stage.adaniports.com · 2019. 6. 18. · Adani Ports and Special Economic Zone Limited, Mundra....

Environmental Clearance Compliance Report

of

Waterfront Development Project,

Mundra, Dist. Kutch, Gujarat

of

Adani Ports and SEZ Limited

for Period:

April-2015 to September-2015

Adani Ports and Special Economic Zone Limited, Mundra.

From : April,15 To : September,15

Status of the conditions stipulated in Environment and CRZ Clearance

Index

Sr. No.

Particulars Page Nos.

1 Compliance Report 1 2 Annexures

Annexure – A Compliance Report of GCZMA Recommendation 10 Annexure – 1 Details of PILs Filed and Replies 14 Annexure – 2 Summary of Environmental Monitoring Reports 15 Annexure – 3 GPCB sample analysis report 103 Annexure – 4 Map showing reclamation area 104 Annexure – 5 Mangrove afforestation details 105




Compliance Report of Environment Clearance




Activities/facilities approved, major components completed and proposed future activities as per Environment/CRZ Clearance are as below:

Description (Type of

Facility or Berth*)

Approved Berths or Length as per

Environmental/CRZ Clearance

So far Developed and In Operation

To be Developed as per

Environmental/CRZ Clearance

Nos. of Berths or Length

Nos. of Berths Nos. of Berths/Facilities

Multipurpose 4 (550 m + 2 Berths)

4

-

Container 16 (2680 m + 2000 m)

3

13*

Ro-Ro 2 - 1

Coal 6 4

2

Dry-Bulk Cargo 5 - 5

Liquid 9 - 9

LNG 2 Is being developed by GSPC LNG Limited as per NOC given by APSEZL.

-

Light & Heavy Engineering

2 - 2

Port Craft 1 (330 m)

- 1

Shipyard 2 - 2

* Construction activity for extending quay length of container terminal @ 1300 Meter (from which 516.5 meter is already constructed) is going on.

In addition to above berths or facilities, following components were also granted. 1. Out of 210 Million Cubic Meter dredging quantity approved, we have dredged 123

Million Cubic Meter is completed till September 2015.

2. Back-up area, back-up facilities like railway line, rail slidings, rail truck loading, open

paved areas, associated buildings, utilities, amenities, etc. and connectivity to rail and

road corridor for each port were approved and majority of them are constructed and

in operation.

Seawater intake channel and outfall channel for power plants, desalination plants and other industrial requirements approved and is already in operation.

1




Half yearly Compliance report for Environment and CRZ Clearance for the project “Water Front Development Project at Mundra, Dist. Kachchh, Gujarat of M/s. Adani Ports and SEZ Limited”

Sr.

No. Specific Conditions

Compliance Status as on

30-09-2015

Specific Conditions

i No existing mangroves shall be destroyed during construction / operation of the Project.

Complied. Details submitted to the Ministry of Environment and forest along with half yearly compliance dated 02.12.2013.

ii There shall be no filling up of the creek and reclamation of the creeks.

Complied. All creeks are free flowing and there is no filling or reclamation of any creek area. Details submitted to the Ministry of Environment and forest along with half yearly compliance dated 02.12.2013.

iii The Project proponent shall comply with all the Orders/directions of the Honorable High Court of Gujarat and Supreme Court in the matter.

Details of all PILs filed against the project and their replies are summarized in Annexure – 1.

iv Adequate safety measures for the offshore structure and ship navigation shall be taken in view of the High Current in the area.

Complied. Details submitted to the Ministry of Environment and forest along with half yearly compliance dated 02.12.2013 & 29.05.2014.

v The shore line changes in the area shall be monitored periodically and the report submitted every 6 months to Regional Office Bhopal.

Shoreline changes study is being carried out.

vi The recommendations of the risk assessment shall be implemented; Any change in the design of the Project shall come before the committee for seeking necessary approval.

Dedicated Liquid Berths are yet not developed. Recommendations of Risk Assessment will be implemented once it is developed. LNG terminal is being developed by GSPC LNG Ltd. for which, separate EC has been obtained.

vii Mangrove plantation of 200 ha to be done in consultation with GEER/GEC of Forest Department, a detailed plan shall be submitted within six months from the date of receipt of this letter.

Details submitted to the Ministry of Environment and forest along with half yearly compliance dated 02.12.2013.

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viii It shall be ensured that during construction and post construction of the proposed jetty the movement of fishermen vessel of the local communities are not interfered with.

Fishing boats are having unhindered access to Gulf of Kutchh.

ix Relocation of the fishermen community if any shall be done strictly in accordance with the norms prescribed by the State Government.

There is no relocation of fishermen communities.

x Marine ecology monitoring shall be done regularly during construction of breakwater and dredging/disposal operation.

Third party marine monitoring is being carried out by NABL and MoEF accredited agency namely Pollucon Laboratory, Surat regularly. Summary of monitoring reports for duration from April’15 to September’15 are enclosed as Annexure – 2. Marine monitoring for west port area has been carried out by M/s. Adani Power Limited. Monitoring reports are also enclosed as Annexure – 2.

xi Regular Monitoring of air quality shall be done in the settlement areas around the Project site and appropriate safeguard measures shall be taken.

Ambient Air Quality Monitoring is being carried out in the settlement area around the project site. Third party ambient air quality monitoring is being carried out by NABL and MoEF accredited agency namely Pollucon Laboratory, Surat. Summary of monitoring reports for duration from April’15 to September’15 are enclosed as Annexure – 2.

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xii Sewage arising in the Port area shall be disposed off after adequate treatment to conform to the standards stipulated by Gujarat State Pollution Control Board and shall be utilized / recycled for Gardening, Plantation and Irrigation.

Sewage generated from port is being treated and treated sewage is used for gardening. Third party monitoring is being carried out by NABL and MoEF accredited agency namely Pollucon Laboratory, Surat. Summary of monitoring reports for duration from April’15 to September’15 are enclosed as Annexure – 2. Sewage generated from the west port area is being sent to STPs of Shantivan Colony for treatment and treated water is being used on land for horticulture purpose within shantivan colony premises, GPCB sample analysis report of the same is enclosed as Annexure – 3.

xiii Adequate Plantation shall be carried out along the roads of the Port premises and a green belt shall be developed.

APSEZL has adopted a strategy to develop an eco-friendly port as well as greeneries across its ports and back up areas. For that purpose, APSEZL has developed its own “Dept. of Horticulture” and is taking better measures/steps to improving environment. So, far APSEZL have developed total 301.80 ha area as green belt with plantation of 597855 saplings.

xiv There shall be no withdrawal of Ground Water in CRZ area, for this Project.

Complied. Source of water: Desalination plant of APSEZL or Narmada water through Gujarat Water Infrastructure Limited.

xv Specific arrangements for rain water harvesting shall be made in the Project design and the rain water so harvested shall be optimally utilized. Details in this regard shall be furnished to this Ministry’s Regional Office at Bhopal within 3 months.


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xvi Land Reclamation shall be carried out only to the extent that it is essential for this Project.

Out of approved reclamation area of 1138 ha for west port, 695 ha area is reclaimed and out of approved reclamation area of 700 ha for south port, 665 ha area is reclaimed till September 2015. Approved dredging quantity is 210 Mm3 out of which total 123 Mm3 is completed till September 2015. This dredged material is used for reclamation (of port back up area) as well as for level raising (of the port back up area, road/rail/ transport/utility corridor and SEZ developable area). Please refer Annexure – 4 for the map showing reclamation area.

xvii No Product other than those permissible in the Coastal Regulation Zone Notification, 1991 shall be stored in the Coastal Regulation Zone area.

Point noted and complied.

General Conditions

i Construction of Proposed structures, if any in the Coastal Regulation Zone area shall be undertaken meticulously confirming to the existing Central/local rules and regulations including Coastal Regulation Zone Notification 1991 and its amendments. All the construction designs/ drawings relating to the proposed construction activities must have approvals of the concerned State Government Departments/ Agencies.

Being complied.

ii Adequate provision for infrastructure facilities such as water supply, fuel, sanitation etc. shall be ensured for construction workers during the construction phase of the project so as to avoid felling of trees/mangroves and pollution of water and the surroundings.


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iii The project authorities must make necessary arrangements for disposal of solid wastes and for the treatment of effluents by providing a proper wastewater treatment plant outside the CRZ area. The quality of treated effluents, solid waste, and noise level etc. must conform to the standards laid down by the competent authorities including the Central/ State Pollution Control Board and the Union Ministry of Environment and Forests under the Environment (Protection) Act, 1986, whichever are more stringent.

Sewage generated from port is being treated and treated sewage is used for gardening. All attributes of environment, viz. air; water; soil; noise are being regularly analyzed and summary of analytical reports are attached as Annexure – 2. These reports depict that all parameters are within prescribed norms. APSEZL adopt 5R concept for environmentally sound management of different types of solid & liquid waste. Municipal Solid Waste - A well-established system for segregation of dry & wet waste is in place, by which all wet waste (Organic waste) is being segregated & utilized for compost manufacturing; compost is further used by in house horticulture team for green belt development. Whereas Dry Recyclable Waste - is being sorted out in various categories & finally being sent for recycling. E- Waste & Used Batteries - Is being sold to registered recycler. Solid Hazardous Waste - is being disposed through common facility i.e. CHWIF. Used/Waste Oil - It is being sold to authorized recycler/reprocesser.

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iv The Proponent shall obtain the requisite consents for discharge of effluents and emissions under the Water (Prevention and Control of pollution) Act, 1974 and the Air (Prevention and Control of pollution) Act, 1981 from the Gujarat Pollution Control Board before commissioning of the Project and copy of each of these shall be sent to this Ministry.

Details submitted to the Ministry of Environment and forest along with half yearly compliance dated 02.12.2013. Consent to Operate (CtO) for south port is merged along with existing port vide Letter no. PC/CCA-KUTCH-39(2)/GPCB ID: 17739 /218894 dated 16.07.2014.

v The sand dunes, corals, and mangroves, if any, on the site shall not be disturbed in any way.

Point noted & complied with.

vi A copy of the clearance letter will be marked to the concerned Panchayat / Local NGO, if any from whom any suggestions /representations has been received while processing the proposal.


vii The funds earmarked for environment protection measures shall be maintained in a separate account and there shall be no diversion of these funds for any other purpose. A year wise expenditure on environmental safeguards shall be reported to this Ministry’s Regional Office at Bhopal and the State Pollution Control Board.

Separate budget for the Environment cell is earmarked every year. All environmental and horticulture activities are considered at group level and budget allocation is also done accordingly. The plan budget for Environment Cell for the year 2015-16 is 484.11 lacs. The spent budget for Environment Cell up to Sep-2015 is 175.88 lacs. The plan budget of Horticulture Cell for the year 2015-16 is 486.83 lacs. The spent budget of Horticulture Cell up to Sep-2015 is 363.29 lacs.

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viii Full support shall be extended to the Officers of this Ministry’s Regional Office at Bhopal and the Officers of the Central and State Pollution Control Boards by the Project Proponents during their inspection for monitoring purposes, by furnishing full details and action plans including the action taken reports in respect of mitigative measures and other environmental Protection activities.

APSEZL is always extending full support to the regulatory authorities.

ix In case of deviation or alteration in the Project including the implementing agency, a fresh reference shall be made to this Ministry for modification in the clearance conditions or imposition of new ones for ensuring environmental protection.

Point noted.

x The Ministry reserves the right to revoke this clearance, if any of the conditions stipulated are not complied with to the satisfaction of this Ministry.

Point noted.

xi This Ministry or any other competent authority may stipulate any other additional conditions subsequently, if deemed necessary, for environmental protection which shall be complied with.

Point noted.

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xii The project proponent shall advertise at least in two local newspapers 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 letters are available with the State Pollution Control Board and may also be seen at the website of the Ministry of Environment & Forest at http://www.envfornic.in. The advertisement shall be made within 7 days from the date of issue of the clearance letter and a copy of the same shall be forwarded to the Regional Office of this Ministry at Bhopal.


xiii The Project proponent shall inform the Regional Office at Bhopal as well as the Ministry the date of financial closure and final approval of the Project by the concerned authorities and the date of start of land development work.

Complied.

xiv Any appeal against this environmental clearance shall lie with the National Environment Appellate Authority, if preferred, within period of 30 days as prescribed under section 11 of the National Environment Appellate Act, 1997.

Point noted.

9




ANNEXURE A CRZ Recommendation Compliance

Report of WFDP




Compliance Status of CRZ Recommendation given by GCZMA for the Waterfront Development Project

Sr.



30-09-2015

Specific Conditions

1 The provisions of the CRZ notification of 1991 and subsequent amendments issued from time to time shall be strictly adhered to by the MPSEZL. No activity in contradiction to the provisions of the CRZ Notification shall be carried out by the MPSEZL.


2 All necessary permissions from different Government Departments/ agencies shall be obtained by the MPSEZL before commencing any activities.

Point noted and complied. Necessary permissions from competent authority have been obtained before commencing any the activities.

3 All major creeks shall be protected and no reclamation shall be done in these creeks and entire development along the creek shall be done after carrying out detailed engineering with an objective of environmental protection including protection of all major creeks to ensure adequate free flow of water and drainage of rain water during rainy seasons.

All creeks are free flowing and there is no filling or reclamation of any creek area. Details submitted to the Ministry of Environment and forest along with half yearly compliance dated 02.12.2013.

4 The project proponent shall conserve the 1254 ha. of area as committed and proposed in their master plan and shall carry out plantation of various mangrove species in the said area.

Complied. Mangrove afforestation details are attached as Annexure – 5.

5 Massive mangroves plantation activity in at least 300 ha. area shall be carried out within a time frame of 5 years as committed by the project proponent. This would be in addition to the earlier commitment for 1200 ha. of mangroves plantation.

Complied. Mangrove afforestation details of APSEZ are attached as Annexure – 5.

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6 No effluent or sewage shall be discharged in to the CRZ area and it shall be treated to conform to the norms prescribed by the Gujarat Pollution Control Board and would be discharged to the point suggested by the NIO in consultation with the GPCB.

Sewage generated from port is being treated and treated sewage is used for gardening. Third party monitoring is being carried out by NABL and MoEF accredited agency namely Pollucon Laboratory, Surat. Summary of monitoring reports for duration from April’15 to September’15 are enclosed as Annexure – 2.

7 All the recommendations and suggestions given by NIO in their Environment Impact Assessment report for conservation / protection and betterment of environment shall be implemented strictly by MPSEZL.

Point noted & being implemented.

8 The construction and operational activities as well as dredging and reclamation activities shall be carried out in such a way that there is no negative impact on mangroves and other coastal/marine habitat except the proposed approx. 63 ha, of area for which the compensation (300 ha.) is proposed.


9 The construction activities and dredging shall be carried out under the supervision/monitoring of the NIO or any such institute of repute.

Dredged material was disposed off at identified location for level raising / reclamation as per EIA study carried out by NIO with all mitigative measures as suggested.

10 The dredge material generated during capital dredging shall be used only for reclamation and that to be generated during maintenance dredging shall be disposed of at the place identified by NIO/CWPRS/WAPCOS through appropriate modeling and it shall be ensured that it does not create any negative impacts.

Point noted and complied

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11 Necessary measures including the shore protection activities shall be undertaken to ensure that there are no erosion in surrounding area due to the proposed activities.


12 The alignment of the jetties/berths and other structures shall be done after conducting the detailed modeling to ensure that there are no erosion and accretion in the region due to proposed activities.


13 The MPSEZL shall contribute financially for any common study or project that may be proposed by this department for environment management / conservation / improvement for the Gulf of Kutchh.

Point noted and will be complied.

14 The construction debris and /or any other type of waste shall not be disposed of into the sea, creek or in the CRZ areas. The construction is over and shall be disposed off in low lying areas in consultation with NIO, NEERI or any such institute of repute.

The construction debris is being disposed off for filling low lying area outside CRZ area.

15 The construction camps shall be located outside the CRZ area and the construction labour shall be provided with the necessary amenities, including sanitation, water supply and fuel and it shall be ensured that the environmental conditions are not deteriorated by the construction labors.

Compiled. Details submitted to the Ministry of Environment and forest along with half yearly compliance dated 02.12.2013.

16 The MPSEZL shall regularly update their Local Oil Spill Contingency and Disaster Management Plan in consonance with the National Oil Spill and Disaster Contingency Plan and shall submit the same to this Department after having it vetted through the Indian Coast Guard.

Oil Spill Contingency Plan & Disaster Management Plan is updated regularly. Disaster Management Plan was submitted on 02.12.2013 while Oil spill contingency plan was submitted to the Ministry of Environment and forest along with half yearly compliance dated 29.05.2014.

17 The MPSEZL shall participate and contribute for the Vessel Traffic Management System to be developed for the Gulf of Kutchh being developed.


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18 The MPSEZL shall bear the coast of external agency that may be appointed by this Department for supervision/monitoring of proposed activities and the environmental impacts of the proposed activities.

Point noted.

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ANNEXURE 1 Details of PILs Filed and Replies

Annexure – 1

A brief of the case related to WFDP is given below:

Kheti Vikas Seva Trust (an association of 200 villagers) has filed a writ petition

dated 24th January 2011 before the Gujarat HC against the state of Gujarat, our

Company, Adani Power Limited and others alleging that the power plant set up

by Adani Power Limited, on the land allotted to our Company for the setting up

of a special economic zone, is in violation of the necessary requirements for

setting up such plants, including environmental laws. The writ petition has

been dismissed by the Gujarat HC on 17th April 2015.

However, an application filed by the petitioner alleging non-compliance of an

order of the Gujarat HC dated 12th July 2011 prohibiting the cutting of

mangroves and other forests during the pendency of the petition without

permission of the state forest and environment department in relation to the

writ petition is still pending.

14




ANNEXURE 2 Summary of Environmental

Monitoring Reports From April’15 to September’15

H. T. Shah Dr. ArunBajpai Lab Manager Lab Manager (Q)

544, BelgiumTowers, Ring Road, Opp. Linear Bus Stand, Surat-395003. (Guj.).

Tele-Fax: (0261)2455751, 2601106, 2601224. E-Mail: [email protected]. Website: www.pollucon.com

“HALF YEARLY ENVIRONMENTAL MONITORING REPORT”

FOR

WATER FRONT DEVELOPMENT PROJECT [SOUTH PORT]

ADANI PORTS AND SPECIAL ECONOMIC ZONE LIMITED

TAL: MUNDRA, KUTCH, MUNDRA – 370 421

MONITORING PERIOD:

APRIL 2015 TO SEPTEMBER 2015

PREPARED BY:

POLLUCON LABORATORIES PVT.LTD.

544, BELGIUM TOWERS, RING ROAD, SURAT – 395 003 PHONE/FAX – (+91 261) 2455 751, 2601 106, 2601 224.

E-mail: [email protected] Web: www.polluconlab.com

T 0820 - 821 ISO 9001:2008 ISO 14001:2004 OHSAS 18001:2007

15

mailto:[email protected]

http://www.polluconlab.com/




MARINE WATER MONITORING SUMMARY REPORT

RESULTS OF MARINE WATER [M1 LEFT SIDE OF BOCHA CREEK - N 22°45'183" E 069°43'241"] SR. NO.

TEST PARAMETERS

UNIT

April 2015 May 2015 June 2015 July 2015 August 2015 September 2015

Test Method SURFACE

BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTO

M SURFAC

E BOTTO

M SURFAC

E BOTTO

M SURFAC

E BOTTO

M

1 pH -- 7.9 8.05 8.01 8.12 8.1 8.15 7.98 8.12 7.58 8.06 8.02 8 IS3025(P11)83

Re.02

2 Temperature oC 30 31 29 30 29 30 28 29 28 29 29 30 IS3025(P9)84R

e.02

3 Total Suspended

Solids mg/L 22 16 16 22 12 18 20 22 14 20 14 20

IS3025(P17)84Re.02

4 BOD (3 Days @ 27

oC) mg/L BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL*

IS 3025 (P44)1993Re.0

3Edition2.1

5 Dissolved Oxygen mg/L 5.4 4.8 5.8 5 5.4 4.4 5.8 4.4 5.6 4.8 5.6 4.6 IS3025(P38)89

Re.99

6 Salinity ppt 40.3 40.9 41.2 41.7 40.2 40.9 41.6 42.2 40.8 41.8 41.2 42.8 APHA (22ndEdi)

2550 B

7 Oil & Grease mg/L BDL* BDL* BDL* BDL* BDL* BDL* 0.18 BDL* 0.24 BDL* BDL* BDL* APHA(22ndEdi)

5520D

8 Nitrate as NO3 mg/L 0.72 0.89 0.56 0.72 0.34 0.52 0.42 0.58 0.54 0.62 0.532 0.598 IS3025(P34)88

9 Nitrite as NO2 mg/L 0.064 0.077 0.021 0.034 0.028 0.046 0.026 0.04 0.022 0.044 0.03 0.047 IS3025(P34)88

NEDA

10 Ammonical Nitrogen

as NH3 mg/L 0.86 0.96 0.96 1.1 1.2 1.4 1.0 1.2 0.9 1.1 0.924 1.1

IS3025(P34)88Cla.2.3

11 Phosphates as PO4 mg/L 0.056 0.074 0.084 0.096 0.94 1.04 0.88 0.94 0.72 0.84 1.03 1.215 APHA(22ndEdi)

4500 C

12 Total Nitrogen mg/L 4.1 4.7 1.54 1.85 1.31 1.606 1.45 1.84 1.61 1.82 1.486 1.745 IS3025(P34)88

13 Petroleum

Hydrocarbon mg/L 6 BDL* 4 BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* PLPL-TPH

14 Total Dissolved

Solids mg/L 49750 50440 48770 49060 47690 48140 49850 50510 48186 49760 48593 48878

IS3025(P16)84Re.02

15 COD mg/L 20 28 24 32 22 28 16 24 18 22 19 28 APHA(22ndEdi) 5520-D Open

Reflux

16 Oxidisable Particular

Organic Carbon % 0.68 0.49 0.5 0.4 0.58 0.48 0.56 0.48 0.52 0.44 0.6 0.44

SOP – PLPL - 07

16




A Flora and Fauna

17 Primary productivity mgC/L/day

3.2 2.1 2.7 1.575 2.925 0.45 2.25 0.45 1.575 0.563 1.125 0.338 APHA (22nd Edi) 10200-J

B Phytoplankton

18.1

Chlorophyll mg/m

3 3.79 2.99 2.75 0.99 2.857 1.602 1.682 0.134 1.81 0.134 1.28 0.267

APHA (22ndEdi) 10200-H

18.2

Phaeophytin mg/m

3 BDL* BDL* BDL* 1.54 BDL* 0.98 0.579 1.717 0.128 1.77 0.98 1.39


18.3

Cell Count Unit x 103/L

114 154 248 109 292 110 221 59 158 41 147 52 APHA (22nd

Edi) 10200-H

18.4

Name of Group Number

and name of group species of each

group

--

Diatom Diatom Diatom Diatom Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

APHA (22nd Edi) 10200-H

Thalassiosira

sp.

Thalassiosira sp.

Thalassionema sp.

Thalassionema sp.

Biddulphia sp.

Nitzschia sp.

Chaetocerous sp.

Fragillaria sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Navicula sp.

Gyrosigma sp

Gomphonema sp.

Rhizosolenia sp.

Navicula sp.

Rhizosolenia sp.

Gyro sigma sp.

Rhizosolenia sp.

Fragillaria sp.

Navicula sp.

Coscinodiscus

sp.

Melosira sp.

Coscinodiscus sp.

Pinnularia sp.

Cyclotella sp.

Pinnularia sp.

Cocconeis sp.

Thallasiosira sp

Cyclotella sp.

Navicula sp.

Pinnularia sp.

Melosira sp.

-- Fragillaria

sp. Rhizosolenia sp.

Pinnularia sp.

Green Algae

Navicula sp.

Cyanophyceae

Synedra sp.

Fragillaria sp.

Asterionella sp.

Biddulphia sp.

Fragillaria sp.

-- Green algae

-- Cyanoph

yceae Chlorella

sp. Gomphonema sp.

Spirulina sp.

Green Algae

Green Algae

Cymbella sp.

Green Algae

-- -- Chlorella

sp. --

Microcystis sp.

Pandorina sp.

Cyanophyceae

Green Algae

Oscillatoria sp.

Chlorella sp.

Synedra sp.

Ulothrix sp.

Ulthrix

Spirulina

sp. Anabaen

a sp. Hydrodictyon sp.

Green Algae

Green Algae

Cyanophyceae

Oscillatori

a sp. Spirogyra

sp. Chlorella

sp. Pandorin

a sp. Oscillatori

a sp.

Green Algae

Pediastru

m sp.

Pediastrum sp.

Spirulina sp.

Volvox

sp. Ulothrix

sp. --

Chlorella

sp. Cyanoph

yceae

Pediastru

m sp. Oscillatori

a sp.

C Zooplanktons

19.1

Abundance (Population)

no/m2 380 270 430 190 250 100 150 40 190 70 280 60 APHA (22nd

Edi) 10200-G

17




19.2



group

--

Polychaetes

Polychaetes

Polychaeteworms

Polychaeteworms

Ctenophores

Polychaetes

Polychaetes

Crustaceans

Polychaete Worms

Isopods Gastropo

ds Copepod

s

APHA (22nd Edi) 10200-G

Bivlaves

Molluscan

Bivalves Molluscan

s Gastropo

ds Decapods Krill

Nematodes

Nematodes

Gastropods

Isopods Polychaete worms

Gastropods

Branchyurans

Gastropods

Decapods Copepod

s --

Copepods

Bivalves Decapods Decapods Decapods Crustace

ans

Copepods

-- Copepods Branchyu

rans -- --

Crustaceans

-- Mollusca

ns -- Krill

-- -- -- -- -- -- Isopods -- Snail -- Namatod

es

-- -- -- -- -- -- Ostracod

s -- -- --

Molluscans

-- -- -- -- -- -- -- -- -- -- Copepod

s 19.3

Total Biomass ml/100 m3

29 18 72 48 79 23 41 8 28 9 38 23 APHA (22nd

Edi) 10200-G

D Microbiological Parameters

20.1

Total Bacterial Count

CFU/ml

1522 1481 1620 1500 1740 1460 1824 1320 1740 1260 1130 870 IS 5402:2002

20.2

Total Coliform /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent APHA(22ndEdi)

9221-D

20.3

Ecoli /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS:1622:1981Edi.2.4(2003-

05)

20.4

Enterococcus /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 15186

:2002

20.5

Salmonella /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 5887 (P-3)

20.6

Shigella /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 1887 (P-7)

20.7

Vibrio /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 5887 (P-5)

18




RESULTS OF SEDIMENT ANALYSIS [M1 LEFT SIDE OF BOCHA CREEK - N 22°45'183" E 069°43'241"] SR. NO.

TEST PARAMETERS UNIT April 2015 May 2015 June 2015 July 2015 August 2015 September 2015

Test Method SEDIMENT SEDIMENT SEDIMENT SEDIMENT SEDIMENT SEDIMENT

1 Organic Matter % 0.57 0.64 0.49 0.52 0.54 0.352 FCO:2007

2 Phosphorus as P mg/kg 137 160 139 154 146 146 APHA(22ndEdi) 4500 C

3 Texture -- Sandy Loam Sandy Loam Sandy Loam Sandy Loam Sandy Loam Sandy Loam --

4 Petroleum Hydrocarbon mg/kg BDL* BDL* BDL* BDL* BDL* BDL* PLPL-TPH

5 Heavy Metals

5.1 Aluminum as Al % 4.8 5 5.2 5 5.4 4.99 AAS APHA 3111 B

5.2 Total Chromium as Cr+3 mg/kg 98 130 176 220 190 189 AAS 3111B

5.3 Manganese as Mn mg/kg 740 860 910 830 880 789 AAS APHA 3111 B

5.4 Iron as Fe % 2.05 2.4 2.5 2.08 3.1 2.61 AAS

APHA(22ndEdi)3111 B

5.5 Nickel as Ni mg/kg 59 48 56 60 58 57.96 AAS

APHA(22ndEdi)3111 B

5.6 Copper as Cu mg/kg 37 54 34 40 36 37.99 AAS

APHA(22ndEdi)3111 B

5.7 Zinc as Zn mg/kg 142 164 156 132 144 143 AAS

APHA(22ndEdi)3111 B

5.8 Lead as Pb mg/kg 2.6 1.8 1.4 1.02 1.22 1.13 AAS

APHA(22ndEdi)3111 B

5.9 Mercury as Hg mg/kg BDL* BDL* BDL* BDL* BDL* BDL* AAS APHA- 3112 B

6 Benthic Organisms

6.1 Macrobenthos -- Polychaete worms

Bivalves Crustaceans

Polychaeteworms Crustaceans

Isopods Decapods

Amphipods Mysids

Echinoderms

Isopods Mysids

Echinoderms Polychaete Worms

Echinoderms Isopods

Knill Anthozoans

Crabs Anthozoans

Isopods Decapods

APHA (22nd Edi) 10500-C

6.2 MeioBenthos -- Gastroriches

Smaller Crustaceans

Nematodes Smaller

Crustaceans Copepods

Hydrozoan Copepods

Nematodes Foraminiferans

Copepods Foraminiferans


2 Population no/m2 308 252 377 440 377 288 APHA (22nd Edi)

10500-C

19




RESULTS OF MARINE WATER [M2 MOUTH OF BOCHA & NAVINAL CREEK - N 22°44'239" E 069°43'757"]

SR. NO.

TEST PARAMETERS

UNIT


Test Method SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

1 pH -- 8.05 8.1 8.1 8.17 7.95 8.02 8.25 8.38 8.14 8.2 7.91 8.03 IS3025(P11)83

Re.02

2 Temperature oC 31 31 30 31 27 28 29 30 29 30 29 30 IS3025(P9)84

Re.02

3 Total Suspended

Solids mg/L 24 38 18 20 21 28 24 34 22 30 16 26

IS3025(P17)84Re.02

4 BOD (3 Days @ 27

oC) mg/L BDL* BDL* BDL* BDL* BDL * BDL * BDL* BDL* BDL* BDL* BDL* BDL*

IS 3025 (P44)1993Re.0

3Edition2.1

5 Dissolved Oxygen mg/L 5.6 4.4 5.4 4.8 5.6 4.6 5.4 4.6 5.8 4.8 5.4 4.4 IS3025(P38)89

Re.99


2550 B

7 Oil & Grease mg/L BDL* BDL* 0.84 BDL* 0.52 BDL* 0.3 BDL* 0.4 BDL* 0.4 BDL* APHA(22ndEdi)

5520D



NEDA

10

Ammonical Nitrogen as NH3

mg/L 0.32 0.46 0.42 0.51 0.81 0.72 0.8 1.0 0.72 0.9 0.32 0.406 IS3025(P34)88

Cla.2.3

11

Phosphates as PO4 mg/L 0.086 0.062 0.14 0.094 0.18 0.11 0.2 0.14 0.18 0.1 0.36 0.27 APHA(22ndEdi)

4500 C

12

Total Nitrogen mg/L 2.1 2.6 1.5 1.2 1.55 1.68 1.4 1.81 1.44 1.82 0.678 0.9 IS3025(P34)88

13

Petroleum Hydrocarbon

mg/L 3.2 BDL* 1.2 BDL* 1.8 BDL* 1.6 BDL* 1.4 BDL* 1.4 BDL* PLPL-TPH

14

Total Dissolved Solids

mg/L 49750 50400 48210 49170 50710 51240 48930 49900 48580 49990 47990 48380 IS3025(P16)84

Re.02

15

COD mg/L 16 18 12 20 18 20 20 22 16 18 14 19 APHA(22ndEdi) 5520-D Open

Reflux

16

Oxidisable Particular Organic Carbon

% 0.82 0.32 0.62 0.48 0.44 0.48 0.4 0.44 0.56 0.46 0.34 0.38 SOP – PLPL -

07

A Flora and Fauna

1 Primary productivity mgC/ 3.2 1.0 1.57 0.45 2.02 0.225 2.7 0.675 1.68 0.45 1.238 0.225 APHA (22nd

20




7 L/day Edi) 10200-J

B Phytoplankton

18.1

Chlorophyll mg/m

3 5.79 5.17 1.22 0.854 2.59 0.187 2.163 0.561 1.92 0.561 1.095 0.134


18.2

Phaeophytin mg/m

3 BDL* BDL* 1.37 1.99 BDL* 2.39 BDL* 0.897 0.227 0.897 1.671 1.493


18.3


170 110 198 50 245 74 254 67 169 39 155 45 APHA (22nd

Edi) 10200-H

18.4



group

--


Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae


Nitzschia sp

Nitzschia sp

Nitzschia sp.

Nitzschia sp.

Coscinodiscus sp.

Navicula sp.

Coscinodiscus sp.

Navicula sp.

Nitzschia sp.

Navicula sp.

Navicula sp.

Navicula sp.

Melosira sp

Coscinodiscus sp

Biddulphia sp.

Coscinodiscus

sp.

Rhizosolenia sp.

Biddulphia sp.

Rhizosolenia sp.

Biddulphia sp.

Synedra sp.

Cyclotella sp.

Synedra sp.

Fragillaria sp.

Asterionella sp

Pleurosigma sp.

Fragillaria sp.

Synedra sp.

Thallasiosira sp.

Nitzschia sp.

Gomphonema sp.

Pinnularia sp.

Rhizosolenia sp.

Fragillaria sp.

Coscinodiscus sp.

Gyrosigma sp.

Coscinodiscus sp

-- Coscinodiscus sp.

Cynophyceae

Green Algae

Pleurosigma sp.

Cymbella sp.

Gyro sigma sp.

Pleurosigma sp.

Green Algae

Asterionella sp.

Pinnularia sp.

Thalassionema sp

-- Thalassionema sp.

Oscillatoria sp.

Ankistrodesmus

sp.

Green Algae

Synedra sp.

Green Algae

Coscinodiscus sp.

Spirogyra sp.

Gyrosigma sp.

cyanophyceae

Desmids -- Desmids -- Pandorin

a sp. Volvox

sp. Tabellari

a sp. Scenedesmus sp.

Green Algae

Chlorella sp.

Cocconeis sp.

Lyngbya sp.

Clostericem sp

-- Closteriu

m sp. --

Chlorella sp.

-- Green Algae

Spirogyra sp.

Chlorella sp.

-- Pinnulari

a sp. Oscillator

ia sp.

-- -- -- -- Volvox

sp. --

Ankistrodesmus

sp. --

Pediastrum sp.

-- Green Algae

--

-- -- -- --

-- Pediastru

m sp. -- Desmids --

Pandorina sp.

--

-- -- -- --

-- Ulothrix

sp. --

Cosmarium sp.

-- Chlorella

sp. --

-- -- -- --

-- Desmids -- Cyanoph

yceae --

Cyanophyceae

--

-- -- -- --

-- Closteriu

m sp. --

Oscillatoria sp.

-- Oscillator

ia sp. --

-- -- -- --

-- -- -- -- -- Nostoc

sp. --

21




-- -- -- --

-- -- -- -- -- -- --

C Zooplanktons

19.1


no/m2 400 200 370 120 400 150 170 30 200 40 320 100 APHA (22nd

Edi) 10200-G

19.2



group

--

Echinoderms

Polychaeteworms

Gastropods

Foraminiferans

Polychaetes

Worms

Gastrpods

Krill Polychae

te Worms

Copepods

Molluscans

Crustaceans

Gastropods


Gastropods

Foraminiferans

Polychaeteworms

Ostracods

Nematodes

Mysids Copepod

s Ctenopho

res Isopods

Gastropods

Copepods

Polychaete worms

Polychaeteworms

-- Nematod

s --

Echino derms

Snail Gastropo

ds Cyclops

Gastropods

-- Krill --

Nematodes

-- -- -- -- -- Decapod

s --

Polychaete

Worms --

Polychaete worms

--

-- -- -- -- -- -- Lamellibranches

-- -- -- Decapod

s --

19.3


29 14 30 4 88 34 55 11 62 7 59 6 APHA (22nd

Edi) 10200-G


20.1


CFU/ml

1745 1904 1850 2020 1880 2100 1930 1580 1850 1620 1670 1420 IS 5402:2002

20.2


9221-D

20.3


05)

20.4


:2002

20.5


20.6


20.7


22




RESULTS OF SEDIMENT ANALYSIS [M2 MOUTH OF BOCHA & NAVINAL CREEK – N 22°44'239" E 069°43'757"] SR. NO.







5 Heavy Metals

5.1 Aluminum as Al % 6.4 5.6 5.4 5.6 5.2 5.2 AAS APHA 3111 B



5.4 Iron as Fe % 2.8 2.4 2.72 2.16 2.62 2.01 AAS APHA(22ndEdi)3111 B

5.5 Nickel as Ni mg/kg 48 56 54 58 60 41.99 AAS APHA(22ndEdi)3111 B

5.6 Copper as Cu mg/kg 52 39 158 110 158 97.9 AAS APHA(22ndEdi)3111 B

5.7 Zinc as Zn mg/kg 114 146 163 148 156 157 AAS APHA(22ndEdi)3111 B

5.8 Lead as Pb mg/kg 2.1 1.9 1.2 1.16 1.24 1.58 AAS APHA(22ndEdi)3111 B

5.9 Mercury as Hg mg/kg 0.8 BDL* BDL* BDL* BDL* BDL* AAS APHA- 3112 B

6 Benthic Organisms

6.1 Macrobenthos --

Polychaete worms

Bivalves Crustaceans

Mysids Polychaeteworms

Crustaceans

Polychaete Worms

Echinoderms Snail Crab

Isopods Echinoderms

Decapods Crab

Amphipods

Polychaete Worms

Anthozoans Echinoderms

Echinoderms Polychaete worms

Isopods Prawn

Decapods


6.2 MeioBenthos -- Nematodes Nematodes Copopods

Foraminiferans Hydrozoa

Foraminiferans Copepods

Ostracodes Hydrozoa

Nematodes Copepods


2 Population no/m2 240 440 503 503 440 337 APHA (22nd Edi) 10500-C

23




RESULTS OF MARINE WATER [M3 EAST OF BOCHAISLAND - N 22°46'530" E 069°41'690"] SR. NO.

TEST PARAMETERS UNIT July 2015 August 2015

Test Method SURFACE BOTTOM SURFACE BOTTOM

1 pH -- 7.62 8.08 7.55 7.92 IS3025(P11)83Re.02

2 Temperature oC 29 30 29 30 IS3025(P9)84Re.02

3 Total Suspended Solids mg/L 22 25 30 38 IS3025(P17)84Re.02

4 BOD (3 Days @ 27 oC) mg/L BDL* BDL* BDL* BDL* IS 3025

(P44)1993Re.03Edition2.1

5 Dissolved Oxygen mg/L 5.4 4.6 5.6 4.8 IS3025(P38)89Re.99

6 Salinity ppt 42.8 43.02 41.66 42.92 APHA (22ndEdi) 2550 B

7 Oil & Grease mg/L 0.2 BDL* 0.3 BDL* APHA(22ndEdi)5520D

8 Nitrate as NO3 mg/L 0.3 0.42 0.28 0.36 IS3025(P34)88

9 Nitrite as NO2 mg/L 0.019 0.028 0.02 0.026 IS3025(P34)88 NEDA

10 Ammonical Nitrogen as NH3 mg/L 0.8 0.9 0.7 0.8 IS3025(P34)88Cla.2.3

11 Phosphates as PO4 mg/L 0.64 0.81 0.58 0.72 APHA(22ndEdi) 4500 C

12 Total Nitrogen mg/L 1.12 1.35 1.08 1.21 IS3025(P34)88

13 Petroleum Hydrocarbon mg/L BDL* BDL* BDL* BDL* PLPL-TPH

14 Total Dissolved Solids mg/L 51288 51492 49920 51430 IS3025(P16)84Re.02

15 COD mg/L 18 28 20 26 APHA(22ndEdi) 5520-D Open

Reflux

16 Oxidisable Particular Organic Carbon % 0.31 0.2 0.28 0.21 SOP – PLPL - 07

A

17 Primary productivity mgC/L/day 2.25 0.225 1.46 0.113 APHA (22nd Edi) 10200-J

B

18.1 Chlorophyll mg/m3 2.05 0.053 1.01 0.24 APHA (22ndEdi) 10200-H

18.2 Phaeophytin mg/m3 0.523 2.52 1.56 2.17 APHA (22ndEdi) 10200-H

18.3 Cell Count Unit x 103/L 254 25 178 18 APHA (22nd Edi) 10200-H

18.4 Name of Group Number

and name of group species of each group

--

Bacillariophyceae Bacillariophyceae Bacillariophyceae Bacillariophyceae


Synedra sp. Nitzschia sp. Cymbella sp. Fragillaria sp. Nitzschia sp. Navicula sp. Pinnularia sp. Pinnularia sp.

Rhizosolenia sp. Gyro sigma sp. Coscinodiscus sp. Navicula sp. Thallasiosira sp Green Algae Rhizosolenia sp. Nitzschia sp.

Coscinodiscus sp. Chlorella sp. Green Algae Gyro sigma sp. Green Algae Desmids Chlorella sp. Green Algae

Scenedesmus sp. Closterium sp. Oedogonium sp. Chlorella sp.

Chlorella sp. -- Oscillatoria sp. -- Spirogyra sp. -- Anabaena sp. -- Cyanophyceae -- -- --

Nostoc sp. -- -- -- Oscillatoria sp. -- -- --

-- -- -- --

24




-- -- -- -- C

19.1 Abundance (Population) no/m2 150 30 213 25 APHA (22nd Edi) 10200-G

19.2 Name of Group Number

and name of group species of each group

--

Polychaete Worms Gastropods Copepods Polychaete Worms


Echinoderms Isopods Ostracods Decapods

Molluscans -- Crustaceans Nauplies

-- -- Krill -- -- -- Ctenophores --

19.3 Total Biomass ml/100 m3 46 7 54 9 APHA (22nd Edi) 10200-G

D

20.1 Total Bacterial Count CFU/ml 1840 1550 1680 1375 IS 5402:2002

20.2 Total Coliform /ml Absent Absent Absent Absent APHA(22ndEdi)9221-D

20.3 Ecoli /ml Absent Absent Absent Absent IS:1622:1981Edi.2.4(2003-05)

20.4 Enterococcus /ml Absent Absent Absent Absent IS : 15186 :2002

20.5 Salmonella /ml Absent Absent Absent Absent IS : 5887 (P-3)

20.6 Shigella /ml Absent Absent Absent Absent IS : 1887 (P-7)

20.7 Vibrio /ml Absent Absent Absent Absent IS : 5887 (P-5)

25




RESULTS OF SEDIMENT ANALYSIS [M3 RIGHT SIDE OF BOCHA CREEK - N 22°46'530" E 069°41'690"]

SR. NO. TEST PARAMETERS UNIT July 2015 August 2015

Test Method SEDIMENT SEDIMENT

1 Organic Matter % 0.52 0.58 FCO:2007

2 Phosphorus as P mg/kg 150 146 APHA(22ndEdi) 4500 C

3 Texture -- Sandy Loam Sandy Loam --

4 Petroleum Hydrocarbon mg/kg BDL* BDL* PLPL-TPH

5

5.1 Aluminum as Al % 5.4 4.8 AAS APHA 3111 B

5.2 Total Chromium as Cr+3 mg/kg 140 180 AAS 3111B

5.3 Manganese as Mn mg/kg 890 860 AAS APHA 3111 B

5.4 Iron as Fe % 2.02 1.88 AAS APHA(22ndEdi)3111 B

5.5 Nickel as Ni mg/kg 52 50 AAS APHA(22ndEdi)3111 B

5.6 Copper as Cu mg/kg 36 38 AAS APHA(22ndEdi)3111 B

5.7 Zinc as Zn mg/kg 138 140 AAS APHA(22ndEdi)3111 B

5.8 Lead as Pb mg/kg 1.6 1.46 AAS APHA(22ndEdi)3111 B

5.9 Mercury as Hg mg/kg BDL* BDL* AAS APHA- 3112 B

6

6.1 Macrobenthos -- Polychaete Worms

Bivalves Anthozoans

Polychaete Worms Echinoderms

Bivalves Mysids

Decapods


6.2 MeioBenthos -- Foraminiferans

Copepods Nematodes Bryozoans


2 Population no/m2 337 385 APHA (22nd Edi) 10500-C

26




RESULTS OF MARINE WATER [M4 JUNA BANDAR N 22°47'577" E 069°43'620"] SR. NO.

TEST PARAMETERS

UNIT


Test Method SURFACE

BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

SURFACE

BOTTOM

1 pH -- 7.95 8.1 8.1 8.2 8.06 8.15 8.26 8.4 8.17 8.34 8.02 8 IS3025(P11)83

Re.02


e.02

3 Total Suspended

Solids mg/L 18 20 26 30 24 28 26 30 28 30 28 32

IS3025(P17)84Re.02

4 BOD (3 Days @ 27


IS 3025 (P44)1993Re.0

3Edition2.1

5 Dissolved Oxygen mg/L 5.4 4 5.6 5 5.8 4.8 5.4 4.8 5.6 5 5.8 4.8 IS3025(P38)89

Re.99

6 Salinity ppt 43.1 44.2 42.7 43.2 40.2 41.6 40 41.2 41.6 42.8 38.4 39.1 APHA (22ndEdi)

2550 B

7 Oil & Grease mg/L BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* APHA(22ndEdi)5

520D



NEDA


as NH3 mg/L 0.72 0.8 0.96 1.24 1.1 1.26 1.2 1.3 0.76 0.94 1.01 1.29

IS3025(P34)88Cla.2.3


4500 C


13 Petroleum

Hydrocarbon mg/L BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* PLPL-TPH

14 Total Dissolved

Solids mg/L 52100 53200 55760 52240 53940 54000 53070 53520 54120 55846 45313 46173

IS3025(P16)84Re.02


Reflux


Organic Carbon % 0.96 0.32 0.6 0.44 0.52 0.44 0.48 0.46 0.82 0.4 0.5 0.46

SOP – PLPL - 07

A Flora and Fauna


3.06 1.9 2.925 0.675 2.475 0.9 1.575 0.225 1.35 0.563 1.575 0.675 APHA (22nd Edi) 10200-J

B Phytoplankton

18 Chlorophyll mg/m 4.2 3.2 2.62 0.64 2.723 0.107 1.148 0.107 1.6 0.187 1.89 0.16 APHA (22ndEdi)

27




.1 3 10200-H

18.2

Phaeophytin mg/m

3 BDL* BDL* BDL* 1.94 BDL* 2.472 0.459 1.837 0.36 1.757 0.067 1.69


18.3


218 180 338 88 304 35 196 24 175 29 162 33 APHA (22nd

Edi) 10200-H

18.4



group

--

Diatom Diato

m Diatom Diatom

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae


Biddulphia sp.

Biddulphia sp.

Biddulphia sp.

Cymbella sp.

Synedra sp.

Pleurosigma sp.

Asterionella sp.

Cocconeis sp.

Asterionella sp.

Coscinodiscus sp.

Asterionella sp.

Tabellaria sp.

Nitzschia sp.

Fragillaria sp.

Thalassionema

sp.

Gyrosigna sp.

Biddulphia sp.

Navicula sp.

Biddulphia sp.

Pinnularia sp.

Biddulphia sp.

Fragillaria sp.

Coscinodiscus sp.

Navicula sp.

Thalassiosira sp.

Gyrosigma sp.

Fragillaria sp.

Nitzschia sp.

Nitzschia sp.

Skeletonema sp.

Coscinodiscus sp.

Gyro sigma sp.

Chaetocerous sp.

Navicula sp.

Navicula sp.

Gyrosigma sp.

Fragillaria sp.

-- Pleurosigma sp.

Biddulphia sp.

Fragillaria sp.

Pleurosigma sp.

Pinnularia sp.

Synedra sp.

Coscinodiscus sp.

Synedra sp.

Nitzschia sp.

Coscinodiscus sp.

Pleurosigma sp.

-- Green algae

Green algae

Cyclotella sp.

-- Skeletone

ma sp. Green Algae

Gyro sigma sp.

Pinnularia sp.

Fragillaria sp.

Asterionella sp.

-- -- Chlorella sp.

Oscillatoria sp.

Green Algae

-- Green Algae

Spirogyra sp.

Green Algae

Green Algae

Surirella sp.

Cyanophyceae

-- -- -- -- Pandorin

a sp. --

Pediastrum sp.

Volvox sp.

Pandorina sp.

Chlorella sp.

Thallasionema sp.

Oscillatoria sp.

-- -- -- -- Ulothrix

sp. --

Chlorella sp.

-- Pediastru

m sp. --

Green Algae

Nostoc sp.

-- -- -- -- Volvox

sp. --

Cyanophyceae

-- Desmids -- Ankistrod

esmus sp.

--

-- -- -- -- -- -- Microcysti

s sp. --

Cosmarium sp.

-- Chlorella

sp. --

-- -- -- -- -- -- Nostoc

sp. -- -- --

Pandorina sp.

--

-- -- -- -- -- -- -- -- -- -- Cyanophy

ceae --

-- -- -- -- -- -- -- -- -- -- Anabaen

a sp. --

-- -- -- -- -- -- -- -- -- -- Oscillatori

a sp. --

C Zooplanktons

19.1


no/m2 310 198 440 210 230 160 130 20 183 67 267 133 APHA (22nd

Edi) 10200-G

28




19.2



group

--

Hydrozoans

Amphipods

Hydrozoans

Amphipods

Chaetognathes

Polychaete Worms

Decapods Ostracod

s Copepods Decapods

Gastropods

Ctenophores


Anthrozoans

Polychaetes

Anthrozoans

Polychaeteworms

Copepods Decapods Copepods Lamellibranches

Krill Ostracod

s Copepods

Gastropods

Gastropods

-- Gastrop

ods Decapods Krill Copepods Krill Decapods

Polychaete Worms

Gastropods

Decapods Krill

Foraminiferans

-- Chaetognaths

Echinoderms

Daphania -- Ostracod

s --

Molluscans

-- Ostracod

s Nematod

es

-- -- -- -- Isopods -- Gastropo

ds -- -- -- Krill --

-- -- -- -- -- -- -- -- -- -- Crustacea

ns --

-- -- -- -- -- -- -- -- -- -- Cyclops -- 19.3


32 10 84 29 56 12 43 7 38 10 75 15 APHA (22nd

Edi) 10200-G


20.1

Total Bacterial Count CFU/ml

1613 1554 1710 1625 1820 1740 1810 1285 1880 1310 1850 1680 IS 5402:2002

20.2

Total Coliform /ml Absent Absen

t Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent

APHA(22ndEdi)9221-D

20.3

Ecoli /ml Absent Absen


IS:1622:1981Edi.2.4(2003-

05)

20.4

Enterococcus /ml Absent Absen


IS : 15186 :2002

20.5

Salmonella /ml Absent Absen

t Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 5887 (P-3)

20.6

Shigella /ml Absent Absen


20.7

Vibrio /ml Absent Absen


29




RESULTS OF SEDIMENT ANALYSIS [M4 JUNA BANDAR N 22°47'577" E 069°43'620"] SR. NO.







5 Heavy Metals










6 Benthic Organisms


Snails Echinoderms

Polychaeteworms Decapods Amphipods

Echinoderms

Polychaete Worms Bivalves Crabs

Amphipods

Chaetognathes Bivalves

Anthozoans

Amphipods Isopods

Decapods Echinoderms

Crabs

Polychaete worms Echinoderms

Isopods Anthozoans


6.2 MeioBenthos -- Copepods

Nematodes Nematodes Copopods

Nematodes Hydrozoa

Nematodes Bryozoans Copepods

Nematodes Namatodes

Foraminiferans Hydrozoa



30




RESULTS OF MARINE WATER [M5 TOWARDS WESTERN SIDE OF EAST PORT – N 22°46'041" E 069°47'296"] SR. NO.

TEST PARAMETERS

UNIT


Test Method SURFACE

BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

SURFACE

BOTTOM

1 pH -- 7.95 8.1 8.02 8.15 8.15 8.3 8.22 8.42 8.14 8.28 8.08 8.14 IS3025(P11)83

Re.02


e.02

3 Total Suspended

Solids mg/L 12 14 10 16 18 21 26 34 20 32 26 30

IS3025(P17)84Re.02

4 BOD (3 Days @ 27


IS 3025 (P44)1993Re.0

3Edition2.1

5 Dissolved Oxygen mg/L 5.4 4.6 5.6 4.4 6 5 5.6 4.8 5.4 4.8 5.4 4.6 IS3025(P38)89

Re.99

6 Salinity ppt 40.6 41.4 40.9 41.3 37.8 38.1 37.6 38 38.4 39.2 39.2 40.4 APHA (22ndEdi)

2550 B

7 Oil & Grease mg/L BDL* BDL* 0.76 BDL* 0.32 BDL * 0.26 BDL* 0.44 BDL* BDL* BDL* APHA(22ndEdi)5

520D



NEDA


as NH3 mg/L 0.28 0.4 0.21 0.34 0.44 0.6 0.54 0.84 0.38 0.46 0.48 0.619

IS3025(P34)88Cla.2.3


4500 C


13 Petroleum

Hydrocarbon mg/L 2.2 BDL* 2.8 BDL* 0.914 1.244 0.502 0.618 0.416 0.72 0.42 BDL* PLPL-TPH

14 Total Dissolved

Solids mg/L 48600 49690 47960 48340 47270 47780 46890 47560 47820 48360 45966 46874

IS3025(P16)84Re.02


Reflux


Organic Carbon % 0.64 0.44 0.56 0.44 0.62 0.48 0.52 0.48 0.54 0.5 0.5 0.42

SOP – PLPL - 07

A Flora and Fauna


2.8 1.1 1.8 0.675 2.7 1.125 1.8 0.675 1.12 0.338 1.688 0.563 APHA (22nd Edi) 10200-J

B Phytoplankton

18 Chlorophyll mg/m 4.4 4 1.44 0.56 3.124 0.267 1.469 0.134 1.7 0.721 1.362 0.294 APHA (22ndEdi)

31




.1 3 10200-H

18.2

Phaeophytin mg/m

3 BDL* BDL* 1.13 2.11 BDL * 2.312 0.363 0.951 0.123 0.363 0.806 0.959


18.3


330 290 212 56 323 77 184 17 205 35 215 40 APHA (22nd

Edi) 10200-H

18.4



group

--

Green algae

Diatom Green algae

Diatom Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae


Pandorina sp.

Rhilosoleniass

sp.

Scenedesmus

sp.

Navicula sp.

Biddulphia sp.

Thallasio nema sp.

Gomphonema sp.

Navicula sp.

Thallasiosira sp

Nitzschia sp.

Rhizosolenia sp.

Nitzschia sp.

Scenedesmus

sp.

Melosira sp.

Diatom Fragillaria

sp. Cymbella

sp. Pinnularia

sp. Rhizosolenia sp.

Fragillaria sp.

Rhizosolenia sp.

Fragillaria sp.

Synedra sp.

Pinnularia sp.

Diatom Navicula sp.

Nitzschia sp.

Pleurosigma sp.

Pleurosigma sp.

Rhizosolenia sp.

Synedra sp.

Pinnularia sp.

Pleurosigma sp.

Biddulphia sp.

Navicula sp.

Fragillaria sp.

Nitzschia sp

-- Navicula sp.

Green algae

Cyanophyceae

Green Algae

Nitzschia sp.

Cyanophyceae

Nitzschia sp.

Synedra sp.

Coscinodiscus sp.

Biddulphia sp.

Coscinodiscus

sp --

Coscinodiscus

sp.

Chlorella sp.

Oscillatoria sp.

Chlorella sp.

Coscinodiscus sp.

Chlorella sp.

Synedra sp.

Green Algae

Skeletonema sp.

Cyanophyceae

Fragillaria sp.

-- Fragillaria sp.

-- Spirulina

sp. Oedogonium sp.

Green Algae

Oscillatoria sp.

Coscinodiscus sp.

Chlorella sp.

Green Algae

Anabaena sp.

-- -- Acananthes sp.

-- -- Pandorin

a sp. Chlorella

sp. Anabaen

a sp. Green Algae

Pediastrum sp.

Spirogyra sp.

Nostoc sp.

-- -- -- -- -- -- Pandorin

a sp. --

Pandorina sp.

-- Pediastru

m sp. --

-- -- -- -- -- -- Spirogyra

sp. --

Chlorella sp.

-- Hydrodictyon sp.

--

-- -- -- -- -- -- -- -- Cyanophy

ceae -- Desmids --

-- -- -- -- -- -- -- -- Nostoc

sp. --

Cosmarium sp.

--

C Zooplanktons

19.1


no/m2 560 280 250 180 290 110 160 40 150 80 260 60 APHA (22nd

Edi) 10200-G

19.2



group

--

Gastropods

Ostracods

Gastropods

Ostracods Copepods Gastropo

ds Copepods

Gastropods

Copepods Decapods Copepods Copepods


Nematodes

Gastropods

Nematods

Polychaeteworms

Decapods Polychaete Worms

Cyclops Ctenopho

res Molluscan

s Bivalves Cyclops

Polychaete worms

Amphipods

-- Chaetognaths

Snails Ostracod

s --

Ostracods

Decapods Ostracod

s Nematod

es Decapods

Ostracods

Chaeto -- -- -- Krill -- Krill -- Polychaet -- Krill --

32




gnaths e Worms

-- -- -- -- -- --

Polychaete Worms

& Gastropo

ds

-- -- -- Polychaete worms

--

19.3


31 22 25 11 97 17 35 4 57 11 69 11 APHA (22nd

Edi) 10200-G


20.1


1495 1318 1586 1227 1886 1430 1580 1140 1650 1390 1830 1630 IS 5402:2002

20.2

Total Coliform /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent APHA(22ndEdi)9

221-D

20.3


05)

20.4


:2002

20.5


20.6


20.7


33




RESULTS OF SEDIMENT ANALYSIS [M5 TOWARDS WESTERN SIDE OF EAST PORT – N 22°46'041" E 069°47'296"] SR. NO.







5 Heavy Metals




5.4 Iron as Fe % 2.9 2.7 2.94 2.14 2.56 2.09 AAS APHA(22ndEdi)3111

B

5.5 Nickel as Ni mg/kg 38 50.2 44.6 52.4 48.44 46.77 AAS APHA(22ndEdi)3111

B

5.6 Copper as Cu mg/kg 64 44 32.8 40.2 36.68 36.39 AAS APHA(22ndEdi)3111

B

5.7 Zinc as Zn mg/kg 140 153 174 210 196 161 AAS APHA(22ndEdi)3111

B

5.8 Lead as Pb mg/kg 2.6 2.1 1.62 1.02 1.44 1.8 AAS APHA(22ndEdi)3111

B


6 Benthic Organisms


Snails Crustaceans

Polychaeteworms Crustaceans Echinoderms

Bivalves Isopods Mysids

Polychaete Worms Anthozoans

Lobsters

Amphipods Decapods

Crustaceans Lobsters

Polychaete Worms Decapods

Crustaceans Crabs

Crabs Mysids

Decapods Bivalves

Polychaete worms


6.2 MeioBenthos -- Foraminiferans

Nematodes Nematodes

Forminiferans

Bryozoan Copepods Ciliates

Nematods Ostracodes Hydrozoa

Nematods Foraminiferans

Gastrotriches Ostracods



34




RESULTS OF MARINE WATER [M7 EAST PORT N 22°47'120" E 069°47'110"]

SR. NO.

TEST PARAMETERS

UNIT


Test Method SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

1 pH -- 8.07 8.17 8.15 8.17 8.05 8.18 8.19 8.23 7.95 8.14 8.1 8.18 IS3025(P11)83

Re.02


e.02

3 Total Suspended

Solids mg/L 14 21 20 26 14 18 18 24 16 22 18 22

IS3025(P17)84Re.02

4 BOD (3 Days @ 27


IS 3025 (P44)1993Re.0

3Edition2.1

5 Dissolved Oxygen mg/L 5.6 4.4 5.8 5 5.4 4.8 5.4 4.6 5.6 4.6 5.6 4.8 IS3025(P38)89

Re.99

6 Salinity ppt 37.5 38.4 38.6 39.2 38.1 38.6 37.8 38 37.8 38.3 38.1 39.2 APHA (22ndEdi)

2550 B

7 Oil & Grease mg/L BDL* BDL* BDL* BDL* 0.44 BDL * 0.16 BDL* 0.12 BDL* BDL* BDL* APHA(22ndEdi)5

520D



NEDA


as NH3 mg/L 0.18 0.32 0.11 0.28 0.32 0.58 0.34 0.46 0.26 0.5 0.295 0.554

IS3025(P34)88Cla.2.3


4500 C


13 Petroleum

Hydrocarbon mg/L 1.8 BDL* BDL* BDL* BDL* BDL* 2.6 BDL* 2.4 BDL* 1.4 BDL* PLPL-TPH

14 Total Dissolved

Solids mg/L 43621

44511

44860 45380 43660 44270 43880 44220 43860 44428 43186 43828 IS3025(P16)84

Re.02


Reflux


Organic Carbon % 0.88 0.56 0.66 0.52 0.64 0.48 0.58 0.5 0.66 0.54 0.82 0.58

SOP – PLPL - 07

A Flora and Fauna


4.0 2.6 2.25 1.12 2.25 0.675 2.02 0.9 1.68 0.113 1.35 0.45 APHA (22nd Edi) 10200-J

35




B Phytoplankton

18.1

Chlorophyll mg/m

3 3.87 3.6 1.55 1.34 2.99 0.347 1.469 0.133 1.28 0.187 1.682 0.107


18.2

Phaeophytin mg/m

3 BDL* BDL* 1.03 1.24 BDL* 2.232 0.849 2.44 1.03 2.39 0.598 2.02


18.3


210 190 285 68 312 42 204 31 215 20 227 29 APHA (22nd Edi)

10200-H

18.4



group

--

Diatom Diato

m Diatom

Diatom

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae


Thalassiasira sp.

Biddulphia sp.

Thalassionema sp.

Biddulphia sp.

Nitzschia sp.

Fragillaria sp.

Nitzschia sp.

Fragillaria sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Fragillaria sp.

Fragillaria sp.

Coscinodiscus sp.

Fragillaria sp.

Biddulphia sp.

Coscinodiscus sp.

Nitzschia sp.

Synedra sp.

Fragillaria sp.

Fragillaria sp.

Melosira sp.

Fragillaria sp.

Cyclotella sp.

Pinnularia sp.

Pleurosigma sp.

Asterionella sp.

Pinnularia sp.

Synedra sp.

Biddulphia sp.

Coscinodiscus sp.

Cyclotella sp.

Amphora sp.



Cyanophyceae

Gyrosigma sp.

Thallasiosira sp.

Pleurosigma sp.

Fragillaria sp.

Pleurosigma sp.

Tabellaria sp.

Green algae

-- Green algae

-- Cymbella

sp. Oscillatori

a sp. Green Algae

Green Algae

Navicula sp.

Skeletonema sp.

Thallasiosira sp.

Cyanophyceae

Pediastrum sp.

-- Pediastru

m sp. --

Green Algae

-- Pandorina

sp. Pandorina

sp. Thallasios

ira sp Pandorina

sp. Pinnularia

sp. Oscillatori

a sp.

Cynophyc

eae Ankistrodesmus sp.

Spirogyra sp.

Pediastrum sp.

Green Algae

Desmids Green Algae

Nostoc sp.

Oscillatori

a sp. Pediastru

m sp. Desmids

Volvox sp.

Chlorella sp.

Chlorella sp.

Green Algae

Cosmariu

m sp. Pandorina

sp. Pandorina

sp. Chlorella

sp.

Cyanophy

ceae Ulothrix

sp.

Oscillatori

a sp. Desmids

Closteriu

m sp. C Zooplanktons

19.1


no/m2 320 220 310 130 240 90 210 70 167 50 280 40 APHA (22nd Edi)

10200-G

19.2


-- Copepo

ds Bivalv

es Copepods

Bivalves

Gastropods

Polychaete Worms

Gastropods

Cyclops Gastropo

ds Molluscan

s Copepods Copepods


36





group

Gastropods

Copepods

Gastropods

Copepods

Copepods Bivalves Copepods Krill Bivalves Platinelmi

nthes Krill

Gastropods

Polychaetes

-- Polychaeteworms

Molluscans

Mysids Molluscan

s Decapods Ostracods Copepods Ostracods Decapods --

Fish larvae

-- Decapods -- Ostracods -- Polychaete Worms

Copepods Cyclops -- Crustacea

ns --

-- -- -- -- Krill -- Cyclops & Ctenopho

res --

Polychaete Worms

-- Ostracods --

-- -- -- -- -- -- -- -- -- -- Fish egg -- 19.3


22 11 69 19 86 21 66 19 48 12 56 5 APHA (22nd Edi)

10200-G


20.1


2331 1895 2077 1981 2100 1850 2130 1620 2210 1870 1760 1580 IS 5402:2002

20.2


t Absent

Absent

Absent Absent Absent Absent Absent Absent Absent Absent APHA(22ndEdi)9

221-D

20.3


t Absent

Absent

Absent Absent Absent Absent Absent Absent Absent Absent IS:1622:1981Edi.2.4(2003-05)

20.4


t Absent

Absent

Absent Absent Absent Absent Absent Absent Absent Absent IS : 15186

:2002

20.5


t Absent

Absent

Absent Absent Absent Absent Absent Absent Absent Absent IS : 5887 (P-3)

20.6


t Absent

Absent


20.7


t Absent

Absent


37




RESULTS OF SEDIMENT ANALYSIS [M7 EAST PORT N 22°47'120" E 069°47'110"]

SR. NO.







5 Heavy Metals





5.5 Nickel as Ni mg/kg 28 41.6 32.4 36.4 38.7 34.35 AAS APHA(22ndEdi)3111 B

5.6 Copper as Cu mg/kg 48 40 48.6 50.1 44.24 44.36 AAS APHA(22ndEdi)3111 B




6 Benthic Organisms

6.1 Macrobenthos -- Crabs Snails

Crustaceans

Bivalves Snails

Crustaceans

Chaetognathes Decapods Bivalves

Echinoderms

Echinoderms Decapods Bivalves Crabs

Turbellaria

Echinoderms Bivalves

Crab Isopods

Polychaete worms Echinoderms

Isopods Decapods


6.2 MeioBenthos -- copepods

Nematodes

Nematodes Copopods Ostracods

Ostracods Hydrozoa

Ostracods Foraminiferans

Hydrozoa

Foraminiferans Copepods

Nematodes Copepods



38




RESULTS OF MARINE WATER [M8 RIGHT SIDE OF BOCHA CREEK N 22°45'987" E 069°43'119"]

SR. NO.

TEST PARAMETERS

UNIT


Test Method SURFACE

BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

SURFACE

BOTTOM SURFAC

E BOTTOM

SURFACE

BOTTOM

1 pH -- 7.9 8.03 7.95 8.05 7.9 8.01 7.85 7.98 7.82 8.1 8.04 8 IS3025(P11)83

Re.02


e.02

3 Total Suspended

Solids mg/L 16 22 18 20 12 14 18 22 14 16 16 20

IS3025(P17)84Re.02

4 BOD (3 Days @ 27


IS 3025 (P44)1993Re.0

3Edition2.1

5 Dissolved Oxygen mg/L 5.8 4.6 6 4.8 5.2 4.6 5.4 4.8 5.6 4.6 5.4 4.6 IS3025(P38)89

Re.99


2550 B

7 Oil & Grease mg/L BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* APHA(22ndEdi)5

520D



NEDA


as NH3 mg/L 0.64 0.73 0.81 0.96 0.58 0.62 0.42 0.52 0.34 0.42 0.554 0.591

IS3025(P34)88Cla.2.3

11 Phosphates as PO4 mg/L 0.038 0.062 BDL* BDL* 0.12 0.16 0.14 0.18 0.14 0.16 0.495 0.585 APHA(22ndEdi)

4500 C


13 Petroleum

Hydrocarbon mg/L BDL* BDL* BDL* BDL* 2.1 BDL* 1.8 BDL* 0.8 BDL* 1.2 BDL* PLPL-TPH

14 Total Dissolved

Solids mg/L 54690 54980 52440 52980 53600 54100 51920 52890 53548 53990 42750 43320

IS3025(P16)84Re.02


Reflux


Organic Carbon % 0.72 0.52 0.6 0.43 0.72 0.32 0.68 0.44 0.7 0.58 0.54 0.62

SOP – PLPL - 07

A Flora and Fauna


2.92 1.06 2.475 0.99 2.925 0.45 2.47 1.125 1.463 0.337 1.463 0.113 APHA (22nd Edi) 10200-J

39




B Phytoplankton

18.1

Chlorophyll mg/m

3 3.8 2.11 2.78 0.83 3.151 0.774 1.92 0.748 1.38 0.427 1.922 0.427


18.2

Phaeophytin mg/m

3 BDL* BDL* BDL* 1.75 BDL* 1.805 0.395 1.98 0.742 1.42 0.021 1.479


18.3


308 220 306 143 358 95 294 75 189 28 202 33 APHA (22nd Edi)

10200-H

18.4



group

--

Diatom Diato

m Diatom Diatom

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae


Biddulphia sp.

Melosira sp.

Biddulphia sp.

Biddulphia sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Fragillaria sp.

Coscinodiscus sp.

Coscinodiscus sp.

Asterionella sp.

Fragillaria sp.

Pleurosigma sp.

Biddulphia sp.

Pleurosigma sp.

Nitzschia sp.

Navicula sp.

Biddulphia sp.

Synedra sp.

Synedra sp.

Pinnularia sp.

Pinnularia sp.

Fragillaria sp.

Navicula sp.

Nitzschia sp.

Nitzschia sp.

Thalassionema

sp.

Pleurosigma sp.

Rhizosolenia sp.

Thallasiosira sp.

Rhizosolenia sp.

Cyclotella sp.

Gyro sigma sp.

Nitzschia sp.

Navicula sp.

Nitzschia sp.

Thalassiosira

sp. --

Fragillaria sp.

Thalassionema sp.

Asterionella sp.

Green Algae

Coscinodiscus sp.

Cheatocerous sp.

Thallasiosira sp

Synedra sp.

Synedra sp.

Gyrosigma sp.

Fragillaria sp.

-- Green algae

-- Synedra

sp. Chlorella

sp. Biddulphi

a sp. Green Algae

Navicula sp.

Skeletonema sp.

Coscinodiscus sp.

Cyanophyceae

Melosira sp.

-- Chlorella

sp. --

Cyclotella sp.

Scenedesmus sp.

Cocconeis sp.

Chlorella sp.

Green Algae

Desmids Cymbella

sp. Oscillatori

a sp.

-- -- -- -- Gyrosigm

a sp. --

Skeletonema sp.

Hydrodictyon sp.

Chlorella sp.

Cosmarium sp.

Pleurosigma sp.

Desmids

-- -- -- -- Cyanophy

ceae --

Green Algae

Spirogyra sp.

Pandorina sp.

-- Cyanophy

ceae Closteriu

m sp.

-- -- -- -- Oscillatori

a sp. --

Chlorella sp.

-- Cyanophy

ceae --

Oscillatoria sp.

--

-- -- -- -- Spirulina

sp. --

Volvox sp.

-- Oscillatori

a sp. --

Nostoc sp.

--

-- -- -- -- Green Algae

-- Pandorin

a sp. -- -- --

Green Algae

--

-- -- -- -- Chlorella

sp. --

Pediastrum sp.

-- -- -- Chlorella

sp. --

-- -- -- -- Volvox

sp. -- -- -- -- --

Pediastrum sp.

--

C Zooplanktons

19.1


no/m2 298 198 370 120 210 80 240 60 217 83 240 80 APHA (22nd Edi)

10200-G

19 Name of Group -- Echino Polyc Echinod Polychaet Bivalves Polychaet Decapods Polychaet Copepods Molluscan Nematod Polychaet APHA (22nd Edi)

40




.2 Number and name of group

species of each group

derms haete erms eworms e Worms e s es e worms 10200-G

Copepods

Bivalves

Copepods

Bivalves Nematod

es Copepods Copepods

Lamellibranches

Decapods Iospods Copepods Isopods

Isopods

-- Isopods Gastropo

ds Gastropo

ds -- Ostracods

Gastropods

Polychaete Worms

Decapods Krill --

Gastropods

-- Gastrop

ods -- Mysids -- Krill

Crustaceans

Gastropods

-- Molluscan

s --

-- -- -- -- -- -- Ctenopho

res -- Cyclops -- -- --

-- -- -- -- -- -- Fish egg -- -- -- -- -- 19.3


18 12 78 26 44 11 81 14 74 15 61 9 APHA (22nd Edi)

10200-G


20.1


1531 1677 1610 1740 1700 1880 1880 1522 1800 1390 1470 1110 IS 5402:2002

20.2



APHA(22ndEdi)9221-D

20.3



IS:1622:1981Edi.2.4(2003-05)

20.4



IS : 15186 :2002

20.5



20.6



20.7



41




RESULTS OF SEDIMENT ANALYSIS [M8 RIGHT SIDE OF BOCHA CREEK – N 22°45'987" E 069°43'119"]

SR. NO.







5 Heavy Metals

5.1 Aluminum as Al % 5.4 5.1 4.9 5.26 5 5.59 AAS APHA 3111 B

5.2 Total Chromium as Cr+3 mg/kg 84 92 104 80 98 99.98 AAS 3111B





5.7 Zinc as Zn mg/kg 172 156 172 150 166 1.62 AAS APHA(22ndEdi)3111 B

5.8 Lead as Pb mg/kg 2.9 2.1 1.7 2 1.96 1.88 AAS APHA(22ndEdi)3111 B


6 Benthic Organisms

6.1 Macrobenthos --

Snails Amphipods Polychaete

worms Crabs

Bivalves Mysids

Chaetognathes

Polychaete Worms Crabs

Decapods Isopods

Polychaete Worms Bivalves

Decapods Echinoderms

Polychaete Worms Bivalves

Echinoderms Crabds Isopods

Polychaete worms Isopods

Decapods Prawn


6.2 MeioBenthos -- Copepods

Nematodes Nematodes Copopods


Ciliates


Copepods

Nematods Foraminiferans

Namatodes Foraminiferans



42




RESULTS OF MARINE WATER [M11 MPT T1 JETTY N 22°42'278" E 069°43'450"]

SR. NO.

TEST PARAMETERS

UNIT


Test Method SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

SURFACE

BOTTOM

1 pH -- 8.05 8.13 8.11 8.24 8.15 8.22 8.1 8.28 8.05 8.18 8 8.09 IS3025(P11)83

Re.02


e.02

3 Total Suspended

Solids mg/L 12 22 16 20 12 16 18 22 20 26 16 20

IS3025(P17)84Re.02

4 BOD (3 Days @ 27


IS 3025 (P44)1993Re.0

3Edition2.1

5 Dissolved Oxygen mg/L 5.6 4.8 6 5.2 5.4 5 5.6 4.8 5.8 5 5.4 4.8 IS3025(P38)89

Re.99


2550 B

7 Oil & Grease mg/L BDL* BDL* BDL* BDL* 0.6 BDL * BDL* BDL* 0.2 BDL* 0.4 BDL* APHA(22ndEdi)

5520D



NEDA


as NH3 mg/L 0.4 0.56 0.56 0.7 0.72 0.86 0.66 0.7 0.5 0.62 0.221 0.351

IS3025(P34)88Cla.2.3


4500 C


13 Petroleum

Hydrocarbon mg/L BDL* BDL* BDL* BDL* 12.4 BDL* 8.6 BDL* 6.4 BDL* 6.2 BDL* PLPL-TPH

14 Total Dissolved

Solids mg/L 52105 52640 51610 51740 50680 51120 53200 53880 51240 51630 46326 47880

IS3025(P16)84Re.02


Reflux


Organic Carbon % 0.98 0.38 0.72 0.48 0.54 0.32 0.64 0.4 0.48 0.66 0.55 0.43

SOP – PLPL - 07

A Flora and Fauna


2.1 0.8 2.02 0.9 2.925 0.225 2.25 0.45 1.8 0.563 1.125 0.338 APHA (22nd Edi) 10200-J

43




B Phytoplankton

18.1

Chlorophyll mg/m

3 5.2 3.57 2.46 2.67 3.284 0.374 2.1 0.267 1.97 0.107 1.44 0.32


18.2

Phaeophytin mg/m

3 BDL* BDL* 0.12 BDL* BDL * 2.205 0.246 2.31 0.155 1.762 0.689 1.511


18.3


270 205 312 169 364 87 278 69 220 55 196 42 APHA (22nd

Edi) 10200-H

18.4



group

--


Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae

Bacillariophyceae


Gyrosigma sp.

Fragillaria sp.

Gyrosigrea sp.

Fragillaria sp.

Rhizosolenia sp.

Biddulphia sp.

Fragillaria sp.

Nitzschia sp.

Asterionella sp.

Fragillaria sp.

Rhizosolenia sp.

Fragillaria sp.

Navicula sp.

Nitzschia sp.

Thalassionema sp.

Gyrosigna sp.

Skeletonema sp.

Pinnularia sp.

Rhizosolenia sp.

Melosira sp.

Nitzschia sp.

Nitzschia sp.

Nitzschia sp.

Nitzschia sp.

Thalassiosira sp.

Melosira sp.

Synedra sp.

Thalassionema sp.

Synedra sp.

Pleurosigma sp.

Nitzschia sp.

Pleurosigma sp.

Navicula sp.

Navicula sp.

Navicula sp.

Navicula sp.

Synedra sp.

-- Green algae

-- Navicula

sp. Green Algae

Synedra sp.

Cymbella sp.

Coscinodiscus sp.

Gyro sigma sp.

Coscinodiscus sp.

Gyrosigma sp.

Green algae

-- Spirogyra

sp. --

Cyanophyceae

Navicula sp.

Spirulina sp.

Lyngbya sp.

Volvox sp.

Pleurosigma sp.

Green Algae

Pleurosigma sp.

Cyanophyceae

Pleurosigma sp.

Green Algae

Spirogyra sp.

-- Chlorella

sp. --

Green Algae

-- Green Algae

Chlorella sp.

Fragillaria sp.

Oscillatoria sp.

Thallasionema sp.

Chlorella sp.

-- -- Ankistrod

esmus sp.

-- Microcyst

is sp. --

Chlorella sp.

Pandorina sp.

Pinnularia sp.

Spirulina sp.

Cyanophyceae

Pandorina sp.

-- -- -- -- Chlorella

sp. --

Pandorina sp.

-- Green Algae

-- Oscillator

ia sp. --

-- -- -- -- Pandorin

a sp. --

Ulothrix sp.

-- Ankistrod

esmus sp.

-- Nostoc

sp. --

-- -- -- -- -- -- Hydrodictyon sp.

-- Chlorella

sp. --

Green Algae

--

-- -- -- -- -- -- -- -- Volvox

sp. --

Chlorella sp.

--

-- -- -- -- -- -- -- -- Hydrodiclyon sp.

-- Pediastru

m sp. --

C Zooplanktons

44




19.1


no/m2 400 300 350 260 270 120 190 50 210 60 325 75 APHA (22nd

Edi) 10200-G

19.2



group

--

Copepods

Decapod larvae

Copepods Decapods Nematod

es Foraminif

erans Polychaete Worms

Foraminiferans

Copepods

Copepods

Polychaete worms

Copepods


Polychaetes

Polychaetes

Polychaeteworms

Polychaeteworms

-- Polychaete Worms

Decapods

Nematodes

Molluscans

Ostracods

Krill Nematod

es

Gastropods

Ostracods

Gastropods

Ostracods

-- -- Cyclops Lamellibranches

Polychaete Worms

Crustaceans

Isopods --

Foraminiferans

-- Decapods -- -- -- Chaetogn

athes -- Knill --

Gastropods

--

Ctenophores

-- Mysids -- -- -- Mollusca

ns --

Gastropods

-- -- --

19.3


30 18 89 22 48 20 37 12 82 14 72 11 APHA (22nd

Edi) 10200-G


20.1


CFU/ml

1927 2177 2130 2410 2250 2500 1925 1350 1850 1430 1470 1180 IS 5402:2002

20.2


9221-D

20.3


05)

20.4


:2002

20.5


20.6


20.7


45




RESULTS OF MARINE WATER [M12 SPM N 22°40'938" E 069°39'191"]

SR. NO.

TEST PARAMETERS UNIT

April 2015 May 2015 June 2015 August 2015 September 2015

Test Method SURFACE

BOTTOM

SURFACE BOTTO

M SURFACE BOTTOM SURFACE BOTTOM SURFACE BOTTOM

1 pH -- 7.99 8.11 8.06 8.17 8.1 8.13 8.14 8.2 7.99 8.05 IS3025(P11)83Re.

02

2 Temperature oC 30 31 29 30 29 30 29 30 29 30 IS3025(P9)84Re.0

2

3 Total Suspended Solids mg/L 16 21 14 18 22 28 18 26 20 26 IS3025(P17)84Re.

02

4 BOD (3 Days @ 27 oC) mg/L BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* BDL* IS 3025

(P44)1993Re.03Edition2.1

5 Dissolved Oxygen mg/L 5.4 4.6 5.6 4.4 5.4 4.6 5.6 4.8 5.8 4.6 IS3025(P38)89Re.

99

6 Salinity ppt 41.4 41.8 41.6 42 39.8 40.4 40.2 41.8 39.6 40.1 APHA (22ndEdi)

2550 B

7 Oil & Grease mg/L BDL* BDL* BDL* BDL* BDL * BDL * BDL* BDL* BDL* BDL* APHA(22ndEdi)552

0D

8 Nitrate as NO3 mg/L 0.56 0.69 0.36 0.51 0.52 0.58 0.48 0.54 0.458 0.888 IS3025(P34)88

9 Nitrite as NO2 mg/L 0.081 0.102 0.072 0.096 0.048 0.072 0.12 0.18 0.037 0.063 IS3025(P34)88

NEDA

10 Ammonical Nitrogen as

NH3 mg/L 0.56 0.62 0.69 0.72 0.84 0.63 0.74 0.82 0.887 1.06

IS3025(P34)88Cla.2.3

11 Phosphates as PO4 mg/L 0.094 0.098 0.14 0.16 0.18 0.2 0.16 0.18 0.585 0.675 APHA(22ndEdi)

4500 C

12 Total Nitrogen mg/L 3.8 4.1 1.12 1.32 1.42 1.3 1.34 1.54 1.382 2.011 IS3025(P34)88

13 Petroleum Hydrocarbon mg/L 4 BDL* BDL* BDL* BDL* BDL* BDL* BDL* 1.56 BDL* PLPL-TPH

14 Total Dissolved Solids mg/L 49608 51210 48710 49810 47480 48120 48020 51308 47310 47738 IS3025(P16)84Re.

02

15 COD mg/L 18 24 24 31 18 20 16 20 24 28 APHA(22ndEdi) 5520-D Open

Reflux


Organic Carbon % 0.76 0.42 0.46 0.3 0.49 0.24 0.68 0.4 0.52 0.32 SOP – PLPL - 07

A Flora and Fauna

17 Primary productivity mgC/L/

day 3.1 1.2 1.35 0.45 2.475 1.013 1.91 0.675 1.575 0.225

APHA (22nd Edi) 10200-J

B Phytoplankton

46




18.1

Chlorophyll mg/m3 3.39 3.81 1.28 0.67 2.67 0.481 1.7 0.427 1.362 0.187 APHA (22ndEdi)

10200-H

18.2

Phaeophytin mg/m3 BDL* BDL* 1.3 1.91 BDL* 2.099 1.65 1.23 0.844 1.77 APHA (22ndEdi)

10200-H

18.3


225 182 179 93 321 40 245 47 225 31 APHA (22nd Edi)

10200-H

18.4

Name of Group Number and name of group

species of each group --

Diatom Diatom Diatom Diatom Bacillarioph

yceae Bacillarioph

yceae Bacillarioph

yceae Bacillarioph

yceae Bacillarioph

yceae Bacillarioph

yceae


Coscinodiscus sp.

Coscinodiscus sp.

Coscinodiscus sp.

Coscinodiscus sp.

Nitzschia sp.

Cymbella sp.

Gyro sigma sp.

Amphora sp.

Rhizosolenia sp.

Thallasionema sp.

Melosira sp.

Asterionalla sp.

Nitzschia sp.

Asterionella sp.

Gomphonema sp.

Nitzschia sp.

Pinnularia sp.

Coscinodiscus sp.

Nitzschia sp.

Fragillaria sp.

Nitzschia sp.

Navicula sp.

Synedra sp. Navicula

sp. Pleurosigm

a sp Synedra

sp. Synedra

sp. Navicula

sp. Navicula

sp. Synedra

sp. Synedra

sp. Cyanophy

ceae Thalassione

ma sp. Nitzschia

sp. Rhizosoleni

a sp. Green Algae

Nitzschia sp.

Synedra sp.

Thallasionema sp.

Pleurosigma sp.

Thalassiosira sp.

Oscillatoria sp.

Biddulphia sp.

-- Cyanophyc

eae Chlorella

sp. Thallasiosir

a sp Fragillaria

sp. Coscinodisc

us sp. Asterionella

sp. Biddulphi

a sp. -- Cynbella --

Oscillatoria sp.

-- Pleurosigm

a sp. Green Algae

Fragillaria sp.

Cyanophyceae

-- -- -- -- Desmids -- Cyanophyc

eae Chlorella

sp. Cyanophyc

eae Oscillatoria

sp.

-- -- -- -- Cosmarium

sp. --

Oscillatoria sp.

Pandorina sp.

Oscillatoria sp.

Desmids

-- -- -- -- Closterium

sp. --

Spirulina sp.

Pediastrum sp.

Nostoc sp. Closterium

sp.

-- -- -- --

-- -- Green Algae

Green Algae

--

-- -- -- --

-- -- Chlorella

sp. Chlorella

sp. --

-- -- -- --

-- -- Volvox sp. Volvox sp. -- C Zooplanktons

19.1

Abundance (Population) no/m2 620 460 480 280 210 130 250 100 280 150 APHA (22nd Edi)

10200-G

19.2

Name of Group Number and name of group

species of each group --

Polychaetes

Bivalves Polychaete

worms Bivalves Nematodes

Polychaete Worms

Copepods Copepods Copepods Isopods


Chaetognaths

Snails Chaetognat

hs Isopods Gastropods Bryozoans Krill

Polychaete Worms

Decapods Hydrozoans

Gastropods

Molluscans

Gastropods Hydrozo

ans Muds

Skipper Snail Gastropods

Crustaceans

Nematodes Namatodes

Bivalves Hydrozoa

ns Bivalves -- Bivalves Hydrozoans Decapods -- Isopods --

47




-- Isopods Decapods -- -- --

Polychaete Worms

& Ostracods

-- Krill --

19.3

Total Biomass ml/100

m3 27 12 36 17 102 28 89 16 75 9


D Microbiological

Parameters

20.1

Total Bacterial Count CFU/ml 2009 1927 2800 1825 2560 2240 1710 1280 1590 1320 IS 5402:2002

20.2

Total Coliform /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent APHA(22ndEdi)922

1-D

20.3

Ecoli /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS:1622:1981Edi.

2.4(2003-05)

20.4

Enterococcus /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 15186 :2002

20.5

Salmonella /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 5887 (P-3)

20.6

Shigella /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 1887 (P-7)

20.7

Vibrio /ml Absent Absent Absent Absent Absent Absent Absent Absent Absent Absent IS : 5887 (P-5)

48




RESULTS OF ETP WATER OUTLET

SR. NO.

PARAMETERS UNIT Liquid Terminal ETP Outlet TEST METHOD April 2015 May 2015 June 2015 July 2015 August 2015 September

2015

1 Colour Co-pt 50 40 20 30 30 20 IS3025(P4)83Re.02

2 pH -- 6.7 7.1 6.56 6.92 7.08 7.17 IS3025(P11)83Re.02

3 Temperature oC 32 31 30 30 30 30 IS3025(P9)84Re.02

4 Total Suspended Solids mg/L 40 38 20 28 24 26 IS3025(P17)84Re.02

5 Total Dissolved Solids mg/L 1890 1890 1562 1909 1960 2024 IS3025(P16)84Re.02

6 COD mg/L 84 92 98 82 92 96 APHA(22ndEdi) 5520-D Open Reflux

7 BOD (3 Days @ 27 oC) mg/L 30 26 28 18 20 24 IS 3025 (P44)1993Re.03Edition2.1

8 Chloride as Cl mg/L 589 587 560 390 540 584 IS3025(P32)88Re.99

9 Oil & Grease mg/L 0.8 0.4 BDL* 0.6 0.2 1 APHA(22ndEdi)5520D

10 Sulphate as SO4 mg/L 174 160 150 220 190 167 APHA(22ndEdi)4500 SO4 E

11 Ammonical Nitrogen as NH3 mg/L 2.1 3.1 4.4 5.6 3 1.75 IS3025(P34)88Cla.2.3

12 % Sodium as Na % 42 45.56 46.19 48.44 44.8 49.26 AAS APHA(22ndEdi) 3500 NA B/ Flame Photometer

13 Nickel as Ni mg/L 0.014 BDL* BDL* BDL* BDL* 0.018 AAS APHA(22ndEdi)3111 B

14 Phenolic Compound mg/L BDL* BDL* BDL* BDL* BDL* BDL* IS3025(P43)92Re.03

15 SAR -- 4.6 6.02 5.4 5.8 BDL* 8.88 By Calculation

16 Total Chromium as Cr+3 mg/L BDL* BDL* BDL* BDL* BDL* BDL* AAS 3111B

17 Hexavalent Chromium as Cr+6

mg/L BDL* BDL* 0.018 BDL* BDL* BDL* APHA(22ndEdi)3500Cr B Colorimetric method

18 Copper as Cu mg/L 0.018 0.011 BDL* 0.012 0.01 0.01 AAS APHA(22ndEdi)3111 B

19 Lead as Pb mg/L BDL* BDL* BDL* BDL* BDL* BDL* AAS APHA(22ndEdi)3111 B

20 Sulphide as S mg/L BDL* BDL* BDL* BDL* BDL* BDL* APHA(22ndEdi) 4500-S

21 Mercury as Hg mg/L BDL* BDL* BDL* BDL* BDL* BDL* AAS APHA- 3112 B

22 Zinc as Zn mg/L 0.066 0.031 0.026 0.042 0.03 0.024 AAS APHA(22ndEdi)3111 B

23 Cadmium as Cd mg/L BDL* BDL* BDL* BDL* BDL* BDL* AAS APHA(22ndEdi)3111 B

24 Cyanide as CN mg/L BDL* BDL* BDL* BDL* BDL* BDL* APHA(22ndEdi)4500CN E

25 Arsenic as As mg/L BDL* BDL* BDL* BDL* BDL* BDL* AAS APHA 3114 B

26 Fluoride as F mg/L 0.72 0.8 0.62 0.74 0.66 BDL* APHA(22ndEdi) 4500 F D SPANDS

27 Insecticides/Pesticides mg/L BDL* BDL* BDL* BDL* BDL* BDL* GC MS

*Below detection limit

49




RESULT OF AMBIENT AIR QUALITY MONITORING

Location & Parameter Unit April 2015

May 2015

June 2015

July 2015

August 2015

September 2015

Test Method

T1 TERMINAL

Respirable Particulate Matter (PM10) µg/m3 75.26 72.81 76.16 79.38 82.88 75.96 IS:5182(P23):Gravimetric CPCB - Method (Vol.I,May-2011)

Particulate Matter (PM2.5) µg/m3 41.80 36.60 41.73 40.87 40.29 38.96 Gravimetric- CPCB - Method (Vol.I,May-2011)

Sulphur Dioxide as SO2 µg/m3 14.27 15.20 15.32 15.45 14.66 11.62 IS:5182(PII):Improved West and Gaeke

Oxides of Nitrogen as NO2 µg/m3 32.09 33.41 34.85 33.22 33.14 30.58 IS:5182(PVI): Jacob & Hochheiser modified (NaOH-NaAsO2)

Method

Carbon Monoxide as CO mg/m3 0.45 0.51 0.55 0.53 0.51 0.44 NDIR Digital Gas Analyzer

Hydrocarbon as CH4 mg/m3 BDL* BDL* BDL* BDL* BDL* BDL* SOP: HC: GC/GCMS/Gas analyzer

Benzene as C6H6 µg/m3 BDL* BDL* BDL* BDL* BDL* BDL* IS 5182 (Part XI):2006/CPCB Method

NEAR FIRE STATION





Method




PUB /ADANI HOUSE





Method




50






May 2015

June 2015

July 2015

August 2015

September 2015

Test Method

AIR STRIP





Method




NEAR SHANTIVAN COLONY’S STP





Method

WTP NEAR CETP





Method

Hydrogen Sulphide (H2S) µg/m3 BDL* BDL* BDL* BDL* BDL* BDL* IS 5182 (Part-VII) 1973

Note: Monthly average is calculated from result of 24 hourly &twice in a week monitoring.

51






May 2015

June 2015

July 2015

August 2015

September 2015

Test Method

CT3 DG HOUSE





Method




52




RESULTS OF NATIONAL AMBIENT AIR QUALITY MONITORING

WEST PORT T1 TERMINAL NEAR FIRE STATION

PUB /ADANI HOUSE

AIR STRIP

NEAR SHANTIVAN COLONY’S

STP

WTP NEAR CETP

CT3 DG HOUSE METHOD OF

MEASUREMENT

TEST PARAMETER UNIT 08/04/2015 08/04/2015 08/04/2015 09/04/2015 07/04/2015 09/04/2015 08/04/2015

Respirable Particulate Matter (PM10)

µg/m3 92.92 78.82 55.50 73.11 57.50 78.68 57.13 IS:5182(Part

23):Gravimetric CPCB - Method (Vol.I,May-2011)

Particulate Matter (PM 2.5)

µg/m3 51.45 45.03 44.14 35.54 36.23 37.17 31.28 Gravimetric- CPCB -

Method (Vol.I,May-2011)

Lead as Pb µg/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)

Benzo (a) Pyrene (BaP)- particulate phase only

ng/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)

Arsenic as As ng/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)

Nickel as Ni ng/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)

Carbon Monoxide as CO mg/m3 0.34 0.16 0.44 0.34 0.48 0.45 0.27 NDIR Digital Gas Analyzer

Benzene as C6H6 µg/m3 BDL* 2.16 BDL* BDL* BDL* BDL* BDL* IS 5182 (Part

XI):2006/CPCB Method

Ammonia (NH3) µg/m3 46.54 28.44 34.53 44.73 25.52 43.57 22.48 CPCB Method (Vol.I,May-

2011)

Sulphur Dioxide (SO2) µg/m3 15.34 19.70 16.70 10.68 12.52 21.55 13.29 IS:5182(Part 2):

Improved West and Gaeke

Oxides of Nitrogen as

NO2 µg/m3 41.36 30.20 36.41 24.54 26.48 33.36 32.39

IS:5182(Part 6):Modified Jacob &

Hochheiser (Na-Arsenite)

Ozone as O3 µg/m3 21.47 25.38 22.35 19.52 18.08 25.82 18.68 IS 5182 (PART IX) 1974 / CPCB Method (Vol.I,May-

2011)

Hydrocarbon as CH4 ppm BDL* BDL* BDL* BDL* BDL* BDL* BDL* SOP: HC: GC/GCMS/Gas

analyzer

53




RESULTS OF NATIONAL AMBIENT AIR QUALITY MONITORING

WEST PORT T1 TERMINAL NEAR FIRE STATION

PUB /ADANI HOUSE

AIR STRIP

NEAR SHANTIVAN COLONY’S

STP

WTP NEAR CETP

CT3 DG HOUSE METHOD OF

MEASUREMENT

TEST PARAMETER UNIT 17/07/2015 17/07/2015 17/07/2015 18/07/2015 16/07/2015 18/07/2015 17/07/2015

Respirable Particulate Matter (PM10)

µg/m3 86.63 79.63 54.89 67.47 62.63 73.52 65.71 IS:5182(Part

23):Gravimetric CPCB - Method (Vol.I,May-2011)

Particulate Matter (PM 2.5)

µg/m3 48.54 32.52 24.57 27.60 39.14 37.17 34.61 Gravimetric- CPCB -

Method (Vol.I,May-2011)

Lead as Pb µg/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)


ng/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)

Arsenic as As ng/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)

Nickel as Ni ng/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* CPCB Method (Vol.I,May-

2011)

Carbon Monoxide as CO mg/m3 0.70 0.46 0.58 0.41 0.60 0.6 0.64 NDIR Digital Gas Analyzer

Benzene as C6H6 µg/m3 BDL* BDL* BDL* BDL* BDL* BDL* BDL* IS 5182 (Part

XI):2006/CPCB Method

Ammonia (NH3) µg/m3 58.51 36.39 46.74 40.63 21.69 36.8 32.64 CPCB Method (Vol.I,May-

2011)

Sulphur Dioxide (SO2) µg/m3 18.80 11.23 22.78 13.73 13.58 20.53 14.54 IS:5182(Part 2):


Oxides of Nitrogen as

NO2 µg/m3 41.66 36.46 39.52 30.42 35.36 33.47 30.07

IS:5182(Part 6):Modified Jacob &


Ozone as O3 µg/m3 24.50 28.39 26.58 21.72 21.48 23.41 22.42 IS 5182 (PART IX) 1974 / CPCB Method (Vol.I,May-

2011)

Hydrocarbon as CH4 ppm BDL* BDL* BDL* BDL* 62.63 BDL* BDL* SOP: HC: GC/GCMS/Gas

analyzer

54




RESULTS OF STACK MONITORING

SR. NO.

TEST PARAMETERS Unit

D.G. Set-1* (1500 KVA) D.G. Set-2* (1500 KVA) D.G. Set-3* (1500 KVA) Test Method

April-2015

1 Particulate Matter mg/Nm3 44.56 38.71 48.53 IS:11255 (Part-I):1985

2 Sulfur dioxide ppm 5.75 2.94 3.25 IS:11255 (Part-II):1985

3 Oxides of Nitrogen ppm 25.43 29.45 33.45 IS:11255 (Part-VII):2005

SR. NO.


D.G. Set-1* (1500 KVA) D.G. Set-2* (1500 KVA) D.G. Set-3* (1500 KVA) Test Method

July-2015

1 Particulate Matter mg/Nm3 38.2 45.82 42.72 IS:11255 (Part-I):1985

2 Sulfur dioxide ppm 7.7 10.62 5.35 IS:11255 (Part-II):1985

3 Oxides of Nitrogen ppm 36.53 34.17 36.04 IS:11255 (Part-VII):2005

*DG sets are used as standby, so stack monitoring is done on quarterly basis.

Results on 11 % O2 Correction when Oxygen is greater than 11 %

55




RESULTS OF NOISE LEVEL MONITORING RESULTS OF NOISE LEVEL MONITORING [DAY TIME]

Noise level in dB (A) Leq - Average Limits in dB (A) Leq

Sr. No. Location Name April 2015 May 2015 June 2015 July 2015 August 2015 September

2015

1 CT3 (Nr. D.G. House) 68.9 64.6 65 58.4 61.9 62.9 75 dB (A) Leq

RESULTS OF NOISE LEVEL MONITORING [NIGHT TIME]

Noise level in dB (A) Leq - Average Limits in dB (A) Leq

Sr. No. Location Name April 2015 May 2015 June 2015 July 2015 August 2015 September

2015

1 CT3 (Nr. D.G. House) 68.8 60 62.9 52 55.9 58.8 70 dB (A) Leq

56




MINIMUM DETECTION LIMIT [MDL]

Water parameter(mg/L)

Sr. No. Test parameter MDL 1 Total Suspended Solids 1

2 Oil & Grease 1 3 BOD 10

4 COD 5

6 Total Dissolved Solids 3 7 Sulphate 0.3

8 Ammonical Nitrogen 0.05 9 Nickel 0.01

10 Phenolic Compound 0.001 11 Fluoride 0.01

12 Copper 0.013 13 Sulphide 0.01

15 Cyanide 0.0001

16 Residual Chlorine 0.1 17 Boron 0.02

17 Insecticides/Pesticides 0.01 19 Nitrate Nitrogen 0.15

20 Phosphorous 0.15 21 Petroleum Hydrocarbon 0.01

22 Lead 0.005 23 Mercury 0.0005

24 Zinc 0.022

25 Cadmium 0.001 26 Arsenic 0.00015

Sediment parameter(mg/kg) 1 Petroleum Hydrocarbon 0.2

Stack parameter

Sr. No. Test parameter MDL

1 Particulate Matter

(mg/Nm3) 10

2 Sulphur Dioxide(ppm) 1.52

3 Oxides of Nitrogen (ppm) 2.65

57





Ambient Air Parameter

Sr. No. Test parameter MDL

1 Particulate Matter (PM10) 10

2 Particulate Matter (PM 2.5) 10

3 Lead as Pb (µg/m3) 0.5

4 Benzo (a) Pyrene (BaP)- particulate phase only(ng/m3) 0.5

5 Arsenic as As (ng/m3) 2

6 Nickel as Ni (ng/m3) 10

7 Carbon Monoxide as CO (mg/m3) 1

8 Benzene as C6H6 (µg/m3) 2

9 Ammonia (NH3) (µg/m3) 10

10 Sulphur Dioxide (SO2) (µg/m3) 5

11 Oxides of Nitrogen (NO2) (µg/m3) 5

12 Ozone as O3 (µg/m3) 5

13 Hydrocarbon (µg/m3) 150

58




“HALF YEARLY ENVIRONMENTAL

MONITORING REPORT”

FOR

WATER FRONT DEVELOPMENT PROJECT [WEST PORT]

ADANI PORTS AND SPECIAL ECONOMIC ZONE LIMITED

TAL: MUNDRA, KUTCH, MUNDRA – 370 421

MONITORING PERIOD:

APRIL 2015 TO SEPTEMBER 2015

PREPARED BY:

POLLUCON LABORATORIES PVT.LTD.

544, BELGIUM TOWERS, RING ROAD, SURAT – 395 003 PHONE/FAX – (+91 261) 2455 751, 2601 106, 2601 224.

E-mail: [email protected] Web: www.polluconlab.com

T 0820 - 821 ISO 9001:2008 ISO 14001:2004 OHSAS 18001:2007

59

mailto:[email protected]

http://www.polluconlab.com/




RESULTS OF STP WATER OUTLET

SR. NO.


SHANTIVAN COLONY STP OUTLET (250 KLD)

April 2015

May 2015

June 2015

July 2015

August 2015

September 2015

TEST METHOD

1 pH -- 7.4 8.1 7.8 7.8 7.79 7.56 IS3025(P11)83Re.02

2 Total Suspended Solids mg/L 26 20 8.0 22 24 26 IS3025(P17)84Re.02


4 Residual Chlorine mg/L 0.7 0.7 0.5 0.7 0.6 0.5 APHA(22ndEdi)4500 Cl

60




SR. NO.


SHANTIVAN COLONY STP OUTLET (350 KLD)

April 2015

May 2015

June 2015

July 2015

August 2015

September 2015

TEST METHOD

1 pH -- 7.1 7.02 7.63 7.67 7.96 7.93 IS3025(P11)83Re.02

2 Total Suspended Solids mg/L 26 22 18 20 24 22 IS3025(P17)84Re.02


4 Residual Chlorine mg/L 0.5 0.6 0.5 0.6 0.7 0.5 APHA(22ndEdi)4500 Cl

Note: - As sewage generation from west port is treated at STP location near to Shantivan colony.

61






May 2015

June 2015

July 2015

August 2015

September 2015

Test Method

WEST PORT - VIEW POINT

Respirable Particulate Matter (PM10) µg/m3 70 65.72 72.43 72.94 74.98 75.90 IS:5182(P23):Gravimetric CPCB - Method (Vol.I,May-2011)



Oxides of Nitrogen as NO2 µg/m3 29.37 27.16 29.73 32.98 30.91 31.99 IS:5182(PVI): Jacob & Hochheiser modified (NaOH-NaAsO2) Method




WEST PORT - MAIN GATE








WEST PORT - Horticulture








Note: Monthly average is calculated based on 24 hourly & twice a week monitoring results

62




RESULT OF NATIONAL AMBIENT AIR QUALITY MONITORING

WEST PORT WEST PORT -VIEW POINT

WEST PORT - HORTI CULTURE

WEST PORT - MAIN GATE METHOD OF MEASUREMENT

TEST PARAMETER UNIT 07th April 2015

Respirable Particulate Matter (PM10) µg/m3 64.63 64.01 68.92 IS:5182(Part 23):Gravimetric CPCB - Method

(Vol.I,May-2011)

Particulate Matter (PM 2.5) µg/m3 34.61 31.12 38.36 Gravimetric- CPCB - Method (Vol.I,May-2011)

Lead as Pb µg/m3 BDL* BDL* BDL* CPCB Method (Vol.I,May-2011)


ng/m3 BDL* BDL* BDL* CPCB Method (Vol.I,May-2011)

Arsenic as As ng/m3 BDL* BDL* BDL* CPCB Method (Vol.I,May-2011)

Nickel as Ni ng/m3 BDL* BDL* BDL* CPCB Method (Vol.I,May-2011)

Carbon Monoxide as CO mg/m3 0.30 0.62 0.25 NDIR Digital Gas Analyzer

Benzene as C6H6 µg/m3 BDL* BDL* BDL* IS 5182 (Part XI):2006/CPCB Method

Ammonia (NH3) µg/m3 20.38 34.38 46.61 CPCB Method (Vol.I,May-2011)

Sulphur Dioxide (SO2) µg/m3 8.40 14.34 19.31 IS:5182(Part 2):


Oxides of Nitrogen as NO2 µg/m3 32.50 35.50 38.56 IS:5182(Part 6):Modified Jacob &


Ozone as O3 µg/m3 20.41 27.48 29.41 IS 5182 (PART IX) 1974 / CPCB Method

(Vol.I,May-2011)

Hydrocarbon as CH4 ppm BDL* BDL* BDL* SOP: HC: GC/GCMS/Gas analyzer

63




RESULT OF NATIONAL AMBIENT AIR QUALITY MONITORING

WEST PORT WEST PORT -VIEW POINT

WEST PORT - HORTI CULTURE

WEST PORT - MAIN GATE METHOD OF MEASUREMENT

TEST PARAMETER UNIT 16th July 2015

Respirable Particulate Matter (PM10) µg/m3 76.01 69.41 93.70 IS:5182(Part 23):Gravimetric CPCB - Method

(Vol.I,May-2011)

Particulate Matter (PM 2.5) µg/m3 40.45 27.38 50.45 Gravimetric- CPCB - Method (Vol.I,May-2011)

Lead as Pb µg/m3 BDL* BDL* BDL* CPCB Method (Vol.I,May-2011)

Benzo (a) Pyrene (BaP)- particulate

phase only ng/m3 BDL* BDL* BDL* CPCB Method (Vol.I,May-2011)

Arsenic as As ng/m3 BDL* BDL* BDL* CPCB Method (Vol.I,May-2011)

Nickel as Ni ng/m3 BDL* BDL* 10.12 CPCB Method (Vol.I,May-2011)

Carbon Monoxide as CO mg/m3 0.25 0.30 0.79 NDIR Digital Gas Analyzer

Benzene as C6H6 µg/m3 BDL* BDL* BDL* IS 5182 (Part XI):2006/CPCB Method

Ammonia (NH3) µg/m3 18.61 28.35 38.48 CPCB Method (Vol.I,May-2011)

Sulphur Dioxide (SO2) µg/m3 16.32 10.39 23.20 IS:5182(Part 2):


Oxides of Nitrogen as NO2 µg/m3 22.66 30.43 41.20 IS:5182(Part 6):Modified Jacob &


Ozone as O3 µg/m3 18.77 24.43 27.51 IS 5182 (PART IX) 1974 / CPCB Method

(Vol.I,May-2011)

Hydrocarbon as CH4 ppm BDL* BDL* BDL* SOP: HC: GC/GCMS/Gas analyzer

64




RESULT OF STACK MONITORING

April 2015 July 2015

SR.

NO. TEST PARAMETERS Unit

D.G. Set-1*

(1500 KVA)

D.G. Set-2*

(1500 KVA)

D.G. Set-1*

(1500 KVA)

D.G. Set-2*

(1500 KVA) Test Method

1 Particulate Matter mg/Nm3 46.42 32.40 52.64 44.92 IS:11255 (Part-I):1985

2 Sulphur Dioxide ppm 2.54 4.49 5.83 3.44 IS:11255 (Part-II):1985

3 Oxides of Nitrogen ppm 24.60 26.96 29.33 29.50 IS:11255 (Part-VII):2005

*DG sets are used as standby, so stack monitoring is done on quarterly basis.

Results on 11 % O2 Correction when Oxygen is greater than 11 %,

65




RESULT NOISE LEVEL MONITORING RESULT OF NOISE LEVEL MONITORING [DAY TIME]

Noise in dB (A) Leq - Average Limits in dB(A) Leq Sr. No. Location Name April 2015 May 2015 June 2015 July 2015 August 2015

September 2015

1 W.B.Main Gate 57.6 56.2 65.8 69.4 55.6 56.3

75 dB (A) Leq 2 W.B.Horticulture Cabin 57.8 68.1 64.0 63.6 67.5 70.1

3 W.B.View Point 60.8 73.9 65.4 66.2 57.2 72.3

RESULT OF NOISE LEVEL MONITORING [NIGHT TIME]

Noise in dB (A) Leq - Average Limits in dB(A) Leq Sr. No. Location Name April 2015 May 2015 June 2015 July 2015 August 2015

September 2015

1 W.B.Main Gate 55.6 44.0 63.4 67.4 49.5 52.4

70dB (A) Leq 2 W.B.Horticulture Cabin 56.2 67.6 62.9 64.2 64.5 65.1

3 W.B.View Point 59.4 73.5 65.9 62.7 59.0 68.2

66





Ambient Air Parameter

Sr.

No. Test parameter MDL

1 Particulate Matter (PM10) 10

2 Particulate Matter (PM 2.5) 10

3 Sulphur Dioxide (SO2) 5

4 Oxides of Nitrogen as NO2 5

5 Lead as Pb (µg/m3): 0.5

6 Benzo (a) Pyrene (BaP)- particulate phase only(ng/m3) 0.5

7 Nickel as Ni (ng/m3) 10

8 Benzene as C6H6 (µg/m3) 2

9 Arsenic as As (ng/m3) 2

10 Hydrocarbon (µg/m3) 150

Stack parameter

Sr.

No. Test parameter MDL

1 Particulate Matter (mg/Nm3) 10

2 Sulphur Dioxide (ppm) 1.52

3 Oxides of Nitrogen as NO2 (ppm) 2.65

67

MARINE MONITORING REPORT

October – 2015(Post-Monsoon)

FOR

M/s. ADANI POWER LIMITED

At

Tunda&Siracha, Tal. Mundra, Dist.: Kutch.

KUTCH, GUJARAT – 370 435

Prepared by

68

1

Prepared by: UniStar Environment & Research Labs Pvt. Ltd.

PREFACE

M/s. Adani Power Limited (APL) is a subsidiary company of Adani Group engaged in

imported coal based thermal power plant at Mundra near village Tunda&Siracha, Taluka

Mundra District Kutch, Gujarat has entrusted the work of carrying out Marine Monitoring to

M/s.UniStar Environment and Research Labs Pvt. Ltd., Vapi.

The monitoring involves Physio-chemical and biological analysis of Marine water. Marine

water quality of Sub-tidal and Intertidal regions, Flora and Fauna analysis in marine water

area and Benthos in inter-tidal and sub-tidal for the coastal area near power plant.

Water sample are collected from five location (station) and Benthos sample are collected

from High water and low water transect area. Samples are brought to the laboratory by field

sampling team and the analysis was carried out in our laboratory and the results are

presented in this report.

These Marine Monitoring reports provide a data obtained from monitoring and analysis

activities undertaken during October 2015.

Date :26/11/2015

M/s.UniStar Environment and

Research Labs Pvt. Ltd.

White house, Char Rasta,

Vapi-396 191

Sampling by Analysis by Approved by

69

2


TABLE OF CONTENTS

NO. Contents Page

no.

Introduction To Project

1.1 Background 4

1.2 Objectives 5

1.3 Study program 5

1.4 Sampling 7

Water quality

2.1 Marine Water quality 8

2.2 Physico-chemical Water analysis result 8

2.3 Marine Sediment analysis (Inter tidal & Sub tidal) 13

Biological characteristics (Biodiversity Studies)

3.1 Planktonic form 16

3.2. Significance of Phytoplankton & Zooplankton 17

3.3 Phytoplankton 17

3.3.1 Drop count method and microscopic observation 18

3.3.2 Planktonic diversity 18

3.4 Zooplankton 21

3.4.1 Drop count method and microscopic observation 21

3.4.2 Zooplankton diversity 21

3.5 Benthic fauna 24

3.5.1 Significance of benthic micro invertebrates 25

3.5.2 Methodology 25

3.5.3 Handling and preservative 27

3.5.4 Identification 27

3.5.5 Benthic biodiversity 27

3.6 Chlorophyll and Pheophytin 30

3.6.1 Method 31

3.6.2 Result 31

3.7 Conclusion 32

Sampling Photographs 33-34

70

3


Figure

No. Contents

Page

No.

Map / Photos / Images

1.1 Study location map 6

1.2 Phytoplankton photographs 20

1.3 Zooplankton photographs 23

1.4 Benthos diversity in project site 29

1.5 Degradation pathways of chlorophyll 30

Sampling Photographs 33-34

On site DO and Temperature analysis

Sediment sample for sub tidal area

Phytoplankton sample Collection

Zooplankton sample collection

benthos sampling

Chlorophyll sampling

Table

No. Contents

Page

no.

Tables

1 Station locations and co ordinates 5

2 Water sampling locations, Pre-Monsoon Season, October 2015 8

3 Analysis Table Of Marine Water Analysis 9

4 Analysis Table Of sub tidal sediment Analysis 13

5 Analysis Table Of Intertidal sediment Analysis 14

6 Test method for Phytoplankton & Zoo Plankton analysis 17

7 Phytoplankton Sampling Station 18

8 Total abundance & groups of phytoplankton observed at the sampling stations 19

9 Zooplankton Sampling Station 21

10 Total abundance, biomass and groups of zooplankton at the sampling stations 22

11 Test method for Benthos analysis 25

12 Sub-tidal Benthos Sampling Sites 26

13 Intertidal Benthos Sampling Sites 26

14 Standing stock and abundance of sub tidal macro benthos 28

15 Standing stock and abundance of Inter tidal macro benthos 29

16 Test method for Chlorophyll a &Pheophytin analysis 30

17 Chlorophyll a and Pheophytin 32

71

4


INTRODUCTION

1.1 Background

Adani Power Limited (APL) is a subsidiary company of Adani Group engaged in imported coal

based thermal power plant with capacity of 4620 MW at Mundra near village

Tunda&Siracha, Taluka Mundra District Kutch, Gujarat.

Adani Power is largest single location private coal based power plant in the world it created

history by synchronizing the first super-critical technology based 660MW generating unit at

Mundra. This is not only the first super-critical generating unit in the country but also the

fastest project implementation ever by any power developer in the country. The Phase III of

the Mundra Project, which is based on supercritical technology, has received ‘Clean

Development Mechanism (CDM) Project’ certification from United Nations Framework

Convention on Climate Change (UNFCCC). This is the world’s first thermal project based on

supercritical technology to get registered as CDM Project under UNFCCC.

Adani Power Ltd. assessing marine environment in terms of water quality, sediment

quality and biological study, with special reference to intake channel and seawater

discharge.

This report is prepared by the M/s.UniStar Environment and Research Labs Pvt. Ltd., at the

instance of APL and addresses the marine environmental issues related to the APL's

operational power plant.

72

5


1.2Objectives:

a) Physico-chemical water parameter to be analyzed for understands the water quality in

study area.

b) Sediment samples will be analyzed for estimate selected trace metals.

c) The prevailing biological status of the study area is evaluated based on thequantitative

and qualitative data on marine life namely Phytoplankton, zooplankton, Sub-tidal/

intertidal Macro benthos and fish stock.

d) To recommend adequate marine environmental management measures

1.3Study program:

Period:

The field investigation is completed during October 2015 (it’s a post-monsoon) and we were

planned in such a manner so as to get a detailed picture of the marine environment

characteristics of the study area during post-monsoon period. Sampling and analysis for

marine environment has been carried out by M/S. UniStar Environment and Research

LabsPvt. Ltd.

Study Station locations:

A total of fivesub-tidal station and three intertidal transects was selected for the sampling,

here we are given exact location and their position were sampled.

Table 1: Station locations and co ordinates

Sub-tidal Station

Station Locations Co ordinates

1 Intake point 220 48’ 37” N 690 32’ 85” E

2 Mouth of intake point 220 46’ 94” N 690 32’ 22” E

3 West port area 220 45’ 26” N 690 34’ 54” E

4 Outfall area 220 45’ 00” N 690 36’ 31” E

5 Outfall area 220 44’ 42” N 690 36’ 36” E

73

6


Intertidal transect

I High water level 220 47’38” N 690 32’ 19” E

Low water level 220 47’ 40” N 690 32’ 15” E

II High water level 220 45’ 62” N 690 34’ 43” E


III High water level 220 45’ 19” N 690 36’ 39” E


Figure 1.1: Study location map

74

7


1.4Sampling

a) Sampling frequency:

All Samplingsub-tidal stations were monitored during flood to ebb. Water samples were

collectedin duplicate (surface and bottom) for assessing water quality and biological

characteristics.

Intertidal sampling was completed during low tide, for assessed Macro benthic fauna

samples were collect in duplicate from each transects as well as other sediment samples.

b) Sampling methodology:

Niskin (5 litre capacity) with a mechanism for closing at a desired depth using

messenger was used for bottom water samples collecting sub–surface water

samples. Sampling at the surface was done using a clean polyethylene bucket.

For the analysis of Benthos sub-tidal sediment samples were collected using Van-

veen grab covering an area of 0.04 m2 as well as intertidal samples was collected

using metal quadrant.

Oblique hauls for Zooplankton were made using Heron Tranter net with calibrated

flow meter. All collection was of 5 min. duration after collection samples were

preserved in 5%formalin.

C) Methods of analysis:

I)Physicochemical Parameter: Samples were analyses by using analytical methods for

estimations of Temperature, Turbidity, PH, SS, Salinity, DO, BOD, COD, Phosphate, Total

nitrogen, Nitrite, Nitrate, Phenols and PHc.

II) Intertidal & Sub-tidal sediment QualityParameters are: Texture,Petroleum

Hydrocarbon(PHc), Phosphorus, Organic Carbon, Aluminium, Iron, Chromium, Nickel, Zinc,

Lead, Copper, Cobalt, Cadmium, Mercury, Arsenic

III)Biological Samples: Phytoplankton, Zooplankton and Macro benthos.

a) Phytoplankton: Sample for cell count was preserved in Lugol’s iodine solution, and

identification of phytoplankton was done under a compound microscope using Sedgwick

Rafter slide.

75

8


b) Chlorophyll: For the estimation of chlorophyll a and Pheophytin, the extinction of the

acetone extract was measured at 665 & 750 nm using spectrophotometer (HACH DR 5000)

before and after treatment with dilute acid respectively.

c) Zooplankton: Volume (biomass) was obtained by displacement method. A portion (25-50

%) of the sample was analyzed under a microscope for faunal composition and population

count.

d) Benthos: The total Macro benthos population (sub tidal& intertidal) was estimated as

number of 1 m2 area and biomass on wet weight basis.

WATER QUALITY

2.1 Marine Water quality:

Sea water samples have been collected during post - monsoon season, 2015

From Five locations, which are listed in Table 2.

Table 2: Water sampling locations, Post-Monsoon Season, October2015

Station no. Location Tide

1 Intake point Flood

2 intake point Ebb to Flood

3 West port area Flood to Ebb

4 Outfall area Flood

5 Outfall area Flood to Ebb

2.2 Physico chemical Water analysis result:

All the water sampled which is collected by sampling team is brought to the lab for Physico

chemical analysis. The water quality at different stations are measured during this

investigation is presented in Table No.3

76

9


Table: 3 Physico chemical Water Analysis Result

No. Parameters

Station 1 Station 2 Test Method Permissible

Surface Bottom Surface Bottom

PHYSICAL QUALITY

1. pH @ 25 ° C 7.8 7.9 7.9 8.0 IS 3025(Part 11)1983

2. Temperature ( 0C ) 32.0 32.2 31.5 31 IS 3025(Part 9)1984

3. Turbidity (NTU) <5

<5

<5

<5 IS 3025(Part 10)1984

CHEMICAL QUALITY

1. Total Suspended Solids (mg/l)

18 24 26 32 (APHA 22ndEd.,2012,2540-

D)

2. Biochemical Oxygen Demand (BOD) (mg/l)

2.9 3.8 2.9 2.9 IS 3025(Part 44)1993Amd.01

3. Sulphate as SO4(mg/l) 3046 3081 3210 3125 (APHA 22ndEd.,2012,4500-

SO4 E)

4. Ammonical Nitrogen)(µmol/l)

1.4 1.9 1.1 1.5 (APHA 22ndEd.,2012,4500-

NH3 B)

5. Salinity (ppt) 35.9 36.1 35.0 35.2 By Calculation

6. Dissolved Oxygen (mg/l)

7.0 7.3 6.7 7.0 IS 3025(Part 38)1989,

(APHA 22nd

Ed,4500-O,B),

7. Total Nitrogen (µmol/l) 40.7 43.4 45.4 47.7 APHA 22ndEd.,2012,4500 NH3 - B

8. Dissolved Phosphate (µmol/l)

2.1 2.3 2.2 2.4 (APHA 22

ndEd.,2012,4500-P,D)

9. Nitrate (µmol/l) 7.7 8.1 5.5 5.8 (APHA 22St Ed.,2012,4500 NO3-B)

10. Nitrite (µmol/l) 0.2 0.2 0.3 0.4 APHA 22St Ed.,2012,4500NO2B

11. Phenol(µmol/l) N.D. N.D. N.D. N.D. APHA 22ndEd.,2012,5530-C,

12. PHc (ppb) N.D. N.D. N.D. N.D. GC Method

Note: MDL = Minimum Detection Limit (MDL: 0.01) and N.D. = Not detectable

77

10


Sr.

No Parameters

Station 3 Station 4 Test Method Permissible


PHYSICAL QUALITY

1. pH @ 25 ° C 7.9 7.9 7.8 7.9 IS 3025(Part 11)1983

2. Temperature 0C 32.5 32.2 32.0 32.3 IS 3025(Part 9)1984

3. Turbidity (NTU) <5 <5 <5 <5 IS 3025(Part 10)1984

CHEMICAL QUALITY

1. Total Suspended Solids (mg/l)

12 15 14 18 (APHA 22ndEd.,2012,2540- D)


2.3 3.5 3.2 2.6 IS 3025(Part 44)1993Amd.01

3. Sulphate as SO4(mg/l)

3075 3210 3310 3375 (APHA 22ndEd.,2012,4500- SO4

E)

4. Ammonical Nitrogen(µmol/l)

N.D. N.D. N.D. N.D. (APHA 22ndEd.,2012,4500- NH3

B)

5. Salinity (ppt) 35.4 35.5 36.3 36.6 By Calculation

6. Dissolved Oxygen (mg/l) 7.3 70 6.7 7.0

IS 3025(Part 38)1989,

(APHA 22nd

Ed.,2012,4500)

7. Total Nitrogen (µmol/l) 57.1 58.6 61.6 62.1 APHA 22ndEd.,2012,4500 NH3 - B

8. DissolvedPhosphate (µmol/l)

2.0 2.1 2.0 2.3 (APHA 22

ndEd.,2012,4500-P,D)

9. Nitrate (µmol/l) 6.3 6.6 6.2 6.3 (APHA 22St Ed.,2012,4500 NO3-B)

10. Nitrite (µmol/l) 0.2 0.3 0.4 0.5 APHA 22St Ed.,2012,4500NO2B

11. Phenol(µmol/l) N.D. N.D. N.D. N.D. APHA 22ndEd.,2012,5530-C,

12. PHc (ppb) N.D. N.D. N.D. N.D. GC Method


78

11


Sr.

No. Parameters

Station 5 Test Method Permissible

Surface Bottom

PHYSICAL QUALITY

1. pH @ 25 ° C 8.0 8.1 IS 3025(Part 11)1983

2. Temperature ( 0C ) 32.0 31.5 IS 3025(Part 9)1984

3. Turbidity (NTU) <5

<5 IS 3025(Part 10)1984

CHEMICAL QUALITY

1. Total Suspended Solids 12 22 (APHA 22ndEd.,2012,2540- D)


2.3 2.3 IS 3025(Part 44)1993Amd.01

3. Sulphate as SO4 (mg/l) 3210 3260 (APHA 22ndEd.,2012,4500- SO4 E)

4. Ammonical Nitrogen(µmol/l)

N.D. N.D. (APHA 22ndEd.,2012,4500- NH3 B)

5. Salinity (ppt) 35.7 35.9 By Calculation

6. Dissolved Oxygen (mg/l) 6.7 7.0 IS 3025(Part 38)1989,

(APHA 22nd

Ed.,2012,4500-O,B),

7. Total Nitrogen (µmol/l) 59.1. 60.6 APHA 22ndEd.,2012,4500 NH3 - B

8. Dissolved Phosphate (µmol/l)

2.3 2.5 (APHA 22nd

Ed.,2012,4500-P,D)

9. Nitrate (µmol/l) 7.6 8.1 (APHA 22St Ed.,2012,4500 NO3-B)

10. Nitrite (µmol/l) 0.5 0.5 APHA 22St Ed.,2012,4500NO2B

11. Phenol(µmol/l) N.D. N.D. APHA 22ndEd.,2012,5530-C,

12. PHc(ppb) N.D. N.D. GC Method


a)Temperature: Marine water temperature of the study area was checked on site,

sosurfacewater temperature observed in the study area in range of 310 c and bottom water

temperature range was320 c. The water temperature generally varied in accordance with

the prevailing air temperature, tidal activity and seasonal variation.

b) pH: The pH of the water is generally buffering effect, influenced by the freshwater and

anthropogenic discharge from land. The observed pH in the study area in range of 7.8 to 8.0

at surface level and 7.9 to 8.1 at bottom level.

79

12


c) Turbidity: Turbidity in all the sampling stations is <5 because water were free from any

turbulence and moreover very clean during the sampling.

d) Salinity: Salinity which is an indicator of seawater, the standard average salinity of sea

water is 34 to 35 ppt, which is variable depending on the riverine flow, any fresh water

discharge from landward side, rainy season and temperature in study area. Average salinity

(ppt) for post monsoon study is 35.0 to 36.3ppt at surface water as well as 35.2 to 36.6ppt

at bottom water.

e) DO & BOD: High Dissolve oxygen level is measured of good oxidizing conditions in an

aquatic environment. In unpolluted waters equilibrium is maintained between its

generation through photosynthesis and dissolution from the atmosphere, and consumption

by the respiration and decay of organic matter in a manner that Dissolve oxygen levels are

close to or above saturation value.

Dissolve oxygen level of the study area is varied from 6.7 mg/l to 7.3 mg/l at water surface

level and 7.0 mg/l to 7.3 mg/l at water bottom level. The comparison of average Dissolve

oxygen value of post monsoon period is 7.0 mg/l which show the good oxidizing conditions

in study area aquatic environment.

BOD was generally indicating effective consumption of oxidisable matter in that water body.

BOD of the study area is varied from 2.3 mg/l to 2.9mg/l at water surface level and 2.3 mg/l

to 3.8 mg/l at water bottom level.

f)Nutrients: Dissolved phosphorus and nitrogen compounds serve as the nutrients for

phytoplankton which is the primary producer in aquatic food chain. Phosphorous

compounds are present predominantly as reactive phosphate while combined nitrogen is

present as nitrate, nitrite and ammonium species. So nutrient concentration (phosphate –

nitrate - nitrite)inthe study area is Phosphate range 2.0 to 2.3 µmol/l in surface water as

well as 2.1 to 2.5 µmol/l at bottom water area, Nitrate range 5.5 to 7.7 µmol/l in surface

water and 5.8to 8.1 µmol/l at bottom water, Nitrite range 0.2 to 0.5 µmol/l in surface level

and 1.1 to 2.8 µmol/l at bottom level. This nutrient concentration values indicate water

healthiness.

g)PHc and phenol: The level of PHc and Phenol is below detection level which indicates

insignificant influence of anthropogenic inputs on the water body in study area.

g)Total suspended solids: The suspended solids generally constitute clay, silt and sand from

the bed sediment and that from the upstream as well as contributed through shore erosion.

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13


Anthropogenic discharges also contribute to suspended solids in the form of contaminates

such as oil and solid waste in polluted area. Suspended solids in the study area are little

variable, surface area range observed 12 to 26 mg/l as well as bottom area range is 14 to32

mg/l.

2.3 Inter tidal & Sub tidal Sediment analysis result:

The Sediment quality at different stations are measured during this investigation is

presented in Table No.4 and Table No.5


Table 4 : Sub Tidal Sediment Analysis Result

No. Parameters SUBTIDAL SEDIMENT QUALITY(µgm/gm) Test Method Permissible

Station 1 Station 2 Station 3 Station 4 Station 5

1. Texture Loamy sand Silty sand Sandy Silty Sand --

2. Aluminium as Al

N.D. N.D. N.D. N.D. N.D. IS 3025(Part 55)2003

3. Cobalt as Co N.D. N.D. N.D. N.D. N.D. AAS Method

4. Copper as Cu

0.3885 0.3831 0.3834 0.2610 0.3672 IS 3025(Part 42)1992amd.01,

5. Zinc as Zn 0.913 0.987 1.206 0.880 1.191 IS 3025(Part 49)1994

6. Mercury N.D. N.D. N.D. N.D. N.D. (APHA 22

ndEd.,2012,3112-B)

7. Phosphorous (Total)

6.20 6.20 6.3 5.3 7.6 (APHA22

ndEd.,2012,4500-

P,D)

8. C(Org.) N.D. N.D. N.D. N.D. N.D. --

9. Chromium 0.4275 0.4146 0.3996 0.2963 0.4145 IS 3025(Part 52)2003,

10. Nickel 0.5325 0.5784 0.5964 0.5101 0.6319 IS 3025(Part 54)2003,

11. Manganese 7.465 7.967 8.451 6.923 9.602 APHA 22

ndEd.,2012,3500

Mn B

12. Iron 312 330.7 357.3 226.6 380.5 IS 3025(Part 53)2003,

13 PHc N.D. N.D. N.D. N.D. N.D. G.C.Method

14 Arsenic N.D. N.D. N.D. N.D. N.D. APHA 22ndEd.,2012,3114-C

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14




Table 5: Inter tidal Sediment Analysis Result

INTER TIDAL SEDIMENT QUALITY (µgm/gm)

Sr.

No Parameters

Transect 1 Transect 2 Test Method Permissible

High Tide Low Tide High Tide Low Tide

1. Texture Silty Silty Sandy Sandy --

2. Aluminium as Al N.D. N.D. N.D. N.D. IS 3025(Part 55)2003

3. Cobalt as Co N.D. N.D. N.D. N.D. AAS Method

4. Copper as Cu 0.1178 0.4646 0.1068 0.1054 IS 3025(Part 42)1992amd.01,

5. Zinc as Zn 0.2268 0.933 0.1372 0.1620 IS 3025(Part 49)1994

6. Mercury N.D. N.D. N.D. N.D. (APHA 22nd

Ed.,2012,3112-B)

7. Phosphorous (Total)

3.26 6.6 3.1 2.77 (APHA 22

ndEd.,2012,4500-

P,D)

8. C(Org.) N.D. N.D. N.D. N.D. --

9. Chromium 0.1230 0.6289 0.2962 0.1145 IS 3025(Part 52)2003,

10. Nickel 0.2090 0.6976 0.1959 0.2544 IS 3025(Part 54)2003,

11. Manganese 2.4865 13.8 3.9632 9.50 APHA 22

ndEd.,2012,3500 Mn

B

12. Iron 95.25 371.3 32.0 70.25 IS 3025(Part 53)2003,

13 PHc N.D. N.D. N.D. N.D. G.C.Method

14 Arsenic N.D. N.D. N.D. N.D. APHA 22nd

Ed.,2012,3114-C

Sr.

No Parameters

Transect 3 Test Method Permissible

High Tide Low Tide

1. Texture Silty sand Silty sand --

2 Aluminium as Al N.D. N.D. IS 3025(Part 55)2003

3. Cobalt as Co N.D. N.D. AAS Method

4. Copper as Cu 0.3569 0.5202 IS 3025(Part42)1992amd.01,

5. Zinc as Zn 0.768 0.916 IS 3025(Part 49)1994

6. Mercury N.D. N.D. (APHA 22nd

Ed.,2012,3112-B)

7. Phosphorous (Total) 5.2 4.5 (APHA 22nd

Ed.,2012,4500-P,D)

8. C(Org.) N.D. N.D. --

9. Chromium 0.6733 0.9760 IS 3025(Part 52)2003,

10. Nickel 0.4865 0.6610 IS 3025(Part 54)2003,

11. Manganese 5.45 10.6972 APHA 22nd

Ed.,2012,3500 Mn B

12. Iron 249.65 328.1 IS 3025(Part 53)2003,

13 PHc N.D. N.D. G.C.Method

14 Arsenic N.D. N.D. APHA 22nd

Ed.,2012,3114-C

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15


The texture of sediment is sandy to sandy loam and sandy clay loam.

The highest phosphorus content (7.6µgm/gm) was recorded at ST-5 and lowest

phosphorous content (5.3 µgm/gm) was found at ST-4 in sub tidal region. In the Inter

tidal region highest phosphorus content (6.6 µgm/gm) was recorded at IT-1(LWL) and

lowest phosphorous content (2.7 µgm/gm) was found at IT-2(LWL)

The Chromium content of marine sediment was ranged from 0.2963 µgm/gm to 0.4257

µgm/gm. The highest chromium content was recorded at ST-1 and lowest at ST-4. And In

Intertidal region the Chromium content was ranged from 0.1145 µgm/gm to 0.9760

µgm/gm. The highest chromium content was recorded at IT-2(LWL) and lowest at IT-3

(LWL)

The highest Nickelcontent (0.6319 µgm/gm) was recorded at ST-5 and lowest Nickel

content (0.5101µgm/gm) was recorded at ST-4.In the Inter tidal region highest

Nickelcontent (0.6976 µgm/gm) was recorded at IT-1(LWL) and lowest Nickel content

(0.1959 µgm/gm) was found at IT-2(HWL).

The highest Copper content (0.3885 µgm/gm) was recorded at ST-1 and lowest copper

content (0.2610 µgm/gm) was recorded at ST-4.In the Inter tidal region highest copper

content (0.5202 µgm/gm) was recorded at IT-3(LWL) and lowest copper content (0.1068

µgm/gm) was found at IT-2(HWL).

The highest Zinc content (1.206 µgm/gm) was recorded at ST-3 and lowest zinc content

(0.0.880 µgm/gm) was recorded at ST-4.In the Inter tidal region highest Zinc content

(0.2268 µgm/gm) was recorded at IT-1(HWL) and lowest Zinc content (0.768 µgm/gm)

was found at IT-3(HWL).

The highest Iron content (380.5µgm/gm) was recorded at ST-5 and lowest Iron content

(226.6 µgm/gm) was recorded at ST-4. In the Inter tidal region highest Iron content

(328.1 µgm/gm) was recorded at IT-3(LWL) and lowest Iron content (32.0 µgm/gm) was

found at IT-2(HWL).

Arsenic, Poly Aromatic hydrocarbon, Mercury, Aluminium, Cobalt and organic carbon

was not detected in any station.

83

16


BIOLOGICAL CHARACTERISTICS (BIODIVERSITY STUDIES):

3.1 Planktonic Forms:

The name plankton is derived from the Greek word “planktons”, meaning “wanderer” or

“drifter”. While some forms of plankton are capable of independent movement and can

swim up to several hundred meters in a single day, their position is primarily determined by

currents in the body of water they inhabit. By definition, organisms classified as "plankton"

are unable to resist ocean currents. Plankton is primarily divided into broad functional

groups:

1. Phytoplankton

2. Zooplankton

This scheme divides the plankton community into broad producer and consumer groups.

a) Phytoplankton:

The organisms responsible for primary production in all aquatic ecosystems are known as

“phytoplankton.” These miraculous microscopic organisms not only form the base of life in

our oceans, but also produce up to 90% of the oxygen in our atmosphere.

Phytoplankton is microscopic plants that live in the ocean, freshwater and other

terrestrial based water systems. There are many species of phytoplankton, each of which

has a characteristic shape, size and function. Marine species of phytoplankton grow

abundantly in oceans around the world and are the foundation of the marine food chain.

Marine Phytoplankton is the producing (autotrophic) component in the ocean. There are

fourteen classes of phytoplankton. Each class of phytoplankton contains unique attributes in

size, cell structure, nutrients and function.

b) Zooplankton:

A consumer is an organism that is incapable of making its own food from light or

inorganic compounds, and feeds on organisms or the remains of other organisms to get the

energy necessary for survival. A consumer is known as a heterotroph (heterone = (an) other

and trophe = nutrition) in the food chain. All animals as well as humans are consumers

(heterotrophic) and therefore must obtain their nutrition from another consumer

(heterotroph) or a producer (autotroph)

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17


3.2 Significance of Phytoplankton and Zooplankton:

Phytoplanktons are the major primary producers of organic matter in the aquatic

ecosystem and especially oceans whose 90% productivity is from the planktons. Collectively,

they directly or indirectly support the entire animal population, apart from those dependent

on chemosynthetic bacteria around submarine vents, and thus form the basis of most

marine food webs. When the mixed layers become shallower in spring, phytoplankton are

exposed to higher light intensity in the upper sunlight ocean. After nutrient enrichment

caused by turbulent mixing of deep water into surface waters in the winters, phytoplankton

can grow rapidly and build up to very high concentration (tens of millions cells per liter) in a

matter of days. The massive build up of phytoplankton in spring directly contributes new

organic carbon to support the zooplankton, which, in turn, benefitslarger marine animals

including fish, squid, birds, and marine mammals in the ocean.

The significance of zooplanktons is found in their role in transferring biological

production from phytoplankton’s to large organisms in the marine food web (e.g. whales,

seals, seabirds, fish and squid) and to the sea floor. A large number of phytoplankton

species are grazed upon by the microscopic protozoan, tunicates, copepods and other

crustaceans. These in turn become food for other animals further linking the food web.

Therefore, variability in the reproduction of copepods would affect the survival of young fish

that depend on them.

Table: 6 Test methods for Phytoplankton & Zooplankton analysis

Sr no. Test performed Method

1 Phytoplankton APHA, Edition 21, Part 10000, 10200 F

2 Zooplankton APHA, Edition 21, Part 10000, 10200 G

3.3Phytoplankton:

Sampling was done from 5 locations, each with 0.5 km distance so the total samples were

ten in number. The sampling location is given in following Table.7

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18


Table 7: Phytoplankton Sampling Station

Station Location Co ordinates Water depth Tide

1 Intake point 220 48’ 37” N 69032’ 85” E 8.0 m Flood

2 intake point 220 46’ 94” N 690 32’ 22” E 9.3 m Ebb - Flood

3 West port area 220 45’ 26” N 69034’ 54” E 15.2 m Flood - Ebb

4 Outfall area 220 45’ 00” N 69036’ 31” E 5.5 m Flood

5 Outfall area 220 44’ 42” N 69036’ 36” E 7.3 m Flood - Ebb

A plastic Niskin sampler with a mechanism for closing at a desired depth was used for

collecting sub – surface water samples as well as sampling at the surface was done using a

clean polyethylene bucket. Samplecollectively conditioned in plastic containers with inert

cap liners. Sample for cell count were preserved in Lugol solution, and identification of

phytoplankton were done under a microscope using Sedgwick Rafter slide.

3.3.1 Drop Count Method and Microscopic Observations 0.5ml of the sample was taken on Sedgwick -Rafter Counting Cells and plankton

number was counted. The identification was done using a Stereo-microscope under 45X or

100X magnification. The planktons were then compared with the descriptive and/or

photographic identification keys given by Desikachary, 1959; Prescott, 1959; Sournia, 1974;

Boltovskoy, 1981; Matsumura – Tundisi, 1986; Round et al., 1990; Santhanam, 1993 etc.

Species were identified to a greater possible taxonomic level.

3.3.2 Plankton Diversity

A total of five stations were distributed throughout the sampling effort. Samples

were collected during October of 2015. A maximum21 genera of phytoplankton Fragillaria,

Navicula, Thalassiosira, Rhizosolenia, Thalassionema,Surirella, Odontella, Pleurosigma,

Pseudonitzschia, Leptocylindrus, Coscinodiscus, Scrippsiella, Cylindrotheca, Skeletonema,

Surirella, Hemialus, Ditylum, Chaetoceros, Bacteriastrum

,Prorocentrum,Dinoflagellates.were identified from station 4 during the period of

investigation and a minimum 18 genera of phytoplankton Dytilium, surirella, Peridinium,

cyclotella, GyrosigmaNavicula, Thalassiosira, Thalassionema, Pleurosigma, Pleurosigma,

Pseudonitzschia, Coscinodiscus, Protoperidinium, Thallsiothrix, Cylindrotheca, Skeletonema,

Hemialus and Coroethron.were identified from station 4. The phytoplankton abundance in

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19


the study region was ranged from 8793 to 16543 cells L-1. Highest phytoplankton abundance

was observed at ST-5 Surface water. However, lowest phytoplankton abundance was

observed at ST-3 surface water. Highest number of groups of phytoplankton (21) found at

ST-4 and also constant in cells number was not much differ (Table:8).

Table 8: Total abundance & groups of phytoplankton at the sampling stations

Station Abundance (cells L-1) Genera

count Phytoplankton groups observed in both

surface and bottom water Surface Bottom

ST-1

9578

14560

18

Dytilium, surirella, Peridinium, cyclotella, GyrosigmaNavicula, Thalassiosira, Thalassionema, Pleurosigma, Pleurosigma, Pseudonitzschia, Coscinodiscus, Protoperidinium, Thallsiothrix, Cylindrotheca, Skeletonema, Hemialus and Coroethron.

ST-2

12456

14560

19

Thallasiothix, Navicula, Thalassiosira, Rhizosolenia, Nitzschia, Thalassionema, Pleurosigma, Odontella, Corethron, Pleurosigma, Pseudonitzschia, Leptocylindrus, Coscinodiscus, Protoperidinium, Cylindrotheca, Skeletonema, Surirella, Meuneria and Ditylum..

ST-3

8793

12489

19

Thalassiosira, Rhizosolenia, Thalassionema,

Pleurosigma, Odontella, Gunardia,

Pseudonitzschia, Coscinodiscus,

Protoperidinium,Navicula, Scrippsiella,

Skeletonema, Gyrosigma, Ditylum,

Chaetoceros, Bacteriastrum, Amphidinium,

Prorocentrum and Cheotocerous

ST-4

15478

13456

21

Fragillaria, Navicula, Thalassiosira, Rhizosolenia, Thalassionema,Surirella, Odontella, Pleurosigma, Pseudonitzschia, Leptocylindrus, Coscinodiscus, Scrippsiella, Cylindrotheca, Skeletonema, Surirella, Hemialus, Ditylum, Chaetoceros, Bacteriastrum ,Prorocentrum,Dinoflagellates..

ST-5

16543

15487

20

Thalassiosira, Rhizosolenia, Thalassionema, Odontella,Corethron,Protoperidinium,Thallasiothrix, Scrippsiella, Cylindrotheca, Skeletonema, peridinium, Ditylum, Chaetoceros, Bacteriastrum,prorocentrum, Gunardia, Pseudonitzschia, Coscinodiscus, Odentella and Ceratium.

87

20


1.2 Phytoplankton under microscope

88

21


3.4 Zooplankton:

Sampling was done from 5 locations, each with 0.5kmdistanceso the total samples were five

in numbers; the sampling details are given in following table 9.

Table 9: Zooplankton Sampling Station

Station Location Co ordinates Water depth Tide

1 Intake point 220 48’ 37” N 690 32’ 85” E 8.0 m Flood

2 intake point 220 46’ 94” N 690 32’ 22” E 9.3 m Ebb - Flood

3 West port area

220 45’ 26” N 690 34’ 54” E 15.2 m Flood - Ebb

4 Outfall area 220 45’ 00” N 690 36’ 31” E 5.5 m Flood

5 Outfall area 220 44’ 42” N 690 36’ 36” E 7.3 m Flood - Ebb

Oblique hauls for Zooplankton were made using Heron Tranter net with calibrated flow

meter. All collection was of 6 min. duration after collection, Sample collectively conditioned

in plastic containers with inert cap liners samples were preserved in formalin and

identification of Zooplankton were done under a microscope.

3.4.1 Drop Count Method and Microscopic Observations

0.5ml of the sample was taken on slide for Counting Cells and Zooplankton number

was counted. The identification was done using a Stereo-microscope under 45X or 100X

magnification. The Zooplanktons were then compared with the descriptive and/or

photographic identification keys given by Desikachary, 1959; Prescott, 1959; Sournia, 1974;

Boltovskoy, 1981; Matsumura – Tundisi, 1986; Round et al., 1990; Santhanam, 1993 etc.

Species were identified to a greater possible taxonomic level.

3.4.2 Zooplankton Diversity

A total of five stations were distributed throughout the sampling effort. Samples were

collected during October of 2015. A maximum 18 genera of ZooplanktonGastropods larvae,

Isopods, Medusae, Mysids, Ostracods, mysids,medusae Amphipods, Copepod, Copepod

nauplii, Fish egg, otsracods, Foraminifera, Siphonophores, Trochophore, Zoeae larvae and

lamellibranchs were identified from station2 during the period of investigation and a

mini.15 genera of Zooplankton Chaetognatha,Copepod, Copepod nauplii, Cumacea, Fish

egg, Cumaceans, Fish larvae, Foraminifera, Polycheatelarvae, Isopods, Ostracods,

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22


Radiolaria, Trochophore,Zoeae larvae and Rotiferswere identified from station 4.Abundance

of zooplankton was ranged in between 2145 to 4527 no. m-3. ST-2 was characterized by

highest zooplankton abundance (4527 no. m-3) and biomass (0.879 ml m-3), whereas lowest

were recorded at ST-4 (abundance 2145 no. m-3 and biomass 0.527ml m-3).

Table 10: Total abundance, biomass and groups of zooplankton at the sampling stations

Station Biomass (m/m-3)

Population (no. m-3)

Total groups

Zooplankton groups observed in the study

ST-1 0.654 3245 16

Gastropod larvae,Isopods, Medusae,

Mysids, Ostracods, Radiolaria,

Siphonophores, Trochophore,

StomatopodZoeae larvae, Chaetognatha,

Copepod nauplii, Cumaceans, Fish larvae,

Foraminifera, and polycheatelarvae.

ST-2 0.879 4527 18

Gastropods larvae, Isopods, Medusae,

Mysids, Ostracods, mysids,medusae

Amphipods, Copepod, Copepod nauplii,

Fish egg, otsracods, Foraminifera,

Siphonophores, Trochophore, Zoeae

larvae and lamellibranchs.

ST-3 0.578 2879 16

Copepod nauplii, Fish egg, Fish larvae,

Foraminifera, Gastropod larvae, Isopods,

Medusae, Mysids, Ostracods, Radiolaria,

Siphonophores, Trochophore, Zoeae

larvae, Stomatopod larvae Zoeae larvae,

Chaetognatha,Copepodnauplii,..

ST-4 0.527 2145 15

Chaetognatha,Copepod, Copepod nauplii,

Cumacea, Fish egg, Cumaceans, Fish

larvae, Foraminifera, Polycheatelarvae,

Isopods, Ostracods, Radiolaria,

Trochophore, Zoeae larvae and Rotifers

ST-5 0.654 2758 17

Decopods hydrozoans larvae, Medusa,

Mysids, Chaetognatha,Lamellibranchs

Copepod nauplii, Cumacea, Fish egg, Fish

larvae, Gastropod larvae, Isopods, Mysids,

Ostracods, Trochophore and Zoeae larvae.

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23


1.3 : Zooplankton under microscope

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24


3.5 Benthic Fauna

Benthic invertebrates are organisms that live on the bottom of a water body (or in the

sediment) and have no backbone. The size of benthic invertebrates spans 6-7 orders of

magnitude. They range from microscopic (e.g.micro invertebrates, <10 microns) to a few

tens of centimeters or more in length (e.g.macro invertebrates, >50 cm).

The benthic zone is the ecological region at the lowest level of a body of water such as an

ocean or a lake including the sediment surface and some sub-surface layers. Organisms

living in this zone are called benthos. They generally live in close relationship with the

substrate bottom; many such organisms are permanently attached to the bottom. The

superficial layer of the soil lining the given body of water is an integral part of the benthic

zone, as it influences greatly the biological activity which takes place there. They may be

found in contact with soil layers which includes sand bottoms, rocky outcrops, coral, and

bay mud.

Benthosis the organisms which live in the benthic zone, and are different from that

elsewhere in the water column. Many are adapted to live on the substrate (bottom). In their

habitats they can be considered as dominant creatures. Many organisms adapted to deep-

water pressure cannot survive in the upper parts of the water column. The pressure

difference can be very significant (approximately one atmosphere for each 10 meters of

water depth). Because light does not penetrate very deep ocean-water, the energy source

for the benthic ecosystem is often organic matter from higher up in the water column which

drifts down to the depths. This dead and decaying matter sustains the benthic food chain;

most organisms in the benthic zone are scavengers or detritivores. Some microorganisms

use chemosynthesis to produce biomass.

Macro invertebrates are mainly dwelling at the bottom of the substratum but at

times may travel upwards in the water column. They may also occupy rock crevices, organic

debris and other microhabitat at the bottom. These organisms by virtue of being relatively

stationary, are constantly exposed to changes undergoing in overlying water, and hence,

respond very well to aquatic pollution. The macro benthic population is very sensitive to

environmental perturbation and is highly influenced by the physicochemical characteristics

of water, nature of substratum, food, predation and other factors. The density of benthic

invertebrates also fluctuates widely with the changes in the season.

92

http://en.wikipedia.org/wiki/Body_of_water

http://en.wikipedia.org/wiki/Benthos

http://en.wikipedia.org/wiki/Water_column

http://en.wikipedia.org/wiki/Detritus

http://en.wikipedia.org/wiki/Food_chain

http://en.wikipedia.org/wiki/Chemosynthesis

http://en.wikipedia.org/wiki/Biomass_(ecology)

25


3.5.1 Significance of benthic macro invertebrates

The biomass of benthic macro invertebrates in estuaries and coastal embayment is

often high. It declines if communities are affected by prolonged periods of poor water

quality especially when anoxia and hypoxia are common. Burrowing and tube-building by

deposit-feeding benthic macro invertebrates (bioturbators) helps to mix the sediment and

enhances decomposition of organic matter. Nitrification and denitrification are also

enhanced because a range of oxygenated and anoxic micro-habitats are created. For

example, the area of oxic-anoxic boundaries and the surface area available for diffusive

exchange are increased by tube-building macro invertebrates. Loss of nitrification and

denitrification (and increased ammonium efflux from sediment) in coastal and estuarine

systems is an important cause of hysteresis, which can cause a shift from clear water to a

turbid state.

The loss of benthic suspension-feeding macro invertebrates can further enhance

turbidity levels because these organisms filter suspended particles including planktonic

algae, and they enhance sedimentation rates through bio deposition (i.e. voiding of their

wastes and unwanted food). Changes in the macro fauna (and flora) cause changes in

nutrient storage pools and in the flux of nutrients between micro fauna (and flora) and

macro fauna and flora. Macro fauna are also important constituents of fish diets and thus

are an important link for transferring energy and nutrients between trophic levels and

driving pelagic fish and crustacean production. It is for these reasons and others, that

benthic invertebrates are extremely important indicators of environmental change.

3.5.2 Methodology

Macro-invertebrates representative samples were collected from selected 5 sampling

stations and 3 sampling transect, the details are as mentioned in the table. Sample were

collected of one season in the month of October 2015

Table: 11: Test method for Benthos analysis

Sr. No Test performed Method

1 Benthos APHA, Edition 21, Part 1000010500 A-10500 D

93

http://www.ozcoasts.org.au/indicators/anoxic_hypoxic_events.jsp

http://www.ozcoasts.org.au/glossary/def_c-d.jsp#decomp

http://www.ozcoasts.org.au/indicators/sediment_org_matter.jsp

http://www.ozcoasts.org.au/glossary/def_m-p.jsp#nitrification

http://www.ozcoasts.org.au/indicators/turbidity.jsp

http://www.ozcoasts.org.au/indicators/fish_assemblages.jsp

26


Table 12: Sub-tidal Benthos Sampling Sites

Table: 13: Intertidal Benthos Sampling Sites

For the analysis of Benthos subtidal sediment samples were collected using Van- veen grab

as well as intertidal samples were collected using metal quadrant.

The total Macro benthos population (sub tidal & intertidal) was estimated as number of 1

m2 area and biomass on wet weight basis.

Station Location Co ordinates Sediment quality

1 Intake point 220 48’ 37” N 690 32’ 85” E Silty sand

2 intake point 220 46’ 94” N 690 32’ 22” E Sandy

3 West port area 220 45’ 26” N 690 34’ 54” E Silty clay

4 Outfall area 220 45’ 00” N 690 36’ 31” E Silty sand

5 Outfall area 220 44’ 42” N 690 36’ 36” E Silty sand

Transect Location Co ordinates Intertidal

expose area (m) Sediment quality

I

High water level

220 47’38” N 690 32’ 19” E

57m

Sandy

Low water level

220 47’ 40” N 690 32’ 15” E

Muddy & sandy

II

High water level

220 45’ 62” N 690 34’ 43” E

35 m

Silty sand

Low water level

220 45’ 86” N 690 34’ 65” E

Sandy

III

High water level

220 45’ 19” N 690 36’ 39” E

53m

Sandy

Low water level

220 45’ 32” N 690 36’ 65” E

Silty clay

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3.5.3 Handling and Preservation

The samples were first sieved and then washed from the sediment. From this, the

samples were transferred along with some water to a coarse sieve with a mesh size of 0.5 to

0.6 mm and a fine one with a mesh width of less than 0.2 mm, one over the other.

Quadrangular wooden box, at the bottom of which sieves of brass of various widths are

inserted, has also been used for sieving macro invertebrates. Sieving yields residue-a

mixture of animals and sediment. The organisms are picked from here by using forceps and

pipettes. They were also hand-picked, if bigger, after keeping the slurry in white

background. For quantitative sampling, each sample was handled separately, avoiding any

loss. After sorting, macro invertebrates were identified to the lowest practical identification

level (LPIL) which in most cases was to the species level unless the organism was a juvenile,

damaged, or otherwise unidentifiable. Macro invertebrates were preserved in 10% formalin.

3.5.4 Identification

Identification of the organisms was done under Stereo-microscope. Pennak (1978), Tonapi

(1980), Ward and Whipple (1992) were used as standard reference for identification of the

macro invertebrates.

3.5.5 Benthic Diversity

Benthic invertebrates in the present study area were distributed on the surface of

bed forms i.e. sandy and Silty clay in nature. The abundance and diversity, species

composition of benthic invertebrates were recorded which is the indicators of changing

environmental conditions. A total 5 sub tidal stations and 3 intertidal transect were

distributed throughout the sampling effort. Samples were collected during March of 2015.

Sub tidal:A maximum 11 group of BenthosTanaids, Isopoda Polychaetes, Decapoda,

Amphipoda, Bivalvia, Gastropoda, Nematoda, Cumacea, Foraminifera and pelecypods, were

identified from station 1 during the period of investigation and a minimum 8 groupFish

larvae, Molluscans,Polychaeta, Bivalvia, Amphipoda, Cumacea, Decapoda and Gastropodsof

Benthic fauna recorded from station 3. In the sub tidal region macro benthos abundance

was higher at ST-5 (2650 no. m-2), whereas lowest abundance was recorded at ST-4 (1810

no. m-2). Benthic group count was ranged from 8 to 11, with maximum groups at ST-1. High

biomass was recorded at ST-5 (28.10 mg. m-2) as compared to other stations(Table: 14).

95

28


Table 14: Standing stock and abundance of sub tidal macro benthos

Station Biomass (mg. m-2)

Abundance (no. m-2)

Total Group Macro benthic groups observed in

the study

ST-1 20.25 1850 11

Tanaids, Isopoda Polychaetes,

Decapoda, Amphipoda, Bivalvia,

Gastropoda, Nematoda, Cumacea,

Foraminifera and pelecypods..

ST-2 22.45 2156 9 Bivalvia, Gastropoda, Polychaeta,

Fish larvae, Isopoda, Amphipoda,

Decapoda, Nematoda, Cumacea

ST-3 21.55 1850 8 Fish larvae, Molluscans,Polychaeta,

Bivalvia, Amphipoda, Cumacea,

Decapoda and Gastropods..

ST-4 22.52 1810 9 Amphipoda, Decapoda, Gastropods,

Polychaeta, Isopoda, Bivalvia,

Mysids, Coeletranes and Isopodes

ST-5 28.10 2650 10

Amphipoda, Polychaeta, Decapoda,

Cumaceans, Nematoda, Tanaids,

Nematodes Bivalvia, Gastropoda,

andBrachyrans.

Inter tidal: A maximum 7 group of BenthosIsopods, Mysids, Bivalvia, Nematoda,

Gastropoda, Amphipoda and Fish eggswere identified from transect II during the period of

investigation and a minimum 5 groupGastropoda, Bivalvia, Nematoda and Isopds of Benthic

fauna recorded from other transect.

In the intertidal regions, highest macro benthos abundance (2245 no. m-2) reported at IT-2

(LW). Highest biomass was recorded at IT-2 (LW) (21.20 mg. m-2) and lowest was at IT-1

(HW) (18.50 mg. m-2) (Table: 15).

96

29


Table:15 Standing stock and abundance of Intertidal macro benthos.

Station Biomass (mg. m-2)

Abundance (no. m-2)

Total Group (No.)

Major Group

IT-1 (LW) 18.50 1560 6 Amphipoda, Gastropoda,Hydrozoans

Nematoda,Bivalves and Polychaeta.

IT-1 (HW) 16.45 1775 6 Mysids, Gastropoda, Foraminifera,

Decapoda, Hydrozoans and Tanaids.

IT-2 (LW) 21.20 2245 7 Isopods, Mysids, Bivalvia, Nematoda,

Gastropoda, Amphipoda and Fish eggs.

IT-2 (HW) 19.80 1950 7

Polychaeta, Gastropoda, Bivalvia,

Nematoda, Amphipoda, Foraminifera and

Crab larvae.

IT-3 (LW) 20.15 1850 5 Tanaids, Gastropoda, Polychaeta,

Isopoda and Bivalves.

IT-3 (HW) 18.56 1650 4 Gastropoda, Bivalvia, Nematoda and

Isopds.

1.4: Benthos diversity in project site

97

30


3.6 Chlorophyll and Pheophytin

Chlorophyll and Pheophytin Levels:

Chlorophyll is the green molecule in plant cells that carries out the bulk of energy fixation in

the process of photosynthesis. Chlorophyll is a measure of algal biomass that is relatively

unaffected by non-algal substances, it is a fairly accurate measure of algal weight and

volume, and, it acts as an empirical link between nutrient concentration and a number of

important biological phenomena. Chlorophyll is also relatively easy to measure.

In addition to the naturally occurring pigments in algal cells, a filtered water sample will also

contain colored degradation products of these pigments. When algal chlorophyll degrades,

it forms a series of degradation products, the nature of which depends on what part of the

molecule that is affected. As chlorophyll degrades, the initial step is either the loss of the

magnesium from the center of the molecule or the loss of the phytol tail.

The former pathway results in the formation of the molecule, phaeophytin; in the

latter pathway, the resulting molecule is termed a chlorophyllide. The degradation scheme is

shown in Figure below. Further degradation of either the phaeophytin or the chlorophyllide

produces a molecule termed a pheophorbide: pheophytin is degraded by the loss of the

phytol tail and a chlorophyllide loses its magnesium ion. When a chlorophyll molecule

breaks down, a number of distinct phaeophytins, chlorophyllides, and pheophorbides will be

produced, depending on the parent molecule.

Figure 1.5 : The Degradation Pathways Of Chlorophyll

CHLOROPHYLL PHEOPHYTIN

CHLOROPHYLLIDE PHEOPHORBIDE

Table 16 :Method of analysis for Chlorophyll a and pheophytin

Sr. no Test performed Method

1 Chlorophyll a and pheophytin APHA, Edition 21, Part 10000, 10200 H

Loss of mg

98

31


3.6.1 Method:

Sampling locations were same as that for the plankton samples. Surface water samples

were collected in clean plastic dark bottles.

Water samples were filtered through Whatman glass microfiber filters (GF/F: 47 mm)

and preserved in 90% acetone for one night in the dark at 4ºC until analysis.

The sample was concentrated by centrifugation. The pellet so obtained was then put in a

tissue grinder with 2 to 3 ml of 90% aqueous acetone solution and macerated at 500

rpm for 1 min.

The sample was transferred to screw capped centrifuge tube. The grinder was rinsed

with a few millimeters of 90% aqueous acetone solution and added to the extraction

slurry. The total volume was adjusted to 10 ml with 90% aqueous acetone.

The sample was centrifuged in closed tubes for 20 min at 500 rpm.

The extract was decanted into a calibrated 15ml screw cap centrifuge tube.

2ml of clarified extract was transferred to 1cm cuvette and optical density was read at

750 and 665 nm.

The extract was then acidified in the cuvette with 0.1 ml of 0.1 N NH4Cl. The acidified

extract is gently agitated and OD was read at 750 and 665 nm, 90 seconds after

acidification.

3.6.2 Results

Chlorophyll estimation results showed that it varied from lowest of 1.59 mg/l on station 2

surface water and highest of 1.88 mg/l on station 4 bottom water. The chlorophyll content

is more in station 4 so may be as a result of high plankton density at this site had conducive

environment. While Pheophytin content varies from lowest 0.16 mg/l on station 2 surface

water and highest 0.95 mg/l on station 2 bottom water. Results of phytoplankton pigment

analysis revealed that, highest chlorophyll a and Pheophytin content (1.98 and 0.59 mg L-1)

was recorded at ST- 4 surface water.

99

32


Table 17: Chlorophyll a and Pheophytin (mg/l)

Station Chlorophyll a Pheophytin


ST-1 1.78 1.15 0.19 0.15

ST-2 1.59 1.69 0.16 0.95

ST-3 1.78 1.65 0.56 0.48

ST-4 1.98 1.88 0.59 0.48

ST-5 1.90 1.66 0.29 0.21

3.8 Conclusion The phytoplankton abundance in the study region was ranged from 8793 to 16543 cells

L-1. Highest phytoplankton abundance was observed at ST-5 Surface water. However,

lowest phytoplankton abundance was observed at ST-3 surface water. Highest number

of groups of phytoplankton (21) found at ST-4 and also constant in cells number was

not much differ.

Results of phytoplankton pigment analysis revealed that, highest chlorophyll a and

phaeophytin content (1.98 and 0.59 mg L-1) was recorded at ST-4 surface water.

Abundance of zooplankton was ranged in between 2145 to 4527 no. m-3. ST-2 was

characterised by highest zooplankton abundance (4527 no. m-3) and biomass (0.879

ml m-3), whereas lowest were recorded at ST-4 (abundance 2145 no. m-3 and

biomass 0.527 ml m-3).

In the sub tidal region macro benthos abundance was higher at ST-5 (2650 no. m-2),

whereas lowest abundance was recorded at ST-4 (1810 no. m-2). Benthic group count

was ranged from 8 to 11, with maximum groups at ST-1. High biomass was recorded

at ST-5 (29.10 mg. m-2) as compared to other stations. Low biomass was recorded at

ST-1 (20.25 mg. m-2) as compared to other stations.

In the intertidal regions, highest macro benthos abundance (2245 no. m-2) reported

at IT-2 (LW). Highest biomass was recorded at IT-2 (LW) (21.20 mg. m-2) and lowest

was at IT-1 (HW) (16.45 mg. m-2)

100

33


DIFFERENT TYPES OF SAMPLING PHOTOGRAPHS

On site DO & Temperature Analysis

Phytoplankton sample Collection

Zooplankton sample Collection

101

34


DIFFERENT TYPES OF SAMPLING PHOTOGRAPHS

Benthos sampling

Chlorophyll sampling

*******************************************

102




ANNEXURE 3 GPCB Sample Analysis Report

Sample ID:170888 - Analysis Completion:06/11/2015

ANALYSIS REPORT FOR

WATER / WASTE WATER SAMPLE

Infrastructure development project / LAB Inward : 12684

Gujarat Pollution Control Board,

Gj Ins. Desert Ecology

Gj Ins. Desert Ecology

Mundra Road

BHUJ-370001

TEST REPORT

Test Report No. : 12684 Date: 10/11/2015

3. Nature of Sample

4. Sample Collected By

5. Quantity of Sample Received

6. Code No. of the Sample

7. Date & Time of Collection & Inwarding

8. Date of Start & Completion of Analysis

9. Sampling Point

10. Flow Details (Remarks)

11. Mode of Disposal

12. Ultimate Receiving Body

13. Temperature on Collection

14. Carboys Nos for

15. Water Consumption & W.W.G (KLPD)

1. Name of the Customer

2. Address

Range of TestingTest MethodSr ResultUnitParameter

2 – 10000 mg/LGravimetric method. (2540 D APHA Standard Methods 22nd edi.)2012mg/lSuspended Solids 1 1

05–50000 mg/l3 – Day BOD test. (IS 3025 (Part 44) 1993 Reaffirmed 1999)-2009mg/lB.O.D (3 Days 27oC) 2 6.8

0.2-5mg/lAPHA 21st edi : 4500 Cl G - DPD Colorimetric methodPPMRESIDUAL CHLORINE 3 0.5

: REP-Representative/Grab, (Insp Type : ROU-Routine Visit)

: K. B. Chaudhary, DEE

: 5000

: 170888

: 28/09/2015 , (1710 to 1710) & 03/10/2015

: 03/10/2015 & 06/11/2015

: From the final treated w/w holding tank of STP ~ (A/T)

: --

: Onland for Gardening/Plantation

: Horticulture

: 30 & pH Range on pH Strip :@7-8 on pHStrip

: W-1 & Color & Appearance :Colourless

: Ind :0.000 , Dom :770.000 & Ind :0.000 , Dom :600.000

: Adani Ports and Special Economic Zone Ltd - 17738

: ,VILLAGE-NANAKAPAYA,TALUKA-MUNDRA

Nana Kapaya-370421, Taluka : Mundra, District : Kutch, GIDC : Not In Gidc

Laboratory Remarks : ---------- By:439-r.o_439 Dt.: 10/11/2015

G.M. Sadhu, R.O Head

16/11/2015N I C

Note :

1. * - These parameters are covered under the scope of NABL.

2. The results refer only to the tested samples and applicable parameters. Endorsement of products is neither inferred nor implied.

3. Samples will be destroyed after 10 days from the date of issue of test report unless otherwise specified.

4. This report is not to be reproduced wholly or in part or used in any advertising media without the permission of the Board in writing.

5. The Board is not responsible for the authenticity for the samples not collected by the Board’s officials.

6. Total liability of our laboratory is limited to the invoiced amount. Any dispute arising out of this report is subject to

Gujarat Jurisdiction only.

7. Permissible Limits: as per Schedule VI of EPA Rules, 1986 as ammended by Second and Third ammendment 1993 for Effluents

8. Physicochemical and microbiological parameters, Std.Methods for Water and Waste Water- 22nd Edition by APHA.

9. Bioassay test (for toxicity) -IS:6582:Part-2:2001; Reaffirmed 2007.

-Field Observation :

103




ANNEXURE 4 Map showing Reclamation Area

LTLT

LT

LT

7.64

7.33

7.3

7.26

7.69

7.71

7.01

7.22

7.04

8.17

7.17

LT

LT

LT

8.31

8.32

8.32

8.32

8.32

8.32

8.32

8.31

8.3

8.12

8.13

8.14

8.12

8.32

8.34

8.15

8.15

8.29

8.33

8.18

8.16

8.32

8.34

8.17

8.17

8.33

8.32

8.14

8.13

8.34

8.35

8.15

8.14

8.28

8.35

8.13

8.15

8.33

8.33

8.15

8.15 8.08

8.14

8.15

8.14

8.12

8.15

8.15

8.16

8.11

8.14

8.05

8.04

8.04

8.01

7.98

8.12

8.13

8.14 8.12

8.12

8.1

8.14

8.15

8.13

8.12

8.12

8.168.13

8.13

8.16

8.168.14

8.13

8.17

8.17

8.13

8.12

8.17

8.16

8.12

8.14

8.17

8.16

8.16

8.17

8.16

8.05

8.13

8.15

8.08

8.1

8.11

8.09

8.11

8.11

8.11

8.14

8.14

8.15

8.16

8.16

8.15

8.15

8.13

8.13

8.14

8.14

8.13

8.12

8.11

8.1

8.32

8.11

8.13

8.48

B1

B2

B3

B5

BREAK WATER

LIGHT

VIEW POINT

COMMUNICATIONTOWERLT

6.07

5.59

6.10

Map Showing Rclamation area under Water Front Development Plan

West port

South port

104

AutoCAD SHX Text

GSB PAVED

AutoCAD SHX Text

O.S.Y-20

AutoCAD SHX Text

HM

AutoCAD SHX Text

FIRE

AutoCAD SHX Text

FIRE

AutoCAD SHX Text

FIRE

AutoCAD SHX Text

HM

AutoCAD SHX Text

FIRE

AutoCAD SHX Text

FIRE

AutoCAD SHX Text

FIRE

AutoCAD SHX Text

W4

AutoCAD SHX Text

W6

AutoCAD SHX Text

W8

AutoCAD SHX Text

W11

AutoCAD SHX Text

W9

AutoCAD SHX Text

W7

AutoCAD SHX Text

W5

AutoCAD SHX Text

W3

AutoCAD SHX Text

W1

AutoCAD SHX Text

W2

AutoCAD SHX Text

W4

AutoCAD SHX Text

W6

AutoCAD SHX Text

W8

AutoCAD SHX Text

W11

AutoCAD SHX Text

W9

AutoCAD SHX Text

W7

AutoCAD SHX Text

W5

AutoCAD SHX Text

W3

AutoCAD SHX Text

W1

AutoCAD SHX Text

W2

AutoCAD SHX Text

ROCK BUND




ANNEXURE 5 Mangrove Afforestation Details

S. NO. Location FY Area (Hectare) Clearance Reference Plantation/Gap Filling Species

A.1Mundra Port Area

(Mundra, Kutch)24.00

Environment Clearace - Mundra

(J-16011/13/95-IA.III dated 25 August 1995)Plantation Avicennia marina

24.00

B.1Mundra Port Area

(Mundra, Kutch)25.00

Environment Clearace - Mundra

(J-16011/30/2003-IA.III dated 21 July 2004)Plantation Avicennia marina

25.00

C.1 2007-08 40.00 Plantation

C.2 2009-10 10.00 Gap Filling Work

C.3 2010-11 10.00 Gap Filling Work

C.4 2011-12 95.40 Plantation

C.5 2012-13 25.40 Plantation

C.6 2013-14-15 70.00 Gap Filling Work

160.80

D.1 2012-13 66.50CRZ Recommendation - Mundra

(Env-10-2005-222-P dated 12 October, 2006)Plantation Avicennia marina

D.2 2013-14 10.00 Gap Filling Work Avicennia marina

66.50

E.1 2011-12 50.00 Plantation Avicennia marina

E.2 2012-13 248.00 Plantation Avicennia marina

298.00

Mangrove Afforestation

Forest Clearance - Mundra

(F.No. 8-2/1999-FC (pt) dated 27 February 2009)

Total Plantation

Total Plantation

Total Plantation

(D.1)

Forest Area

(Mundra)

Total Plantation

(E.1+E.2)

CRZ Recommendation - Mundra

(Env-10-2005-222-P dated 12 October, 2006)

Kukadsar

(Mundra, Kutch)

Total Plantation

(C.1+C.4+C.5)

Luni/Hamiramora

(Mundra, Kutch)

Avicennia marina

Rhizophora mucronata

Ceriops tagal

105


F.1 2012-13 50.00CRZ Recommendation - Mundra


F.2 2013-14 20.00 Gap Filling Work Avicennia marina

50.00

G.1 2007-08 40.10CRZ Recommendation - Mundra

(Env-10-2005-222-P dated 12 October, 2006)Plantation

G.2 2008-09 10.00 Gap Filling Work


G.4 2011-12 50.00Environment Clearance - Dahej

(11-37/2007-IA-III dtd 11 November, 2008)Plantation



G.7 2012-13 20.50CRZ Recommendation - Mundra

(Env-10-2005-222-P dated 12 October, 2006)Plantation

G.8 2012-13 200.00Environment Clearance - Mundra

(10-47/2008-IA.III dtd. 12th Jan,2009)Plantation

G.9 2013-14-15 50.00 Gap Filling Work

310.60

H.1Sat Saida Bet

(Kutch)2014-15 250.00

Commitment with KPT for 250 Ha. - Tuna

(By undertaking dated 3 June, 2013)Plantation Avicennia marina

250.00Total Plantation

Total Plantation

(G.1 + G.4 + G.7 + G.8)

Total Plantation

(F.1)

Jakhau Village

(Abdasa, Kutch)

Avicennia marina


Ceriops tagal

Jangi village

(Bhachau, Kutch)

106


I.1 2006-07 200.00 Plantation

I.2 2007-08 100.00 Plantation

I.3 2007-08 100.00Environment Clearance - Dahej

(11-37/2007-IA-III dtd 11 November, 2008)Plantation

I.4 2008-09 200.00 Plantation

I.5 2010-11 200.00 Plantation

800.00

J.1Village Talaza

(Bhavnagar)2011-12 50.00

Environment Clearance - Dahej

(11-37/2007-IA-III dtd 11 November, 2008)Plantation Avicennia marina

J.2Village Narmada

(Bhavnagar)2014-2015 250.00



300.00

K.1Village Malpur

(Bharuch)2012-13-14 200.00

CRZ Recommendation - Dahej

ENV-10-2006-71-P dtd 29th May, 2007Plantation Avicennia marina

K.2Village Kantiyajal

(Bharuch)2014-15 50.00 Plantation Avicennia marina

K.3Village Devla

Bharuch2014-15 50.00 Plantation Avicennia marina

K.4Village Devla

Bharuch2015-16 100.00 In Progress Avicennia marina

400.00

L.1Village Tada Talav

(Khambat, Anand)2015-16 100.00 In Progress Avicennia marina

L.2Village Tada Talav

(Khambat, Anand)2015-16 100.00 In Progress Avicennia marina

200.00

2884.90

Environment and CRZ clearance - Mundra SEZ

(10-138/2008/IA.III dated 15 July 2014)

Total Plantation

(L.1 + L.2)

G. Total (Plantaion done + In Progress)

Total Plantation

(I.1 + I.2 + I.3 + I.4 + I.5)

Total Plantation

(J.1 + J.2)

CRZ Recommendation - Hazira

ENV-10-2012-30-E dtd 11th May,2012

Total Plantation

(K.1 + K.2 + K.3 + K.4)

Village Dandi

(Navsari)





Avicennia marina


Ceriops tagal

107

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