Observations and Compliances
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03.01.2017 Observations and Compliances Observations and Compliances Observations and Compliances Observations and Compliances Observations and Compliances Observations and Compliances Observations and Compliances Revised Form 1 & 1A (Revision 2) is also attached herewith. ENCLOSURE - 1 From: <[email protected]> Date: 25 November 2559 BE at 2:59:36 PM IST To: <[email protected]> Cc: <[email protected]> Subject: Withdraw of EC Acceptance Letter for withdrawal of EC apllication State Environment Impact Assessment Authority Maharashtra Member Address Dated: 25 Nov 2016 To, KOLTE PATIL DEVELOPERS LTD , Mumbai (Suburban) Maharashtra , 400051 Subject : Withdraw of EC Sir, This has reference to your proposal No. SIA/MH/NCP/58827/2016 dated 06 Sep 2016 regarding withdrawal of Environmental/CRZ Clearance for the above mentioned proposal. 2.0 This is to inform that your request for withdrawal of EC has been accepted in the SEIAA an hence forth, your apllication will be treated as withdrawn. Yours Sincerely SEIAA, Maharashtra ENCLOSURE - 2 ENCLOSURE - 3 FLOORWISE BUILT-UP AREA FLOORS Wing A Wing B Wing C TOTAL LOWER GROUND (For Wing A) 730.56 -- 730.56 BASEMENT (Common for Wing B & C) -- 1461.11 1461.11 GROUND FLOOR (Common for all Wings) 2203.25 2203.25 PODIUM LVL (Common for all Wings) 2358.61 2358.61 1ST FLOOR 335.81 247.66 247.65 831.12 2ND FLOOR 335.81 247.66 247.65 831.12 3RD FLOOR 335.81 247.66 247.65 831.12 4TH FLOOR 335.81 247.66 247.65 831.12 5TH FLOOR 335.81 247.66 247.65 831.12 6TH FLOOR 342.21 260.13 260.12 862.46 7TH FLOOR 335.81 248.9 248.89 833.6 8TH FLOOR 335.81 251.9 251.9 839.61 9TH FLOOR 335.81 251.9 251.9 839.61 10TH FLOOR 335.81 251.9 251.9 839.61 11TH FLOOR 335.81 251.9 251.9 839.61 12TH FLOOR 335.81 251.9 251.9 839.61 13TH FLOOR 338.6 258.24 258.24 855.08 14TH FLOOR 335.81 251.9 251.9 839.61 15TH FLOOR 335.81 251.9 251.9 839.61 16TH FLOOR 335.81 251.9 251.9 839.61 17TH FLOOR 335.81 251.9 251.9 839.61 18TH FLOOR 335.81 251.9 251.9 839.61 19TH FLOOR 246.02 122.02 122.01 490.05 TOTAL 22346.42 TOTAL B/UP AREA PROPOSED (WING- A+ B + C) = 22346.42 SQMT ENCLOSURE - 4 ENVIRONMENTAL MANAGEMENT PLAN – CONSTRUCTION PHASE No. Component Description Total Cost (Rs. in Lacs) 1 Air Environment Dust Suppression 4.32 Air & Noise Quality Monitoring On site sensors #10.00 By outside *0.88 MOEF Approved Laboratory 2 Water Environment Drinking water analysis *0.72 3 Land Environment Site Sanitation 5.00 4 Health & Hygiene Disinfection at site 3.60 Health Check-up of workers 13.50 Total Cost 38.02 ENVIRONMENTAL MANAGEMENT PLAN – OPERATION PHASE Operational and Capital cost No. Component Description Maintenance cost Rs. in Lac. ( Rs. in Lacs/yr) 1 Air Environment & Biological Cost for Gardening 5.54 1.20 Environment Cost for Ambient air & Noise *No set up cost is 0.22 Monitoring involved Cost for DG Stack Exhaust *No set up cost is 0.05 Monitoring involved 2 Water Waste water Cost for sewage Treatment Plant 34.95 23.78 Environment treatment Cost for Waste On site sensors 18.00 1.00 water By outside *No set up cost is 0.03 Monitoring MOEF involved Approved Laboratory Water Cost for RWH tank 4.00 0.20 Conservation (Rain Water Cost for treatment unit for rain 9.00 0.03 Harvesting water tank System) Rain Water Quality Monitoring *No set up cost is 0.14 involved 3 Land Environment Cost for Treatment of 9.00 1.90 (Solid Waste Management) biodegradable garbage in OWC Cost for monitoring of OWC *No set up cost 0.08 manure is involved 4 Energy Conservation Cost for Solar System 65.40 3.24 Total Cost 145.89 31.87 ENCLOSURE -5: COORDINATED LAYOUT PLAN ENCLOSURE - 6 ENTRY/EXIT Ramp to P1 ENTRY/EXIT Babudev Babudev RanadeRoad ENTRY/EXIT Cross Road Vehicular Movement Fire Tender Movement 1 VEHICULAR MOVEMENT & TRAFFIC MANAGEMENT PLAN – GROUND LEVEL 3 2 ENTRY/EXIT 2 3 Ramp to P1 ENTRY/EXIT 2 VEHICULAR MOVEMENT & TRAFFIC MANAGEMENT PLAN – LOWER GROUND LEVEL/BASEMENT LEVEL 2 1 2 2 ENTRY/EXIT 3 VEHICULAR MOVEMENT & TRAFFIC MANAGEMENT PLAN – PODIUM LEVEL 1 1 1 Ramp from GF 1 4 ENCLOSURE - 7 ENCLOSURE - 8A Assessment of ground level concentration of pollutants due to DG set (500KVA) Generator set emissions were below model acceptable levels. Hence ground level concentrations can not be generated. In turn the emissions were well within prescribed limits. ENCLOSURE - 8B Air Dispersion Modeling Report M/s Kolte-Patil Developers Ltd. Dahisar Ultra-Tech Environmental Consultancy & Laboratory Saudamini Commercial Complex, Building C-3, 2nd Floor, Right to Bhusari colony, Paud Road, Kothrud, Pune-411038, Maharashtra. M/s. Kolte-Patil Developers Ltd., Dahisar AIR EMISSION AND DISPERSION MODELING 1.1. Introduction M/s. Kolte-Patil Developers Ltd. is developing a residential complex at plot adjacent to Laxman Mhatre Road. The process of determining power backups along with future traffic levels generated and attracted to the whole development involves the identification of suitable assumptions. Proposed development will have 209 four wheeler parking. Approximate completion time will be three years. The impact on ambient air quality was assessed hereunder in view of the following activities: Analysis and plots as per present traffic Construction source emissions Vehicular re-suspended dust Wind erosion from stockpiling of earlier excavated material and back filling Future analysis considering 25yr traffic projection Dispersion modeling has been carried out using area source emissions with meteorology data to predict ground level Fugitive Dust concentration. Existing peripheral road traffic along with constriction phase scenario i.e. fugitive dust emissions and operational phase traffic pattern and generator use because of the development is estimated in this Chapter. 1.2. Analysis details 1.2.1. Tools and methods The major source of pollutant in the vicinity of the proposed project is vehicular exhaust i.e. line source. The fugitive sources of particulate matter in the vicinity of the proposed project are area polygon source i.e. actual construction activity and volume source i.e. excavation and stockpiling of excavated soil. And re-suspension of road dust because of vehicular movement. There are no other significant sources of fugitive dust pollution in the neighborhood. Source dispersion analysis is assumed based on AERMOD ViewTM model. This model enables analysis with respect to PM10, PM2.5, NOx and CO and gives results in easy to understand graphical format. The following steps are involved in the analysis: I. Inputs are entered into the software as per the general modeling parameters. Page 2 M/s. Kolte-Patil Developers Ltd., Dahisar II. Information on the roadway network, traffic volume, excavated and stockpiled soil, construction activity, generator set and receptor is added to the software. III. The analysis process is done by the model. 1.3. Input(s) needed and assumption Table 1 illustrates series of input and some of assumptions gone into the model. Table 1: Input and Assumptions Sr. No Inputs Required Availability for this project 1. Traffic Parameters Traffic Volume Yes Traffic Composition Yes Type of Fuel used by each category Yes Average Speed of the Vehicles No 2. Construction Parameters Heavy construction activity & Construction Yes of haul road Construction vehicle plying Yes Excavation, Soil Stockpiling Yes 3. Generator Set Capacity Yes Stack details Referred – CPCB’86 4. Meteorological Wind Speed, Wind Direction, Cloud Cover, IMD Weather data Parameters Temperature, Humidity, Station Pressure, etc. 5. Emission Parameters Expressed in grams/distance travelled CPCB 2007 Expressed in grams/m2/second emitted US-EPA, AP42 Expressed in grams/second emitted US-EPA, AP42 6. Road Geometry Road Width Google image Median Width Actual 7. Receptor Location Uniform grid Uniform grid 1.4. Methodology Vehicle number is the most important parameter to quantify the emissions from mobile sources in addition to the distance travelled by each of the vehicles also known as Vehicle Kilometers Travelled (VKT). Emission factors of different types and origin have been used in the past by researches. However, the commonest method and more appropriate method based on the data available is to use emission factor in terms of pollutant mass per kilometer run of the vehicle. The emission factors developed for Indian conditions have been taken from a report “Air Quality Monitoring Project- Indian Clean Air Program, 2007” prepared by CPCB (with ARAI). Page 3 M/s. Kolte-Patil Developers Ltd., Dahisar Heavy construction activity and construction of haul road dust emissions were represented as gm/m2/sec (Ref: USEPA’s Compilation of Air Pollutant Emission Factors, 5th edition, 1995 (AP-42), Section 13.2.3.3). Emission factor for traffic on dusty ground referred from “USEPA’s Compilation of Air Pollutant Emission Factors, 5th edition, 1995 (AP-42), Section 13.2.2”. Fugitive dust emission calculations were done with wind erosion emission factor of activity was taken from “USEPA’s Compilation of Air Pollutant Emission Factors, 5th edition, 1995 (AP-42), Section 13.2.5”. For the generators proposed on site details procured from Emission Regulations – Part IV, CPCB’86 was utilized for emissions estimation. Widespread method based on the data available was to use emission factor in terms of pollutant mass per second generator operated. The emission factors have been taken from “AP42 Ref Stationary Internal Combustion Engines Diesel Fired Ref 3.1” prepared by US – EPA.