File 2 Final Bethpage Offsite SVI Monitoring Plan.pdf
PDF 15 MB Posted
- Attached to
- N4008526R0051 EV32 Bethpage Site 1 and Site 4 OM and M of Site 1 and Site 4 On Property Remedial Systems
- Solicitation number
- N4008526R0051
About this file
This document is a Final Supplemental Offsite Soil Vapor Intrusion Monitoring Plan for the Soil Vapor Extraction (SVE) Containment System at Site 1 - Former Drum Marshalling Area, located at the Naval Weapons Industrial Reserve Plant (NWIRP) in Bethpage, New York. Prepared by Tetra Tech NUS, Inc. under Contract No. N62470-08-D-1001, the plan details the installation of 10 new Soil Vapor Pressure Monitoring (SVPM) points and monitoring procedures to evaluate the effectiveness of the SVE Containment System in controlling potential soil vapor intrusion.
The monitoring plan includes quarterly pressure measurements from 18 offsite SVPMs, annual soil gas sampling using SUMMA canisters, and comprehensive system monitoring. Key objectives include tracking vacuum field measurements, collecting soil gas samples for volatile organic compound (VOC) analysis, and assessing the potential for soil vapor intrusion into residential homes. The plan was developed in response to historical releases of chlorinated solvents and previous soil gas testing that indicated potential contamination near residential areas. The New York State Department of Environmental Conservation (NYSDEC) and New York State Department of Health (NYSDOH) reviewed and approved the monitoring approach.
View the file
Other files
Show all 14
On GovTribe
Work with this file
- Download the original file
- Contacts named in this file
- Similar government files
- Ask GovTribe AI about this file
Text version
FINAL SUPPLEMENTAL
OFFSITE SOIL VAPOR INTRUSION MONITORING
PLAN FOR THE
SOIL VAPOR EXTRACTION CONTAINMENT
SYSTEM
SITE 1 – FORMER DRUM MARSHALLING AREA
NWIRP BETHPAGE
Bethpage, New York
Naval Facilities Engineering Command
Mid-Atlantic
Contract No. N62470-08-D-1001 Contract Task Order WE06
FEBRUARY 2012
i
TABLE OF CONTENTS
SECTION PAGE
ACRONYMS ............................................................................................................................................ A-1
1.0 INTRODUCTION ......................................................................................................................... 1-1
2.0 OFFSITE SVPM INSTALLATION ............................................................................................... 2-1
3.0 SVE CONTAINMENT SYSTEM OFFSITE VACUUM FIELD MONITORING ............................. 3-1
4.0 OFFSITE SOIL GAS MONITORING ........................................................................................... 4-1
5.0 REPORTING ............................................................................................................................... 5-1
REFERENCES ........................................................................................................................................ R-1
APPENDICES
A NYSDEC Letter B SVPM and SVE Construction Logs C SVE, SVPM Vacuum Measurement, and Soil Gas Sampling Log Sheets D Termination of Mitigation System Operations - Enclose from NYSDEC letter
(January 24, 2012)
TABLES
NUMBER
1 SVE and SVPM Construction Details 2 Offsite Soil Gas Monitoring Sample Nomenclature and Analytical Method
FIGURES
NUMBER
1 General Location Map 2 Site Location Map 3 SVE/SVPM Location Map ii
ACRONYMS
APU air purification unit
AS/SVE air sparging/soil vapor extraction
CLEAN Comprehensive Long-Term Environmental Action Navy
CTO contract task order
DCA 1, 1-dichloroethane
DCE 1, 1-dichloroethene
DPT direct-push technology
ELAP Environmental Laboratory Approval Program
GAC granular activated carbon in-wc inches of water column mL milliliter mL/min milliliter per minute
NFA no further action
NWIRP Naval Weapons Industrial Reserve Plant
NYSDEC New York State Department of Environmental Conservation
NYSDOH New York State Department of Health
OM&M Operation, Maintenance, and Monitoring
PCE Tetrachloroethene
SSD sub-slab depressurization
SVE soil vapor extraction
SVI soil vapor intrusion
SVPM Soil Vapor Pressure Monitor
TCA 1, 1, 1-trichloroethene
TCE trichloroethene
Tetra Tech Tetra Tech NUS, Inc.
VOC volatile organic compound
USEPA United States Environmental Protection Agency µg/m micrograms per cubic meter
1-1
1.0 INTRODUCTION
Tetra Tech NUS Inc. (Tetra Tech) under Contract Task Order (CTO) WE06 prepared this
Supplemental Offsite Soil Vapor Intrusion (SVI) Monitoring Plan for the Naval Facilities
Engineering Command Mid-Atlantic under the Comprehensive Long-Term Environmental Action
Navy (CLEAN) contract number N62470-08-D-1001. This plan presents the additional soil vapor pressure and analytical monitoring to evaluate the effectiveness of the Soil Vapor Extraction
(SVE) Containment System at Site 1 – Former Drum Marshalling Area, Naval Weapons Industrial
Reserve Plant (NWIRP) Bethpage, Long Island, New York in controlling potential SVI. This plan details the installation of additional Soil Vapor Pressure Monitoring (SVPM)/soil gas monitoring points and the vacuum field and soil gas monitoring to be conducted in the residential neighborhood east of Site 1 at NWIRP Bethpage (Figures 1 and 2). This monitoring plan supplements the Final Operation, Maintenance, and Monitoring (OM&M) plan submitted in June
2010 (Tetra Tech EC, 2010) that addresses onsite actions.
Site 1 – Former Drum Marshalling Area was impacted by the historic releases of chlorinated solvents and was initially remediated via an air sparging/soil vapor extraction (AS/SVE) system between 1998 and 2002. The treatment and remedial goals were based on protection of groundwater. Soil gas testing conducted in January 2008 indicated elevated concentrations of
Volatile Organic Compounds (VOCs) along the eastern boundary of Site 1 that could potentially affect the adjacent residential neighborhood (Tetra Tech, 2008). Additional soil gas testing was conducted in the Town of Oyster Bay right-of-ways from October 2008 through January 2009 to evaluate the potential migration of contaminated soil vapor off-site (Tetra Tech, 2009a). Based on evaluation of this soil gas data, sampling (indoor air, outdoor air, and sub-slab soil vapor) were conducted to evaluate potential vapor intrusion into residential homes.
From January through April 2009, soil vapor intrusion sampling was conducted in 18 residential homes located east and adjacent to Site 1 (Tetra Tech, 2009b). Between February and May
2011, as an interim measure, granular activated carbon (GAC)-based air purification units (APUs) and sub-slab depressurization systems (SSDs) were placed in homes to mitigate vapor intrusion concerns (Navy, 2009c).
From May through November 2009, indoor air monitoring was conducted to evaluate the mitigation measures implemented in homes and monitor air quality (Tetra Tech, 2009d and e, 2010). In December 2009, construction of the SVE Containment System along the eastern boundary of Navy property was completed. System start up activities began in late December
1-2 CTO-WE06
2009 and was finished in early January 2010. The SVE Containment System continues to operate at Site 1.
Indoor air monitoring activities continued through February 2011, with sampling events conducted in March, July, August, November 2010, and February 2011. The results are presented in the
June 2011 Data Summary Report and Home Evaluation (Tetra Tech, 2011b). By November
2010, all indoor air concentrations were below the New York State Department of Health
(NYSDOH) air guideline values (NYSDOH, 2006). Also, based on the comparison of the sub-slab soil vapor and indoor air results to the NYSDOH decision matrices, no further action (NFA) was the recommended action for all of the homes with only the SVE Containment System in operation. The VOC concentrations in soil gas (SVPMs) and the sub-slab samples collected in the homes have shown consistent decreasing trends. VOC reductions ranged from 99.98% to
99.99% for trichloroethene (TCE), tetrachloroethene (PCE), and 1, 1, 1-trichloroethane (TCA) in the sub-slab and corresponding soil gas locations.
The results of pressure measurements collected from the offsite SVPMs and from the sub-slab locations in the homes combined with the decrease observed in VOC concentrations indicate a vacuum field has been established throughout the study area. The pressure measurements collected from SVPMs along 11 th Street were consistent with the readings collected from the sub-slab sample points in the homes and demonstrated that a measurable vacuum field had been established. Vacuum measurements along 10 th Street were not as consistent, but when coupled with analytical data, confirm that the area is being effectively treated.
The June 2011 Data Summary Report and Home Evaluation provided recommendations to address and monitor offsite soil vapor intrusion, as follows:
Continue operation of the SVE Containment System
Add a shallow SVPM to each existing SVPM cluster located in the Town of Oyster Bay right-of ways to better monitor the SVE Containment System vacuum field and track soil vapor conditions under the homes. Install additional clusters of shallow, intermediate, and deep SVPMs in the northern portion of the residential block on both 10 th and 11 th
Streets and repair and/or replace SVPM-2007I on 10 th Street (Figure 3).
Conduct quarterly rounds of pressure measurements from the SVE/SVPMs to monitor the SVE Containment System vacuum field
Based on the vacuum field and onsite system monitoring, optimize the operation and flow distribution of the SVE Containment System.
1-3 CTO-WE06
Conduct annual SVPM soil gas sampling for VOCs until the source area has been remediated
If concentrations of TCE greater than 250 micrograms per cubic meter (µg/m ) or PCE and TCA greater than 1,000 µg/m are observed in the shallow or intermediate SVPM soil gas samples, re-evaluate SVE Containment System operation, attempt to determine if there is a new source for these detections, and if necessary, re-evaluate soil vapor intrusion sampling in select residential homes.
These conclusions and recommendations were outlined in the June 2011 “Data Summary Report and Home Evaluation, January to March 2011, Soil Vapor Intrusion Investigation, Site 1 – Former
Drum Marshalling Area, NWRIP Bethpage” (Tetra Tech 2011b). The report was reviewed by the
New York State Department of Environmental Conservation (NYSDEC) and the NYSDOH
(Appendix A). This Offsite Vapor Intrusion Monitoring Plan has been developed to ensure the offsite vacuum field is maintained and the SVE Containment System continues to function as the mitigation system for the impacted and potentially impacted homes in the neighborhood.
2-1 CTO-WE06
2.0 OFFSITE SVPM INSTALLATION
Based on an evaluation of the SVE Containment System conducted in February and June 2011, a vacuum field was established throughout the offsite study area (Tetra Tech, 2011b). The vacuum field was confirmed at all samples depths along 11 th Street and was more pronounced near the southeast corner of Site 1 and less pronounced near the northeast corner of Site 1.
However, the evaluation also determined that additional SVPMs are needed to more effectively monitor the offsite vacuum field. A vacuum field was also verified for the homes on 10 th Street, although the readings were close to the limit of the field instrument (0.01 inches of water column
[in-wc]).
Currently nine offsite SVPMs are present. Ten new SVPMs will be installed in the offsite residential neighborhood to enhance the SVPM vacuum field monitoring network (Figure 3).
Existing SVE and SVPM construction logs are provided in Appendix B and details are summarized on Table 1. The new SVPMs will be installed via direct push technology (DPT) to the targeted depths as described in Table 1. Each of the new locations correspond to soil boring locations advanced during the Phase II soil gas sampling conducted in October 2008 and
January 2009 (Tetra Tech, 2009a). The two new SVPM clusters (BPS1-SVPM-2001 and -2006) will be installed on 10 th and 11 th Streets in the northern portion of the residential block and consist of three SVPMs to depths of 10 feet (shallow – S), 25 feet (intermediate – I), and 45 feet (deep –
D). Three shallow SVPMs will be installed at existing SVPM clusters BPS1-SVPM-2003, -2004, and -2007. The existing SVPM, BPS1-SVPM-2007I, which appears to be damaged, will be replaced.
To facilitate the pressure readings and soil gas sampling, installation of each SVPM will consist of placement of a 6-inch long stainless steel soil gas implant to the targeted depths at each location.
High-density polyethylene tubing will extend from the implant to the ground surface for measurements and sampling. Between the existing and new SVPMs, implants will be placed at each location as presented on Table 1. The annular space just below and around each implant will be filled with No. 2 sand to a height of approximately 2 or 3 feet above the implant. Granular bentonite will be used as a seal and placed to a minimum thickness of approximately 2 or 3 feet and hydrated to provide a seal in between each soil gas implant. The remainder of the annulus above the shallow implant will be filled with bentonite/cement grout to the ground surface. The end of the poly tubing will have barbed fittings for attaching a pressure gauge and canisters, to obtain vacuum readings and to collect soil gas samples. Each SVPM will be completed with a flush mount well cover.
3-1 CTO-WE06
3.0 SVE CONTAINMENT SYSTEM OFFSITE VACUUM FIELD MONITORING
A total of eighteen offsite SVPMs will be used to monitor the SVE Containment System vacuum field and determine the effectiveness of the system in capturing and containing offsite soil vapors in the residential area east of Site 1. Table 1 presents SVPM construction details for the existing and new monitoring points. Vacuum readings for the existing SVE wells will also be monitored.
Pressure readings will be collected on a quarterly basis to confirm and monitor the SVE
Containment System vacuum field.
Vacuum/soil vapor pressure measurements will be recorded in inches of water column gauge pressure (in-wc). Field forms for recording pressure measurements, other system information, and soil gas sampling logs are provided in Appendix C.
Gauge pressure is used to evaluate the pressure gradient (pressure or vacuum). These vacuum/pressure readings in the subsurface can be temporarily effected by high and low pressure systems moving through an area. Decreasing atmospheric pressures can result in a temporary positive (or less negative) gauge reading in the subsurface. The time required for soil gas to equilibrate with the atmosphere is dependent on the depth of the sample point, the vertical conductivity of the soil, and the presence of low permeability surface features. As a result, changes in atmospheric pressure during the monitoring period must be considered during evaluation of the data.
As a part of the SVE Containment System monitoring, valve positions will be recorded for each of the SVE wells. The valves are located in the Flow Monitoring Station located in the southeast corner of Site 1 (Figure 3). The Flow Monitoring Station consists of an 8 ft wide x 8 ft tall x 20 ft long Conex box in which all of the SVE lines from the fenceline SVE wells collect into a single manifold and from this location a single underground pipeline has been routed to the Treatment
Building. The valves for the five new SVE wells south of Plant #3 are located at each individual
SVE well location as presented in Figure 3. These new SVE wells are being operated to help address residual VOCs in onsite soils utilizing excess capacity of the SVE blowers.
In addition to quarterly recording of the pressure and valve positions for the SVE wells, the flow rate will be measured at the main manifold in the Flow Control Station and in the Treatment
Building. Data will also be collected on blower operation, pre-carbon temperature, pre-blower pressure, and the presence of condensate in the system piping inside the treatment building.
4-1 CTO-WE06
4.0 OFFSITE SOIL GAS MONITORING
Eighteen soil gas samples will be collected from the SVPMs annually to monitor the continued effectiveness of the SVE Containment System in reducing VOCs in offsite soil vapor in the residential area east of Site 1. Table 1 presents the SVPM construction details for the existing and proposed monitoring points. The SVPM locations are presented on Figure 3. The specific activities for the annual rounds of soil gas sampling will be as follows:
1. Collect flow rate from SVE Containment System at operations building
2. Collect an initial round of vacuum readings from the 18 SVPMs
3. Collect soil gas samples from the 18 SVPMs
4. Collect a second round of vacuum readings from the 18 SVPMs
Sample nomenclature and analysis for the soil gas sampling are presented in Table 2. The field sampling team will maintain a Soil Gas Sample Log Sheet, as presented in Appendix C, for each sample collected. Other pertinent information regarding sample identification or sample collection will be recorded in the field logbook.
The soil gas sampling procedures for each SVPM will be as follows:
1. Connect valve assembly to the sampling port of the SVPM.
2. Connect a vacuum pump to the valve assembly. Purge one to three tubing and implant volumes of soil gas (see table below for appropriate volumes) from the SVPM using the vacuum pump at a rate that should not exceed 200 milliliter per minute (mL/min).
Pre-Sample Purging Requirements
SVPM ¼-Inch Tubing Length (feet)
Purge Goal (1 to 3 Volumes - mL)
Purge Time at 100 mL/minute (minute)
Shallow (S) 10 97 to 290 1 to 3
Intermediate (I) 25 240 to 730 2.5 to 7
Deep (D) 45 440 to 1,300 4.5 to 13
3. Record on the Soil Gas Sample Log Sheet and/or field notebook the flow controller number with the appropriate SUMMA canister number. Isolate vacuum pump and collect soil gas sample with SUMMA canister.
SUMMA
canisters will be utilized for collecting all soil gas samples. The soil gas samples will be obtained over a 30-minute time period. SUMMA canisters will be shipped to the laboratory via overnight carrier (e.g., Federal Express) for analysis.
4-2 CTO-WE06
Ambient air samples will also be collected simultaneously during the soil gas sampling to evaluate potential chemicals in the local ambient air. The SUMMA canister will be positioned at an upwind location at a height of 4 ft above grade. The ambient air sample will be obtained over an eight-hour period. If SVPM sampling takes more than one day, an additional ambient air sample may be collected. Ambient air samples will be shipped to the laboratory as described above.
The soil gas samples will be analyzed for the site specific compound list: 1,1-dichloroethane
(DCA) , 1,1-dichloroethene (DCE), TCA, 1,2-dichloroethane, cis-1,2-dichloroethene, trans-1,2-dichloroethene, TCE, PCE, vinyl chloride; and in accordance to United States Environmental
Protection Agency (USEPA) Method TO-15 VOCs by an Environmental Laboratory Approval
Program (ELAP) certified laboratory (USEPA, 1999).
During the initial soil gas sampling event, or if there is evidence that the integrity of the SVPMs have been compromised (i.e., damaged well cover or tubing), tracer gas (helium) testing will be conducted in accordance with NYSDOH Soil Vapor Guidance Section 2.7.5.
5-1 CTO-WE06
5.0 REPORTING
SVPM readings will be reported in the quarterly OM&M reports. The results of the annual soil gas monitoring, including system performance details, field documentation, sampling sheets, and other operational information collected during the operation, monitoring, and maintenance of the SVE
Containment System will be reported in the annual monitoring report.
In addition, the annual report will evaluate the need for continued operation of the SVE Containment
System in accordance with NYSDOH “Termination of mitigation systems operations” (see Appendix
D).
R-1
REFERENCES
New York State Department of Health (NYSDOH), 2006. Final Guidance for Evaluating Soil Vapor Intrusion in the State of New York. October.
Tetra Tech EC, Inc. (Tetra Tech), 2010. Final Operation and Maintenance Plan for Soil Vapor Extraction Containment System, Site 1 – Former Drum Marshalling Yard. Naval Weapons Industrial Reserve Plant, Bethpage, New York. June.
Tetra Tech NUS, Inc. (Tetra Tech), 2008. Site 1-Soil Vapor Investigation. Naval Weapons Industrial Reserve Plant, Bethpage, New York. April.
Tetra Tech NUS, Inc. (Tetra Tech), 2009a. Site 1 – Phase II Soil Vapor Report, Site 1 – Former Drum Marshalling Area. Naval Weapons Industrial Reserve Plant, Bethpage, New York. August.
Tetra Tech NUS, Inc. (Tetra Tech), 2009b. Data Summary Report Soil Vapor Intrusion Investigation, Site 1 – Former Drum Marshalling Area. Naval Weapons Industrial Reserve Plant, Bethpage, New York. August.
Tetra Tech NUS, Inc. (Tetra Tech), 2009d. Quarterly Data Summary Report Indoor Air and SSD Monitoring (May, June, and July 2009) Site 1 - Former Drum Marshalling Area, Naval Weapons Industrial Reserve Plant, Bethpage, New York. October.
Tetra Tech NUS, Inc. (Tetra Tech), 2009e. Quarterly Data Summary Report Indoor Air and SSD Monitoring (August, September, and October 2009) Site 1 - Former Drum Marshalling Area, Naval Weapons Industrial Reserve Plant, Bethpage, New York. December.
Tetra Tech NUS, Inc. (Tetra Tech), 2010. Quarterly Data Summary Report Soil Vapor Intrusion Monitoring (November and December 2009, and January 2010). Site 1 - Former Drum Marshalling Area, Naval Weapons Industrial Reserve Plant, Bethpage, New York. February.
Tetra Tech NUS, Inc. (Tetra Tech), 2011a. Modification to Existing SVE Containment System, Site 1 – Former Drum Marshalling Area. Naval Weapons Industrial Reserve Plant, Bethpage, New York. September.
Tetra Tech NUS, Inc. (Tetra Tech), 2011b. Data Summary Report and Home Evaluation (January
- March 2011) Soil Vapor Intrusion Investigation Site 1 - Former Drum Marshalling Area Naval Weapons Industrial Reserve Plant, Bethpage, New York, June.
United States Environmental Protection Agency (USEPA), 1999. Compendium of Methods for the Determination of Toxic Organic Compounds in Ambient Air Second Edition Compendium Method TO-15 Determination Of Volatile Organic Compounds (VOCs) In Air Collected In Specially- Prepared Canisters And Analyzed By Gas Chromatography/ Mass Spectrometry (GC/MS).
January.
United States Environmental Protection Agency (USEPA), 2008. EPA Regional Screening Levels for Residential Air, Oak Ridge National Laboratory (ORNL), updated September 2008, retrieved from the EPA website, http://www.epa.gov/reg3hwmd/risk/human/rb-concentration_table/index.htm
U.S. Navy. (Navy), 2009c. Time Critical Removal Action – Off Site Soil Vapor Intrusion Site 1- Former Drum Marshalling Area Naval Weapons Industrial Reserve Plant Bethpage, New York, June.
http://www.epa.gov/reg3hwmd/risk/human/rb-concentration_table/index.htm http://www.epa.gov/reg3hwmd/risk/human/rb-concentration_table/index.htm
TABLES
TABLE 1
SVE AND SVPM CONSTRUCTION DETAILS
SITE 1 - FORMER DRUM MARSHALLING AREA
NWIRP BETHPAGE, NEW YORK
LOCATION LOCATION ID TYPE STATUS DEPTH
11th Street
BPS1-SVPM2001S SVPM New 8-10
BPS1-SVPM2001I SVPM New 23-25
BPS1-SVPM2001D SVPM New 43-45
11th Street
BPS1-SVPM2002S SVPM Existing 8-10
BPS1-SVPM2002I SVPM Existing 23-25
BPS1-SVPM2002D SVPM Existing 42-44
11th Street
BPS1-SVPM2003S SVPM New 8-10
BPS1-SVPM2003I SVPM Existing 23-25
BPS1-SVPM2003D SVPM Existing 43-45
Sycamore Avenue
BPS1-SVPM2004S SVPM New 8-10
BPS1-SVPM2004I SVPM Existing 23.5-25.5
BPS1-SVPM2004D SVPM Existing 40-42
10th Street
BPS1-SVPM2006S SVPM New 8-10
BPS1-SVPM2006I SVPM New 23-25
BPS1-SVPM2006D SVPM New 43-45
10th Street
BPS1-SVPM2007S SVPM New 8-10
BPS1-SVPM2007IR SVPM Replacement 23-25
BPS1-SVPM2007D SVPM Existing 40-42
Onsite Fenceline SVE 101I SVE Well Existing 25-35
Onsite Fenceline SVE 101D SVE Well Existingg 40-60
Onsite Fenceline SVE 102I SVE Well Existing 25-35
Onsite Fenceline SVE 102D SVE Well Existing 40-60
Onsite Fenceline SVE 103I SVE Well Existing 25-35
Onsite Fenceline SVE 103D SVE Well Existing 40-60
Onsite Fenceline SVE 104I SVE Well Existing 25-35
Onsite Fenceline SVE 104D SVE Well Existing 40-60
Onsite Fenceline SVE 105I SVE Well Existing 25-35
Onsite Fenceline SVE 105D SVE Well Existing 40-60
Onsite Fenceline SVE 106I SVE Well Existing 25-35
Onsite Fenceline SVE 106D SVE Well Existing 40-60
Onsite SVE 107 SVE Well Existing 33-53
Onsite SVE 108 SVE Well Existing 33-53
Onsite SVE 109 SVE Well Existing 34-54
Onsite SVE 110 SVE Well Existing 33-53
Onsite SVE 111 SVE Well Existing 38-58
SVE: Soil Vapor Extraction Well
SVPM: Soil Vapor Pressure Monitoring
(SVPM) BPS1 DUP01 Air 1
TABLE 2
OFFSITE SOIL GAS MONITORING
SAMPLE NOMENCLATURE AND ANALYTICAL METHOD
SITE 1 - FORMER DRUM MARSHALLING AREA
NWIRP BETHPAGE, NEW YORK
Location Sample ID Matrix VOCs-TO15A (1)
SVPM 2001
BPS1-SVPM2001S-XXXXXX Air 1
BPS1-SVPM2001I-XXXXXX Air 1
BPS1-SVPM2001D-XXXXXX Air 1
SVPM 2002
BPS1-SVPM2002S-XXXXXX Air 1
BPS1-SVPM2002I-XXXXXX Air 1
BPS1-SVPM2002D-XXXXXX Air 1
SVPM 2003
BPS1-SVPM2003S-XXXXXX Air 1
BPS1-SVPM2003I-XXXXXX Air 1
BPS1-SVPM2003D-XXXXXX Air 1
SVPM 2004
BPS1-SVPM2004S-XXXXXX Air 1
BPS1-SVPM2004I-XXXXXX Air 1
BPS1-SVPM2004D-XXXXXX Air 1
SVPM 2006
BPS1-SVPM2006S-XXXXXX Air 1
BPS1-SVPM2006I-XXXXXX Air 1
BPS1-SVPM2006D-XXXXXX Air 1
SVPM 2007
BPS1-SVPM2007S-XXXXXX Air 1
BPS1-SVPM2007IR-XXXXXX Air 1
BPS1-SVPM2007D-XXXXXX Air 1
Duplicate (SVPM)Duplicate BPS1 DUP01- Air 1
Duplicate (SVPM) BPS1-DUP02 Air 1
Field Blank BPS1-FB2001-XXXXXX Air 1
Field Blank BPS1-FB2002-XXXXXX Air 1
VOCs: Volatile organic compounds. (Site specific list: 1,1-dichloroethane, 1,1-dichloroethene, 1,1,1-trichloroethane, 1,2-dichloroethane, cis-1,2-dichloroethene, trans-1,2-dichloroethene, trichloroethene, tetrachloroethene, vinyl chloride)
XXXXXX: Sample date. For example, BPS1-SVPM2004D-082610, would be collected on August 26, 2010.
1 : 21-Day results from Navy-approved laboratory via method TO-15.
DUP: Duplicate sample
SVPM: Soil Vapor Pressure Monitoring
FB: Field Blank (Ambient Air Sample)
FIGURES
MELISSA.CUSHING
Text Box
SVE102D
SVE102I
SVE101D
SVE101I
SVE103D
SVE103I
SVE104D
SVE104I
SVE105D
SVE105I
SVE106D
SVE106I
BPS1SVPM2007S
BPS1SVPM2001S
BPS1SVPM2001I
BPS1SVPM2001D
BPS1SVPM2006S
BPS1SVPM2006I
BPS1SVPM2006D
BPS1SVPM2004S
Site 1
Plant 3
Plant 17
Flow Monitoring Station
SVE111D
SVE110D
SVE109D
SVE108D
SVE107D
Treatment Building
BPS1SVPM2007D
BPS1SVPM2004I
BPS1SVPM2004D
BPS1SVPM2003S
BPS1SVPM2003I
BPS1SVPM2003D
BPS1SVPM2002S
BPS1SVPM2002I
BPS1SVPM2007I
BPS1SVPM2002D
th
St th
St
Maple Ave
Sycamore Ave
³
125 1250 Feet
SVE AND SVPM LOCATION MAP
SITE 1 - FORMER DRUM MARSHALLING AREA
NAVAL WEAPONS INDUSTRIAL RESERVE PLANT
BETHPAGE, NEW YORK
DATE
AS NOTED
SCALE
DATECHECKED BY
DRAWN BY
MMC 12/6/11
RMS 12/6/11
DATEREVISED BY
CONTRACT NUMBER
APPROVED BY
REVFIGURE NO.
APPROVED BY
DATE
DATE
112G02019
CTO NUMBER
WE06
Legend !> New Proposed Soil Vapor Pressure Monitor !? Soil Vapor Pressure Monitor !. Soil Vapor Extraction Well
Fence Line th
ST
no r p
:\G
IS
_fi les
\B eth pa ge
|M ap
_D
OC
S\M
XD
|R
OB
_S
VP
M| _1
1.m xd M
C
Demolished Bldg
Demolished Bldg
Demolished Bldg
Demolished Bldg
Demolished Bldg
Demolished Bldg
APPENDICES
APPENDIX A
NYSDEC LETTER
New York State Department of Environmental Conservation Division of Environmental Remediation Remedial Bureau A, 11th Floor 625 Broadway, Albany, New York 12233-7015 Phone: (518) 402-9620· Fax: (518) 402-9022 Website: www.dec.ny.qov Joe Martens
Commissioner
July 27,2011
Lora Fly Naval Facilities Engineering Command MidLant Building Z-144 9742 Maryland Avenue Norfolk,VA 23511-3095
RE: Naval Weapons Industrial Reserve Plant Site Bethpage, Nassau County NYSDEC site No.1-30-003B.
Dear Ms. Fly:
The Naval Facilities Engineering Command Midlant has submitted a document entitled "Data Summary Report and Home Evaluation, January to March 2011, Soil Vapor Intrusion Investigation, Site I-Fonner Drum Marshalling Area, NWIRP Bethpage, June 2011." This report has been reviewed by the New York State Department of Environmental Conservation ( NYSDEC) and the New York State Department of Health (NYSDOH). By means of this letter, the NYSDEC approves the Data Summary Report and has the following comments to be included in the Operation, Maintenance and Monitoring (OMM) and ultimate removal of the air purifying units and sub-slab depressurization systems related to Site 1 Fonner Drum Marshalling Area of the NWlRP Bethpage facility.
1. Since the Site 1 Soil Vapor Extraction (SVE) system will be acting as the sole soil vapor intrusion mitigation system for impacted or potentially impacted homes, the engineer should include a system of periodic pressure differential measurements that confinns the potential for soil vapor intrusion to impact the homes continues to be mitigated.
2. The soil vapor extraction system in place at Site 1has a fonnal operations, monitoring and maintenance (OM&M) plan in place for the machinery associated with SVE system that does not include sampling to evaluate monitoring the SSD systems mitigation of the potential for soil vapor intrusion. Therefore, an OM&M plan should be developed and submitted documenting the basic procedures and schedule for conducting pressure measurements and sampling of the soil vapor pressure monitoring points, for the measurements of pressure differentials and/or any additional recommendations of the engineer.
Overall the NYSDEC and the NYSDOH concur with the report's recommendations that there is no longer a need for the Navy to support the operation of air purifying units and sub-slab depressurization systems installed in these homes, and that these systems can be removed at the request of the home owner. The scope of activities and the sampling frequency cited are adequate, with the addition of the appropriate pressure differential readings and/or additional recommendations of the engineer, to be submitted in the OMM plan to be put in place, to ensure that the SVE system is functioning as the soil vapor intrusion mitigation system for the impacted and potentially impacted homes in the area.
In the meantime, if you have any questions, please contact me directly at (518)402-9620.
Sincerely, f5:c1:j~ Project Engineer .E/U Remedial Bureau A Division of Environmental Remediation ecc: J. Swartwout/So ScharflFile W. Parish, Region 1 S. Karpinski, NYSDOH J. De Franco NCDHS C. Stein, USEPA D. Brayack, Tetra Tech NUS R. Sok, Tetra Tech NUS
EDOCS: 13003B-VapoT Intrusion: June 2011 Data Summary Report Comment Letter
APPENDIX B
SVPM AND SVE CONSTRUCTION LOGS
APPENDIX C
SVE, SVPM VACUUM MEASUREMENT, AND SOIL
GAS SAMPLING LOG SHEETS
NWIRP BETHPAGE - SITE 1 - OFFSITE SOIL VAPOR MONITORING
SVPM VACUUM/PRESSURE MEASUREMENT SHEET
Site Name: Site 1 - Former Drum Marshalling Area Project /CTO No.:
Company: Personnel:
Weather Conditions: Measuring Device:
SVPM Date Time Pressure ID Number (inches of water)
BPS1-SVPM2001S
BPS1-SVPM2001I
BPS1-SVPM2001D
BPS1-SVPM2002S
BPS1-SVPM2002I
BPS1-SVPM2002D
BPS1-SVPM2003S
BPS1-SVPM2003I
BPS1-SVPM2003D
BPS1-SVPM2004S
BPS1-SVPM2004I
BPS1-SVPM2004D
BPS1-SVPM2006S
BPS1-SVPM2006I
BPS1-SVPM2006D
BPS1-SVPM2007S
BPS1-SVPM2007I
BPS1-SVPM2007D
Comments and Observations
NWIRP BETHPAGE - SITE 1 - OFFSITE SOIL VAPOR MONITORING
SVE CONTAINMENT SYSTEM MEASUREMENT SHEET
Site Name: Site 1 - Former Drum Marshalling Area Project /CTO No.:
Company: Personnel:
Weather Conditions: Measuring Device:
SVE Date Time Pressure ID Number (inches of water)
Conex Box - Main
SVE 101I
SVE 101D
SVE 102I
SVE 102D
SVE 103I
SVE 103D
SVE 104I
SVE 104D
SVE 105I
SVE 105D
SVE 106I
SVE 106D
SVE 107 NA
SVE 108 NA
SVE 109 NA
SVE 110 NA
SVE 111 NA
SVE System Data Date Time Measurement Comments and Observations
Blower Running
Flow Rate
Temp (Pre-Carbon)
Pressure (Pre-Blower)
Moisture In Header
Valve Position Comments and Observations
SOIL GAS SAMPLING LOG SHEET
Project Site Name: Sample ID No.:
Project/CTO No.: Sample Location:
Company: Sampled By:
SAMPLING DATA:
Date: Wind speed Wind
Direction Ambient temperature Barometric Pressure
Relative Humidity
Time: (Visual) (estimated) (°F) (in.) (%)
Container Type:
Duplicate Sample (if collected)
Canister # Filter Type/Flow
Start Time Vacuum in Hg in Hg End Time Vacuum in Hg in Hg
Purge Data (Time) Flow Rate
(mL/minute) Total volume
PID
Reading
(ppm)
Helium Reading
(ppm)
Notes:
Weather Description
Comments/Observations
NWIRP Bethpage Site 1
Canister # Filter Type/Flow
APPENDIX D
TERMINATION OF MITIGATION SYSTEM
OPERATIONS - ENCLOSURE FROM NYSDEC
LETTER (JANUARY 24, 2012)
| TABLE OF CONTENTS |
| ACRONYMS |
| 1.0 INTRODUCTION |
| 2.0 OFFSITE SVPM INSTALLATION |
| 3.0 SVE CONTAINMENT SYSTEM OFFSITE VACUUM FIELD MONITORING |
| 4.0 OFFSITE SOIL GAS MONITORING |
| 5.0 REPORTING |
| REFERENCES |
| TABLES |
| TABLE 1 - |
SVE AND SVPM CONSTRUCTION DETAILS
TABLE 2 - OFFSITE SOIL GAS MONITORING
| FIGURES |
| FIGURE 1 - GENERAL LOCATION MAP |
| FIGURE 2 - SITE LOCATION MAP |
| FIGURE 3 - SVE AND SVPM LOCATION MAP |
| APPENDICES |
| APPENDIX A NYSDEC LETTER |
| APPENDIX B SVPM AND SVE CONSTRUCTION LOGS |
| APPENDIX C SVE, SVPM VACUUM MEASUREMENT, AND SOIL GAS SAMPLING LOG SHEETS |
| APPENDIX D TERMINATION OF MITIGATION SYSTEM OPERATIONS - ENCLOSURE FROM NYSDEC LETTER (JANUARY 24, 2012) |
File details come from the government source that posted it. Updated .