s no a. specific conditions compliance status · holi-nayagram road, once the same is handed over...
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S No A. Specific Conditions Compliance status
iCatchment Area Treatment Plan as has been proposed should be completed in 5
years. Work is to be executed by Forest Dept., GoHP as per approved CAT Plan
iiPrior approval under Forest (Conservation) Act, 1980 for diversion of forest land
should be taken. No physical work will be initiated without forest clearance for
this project.
Complied.
1. Approval for diversion of Forest Land was accorded by MoEF on dated 26-
Oct-2013.
2. Govt. of Himachal Pradesh (GoHP) accorded diversion of Forest land on
dated 28-Jan-2013.
3. Construction of project was started after Forest land diversion.
iii
In all there are 288 project affected families (PAFs) whose land is likely to be
acquired permanently and 2 PAFs who will lose land as well as house. The
rehabilitation & resettlement of project affected person should be completed
before commissioning of the project.
Complied.
The R & R Plan is approved by DC Chamba, GoHP on 10-Jan-2014.
Implementation of R&R plan started. First instalment towards pension to
identified vulnerable persons made.
iv
The following commitments made during the public hearing should be fulfilled:
a) Appointment of two numbers of MD doctors and one of them shall be lady
doctor. Both these doctors are to be on the pay rolls of the company. b) Training
of the 120 Nos of local youths for the ITI course. c) Strengthening of the existing
Holi-Nayagram road, once the same is handed over to GMR after necessary
clearance.
Noted and process of compliance is initiated as follows:-
a)Advertisement in local newspaper was done on 18-May-11 and again on dt 24-
Jan-2012 and intimation to local employment exchanges done.
1. One MBBS doctor along with two paramedical staff was appointed at site
from 15-Aug-2013.
2. Till date no suitable Lady doctor responded to advertise due to remote
location. Matter is under discussion and constant followup with Govt. officials.
(b) Company is committed to provide assistance to locals who will successfully
enroll into ITI Course. Till date, no local is selected for the ITI course. We are
provding support to the studen community by organising career counseling
sessions, traianing through our CSR activities. We are providng emplyement to
the locals in the project apart from providng various training enabiling them to
get more jobs at other locations too. (C) Noted.
vEnvironment flow should be 20% of the average lean season flow of 90%
dependable year for four consecutive leanest months.
Noted and Will be complied at operation phase.
vi
Biodiversity conservation & management plan as proposed in the EMP should
be implemented in totality. From the study area 272 flowering plant species were
recorded which include 28 trees, 48 shrubs, 10 climbers and 186 herbs. However
listing of bryophytes/ Pteridophytes has not been done. this may be done and
submitted within three months.
Forest Dept. GoHP will implement the Biodiversity Conservation &
Management Plan. List of Bryophytes/ Pteridophytes are provided to MoEF
vide our letter dt 13-Jan-11.
ol
vii
Fishery conservation & Management plan as proposed in the EMP should be
undertaken in consultation with the Fisheries department, Government of
Himachal Pradesh. The up gradation of existing facilities of fish firm at Holi in
Chamba district should also be done meet the demand of fish seeds.
Noted and will be done by fishery department, GoHP. Required Fishery
development fund as demanded by fishery department has been submitted on
27-Sept-11 and final instalment on 10-Mar 2014. NOC is also issued by Fishery
dept, GoHP on 22-May 2014.
viiiAll the equipments which are likely to generate high noise levels are to be fully
mollified (noise reduction measures.)
Noted and equipments used in project construction are complying with the
noise levels. The same has been checked by Chamba Pollution Control Board.
ix
Consolidation and compaction of the muck should be carried-out in the muck
dumping sites and the dumping sites should be above high flood level. The
proposed plan envisages generation of total volume of Muck as 21.64 lakh cum
(including 40% swell factor). Out of which about 9.32 lacs cum of muck will be
utilized as construction material for various project components and 12.32 lacs
cum of muck will be disposed off at pre designated seven number of disposal
sites.
Noted and will be complied by fishery department, GoHP. Muck is disposed off
in pre designated sites which are approved by SPCB, GoHP only.
Monthly Muck generation, utilisation and disposal status on these site is
regularly submitted to SPCB, GoHP.
x
Green belt development is proposed around project areas, reservoir periphery
(12.00 Ha) road side (13.8km) and other components. The average width of green
belt around reservoir rim will be around 40 m varying from about 15 m at places
to 120 m or as physiographic and land feature allow. The allocated amount of Rs
9.28 lakhs for green belt development should strictly be used for the purpose.
Noted and will be complied in consultation with GoHP departments.
Bajoli-Holi HEP (180MW) - Half yearly status report Jan - June 2015
Annexure-I
xi
The environment clearance does not necessarily imply that forestry clearance
shall be granted to the project and that the proposal for the forestry clearance
shall be considered by respective authorities on their merit. The investment
made in the project, if any based on environment clearance so granted, shall be
entirely at cost and risk of the project proponent.
Noted.
S No B. General Conditions Compliance status
iAdequate free fuel arrangement should be made for the labour force engaged in
the construction work at project cost so that indiscriminate felling of trees is
prevented.
Noted. Community kitchen facility is provided by Contractor which is factored
in the Project cost under Energy Conservation Measures.
iiFuel depot may be opened at the site to provide the fuel (kerosene/wood/LPG).
Medical facilities as well recreational facilities should also be provided to the
labourers.
Noted. Fuel depot is opened at site by Contractor. Medical and recreation
facility for laborers will be done by Contractors.
iiiAll the labourers to be engaged for construction works should be thoroughly
examined by health personal and adequately treated before issuing them work
permit.
Noted. Appropriate health checkups are done for construction workforce by
proponent and contractor.
iv
Restoration of construction area including dumping site of excavated materials
should be ensured by leveling, filling up of burrow pits, landscaping etc. The
area should be properly treated with suitable plantation.
Noted. Will be complied as per the guidance of SPCB, GoHP and other GoHP
departments.
vFinancial provision should be made in the total budget of the project for
implementation of the above suggested safeguard measures.Noted. Adequate provision is provided in Project cost under Environment Cost.
viSix monthly monitoring reports should be submitted to the Ministry and its
Regional Office, Chandigarh for review.Noted and regularly submitting the same
vii
Officials from regional office MoEF, Chandigarh who would be monitoring the
implementation of environmental safeguards should be given full cooperation,
facility and documents / data by the project proponents during their inspection.
Noted and Full cooperation will be accorded.
Last visit was taken in Sep 2013 and all data available with the project
proponent has been provided. Full cooperation will be extended for future
visits.
5The responsibility of implementation of environmental safeguards rests fully
with the M/s GMR Bajoli Holi Hydro Power Pvt. Ltd & Government of
Himachal Pradesh.
Noted.
6The total amount of Rs. 15603.28 Lakhs kept in the budgetary provisions for
implementation of environmental management plan should be strictly adhered
and not to be diverted for any other purpose.
Noted. Till date we have utilized approximately an amount of Rs. 9016.00 Lakhs
towards environment & ecology.
7In case of change in the scope of the project, project would require a fresh
appraisal.Noted. There is no change in the scope of the project.
8
The Ministry reserves the right to add additional safeguard measures
subsequently, if found necessary and to take action including revoking of the
clearance under the provisions of the Environment (Protection) Act, 1986, to
ensure effective implementation of the suggested safeguard measure in a time
bound and satisfactory manner.
Noted.
9This clearance letter is valid for a period of 10 years from the date of issue of this
letter for commencement of construction work.
Complied and Construction in the project area already commenced from 29-
May-2013.
10
A copy of the clearance letter shall be sent by the proponent to concerned
Panchayat, Zilla Parishad/Municipal corporation, Urban local body and the
local NGO, if any, from whom suggestions/representation, if any, were received
while processing the proposal. The clearance letter shall also be on the website of
the company by the proponent.
Complied. Notification is mentioned on company web site and copy of the
letters are provided to local panchayats and other Govt Depts.
11
The proponent should advertise at least in two local newspaper widely
circulated in the region around the project, one of which shall be in the
vernacular language of the locality concerned informing that the project has
been accorded environmental clearance and copies of clearance letter are
available with the state Pollution Control Board/Committee and may also be
seen at Website of the Ministry of Environment and Forest at
http:www.envfor.nic.in
Complied. Advertisement in the newspaper was published on 10th June 2011
in Divya Himachal, Dainik Tribune for (Local newspaper in Vernacular,
(Hindi)). Along with in English News paper Tribune and Himachal Times
which have wide circulation in the project area.
Copy of the advertisement was already provided to your office vide letter dt 7-7-
2011.
12
The project proponent shall also submit six monthly reports on the status of
compliance of the stipulated EC condition including result of monitored data
(both in hard copies as well as by e-mail) to the respective Regional office of
MoEF, the respective office of CPCB and the SPCB.
Noted and submitting the same regularly. The monitoring report for pre-
monsoon data (April 2015) on Air Quality, River Water Quality is also being
submitted.
May - 2015
Sponsor:-
M/s. GMR Bajoli Holi Hydropower Private Ltd.,Ratan Chand Building, VPO Kuleth Holi Tehsil,
Bharmour, Chamba,
Himachal Pradesh-176 326.
Prepared By:-
Recognised by MoEF (GOI) Notifn. No. D.L.33004/99 Dt.24.10.2007NABL T-1550 (Chemical), T-1826 (Biological), T-2344 (Mechanical) dt.04/10/2012 valid up to 03.10.2014
Accredited under the QCI-NABET Scheme for EIA ConsultantBIS vide No.CL/CQAPD/OSL (7124116) dt.16.12.2011
Certified by ISO 9001:2008, ISO 14001:2004, ISO 18001:2007 Head Office: 60, Bajiprabhu Nagar, Nagpur-440 033, MS
Lab. : FP-34, 35, Food Park, MIDC, Butibori, Nagpur – 441122
Ph.: (0712) 2242077, 9373287475 Fax: (0712) 2242077Email: [email protected], [email protected]
Website: www.anaconlaboratories.com,
Environmental Monitoring Report
At
GMR Bajoli Holi Hydropower Project
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Environmental Monitoring Report
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ANACON LABORATORIES PVT. LTD. 1
LIST OF CONTENTS
TABLE NO. TABLE NAME PAGE NO.
1 Details of air monitoring locations 2
2 Sampling frequency 3
3 Measurement techniques for various pollutants 3
4 Summary of ambient air quality results (Powerhouse AAQ - 1) 3
5 Summary of ambient air quality results (Deol Colony AAQ - 2) 7
6 Summary of ambient air quality results (Adit – 2 AAQ - 3) 10
7 Summary of ambient air quality results ( Dam site AAQ - 4) 13
8 Location : SW-1 Dam site (River water) 16
9 Location : SW 2 Adit -2 (River water) 16
10 Location : SW 3 – Adit -3 (River water) 17
11 Location : SW 4 – Adit-4 (River water) 18
12 Location : SW 5 – Deol Colony (River water) 18
13 Location : SW 6 – Power House (River water) 19
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LIST OF FIGURE
FIGURE NO. FIGURE NAME PAGE NO.
1 Power house (AAQ - 1) PM10 4
2 Power house (AAQ - 1) PM2.5 5
3 Power house (AAQ - 1) SO2 5
4 Power house (AAQ - 1) NOx 6
5 Power house (AAQ - 1) CO 6
6 Deol colony (AAQ - 2) PM10 7
7 Deol colony (AAQ - 2) PM2.5 8
8 Deol colony (AAQ - 2) SO2 8
9 Deol colony (AAQ - 2) NOx 9
10 Deol colony (AAQ - 2) CO 9
11 Adit 2 (AAQ – 3) PM10 10
12 Adit 2 (AAQ – 3) PM2.5 11
13 Adit 2 (AAQ – 3) SO2 11
14 Adit 2 (AAQ – 3) NOx 12
15 Adit 2 (AAQ – 3) CO 12
16 DAM site (AAQ - 4) PM10 13
17 DAM site (AAQ - 4) PM2.5 14
18 DAM site (AAQ - 4) SO2 14
19 DAM site (AAQ - 4) NOx 15
20 DAM site (AAQ - 4) CO 15
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1.1 Introduction
The Bajoli Holi Hydroelectric project (180 MW) is proposed as a Greenfield run of the river
scheme in Chamba district of Himachal Pradesh. The project is located at a distance of about 220 KM
from Pathankot.
The project activity is being developed by GMR Bajoli Holi Hydropower Private Limited
(GBHHPL), which is a special purpose vehicle (SPV) formed by GMR Energy Limited which is a part of
the GMR Group. The GMR group is headquartered in Banglore and has been developing projects in high
growth areas such as Airports, Energy, Highways and Urban Infrastructure.
In accordance with the Environmental Clearances dated 24th Jan 2011, the developer is obliged to
fulfill the requirements of EIA-EMP during project construction and operation. The stipulated conditions
in consent to operate/establish, states that noise and ambient air Quality, Emissions/effluent to be
maintained as per schedule III and IV of Environment Protection Rules 1986 as amended and prescribed
by the Board.
1.2 Environmental Monitoring Methodology
The methodology adopted for carrying out environmental monitoring was as per the guidelines
given by CPCB. Data in the study area was collected by conducting field study/primary sampling during
the study period with respect to the different environmental attributes.
. Three seasonal monitoring/sampling and analysis of ambient air and water quality.
2. Air quality to be monitored of 24 hourly (4 stations *2days/week*4weeks *3seasons)
3. Preparation and submission on Environment Monitoring Report.
4. Responding to clarification/questions raised by GBHHPL.
The ambient air quality monitored is to be done at 4 locations for month of May 2015 (24 Hourly)
basis in line CPCB guidelines of ambient air quality sampling and monitoring.
Seasonal monitoring of environmental parameters is of immense importance to assess the status of
environment monitoring. With the knowledge of baseline conditions, the monitoring program will serve
as an indicator for any deterioration in environmental conditions due to monitoring of the project Suitable
mitigation steps will be taken in time to safeguard the environment, based on monitoring reports.
Monitoring is important in the control of pollution since the efficiency of control measures can only be
determined by monitoring.
1.3 Detail rationale for sampling location & monitoring stations
Selection of monitoring stations
The status of the ambient air quality was assessed through a scientifically designed ambient air quality
monitoring network. The design of monitoring network in the air quality surveillance program was based
on the following considerations:
Meteorological conditions on synoptic scale
Topography of the study area
Representatives of regional background
Population and sensitive areas
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Representation of valid cross sectional distribution in downwind direction
In order to find out the impact of surrounding activity on sensitive receptors, it is necessary to
monitor Environmental Quality to know the level of concentrations of pollutants within area. Accordingly
GMR through Anacon Laboratories Pvt. Ltd., Nagpur has been monitoring at following locations for air
and water on seasonal sampling.
1.4 Ambient Air Quality Monitoring & Water Sampling Result
1.4.1 Ambient air quality monitoring results
1.4.1.1 Monitoring locations
Ambient air monitoring was carried out at 4 locations. The details about monitoring locations are
presented in Table 1.
TABLE 1
DETAILS OF AIR MONITORING LOCATIONS
Sr. No. Air Monitoring Location
1. Power House
2. Deol Colony
3. Adit 2
4. Dam Site
The above monitoring stations are selected on the basis of downwind and upwind directions with respect
to the GMR site. Anacon Laboratories Pvt. Ltd., Nagpur is carrying out seasonal monitoring for
parameters PM2.5, PM10, SO2, NOx and CO at above mentioned ambient air quality monitoring (AAQM)
locations.
1.4.1.2 Monitored parameters and frequency of sampling
Methods and Instruments used for Sampling
The air samples were analyzed as per methods specified by Central Pollution Control Board
(CPCB). Sampling frequency and measurement techniques are presented in Tables 2&3.
The levels of Particulate Matter PM10 and PM2.5, Sulphur Dioxide (SO2), Oxides of Nitrogen (NOX)
and Carbon Monoxide (CO) were monitored for establishing the baseline status. PM10 and PM2.5 was
collected with the help of respirable particulate sampler operating 24 hours by drawing air which passes through
the cyclone at the rate of 1.0 -1.3 m3/min which collects the particles less than 10 µm diameter over glass fiber
filter paper and the bigger particulates from 10 to 100 µm are collected into the cup provided at the bottom of
the cyclone. The dust deposited over the filter paper is measured as PM2.5 and the smaller particulates from 2.5
µm are collected into the membrane filter paper.
Sampling was carried out continuously for 24 hourly monitoring twice a week at each station
during the stipulated study period using pre-calibrated respirable dust samplers in each of the stations.
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Earmarked samples were collected for Particulate Matter-PM10 & PM2.5, SO2 and NOx for 24
hourly. Collected samples were sent to Laboratories for analysis.
TABLE 2
SAMPLING FREQUENCY
Parameters Sampling frequency
Particulate Matter (PM10) 24 hourly sample twice a week for 4 Week.
Particulate Matter (PM2.5) 24 hourly sample twice a week for 4 Week.
Sulphur dioxide (So2) 24 hourly sample twice a week for 4 Week.
Oxides of Nitrogen (NOx) 24 hourly sample twice a week for 4 Week.
Carbon Monoxide (CO) 8 hourly basis for 24 hour sample for 4 Week.
TABLE 3
MEASUREMENT TECHNIQUES FOR VARIOUS POLLUTANTS
S.No. Parameter Technique Technical Protocol
1. Particulate Matter (PM10) Respirable Dust Sampler
(Gravimetric Method)
Gravimetric (HVS)-IS: 5182: Part-
23 -2006
2. Particulate Matter (PM2.5) Fine Particulate Sampler
(Gravimetric Method)
Gravimetric (HVS)-IS: 5182: Part-4
with cyclone
3. Sulphur Dioxide (SO2) Modified West and Gaeke Clorimetric IS: 5182: (Part-2)2001
4. Oxide of Nitrogen (NOX) Jacob&Hochheiser Method Clorimetric IS: 5182: (Part-6)2006
5. Carbon Monoxide NDIR IS: 5182 (Part 10): 1999
1.4.1.3 Ambient air quality results
The background levels of PM10, PM2.5, SO2, NOx and CO measured are required to compute ambient
air quality. The monitoring locations are selected at the above mentioned locations at downwind and upwind
directions wrt project site. The minimum, maximum concentration, average, and 98th percentile are presented in
Tables.
(A) Power House (AAQ-1):
The summary of ambient air quality monitoring results for the month of May-2015 is presented in detail
in Table 4 & Annexure I. 98th percentile, maximum and minimum values etc have been computed from
the collected raw data for all the AAQ monitoring station. The data has been compared with the standards
prescribed by Central Pollution Control Board (CPCB)/NAAQ for residential and rural zone.
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TABLE 4
SUMMARY OF AMBIENT AIR QUALITY RESULTS
Power House (AAQ-1)
Date of
monitoring
PM10 (µg/m3)
PM2.5 (µg/m3)
SO2 (µg/m3)
NOX (µg/m3)
CO (mg/m3)
04.05.2015 84.7 41.6 11.4 24.7 0.241
07.05.2015 87.1 52.9 14.7 26.1 0.307
11.05.2015 81.2 46.3 9.4 19.3 0.239
15.05.2015 76.4 24.8 7.3 21.6 0.193
18.05.2015 84.9 23.7 9.1 24.1 0.217
22.05.2015 85.1 42.3 11.2 28.4 0.294
25.05.2015 82.7 26.1 8.7 22.7 0.257
28.05.2015 73.9 19.4 8.2 21.2 0.183
NAAQS CPCB 100 60 80 80 2.0
Maximum 87.1 52.9 14.7 28.4 0.307
Minimum 73.9 19.4 7.3 19.3 0.183
Average 82.0 34.6 10.0 23.5 0.241
98% le 86.8 52.0 14.2 28.1 0.305
Observation of results
PM10: PM10 concentration ranged from 73.9-87.1 µg/m3 at power house (AAQ-1). The maximum
concentration of 87.1 µg/m3 and minimum concentration of 73.9 µg/m3 was recorded during study period.
The average value is recorded 82.0 μg/m3 and 98th percentile value 86.8. The statistical analysis of PM10 is
presented in Table 4 and Figure 1.
FIGURE 1: POWER HOUSE (AAQ-1) PM 10
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PM2.5: PM2.5 concentration ranged from 19.4-52.9 µg/m3 at power house (AAQ-1). The maximum
concentration of 52.9 µg/m3 and minimum concentration of 19.4 µg/m3 was recorded during study period.
The average value is recorded 34.6 μg/m3 and 98th percentile value 52.0. The statistical analysis of PM2.5
is presented in Table 4 and Figure 2.
FIGURE 2: POWER HOUSE (AAQ-1) PM 2.5
Sulphur Dioxide (SO2): SO2 concentration ranged from 7.3 to 14.7 µg/m3 at power house (AAQ-1). The
maximum concentration of 14.7 µg/m3 and minimum concentration of 7.3 µg/m3 was recorded during
study period. The average value is recorded 10 μg/m3 and 98th percentile value 14.2. The statistical
analysis of SO2 is presented in Table 4 and Figure 3.
FIGURE 3: POWER HOUSE (AAQ-1) SO2
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Oxides of Nitrogen (NOx): Nox concentration ranged from 19.3 to 28.4 µg/m3 at power house (AAQ-1).
The maximum concentration of 28.4 µg/m3 and minimum concentration of 19.3 µg/m3 was recorded
during study period. The average value is recorded 23.5 μg/m3 and 98th percentile value 28.1. The
statistical analysis of NOx is presented in Table 4 and Figure 4.
FIGURE 4: POWER HOUSE (AAQ-1) NOx
Carbon monoxide (CO): CO concentration ranged from 0.183 to 0.307 µg/m3 at power house (AAQ-1).
The maximum concentration of 0.307 µg/m3 and minimum concentration of 0.183 µg/m3 was recorded
during study period. The average value is recorded 0.241 μg/m3 and 98th percentile value 0.305. The
statistical analysis of CO is presented in Table 4 and Figure 5.
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FIGURE 5: POWER HOUSE (AAQ-1) CO
(B) Deol Colony (AAQ-2):
The summary of ambient air quality monitoring results for the month of May-2015 is presented in detail
in Table 5 & Annexure I. 98th percentile, maximum and minimum values etc have been computed from
the collected raw data for all the AAQ monitoring station. The data has been compared with the standards
prescribed by Central Pollution Control Board (CPCB)/NAAQ for residential and rural zone.
TABLE 5
SUMMARY OF AMBIENT AIR QUALITY RESULTS
Deol Colony (AAQ-2)
Date of monitoring PM10 (µg/m3) PM2.5 (µg/m3) SO2 (µg/m3) NOX (µg/m3) CO (mg/m3)
04.05.2015 46.2 14.9 6.1 13.8 0.167
07.05.2015 51.7 16.2 6.8 14.9 0.201
11.05.2015 47.3 14.3 5.7 13.2 0.183
15.05.2015 53.9 17.1 6.4 16.1 0.189
18.05.2015 43.1 13.8 5.9 14.7 0.162
22.05.2015 46.3 14.9 6.1 13.8 0.173
25.05.2015 51.2 16.1 6.3 17.3 0.191
28.05.2015 47.7 14.3 5.7 16.2 0.168
NAAQS CPCB 100 60 80 80 2.0
Maximum 53.9 17.1 6.8 17.3 0.201
Minimum 43.1 13.8 5.7 13.2 0.162
Average 48.4 15.2 6.1 15.0 0.179
98% le 53.6 17.0 6.7 17.1 0.200
Observation of results
PM10: PM10 concentration ranged from 43.1 to 53.9 µg/m3 at Deol Colony (AAQ-2). The maximum
concentration of 53.9 µg/m3 and minimum concentration of 43.1 µg/m3 was recorded during study period.
The average value is recorded 48.4 μg/m3 and 98th percentile value 53.6. The statistical analysis of PM10 is
presented in Table 5 and Figure 6.
FIGURE 6: DEOL COLONY (AAQ-2) PM 10
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PM2.5: PM2.5 concentration ranged from 13.8 to 17.1 µg/m3 at deol colony (AAQ-2). The maximum
concentration of 17.1 µg/m3 and minimum concentration of 13.8 µg/m3 was recorded during study period.
The average value is recorded 15.2 μg/m3 and 98th percentile value 17.0. The statistical analysis of PM2.5
is presented in Table 5 and Figure 7.
FIGURE 7: DEOL COLONY (AAQ-2) PM 2.5
Sulphur Dioxide (SO2): SO2 concentration ranged from 5.7 to 6.8 µg/m3 at deol colony (AAQ-2). The
maximum concentration of 6.8 µg/m3 and minimum concentration of 5.7 µg/m3 was recorded during study
period. The average value is recorded 6.1 μg/m3 and 98th percentile value 6.7. The statistical analysis of
SO2 is presented in Table 5 and Figure 8.
FIGURE 8: DEOL COLONY (AAQ-2) SO2
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Oxides of Nitrogen (NOx): Nox concentration ranged from 13.2 to 17.3 µg/m3 at deol colony (AAQ-2).
The maximum concentration of 17.3 µg/m3 and minimum concentration of 13.2 µg/m3 was recorded
during study period. The average value is recorded 15.0 μg/m3 and 98th percentile value 17.1. The
statistical analysis of NOx is presented in Table 5 and Figure 9.
FIGURE 9: DEOL COLONY (AAQ-2) NOx
Carbon monoxide (CO): CO concentration ranged from 0.162 to 0.201 µg/m3 at deol colony (AAQ-2).
The maximum concentration of 0.201 µg/m3 and minimum concentration of 0.162 µg/m3 was recorded
during study period. The average value is recorded 0.179 μg/m3 and 98th percentile value 0.201. The
statistical analysis of CO is presented in Table 5 and Figure 10.
FIGURE 10: DEOL COLONY (AAQ-2) CO
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(C) Adit-2 (AAQ-3):
The summary of ambient air quality monitoring results for the month of May-2015 is presented in detail
in Table 6 & Annexure I. 98th percentile, maximum and minimum values etc have been computed from
the collected raw data for all the AAQ monitoring station. The data has been compared with the standards
prescribed by Central Pollution Control Board (CPCB)/NAAQ for residential and rural zone.
TABLE 6
SUMMARY OF AMBIENT AIR QUALITY RESULTS
Adit-2 (AAQ-3)
Date of monitoring PM10 (µg/m3) PM2.5 (µg/m3) SO2 (µg/m3) NOX (µg/m3) CO (mg/m3)
05.05.2015 52.7 16.2 6.4 14.7 0.218
08.05.2015 56.1 17.3 7.3 16.1 0.237
12.05.2015 48.2 14.8 6.1 14.2 0.191
16.05.2015 51.6 16.1 6.8 14.9 0.216
19.05.2015 47.3 14.9 5.7 16.1 0.208
23.05.2015 53.9 17.2 7.1 18.2 0.197
26.05.2015 56.1 16.4 6.7 16.4 0.201
29.05.2015 48.3 14.9 5.8 14.7 0.173
NAAQS CPCB 100 60 80 80 2.0
Maximum 56.1 17.3 7.3 18.2 0.237
Minimum 47.3 14.8 5.7 14.2 0.173
Average 51.8 16.0 6.5 15.7 0.205
98% le 56.1 17.3 7.3 17.9 0.234
Observation of results
PM10: PM10 concentration ranged from 47.3 to 56.1 µg/m3 at Adit 2 (AAQ-3). The maximum
concentration of 56.1 µg/m3 and minimum concentration of 47.3 µg/m3 was recorded during study period.
The average value is recorded 51.8 μg/m3 and 98th percentile value 56.1. The statistical analysis of PM10 is
presented in Table 6 and Figure 11.
FIGURE 11: ADIT 2 (AAQ-3) PM 10
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PM2.5: PM2.5 concentration ranged from 14.8 to 17.3 µg/m3 at Adit 2 (AAQ-3). The maximum
concentration of 17.3 µg/m3 and minimum concentration of 14.8 µg/m3 was recorded during study period.
The average value is recorded 16.0 μg/m3 and 98th percentile value 17.3. The statistical analysis of PM2.5
is presented in Table 6 and Figure 12.
FIGURE 12: ADIT 2 (AAQ-2) PM 2.5
Sulphur Dioxide (SO2): SO2 concentration ranged from 5.7 to 7.3 µg/m3 at Adit 2 (AAQ-3). The
maximum concentration of 7.3 µg/m3 and minimum concentration of 5.7 µg/m3 was recorded during study
period. The average value is recorded 6.5 μg/m3 and 98th percentile value 7.3. The statistical analysis of
SO2 is presented in Table 6 and Figure 13.
FIGURE 13: ADIT 2 (AAQ-2) SO2
Oxides of Nitrogen (NOx): Nox concentration ranged from 14.2 to 18.2 µg/m3 at Adit 2 (AAQ-3). The
maximum concentration of 18.2 µg/m3 and minimum concentration of 14.2 µg/m3 was recorded during
study period. The average value is recorded 15.7 μg/m3 and 98th percentile value 17.9. The statistical
analysis of NOx is presented in Table 6 and Figure 14.
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FIGURE 14: ADIT 2 (AAQ-3) NOx
Carbon monoxide (CO): CO concentration ranged from 0.173 to 0.237 µg/m3 at Adit 2 (AAQ-3). The
maximum concentration of 0.237 µg/m3 and minimum concentration of 0.173 µg/m3 was recorded during
study period. The average value is recorded 0.205μg/m3 and 98th percentile value 0.234. The statistical
analysis of CO is presented in Table 6 and Figure 15.
FIGURE 15: ADIT 2 (AAQ-3) CO
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(D) Dam Site (AAQ-4):
The summary of ambient air quality monitoring results for the month of May-2015 is presented in detail
in Table 7 & Annexure I. 98th percentile, maximum and minimum values etc have been computed from
the collected raw data for all the AAQ monitoring station. The data has been compared with the standards
prescribed by Central Pollution Control Board (CPCB)/NAAQ for residential and rural zone.
TABLE 7
SUMMARY OF AMBIENT AIR QUALITY RESULTS
Dam Site (AAQ-4)
Date of monitoring PM10 (µg/m3) PM2.5 (µg/m3) SO2 (µg/m3) NOX (µg/m3) CO (mg/m3)
05.05.2015 72.9 31.2 9.3 18.3 0.317
08.05.2015 68.2 27.9 8.2 19.1 0.283
12.05.2015 79.4 32.8 9.7 21.6 0.304
16.05.2015 84.1 31.1 10.4 24.7 0.326
19.05.2015 76.3 28.2 8.3 19.4 0.238
23.05.2015 77.3 37.4 9.6 23.8 0.327
26.05.2015 89.5 34.7 8.7 21.4 0.314
29.05.2015 81.3 29.1 9.4 18.2 0.268
NAAQS CPCB 100 60 80 80 2.0
Maximum 89.5 37.4 10.4 24.7 0.327
Minimum 68.2 27.9 8.2 18.2 0.238
Average 78.6 31.6 9.2 20.8 0.297
98% le 88.7 37.0 10.3 24.6 0.327
Observation of results
PM10: PM10 concentration ranged from 68.2 to 89.5 µg/m3 at Dam site (AAQ-4). The maximum
concentration of 89.5 µg/m3 and minimum concentration of 68.2 µg/m3 was recorded during study period.
The average value is recorded 78.6 μg/m3 and 98th percentile value 88.7. The statistical analysis of PM10 is
presented in Table 7 and Figure 16.
FIGURE 16: DAM SITE (AAQ-4) PM 10
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PM2.5: PM2.5 concentration ranged from 27.9 to 37.4 µg/m3 at Dam site (AAQ-4). The maximum
concentration of 37.4 µg/m3 and minimum concentration of 27.9 µg/m3 was recorded during study period.
The average value is recorded 31.6 μg/m3 and 98th percentile value 37.0. The statistical analysis of PM2.5
is presented in Table 7 and Figure 17.
FIGURE 17: DAM SITE (AAQ-4) PM 2.5
Sulphur Dioxide (SO2): SO2 concentration ranged from 8.2 to 10.4 µg/m3 at Dam site (AAQ-4). The
maximum concentration of 10.4µg/m3 and minimum concentration of 8.2 µg/m3 was recorded during
study period. The average value is recorded 9.2 μg/m3 and 98th percentile value 10.3. The statistical
analysis of SO2 is presented in Table 7 and Figure 18.
FIGURE 18: DAM SITE (AAQ-4) SO2
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Oxides of Nitrogen (NOx): Nox concentration ranged from 18.2 to 24.7 µg/m3 at Dam site (AAQ-4). The
maximum concentration of 18.2 µg/m3 and minimum concentration of 14.2 µg/m3 was recorded during
study period. The average value is recorded 20.8 μg/m3 and 98th percentile value 24.6. The statistical
analysis of NOx is presented in Table 7 and Figure 19.
FIGURE 19: DAM SITE (AAQ-4) NOx
Carbon monoxide (CO): CO concentration ranged from 0.238 to 0.327 µg/m3 at Dam site (AAQ-4). The
maximum concentration of 0.327 µg/m3 and minimum concentration of 0.238 µg/m3 was recorded during
study period. The average value is recorded 0.297μg/m3 and 98th percentile value 0.327. The statistical
analysis of CO is presented in Table 7 and Figure 20.
FIGURE 20: DAM SITE (AAQ-4) CO
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1.5 Surface Water Quality
The existing status of water quality (physic-chemical and bacteriological) for surface water was
assessed by collecting the water samples from Dam site, Adit-2, Adit-3, Adit-4, Deol Colony and Power
House. The physico-chemical analysis was carried out for samples collected during study period.
Characteristics of surface water is presented in Tables 8-13.
TABLE 8
Location:-SW-1-Dam Site (River Water)
(Date of Sampling:-14.05.2015)-
Sr. No Test Parameter Measurement Unit Test Method Test Result
1. pH value - IS 3025 (Part 11) 8.04 at 230C
2. Colour Hazen units IS 3025 (Part 4) 9
3. Odour - IS 3025 (Part 5) Agreeable
4. Turbidity NTU IS 3025 (Part 10) 7.3
5. Suspended Solids (SS) mg / l IS : 3025 (Part
17) < 10
6. Total dissolved solids (TDS) mg / l IS 3025 (Part 16) 257
7. Chemical oxygen demand
(COD) mg / l IS 3025 (Part 58) 12.7
8. Biochemical oxygen demand
(BOD at 270C for 3 days) mg / l IS 3025 (Part 44) 3.8
9. Iron (as Fe) mg / l IS 3025 (Part 2) 0.41
10. Oil and Grease mg / l IS 3025 (Part -
39) < 4
11. Total coliform MPN/100 ml IS 1622 Present
Note: 1. Results relate to tested sample only.2. Test report should not be reproduced partially. 3. *Permissible
limit in the absence of alternate source. 4. ‘mg/l’ is equivalent to ‘ppm’ 5. ‘µg/l’ is equivalent to ‘ppb’ 6. ‘<’
indicates detection limit of the laboratory. 7. MPN-Most probable number.
REMARKS: Based upon request of the party, sample was tested for above mentioned parameters only.
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TABLE 9
Location:-SW-2-Adit-2 (River Water)
(Date of Sampling:-14.05.2015)
Note:1. Results relate to tested sample only.2. Test report should not be reproduced partially. 3. *Permissible limit in the absence
of alternate source. 4. ‘mg/l’ is equivalent to ‘ppm’ 5. ‘µg/l’ is equivalent to ‘ppb’ 6. ‘<’ indicates detection limit of the
laboratory. 7. MPN-Most probable number.
REMARKS: Based upon request of the party, sample was tested for above mentioned parameters only.
Sr. No. Test Parameter Measurement Unit Test Method Test Result
1. pH value - IS 3025 (Part 11) 7.83 at 230C
2. Colour Hazen units IS 3025 (Part 4) 9
3. Odour - IS 3025 (Part 5) Agreeable
4. Turbidity NTU IS 3025 (Part 10) 8.0
5. Suspended Solids (SS) mg / l IS : 3025 (Part 17) < 10
6. Total dissolved solids (TDS) mg / l IS 3025 (Part 16) 317
7. Chemical oxygen demand (COD) mg / l IS 3025 (Part 58) < 4
8. Biochemical oxygen demand
(BOD at 270C for 3 days) mg / l IS 3025 (Part 44) < 2
9. Iron (as Fe) mg / l IS 3025 (Part 2) 0.19
10. Oil and Grease mg / l IS 3025 (Part -39) < 4
11. Total coliform MPN/100 ml IS 1622 Present
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TABLE 10
Location:-SW-3-Adit-3 (River Water)
(Date of Sampling:-14.05.2015)
Sr. No. Test Parameter Measurement Unit Test Method Test Result
1. pH value - IS 3025 (Part 11) 8.16 at 230C
2. Colour Hazen units IS 3025 (Part 4) 7
3. Odour - IS 3025 (Part 5) Agreeable
4. Turbidity NTU IS 3025 (Part 10) 7
5. Suspended Solids (SS) mg / l IS : 3025 (Part 17) < 10
6. Total dissolved solids (TDS) mg / l IS 3025 (Part 16) 281
7. Chemical oxygen demand (COD) mg / l IS 3025 (Part 58) 8.2
8. Biochemical oxygen demand
(BOD at 270C for 3 days) mg / l IS 3025 (Part 44) 3.1
9. Iron (as Fe) mg / l IS 3025 (Part 2) 0.24
10. Oil and Grease mg / l IS 3025 (Part -39) < 4
11. Total coliform MPN/100 ml IS 1622 Present
Note:1. Results relate to tested sample only.2. Test report should not be reproduced partially. 3. *Permissible limit
in the absence of alternate source. 4. ‘mg/l’ is equivalent to ‘ppm’ 5. ‘µg/l’ is equivalent to ‘ppb’ 6. ‘<’ indicates
detection limit of the laboratory. 7. MPN-Most probable number.
REMARKS: Based upon request of the party, sample was tested for above mentioned parameters only.
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TABLE 11
Location:-SW-4-Adit-4 (River Water)
(Date of Sampling:-14.05.2015)
Sr. No Test Parameter Measurement Unit Test Method Test Result
1. pH value - IS 3025 (Part 11) 6.93 at 230C
2. Colour Hazen units IS 3025 (Part 4) 13
3. Odour - IS 3025 (Part 5) Agreeable
4. Turbidity NTU IS 3025 (Part 10) 12
5. Suspended Solids (SS) mg / l IS : 3025 (Part 17) < 10
6. Total dissolved solids (TDS) mg / l IS 3025 (Part 16) 304
7. Chemical oxygen demand
(COD) mg / l IS 3025 (Part 58) 8.2
8. Biochemical oxygen demand
(BOD at 270C for 3 days) mg / l IS 3025 (Part 44) 3.1
9. Iron (as Fe) mg / l IS 3025 (Part 2) 0.18
10. Oil and Grease mg / l IS 3025 (Part -39) < 4
11. Total coliform MPN/100 ml IS 1622 Absent
Note:1. Results relate to tested sample only.2. Test report should not be reproduced partially. 3. *Permissible limit
in the absence of alternate source. 4. ‘mg/l’ is equivalent to ‘ppm’ 5. ‘µg/l’ is equivalent to ‘ppb’ 6. ‘<’ indicates
detection limit of the laboratory. 7. MPN-Most probable number.
REMARKS: Based upon request of the party, sample was tested for above mentioned parameters only.
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TABLE 12
Location:-SW-5-Deol Colony (River Water)
(Date of Sampling:-14.05.2015)
Sr. No Test Parameter Measurement
Unit Test Method Test Result
1. pH value - IS 3025 (Part 11) 7.19 at 230C
2. Colour Hazen units IS 3025 (Part 4) 3
3. Odour - IS 3025 (Part 5) Agreeable
4. Turbidity NTU IS 3025 (Part 10) 2.1
5. Suspended Solids (SS) mg / l IS : 3025 (Part 17) < 10
6. Total dissolved solids (TDS) mg / l IS 3025 (Part 16) 284
7. Chemical oxygen demand
(COD) mg / l IS 3025 (Part 58) < 4
8. Biochemical oxygen demand
(BOD at 270C for 3 days) mg / l IS 3025 (Part 44) < 2
9. Iron (as Fe) mg / l IS 3025 (Part 2) 0.16
10. Oil and Grease mg / l IS 3025 (Part -39) < 4
11. Total coliform MPN/100 ml IS 1622 Absent
Note:1. Results relate to tested sample only.2. Test report should not be reproduced partially. 3. *Permissible limit
in the absence of alternate source. 4. ‘mg/l’ is equivalent to ‘ppm’ 5. ‘µg/l’ is equivalent to ‘ppb’ 6. ‘<’ indicates
detection limit of the laboratory. 7. MPN-Most probable number.
REMARKS: Based upon request of the party, sample was tested for above mentioned parameters only.
TABLE 13
Location:-SW-6-Power House (River Water)
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(Date of Sampling:-14.05.2015)
Sr. No Test Parameter Measurement Unit Test Method Test Result
1. pH value - IS 3025 (Part 11) 8.29 at 230C
2. Colour Hazen units IS 3025 (Part 4) 7
3. Odour - IS 3025 (Part 5) Agreeable
4. Turbidity NTU IS 3025 (Part 10) 6.2
5. Suspended Solids (SS) mg / l IS : 3025 (Part 17) < 10
6. Total dissolved solids (TDS) mg / l IS 3025 (Part 16) 417
7. Chemical oxygen demand (COD) mg / l IS 3025 (Part 58) 9.4
8. Biochemical oxygen demand
(BOD at 270C for 3 days) mg / l IS 3025 (Part 44) 3.2
9. Iron (as Fe) mg / l IS 3025 (Part 2) 0.27
10. Oil and Grease mg / l IS 3025 (Part -39) < 4
11. Total coliform MPN/100 ml IS 1622 Present
Note: 1. Results relate to tested sample only.2. Test report should not be reproduced partially. 3. *Permissible limit
in the absence of alternate source. 4. ‘mg/l’ is equivalent to ‘ppm’ 5. ‘µg/l’ is equivalent to ‘ppb’ 6. ‘<’ indicates
detection limit of the laboratory. 7. MPN-Most probable number.
REMARKS: Based upon request of the party, sample was tested for above mentioned parameters only.
1.6 Conclusions and Recommendations
High concentration of PM10 at dam site and power house (air quality monitoring site) was due to dust
emission due to vehicular traffic and construction activity near the monitoring site. The overall ambient air
quality with respect to parameters of significance was found to be within prescribed AAQMS by CPCB.
One or more of the following measures may be implemented to minimize impact on air quality during
construction and operation of the project.
Water sprinkling on site for dust suppression
Use of covering sheets shall be done for trucks carrying construction materials to prevent air borne
dust
All material storage adequately shall be covered to avoid dust / particulate emission
Use of CPCB approved DG sets
Proper maintenance of DG sets
Adequate parking provision and proper traffic arrangement for smooth traffic flow
Vehicles having valid pollution under control certificate shall be allowed to ply
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Overall, the surface quality of sampling site was found to be good physico-chemically, however
bacteriologically found to be contaminated and need chlorination before use
1.7 List of Tables
LIST OF TABLES
TABLE
NO.
TABLE NAME PAGE NO.
1 Details of air monitoring locations 2
2 Sampling frequency 3
3 Measurement techniques for various pollutants 3
4 Summary of ambient air quality results (Powerhouse AAQ - 1) 3
5 Summary of ambient air quality results (Deol Colony AAQ - 2) 7
6 Summary of ambient air quality results (Adit – 2 AAQ - 3) 10
7 Summary of ambient air quality results ( Dam site AAQ - 4) 13
8 Location : SW-1 Dam site (River water) 16
9 Location : SW 2 Adit -2 (River water) 16
10 Location : SW 3 – Adit -3 (River water) 17
11 Location : SW 4 – Adit-4 (River water) 18
12 Location : SW 5 – Deol Colony (River water) 18
13 Location : SW 6 – Power House (River water) 19
1.8 List of Figures
LIST OF FIGURES
FIGURE NO. FIGURE NAME PAGE NO.
1 Power house (AAQ - 1) PM10 4
2 Power house (AAQ - 1) PM2.5 5
3 Power house (AAQ - 1) SO2 5
4 Power house (AAQ - 1) NOx 6
5 Power house (AAQ - 1) CO 6
6 Deol colony (AAQ - 2) PM10 7
7 Deol colony (AAQ - 2) PM2.5 8
8 Deol colony (AAQ - 2) SO2 8
9 Deol colony (AAQ - 2) NOx 9
10 Deol colony (AAQ - 2) CO 9
11 Adit 2 (AAQ – 3) PM10 10
12 Adit 2 (AAQ – 3) PM2.5 11
13 Adit 2 (AAQ – 3) SO2 11
14 Adit 2 (AAQ – 3) NOx 12
15 Adit 2 (AAQ – 3) CO 12
16 DAM site (AAQ - 4) PM10 13
17 DAM site (AAQ - 4) PM2.5 14
18 DAM site (AAQ - 4) SO2 14
19 DAM site (AAQ - 4) NOx 15
20 DAM site (AAQ - 4) CO 15
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1.9 Rules and Regulations
1.9.1 Air
1948 – The Factories Act and Amendment in 1987 was the first to express concern for the working
environment of the workers. The amendment of 1987 has sharpened its environmental focus and
expanded its application to hazardous processes.
1981 - The Air (Prevention and Control of Pollution) Act provides for the control and abatement of air
pollution. It entrusts the power of enforcing this act to the CPCB.
1982 - The Air (Prevention and Control of Pollution) Rules defines the procedures of the meetings of the
Boards and the powers entrusted to them.
1982 - The Atomic Energy Act deals with the radioactive waste.
1987 - The Air (Prevention and Control of Pollution) Amendment Act empowers the central and state
pollution control boards to meet with grave emergencies of air pollution.
1988 - The Motor Vehicles Act states that all hazardous waste is to be properly packaged, labelled, and
transported.
1.9.2 Water
1882 - The Easement Act allows private rights to use a resource that is, groundwater, by viewing it as an
attachment to the land. It also states that all surface water belongs to the state and is a state property.
1897 - The Indian Fisheries Act establishes two sets of penal offences whereby the government can sue
any person who uses dynamite or other explosive substance in any way (whether coastal or inland) with
intent to catch or destroy any fish or poisonous fish in order to kill.
1956 - The River Boards Act enables the states to enroll the central government in setting up an
Advisory River Board to resolve issues in inter-state cooperation.
1970 - The Merchant Shipping Act aims to deal with waste arising from ships along the coastal areas
within a specified radius.
1974 - The Water (Prevention and Control of Pollution) Act establishes an institutional structure for
preventing and abating water pollution. It establishes standards for water quality and effluent. Polluting
industries must seek permission to discharge waste into effluent bodies.
The CPCB (Central Pollution Control Board) was constituted under this act.
1977 - The Water (Prevention and Control of Pollution) Cess Act provides for the levy and collection
of cess or fees on water consuming industries and local authorities.
1978 - The Water (Prevention and Control of Pollution) Cess Rules contains the standard definitions
and indicate the kind of and location of meters that every consumer of water is required to affix.
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1991 - The Coastal Regulation Zone Notification puts regulations on various activities, including
construction, are regulated. It gives some protection to the backwaters and estuaries.
Ecological Monitoring Report of Bajoli Holi HEP
Year 2014
Prepared by
Ecological Unit
Bajoli Holi Hydro Power Pvt. Ltd.
Ecological Monitoring Report of Bajoli Holi HEP – 2014
Page 1 of 20
Contents
1.0 INTRODUCTION .................................................................................................................... 2
2.0 EIA & EMP STUDIES OF PROJECT ......................................................................................... 3
3.0 PROJECT AREA ...................................................................................................................... 3
4.0 METHODOLOGY ................................................................................................................... 4
5.0 FOREST TYPE IN PROJECT AREA ........................................................................................... 5
6.0 FLORISTIC COMPOSITION IN STUDY AREA ........................................................................... 6
6.1 Taxonomic Diversity ......................................................................................................... 6
6.2 Vegetation Profile of Study Area ...................................................................................... 6
6.2.1 Dam Site and Submergence Area ................................................................................. 6
6.2.2 Downstream of Dam Site .............................................................................................. 7
6.2.3 Power House Area ........................................................................................................ 7
7.0 FAUNAL DIVERSITY ............................................................................................................... 7
8.0 IMPORTANT SPECIES OF CONSERVATION IMPORTANCE CITED DURING STUDY ................ 8
9.0 WAY FORWARDS .................................................................................................................. 8
PHOTOGRAPHS OF FLORA AND FAUNA RECORDED DURING SURVEY ......................................... 10
LIST OF FLORA AND FAUNA RECORDED DURING SURVEY ............................................................ 13
Ecological Monitoring Report of Bajoli Holi HEP – 2014
Page 2 of 20
1.0 INTRODUCTION
The proposed Bajoli Holi HEP (180 MW) is run-of-the-river scheme implemented by
GMR Bajoli Holi Power Pvt. Ltd. The project is located on Ravi River in Holi Sub-tehsil,
Chamba district, Himachal Pradesh. The project will divert water from 66 m high dam
through 15.53 km long HRT on left bank of Ravi River. The power house is proposed on
the left bank of Ravi River near Kee nala having generation capacity 180 MW (3x60
MW).
The Detailed Project report was prepared for BHHEP which was also approved by
Central Electricity Authority on 30th May 2011. The project construction was started in
the month of May 2013 after securing all the approval required start of project
construction. The Muck Disposal sites proposed in the project area was verified and
approved by the Regional Office SPCB, Chamba, in compliance to Consent to Establish
(CoE) issued by SPCB, GoHP.
2.0 PRESENT STUDY REQUIREMENT
Total forest land requirement for the project is 75.304 ha. The final approval for
diversion of Forest Land for Bajoli Holi HEP was granted by MoEF on 26th Oct 2012 and
sanction for diversion of forest land by Department of Forest, Himachal Pradesh on 28th
Jan 2013.
Condition no 5 in both approvals read as “The user agency shall set up Ecological
Monitoring Unit to monitor the impact of the project on flora and fauna of the area”.
In compliance to approval accorded line with this the Ecological Monitoring Unit was
established at project site. The Unit composed of following team members.
Sl No Members for Ecological Monitoring Unit Alternative Members
1 Mr. Anil Bhatnagar Project Director Mr. Narinderkumar Mahajan
2 Mr. Shivarama M. S Head of EHS at Corporate office
Mr. Vivek Sadevra Corporate Environment Team
3 Mr. Radheyshyam Yadav Project site Environment Team
Mr. Mahesh Khatodia Project site Environment Team
The Ecological Monitoring Report for the year 2013 was submitted to DFO, Bharmour,
Himachal Pradesh on 13th May 2014.
Ecological Monitoring Report of Bajoli Holi HEP – 2014
Page 3 of 20
3.0 EIA & EMP STUDIES OF PROJECT
The EIA & EMP Report is prepared on the basis of approved ToR from the MoEF and the
Environmental Clearance was accorded by MoEF on 24th Jan 2011.
The baseline survey for the EIA of proposed Bajoli Holi H. E. project was carried out in
three seasons viz. Pre monsoon (April - May 2008), Monsoon (August 2008) and winter
(November 2008).
Floristic Diversity
During EIA studies the floristic diversity was represented by 272 flowering plant species
from the study area (10km radius from project site). 272 plant species is further divided
into 28 trees, 48 shrubs, 10 climbers and 186 herbs. The Betulaceae and Pinaceae are
the dominant families in the trees with four species each, shrubs layer is dominated by
the Rosaceae, Fabaceae and Lamiaceae. The herbaceous vegetation was dominated by
Poaceae, Cyperaceae and Asteraceae. Gymnosperms are represented by single family
Pinaceae.
None of the species recorded from project area during EIA Studies falls under rare,
endangered and threatened plants of the Red Data Book (RDB) of India (Nayar & Sastry
1987-90) categories of Indian plants.
Faunal Elements
During three seasons study for EIA 5 species of mammals, 122 birds, 4 harpetofauna, 33
insects and 35 butterfly species are recorded.
Out of the 5 mammal species recorded during EIA studies, 2 are listed under Schedule I
and 3 species under Schedule II of Wild Life (Protection) Act, 1972.
4.0 PROJECT AREA
The Bajoli Holi H. E. Project is located near the Bajol and Holi village in the Chamba
District of Himachal Pradesh. The project falls under the Holi sub-division of Bharmour
Tehsil Forest Division. The area around the proposed project is located in the Lesser
Himalaya in Ravi Basin and is characterized by sharp crested ridges and deeply dissected
valleys.
Ecological Monitoring Report of Bajoli Holi HEP – 2014
Page 4 of 20
Figure 1.1: Project area
5.0 METHODOLOGY
The ecological survey was carried in the month of September 2014 to enlist the Floristic
and Faunal wealth of project area. The methodology followed for the sampling of
floristic and faunal diversity is discussed below.
Forest Types and Forest Cover
The details on forest types in the project area were based on field surveys in the area
supplemented with the working plans of the forest divisions of the area. The major
forest types, sub-tropical, temperate, sub-alpine and alpine, encountered in the area
were described based on the classification of Champion and Seth (1968), Bharmaur
Division Forest Working Plan.
Floristic Composition
The detailed account of floristic composition has been described based on the primary
surveys in the project area. The field sampling was carried in the month of August 2013
to enlist the Floristic diversity. The plant species recorded from the project area were
identified based on the regional floras.
Ecological Monitoring Report of Bajoli Holi HEP – 2014
Page 5 of 20
Faunal Diversity
The faunal study based on direct sighting and indirect evidences such as calls, signs and
trophies of mammals were recorded in the project area.
6.0 FOREST TYPE IN PROJECT AREA
12/C1c Moist Deodar Forest
Moist Deodar forests are dominant in the study area. The left bank of the Ravi River
shows such type of forest at elevation varying from 1700m to 2500m. As the elevation
increases the Cedrus deodara shows clear patch. Some blue pine (Pinus wallichiana) also
found mixed. At the lower altitude Deodar forest mixed with Quercus semecarpifolia,
Populus ciliata, etc. The under growth consists of Coriaria nepalensis, Cotoneaster
microphyllus, Daphne retusa, Desmodium elegans, Rabdosia rugosa, Rhamnus
purpureus, Sorbaria tomentosa, Wikstroemia canescens, etc.
12/C1d Western Mixed Coniferous Forest
These are mixed coniferous forest of Pinus wallichiana, Picea smithiana and Cedrus
deodara. These types of forest occur between the altitudinal zones of 2000m to 3500m.
This type of forest recorded near Urna to Dhardi village on the left bank of the Ravi
River.
12/C1e Moist Temperate Forest
Moist temperate forests are found from an elevation of 1800m to 2750m. Due to moist
condition the conifers not found in this area and dominated by deciduous species. The
predominant species are Aesculus indica, Corylus jacquemontii, Acer caesium, Juglans
regia, Picea smithiana, Abies pindrow, etc. These types of forest are common near the
road side from Gharo to Deol village.
12/C2a Quercus semecarpifolia (Ban Oak) Forest
The Quercus semecarpifolia is the dominant species followed by Pinus wallichiana,
Cedrus deodara and Acer caesium. These types of forest are recorded near power house
area and Deol to Holi village on the left bank of Ravi River.
12/1S1 Alnus nepalensis Forest
Alnus nepalensis occurs in pure patches especially near the banks of Ravi River. The
associate species are Populus ciliata, Celtis australis and Quercus semecarpifolia. This
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forest recorded near power house area and downstream to dam site near Gharo, Deol
and Holi village.
7.0 FLORISTIC COMPOSITION IN STUDY AREA
7.1 Taxonomic Diversity
206 plant species recorded from the project area. This includes 21 trees, 38 shrubs, 6
climbers, 123 herbs, 6 pteridophytes, 5 Lichens, 4 bryophytes and 4 Fungi. The detailed
list of plant species recorded during the ecological survey is given in Table 1.1.
Figure 1.2: Floristic Composition in Project Area
7.2 Vegetation Profile of Study Area
7.2.1 Dam Site and Submergence Area
The Right bank of river is south facing with moderate to steep slope and receives
maximum sunlight and also covered with grasses. The trees and shrubs are sparse on
right bank and only grow near the shady areas. The common grasses are Bromus
10%
18%
3%
60%
3%2%2%2%
Trees Shrubs Climbers Herbs
Pteridophytes Lichens Bryophytes Fungi
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japonicas, Cymbopogon distans, Microstegium nudum, Poa alpine, Poa nepalensis,
Paspalum paspaloides, etc.
The left bank represented by the Moist Deodar Forest, dominated by the Cedrus
deodara and Pinus wallichiana. The middle canopy was totally absent in forest and only
represented by the shrubs and herbs. Cotoneaster microphyllus, Daphne retusa,
Desmodium elegans, Girardinia diversifolia, Indigofera heterantha, Rubus ellipticus,
Sorbaria tomentosa and Wikstroemia canescens are the common shrubs species. The
herbaceous layer represented by Anaphalis triplinervis, Cirsium arvense, Galium vernum,
Mentha longifolia, Prunella vulgare, Salvia lanata and Viola pilosa.
7.2.2 Downstream of Dam Site
The right bank remains covered with grass throughout the area. Left bank shows varied
type of vegetation from Nayagram to Holi because of altitudinal gradient. Cedrus
deodara was frequent near the Nayagram village with Pinus wallichiana, Aesculus indica,
Lyonia ovalifolia, Pyrus pashia and Salix karelinii.
From Nayagram to Gharo the tree canopy is dominated by the Cedrus deodara and
Pinus wallichiana on higher elevation and Alnus nepalensis near the river bank mixed
with Pinus wallichiana, Populus ciliata and Salix karelinii. Moist deciduous forest
recorded near Gharo to Deol having species composition of Cedrus deodara and Pinus
wallichiana. Quercus semecarpifolia forest is observed near the Deol to Holi village and
further up to the Tayari village with some patches of Alnus nepalensis near the helipad
area.
7.2.3 Power House Area
The power house is on the left bank of the Ravi River and right bank of Kee nala near the
Tayari village. This area is covered with the Ban oak forest dominated by Quercus
semecarpifolia with few trees of Cedrus deodara, Pinus wallichiana. The Alder (Alnus
nepalensis) forest is present only near the river side. Desmodium elegans, Wikstroemia
canescens, Rabdosia rugosa, Deutzia compacta, Lonicera quinquelocularis, Sorbaria
tomentosa, Cotoneaster microphyllus, Indigofera heterantha, etc. represent the shrub
layer. The common herbaceous species found are Anaphalis triplinervis, Echinops
cornigerus, Salvia moorcroftiana, Poa annua, Mentha arvensis, Inula royleana,
Campanula latifolia, Phytolacca acinosa, Pimpinella acuminata, etc.
8.0 FAUNAL DIVERSITY
The faunal diversity study was carried out in the project area. The project area was
divided into different strata based on vegetation and topography. The transect sampling
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for mammals, birds and reptiles were not possible in project area due to difficult terrain,
hence trails were used for faunal diversity study. The trails were studies along the active
project construction areas and undisturbed areas.
During the survey 1 mammal, 27 birds, 3 reptiles, 11 butterflies, 4 dragonflies and 17
insects species are recorded from the project area. The detailed list of recorded faunal
diversity is given in Table 1.2 to 1.7.
Figure 1.3: Faunal Composition in Project Area
9.0 IMPORTANT SPECIES OF CONSERVATION IMPORTANCE RECORDE DURING
STUDY
No plant species of conservation importance were recorded form the project area.
In faunal diversity Rhesus Macaque is enlisted in Schedule II of Wildlife Protection Act,
1972 (WPA, 1972) and Least concern in IUCN Red List (Ver. 3.1).
The birds like Himalayan Woodpecker, Plum-headed Parakeet, Red-Vented Bulbul and
Rock Bunting listed are in Schedule IV and Common Crow under Schedule V of WPA,
1972.
10.0 WAY FORWARDS
Based on the first Ecological Survey following steps will be implemented during the next
year monitoring.
1. Seasonal monitoring for flora and fauna
0
5
10
15
20
25
30
Mammals Avifauna Reptiles Butterflies Dragonflies OtherInsects
Nu
mb
er
of
Spe
cie
s
Faunal Diversity
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2. Involvement of locals in the ecological monitoring to understand the their issues and
suggestion
3. Organization of flora and fauna conservation and awareness camps in schools.
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PHOTOGRAPHS OF FLORA AND FAUNA RECORDED DURING SURVEY
Herbs recorded from Project Area
Berberis angulosa (Shrub) Alnus nepalensis (Tree)
Geranium wallichianum Anemone vitifolia
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Butterflies recorded from Project Area
Large Hedge Blue (Celastrina huegelii) Great Satyr (Auocera padma)
Birds recorded from Project Area
Common Hoopoe Grey Bushchat
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Oriental White-eye White Wagtail
Plumbeous Water Redstart White-capped Water Redstart
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LIST OF FLORA AND FAUNA RECORDED DURING SURVEY
Table 1.1: List of Plants Recorded from the Project Area
Trees
Sr. No. Family Botanical Name
1 Aceraceae Acer caesium
2 Anacardiaceae Rhus javanica
3 Betulaceae Alnus nepalensis
4 Betulaceae Alnus nitida
5 Betulaceae Betula utilis
6 Betulaceae Corylus jacquemontii
7 Cupressaceae Cupressus torulosa
8 Fagaceae Quercus leucotrichophora
9 Fagaceae Quercus semecarpifolia
10 Juglandaceae Juglans regia
11 Meliaceae Toona serrata
12 Moraceae Morus serrata
13 Oleaceae Fraxinus micrantha
14 Pinaceae Cedrus deodara
15 Pinaceae Pinus wallichiana
16 Rosaceae Pyrus pashia
17 Salicaceae Populus ciliata
18 Salicaceae Salix denticulata
19 Sapindaceae Aesculus indica
20 Ulmaceae Celtis australis
21 Ulmaceae Ulmus villosa
Shrubs
Sr. No. Family Botanical Name
1 Agavaceae Agave americana
2 Acanthaceae Barleria cristata
3 Acanthaceae Pteracanthus alatus
4 Amaranthaceae Cyathula tomentosa
5 Asteraceae Artemisia roxburghiana
6 Asteraceae Artemesia dubia
7 Berberidaceae Berberis angulosa
8 Buxaceae Sarcococca saligna
10 Caprifoliaceae Abelia triflora
11 Caprifoliaceae Lonicera quinquelocularis
12 Coriariaceae Coriaria napalensis
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13 Elaeagnaceae Elaeagnus parvifolia
14 Ericaceae Lyonia ovalifolia
15 Fabaceae Astragalus chlorostachys
16 Fabaceae Desmodium elegans
17 Fabaceae Desmodium multiflorum
18 Fabaceae Indigofera heterantha
19 Fabaceae Lespedeza juncea
20 Hydrangeaceae Deutzia compacta
21 Loganiaceae Buddleja asiatica
22 Rosaceae Cotoneaster bacillaris
23 Rosaceae Cotoneaster microphyllus
24 Rosaceae Prinsepia utilis
25 Rosaceae Sorbaria tomentosa
26 Rosaceae Spiraea canascens
27 Rosaceae Rosa brunonii
28 Rosaceae Rubus ellipticus
29 Rosaceae Rubus foliolous
30 Rosaceae Rubus niveus
31 Rubiaceae Leptodermis lanceolata
32 Rutaceae Zanthoxylum armatum
33 Saxifragaceae Deutzia compacta
34 Solanaceae Datura stramonium
35 Thymelaeaceae Daphne mucronata
36 Thymelaeaceae Wikstroemia canescens
37 Urticaceae Girardinia diversifolia
38 Urticaceae Urtica dioica
Herbs
Sr. No. Family Botanical Name
1 Amaranthaceae Achyranthes bidentata
2 Amaranthaceae Amaranthus hybridus
3 Amaranthaceae Chenopodium album
4 Apiaceae Bupleurum falcatum
5 Apiaceae Heracleum canescens
6 Apiaceae Pimpinella acuminata
7 Araceae Arisaema concinnum
8 Araceae Arisaema intermedium
9 Asteraceae Adenocaulon himalaicum
10 Asteraceae Anaphalis contorta
11 Asteraceae Anaphalis triplinervis
12 Asteraceae Arctium lappa
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13 Asteraceae Artemisia capillaris
14 Asteraceae Bidens pilosa
15 Asteraceae Cichorium intybus
16 Asteraceae Cirsium arvense
17 Asteraceae Cirsium falconeri
18 Asteraceae Erigeron alpinus
19 Asteraceae Inula cuspidata
20 Asteraceae Lactuca lessertina
21 Asteraceae Senecio chrysanthemoides
22 Asteraceae Tagetes minuta
23 Asteraceae Taraxacum officinale
24 Balsaminaceae Impatiens brachycentra
25 Balsaminaceae Impatiens edgeworthii
26 Balsaminaceae Impatiens glandulifera
27 Balsaminaceae Impatiens sulcata
28 Balsaminaceae Impatienssp.
29 Boraginaceae Cynoglossum glochidiatum
30 Boraginaceae Cynoglossum lanceolatum
31 Brassicaceae Arabis amplexicaulis
32 Brassicaceae Erysimum hieraciifolium
33 Campanulaceae Campanula pallida
34 Cannabaceae Canabis sativa
35 Caryophyllaceae Cerastium davuricum
36 Caryophyllaceae Silene viscosa
37 Caryophyllaceae Stellaria media
38 Crassulaceae Sedum multicaule
39 Cyperaceae Bulbostylis barbata
40 Cyperaceae Carex alpina
41 Cyperaceae Carex cruenta
42 Cyperaceae Carex foliosa
43 Cyperaceae Carex nubigena
44 Cyperaceae Carex psychrophila
45 Cyperaceae Carex remota
46 Cyperaceae Cyperus flavidus
47 Cyperaceae Cyperus nutans
48 Cyperaceae Eriophorum comosum
49 Dipsacaceae Dipsacus inermis
50 Euphorbiaceae Euphorbia hirta
51 Fabaceae Astragalus chlorostachys
52 Fabaceae Lespedeza juncea
53 Fabaceae Lotus corniculatus
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54 Fabaceae Trifolium repens
55 Fabaceae Trigonella corniculata
56 Geraniaceae Geranium lucidum
57 Hypericaceae Hypericum oblongifolium
58 Lamiaceae Ajuga parviflora
59 Lamiaceae Clinopodium vulgare
60 Lamiaceae Isodon rugosus
61 Lamiaceae Leucas lanata
62 Lamiaceae Leucas lanata
63 Lamiaceae Mentha longifolia
64 Lamiaceae Nepeta laevigata
65 Lamiaceae Rabdosia rugosa
66 Lamiaceae Salvia lanata
67 Lamiaceae Salvia moorcroftiana
68 Lamiaceae Thymus linearis
69 Malvaceae Malva verticillata
70 Onagraceae Epilobium parviflorum
71 Onagraceae Oenothera rosea
72 Orchidaceae Spiranthes sinensis
73 Orobanchaceae Leptorhabdos parviflora
74 Orobanchaceae Orobanche alba
75 Oxalidaceae Oxalis corniculata
76 Phytolaccaceae Phytolacca acinosa
77 Plantaginaceae Plantago himalaica
78 Poaceae Acrachne racemosa
79 Poaceae Agrostis canina
80 Poaceae Agrostis pilosula
81 Poaceae Bothriochloa kuntzeana
82 Poaceae Bromus japonicus
83 Poaceae Bromus mollis
84 Poaceae Chrysipogon echinulatus
85 Poaceae Cymbopogon distans
86 Poaceae Cynodon dactylon
87 Poaceae Digitaria stricta
88 Poaceae Eleusiana coracena
89 Poaceae Festuca valesiaca
90 Poaceae Microstegium nudum
91 Poaceae Miscanthus nepalensis
92 Poaceae Oplismenus undulatifolius
93 Poaceae Panicum miliaceum
94 Poaceae Paspalum paspaloides
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95 Poaceae Phacelurus speciosus
96 Poaceae Poa alpina
97 Poaceae Poa annua
98 Poaceae Poa augustifolia
99 Poaceae Poa nepalensis
100 Poaceae Poa supina
101 Poaceae Poa trivialis
102 Polygonaceae Fagopyrum dibotrys
103 Polygonaceae Polygonum aviculare
104 Polygonaceae Rumex hastatus
105 Polygonaceae Rumex nepalensis
106 Ranunculaceae Anemone vitifolia
107 Ranunculaceae Aquilegia moorcroftiana
108 Ranunculaceae Delphinium denudatum
109 Ranunculaceae Thalictrum elegans
110 Rosaceae Fragaria nubicola
111 Rosaceae Fragaria vestita
112 Rosaceae Potentilla utilis
113 Rubiaceae Galium sp.
114 Rubiaceae Galium verum
115 Saxifragaceae Bergenia ciliata
116 Scrophulariaceae Leptorhabdos parviflora
117 Scrophulariaceae Verbascum thapsus
118 Solanceae Solanum nigrum
119 Solanceae Solanum pseudo-capsicum
120 Urticaceae Pilea umbrosa
121 Violaceae Viola betonicifolia
122 Violaceae Viola pilosa
123 Acanthaceae UDI
Pteridophytes
Sr. No. Family Botanical Name
1 Aspleniaceae Asplenium adiantum-nigrum
2 Equisetaceae Equisetum arvense
3 Polypodiaceae Pleopetis clathrata
4 Polypodiaceae Pleopetis excavata
5 Polypodiaceae Pleopetis loriformis
6 Pteridaceae Adiantum caudatum
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Climbers
Sr. No. Family Botanical Name
1 Cucurbitaceae Solena heterophylla
2 Cuscutaceae Cuscuta reflexa
3 Dioscoreaceae Dioscorea deltoidea
4 Oleaceae Jasminum humile
5 Ranunculaceae Clematis connata
6 Rubiaceae Rubia cordifolia
Lichens
Sr. No. Family Botanical Name
1 Acarosporaceae Piccolia sp.
2 Buelliaceae Buellia sp.
3 Parmeliaceae Parmelia sp.
4 Physciaceae Heterodermia sp.
5 Usneaceae Usnea sp.
Bryophytes
Sr. No. Family Botanical Name
1 Funariaceae Funaria hygrometrica
2 Polytrichaceae Pogonetum microstomum
3 Polytrichaceae Polytrichum densifolium
Fungi
Sr. No. Family Botanical Name
1 Cyphellaceae Chondrostereum purpureum
2 Atheliaceae Amphinema byssoides
3 Atheliaceae Athelia decipiens
4 Amanitaceae Amanita sp.
Table 1.2: List of Mammals
Sr. No. Common Name Scientific Name WPA, 1972 IUCN
1 Rhesus Macaque Macaca mulatta Schedule II LV
Table 1.3: List of Avifauna
Sr. No. Common Name Scientific Name WPA, 1972
1 Ashy Drongo Dicrurus leucocephaeus
2 Black Bulbul Hypsipetes leucocephalus
3 Black Drongo Dicrurus macrocerus
4 Blue Rock Pigeon Columba livia
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5 Common Crow Corvus corax Schedule V
6 Common Hoopoe Upupa epops
7 Eurasian Blackbird Turdus obscurus
8 Great Barbet Megalaima virens
9 Greenish Warbler Phylloscopus trochiloides
10 Grey Bushchat Saxicola ferreus 11 Grey Wagtail Motacilla cinerea
12 Himalayan Bulbul Pycnonotus jocosus
13 Himalayan Griffon Gyps fulvus
14 Himalayan Woodpecker Dendrocopos himalayensis Schedule IV
15 House Crow Corvus splendens
16 House Sparrow Passer domesticus
17 Hume's Warbler Phylloscopus humei
18 Oriental Turtle Dove Streptopelia orientalis
19 Oriental White-eye Zosterops palpebrosus
20 Plumbeous Water Redstart Rhyacornis fuliginous
21 Plum-headed Parakeet Pisttacula cyanocephala Schedule IV
22 Red-Vented Bulbul Pycnonotus cafer Schedule IV
23 Rock Bunting Emberiza fucata Schedule IV
24 Russet Sparrow Passer rutilans
25 White Wagtail Motacilla alba 26 White-capped Water Redstart Chaimarrornis leucocephalus
27 Yellow Wagtail Motacilla flava
Table 1.4: List of Reptiles
Sr. No. Common Name Zoological Name
1 Kashmir Agama Laudakia tuberculata
2 Toad Agama Phyrnocephalus theobaldi
3 Snake Skink Lygosoma punctatus
Table 1.5: List of Butterflies
Sr. No. Common Name Scientific Name
1 Blue Admiral Kaniska canace
2 Chestnut Tiger Parantica sita
3 Chocolate Pansy Junonia iphita
4 Large Hedge Blue Celastrina huegelii
5 Indian Cabbage White Pieris canidia
6 Lemon Pansy Junonia lemonias
7 Green Commodore Sumalia daraxa
8 Himalayan Sergent Athyma oplina
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9 Common Fivering Ypthima baldus
10 Common Argus Callerebia nirmala
11 Great Satyr Auocera padma
Table 1.6: List of Dragonflies
Sr. No. Common Name Scientific Name
1 Common Darter Sympetrum striolatum
2 Common Hawker Othetrum coerulescens
3 Scarlet Darter Crocothemis erythraia
4 Scarlet Skimmer Crocothemis servlia
Table 1.7: List of insects
Sr. No. Common name Scientific name
1 Blue Banded Bee Amegilla cingulata
2 Brown Prionid Orthosoma brunneum
3 Burying Mantid Sphodropoda sp.
4 Caleda Caleda captiva
5 Common Long Winged Beefly Complosia sp.
6 Eastern Golden Haired Blowfly Calliphora stygia
7 Floer Feeding Marsh Fly Scaptia auriflua
8 Froggatt's Buzzer Froggattina austratis
9 Grasshopper -
10 Green Shield Bug Palomena prasina
11 Honey Bee Apis sp.
12 Jewel Beetle Chrysochroa sp.
13 Robber Fly Promaschus ruficeps
14 Spider Feeder Robber Fly Leptogaster sp.
15 Spider Predator Robber Fly Ommatius sp.
16 Vinegar Fly Drosophila sp.
17 Yellow Winged Locust Gastrimargus musicus