lung Cancer and will be kept under surveillance
and immediate action will be taken.Regular
urinalysis, x-rays, and a bronchoscopy (a test that
detects asbestos fibers within lungs, and also
determines the extent of the damage done by
asbestos exposure), will be done in every 6
months.
35.0 20.0 20.0 1%
Total 168.0 70.0 45.1 2%
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9.8 CONCLUSIONS
It is predicted that socio-economic impact due to this project will provide opportunities for
employment to local inhabitants. There are no Resettlement and Rehabilitation issues
involved in this project. The social development project infrastructures will be of use to
the people of the study area. The contribution to the revenue (State Govt.) will augment
the public expenditure. The entire project area is devoid of any endangered flora and
fauna. Thus, the proposed project is not likely to affect the environment or adjacent
ecosystem adversely.
**********
Project: VISAKA INDUSTRIES LTD
Document No.: EESPL/VIL/002/358-EC/IND/2013
Enkay Enviro Services Pvt. Ltd., Jaipur
DISCLOSURE OF CONSULTANT ENGAGED
Declaration by Experts contributing to the EIA of “Visaka Industries Ltd.”
I, hereby, certify that I was a part of the EIA team in the following capacity that developed the
above EIA.
EIA Coordinator
Name KN Sudershan Rao
Functional Area Experts: -
S. No. Functional
Areas
Name of the Expert/s Involvement (Proposed)
(Period & Task)
1 AP K N Sudershan Rao
Dr. Yati Kachhawa
• Relevant inventorization
• Prediction of air pollution
and its management
2 WP Yashwant Bordiya
Supriya Sharma
• Relevant inventorization
• Data input in
report
• Prediction of water
pollution and its
management.
• Water Balance.
3 SHW Yashwant Bordiya
Prabhakar Sharma
• Identification of nature of
waste, categorization, and
quantity of generated.
4 SE Shubhangi Tibra • Secondary data: Census
of India, 2011.
• Socio- Economic
observation and impact
assessment.
• Public Health & Safety
plan
• Enterprises social
commitment
5 EB Dr.Yati Kachhawa
Supriya Sharma (Trainee)
• Ecological and biodiversity
survey
• Identification of species
(flora and fauna).
• Impact prediction and
Management
6 HG Vikrant Mahendran • Hydrogeological survey
for assessing aquifer
distribution for the area.
• Water resource evaluation
of the area.
Project: VISAKA INDUSTRIES LTD
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• Pre-monsoon & post-
monsoon collection of
water level & quality data.
7 GS Vikrant Mahendran • Field survey for assessing
the regional and local
geology of the area.
8 AQ K N Sudershan Rao
Mrs. Neha Bhargava
• Collection of micro
metrological data
• Inventorization of source
inputs
• Running of air modelling
• Interpretation of obtained
results.
9 NV KN Sudershan Rao • Prediction of Noise
pollution.
• Mitigation measures
10 LU Prabhakar Sharma • Satellite imaginary.
• Inference
11 RH KN Sudershan Rao • Assessment of risk
involved, if any.
• Management plan for
safety.
Declaration by the Head of the Accredited Consultant Organization
I, Sunita Mantri, hereby, confirm that the above mentioned experts prepared the EIA of “
Visaka Industries Ltd.” I also confirm that I shall be fully accountable for any mis-leading
information mentioned in this statement.
Signature
Name Mrs. Sunita Mantri
Designation CMD
Name of the EIA Consultant Organization Enkay Enviro Services Pvt. Ltd.
NABET Certificate No. & Issue Date At serial no. 43 as per the List of Accredited
EIA Consultant Organizations as on January
08, 2015