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2900 - Site Mitigation Program
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PR0009229
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WORK PLANS
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Last modified
6/27/2020 8:05:45 AM
Creation date
6/26/2020 5:02:08 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0009229
PE
2960
FACILITY_ID
FA0004047
FACILITY_NAME
STOCKTON ARMY AIR SUPPORT FAC
STREET_NUMBER
2000
STREET_NAME
STIMSON
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
17726004
CURRENT_STATUS
01
SITE_LOCATION
2000 STIMSON ST
P_LOCATION
01
QC Status
Approved
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4; RESPONSE TO COMMENTS (December 2010) <br /> DRAFT WORK PLAN FOR GROUNDWATER MONITORING WELL INSTALLATION, SOIL GAS AND GROUNDWATER INVESTIGATION,AND <br /> GROUNDWATER MONITORING, October 2010 <br /> Army Aviation Support Facility, 2000 Stimson Road, Stockton, CA <br /> OTIE Contract Number:W91238-09-D-0017, DO 0004,Amendment 01 <br /> 8 Doc. Source Section/Page Comment Response(Contractor) <br /> 4 WP CVRWQCB — The proposed soil vapor sampling program in the Draft Per CVRWQCB recommendation,the depths of all soil <br /> Work Plan targets a zone from 20 to 35 feet below ground vapor samples will be based upon the lihtologies <br /> surface(bgs). This depth range was selected because encountered (logged in the field), photoionization <br /> groundwater is anticipated at approximately 35 to 40 feet detector(PID)readings, and the field experience of the <br /> bgs and the upper 20 feet of vadose zone is expected to site geologist. Encountered soils(i.e. borings)will be <br /> be relatively impermeable based on previous borings screened with a PID for VOCs. Boring depths with <br /> advanced at the site. This proposed soil vapor sampling elevated levels of VOCs(as compared to all boring <br /> program may provide data on vapors off-gassing from the intervals screened)will be noted.These values will <br /> local water table, but it may not adequately characterize contribute to the decision of associated soil vapor <br /> areas where solvents were potentially released into the sample depths. <br /> subsurface(source areas). The more permeable soils <br /> should be targeted, but the upper vadose zone should be In the case of soil vapor samples planned within a <br /> targeted too if the boring location is adjacent to a suspected source area(inferred by location or elevated <br /> suspected solvent release area such as the former or PID readings)possessing what appear to be <br /> existing wash rack or associated clarifiers. Central Valley impermeable soils, one sample attempt per discrete <br /> Water Board staff recommends selecting the proposed location will be made, prior to attempting a sample at a <br /> soil vapor sample depths based on the actual soils more feasible(i.e. more permeable)sample depth. <br /> encountered at each proposed boring locations rather <br /> than assume the upper 20 feet of the vadose zone is too The text of the Work Plan has been revised to reflect <br /> impermeable to yield viable soil vapor samples across the that the aforementioned response. <br /> site. Furthermore, CANG should make a few attempts to <br /> sample the shallow vadose zone in the suspected source <br /> areas even if the soils appear to be impermeable. <br /> 5 WP CVRWQCB — CANG should consider using a mobile lab or portable See response to Comment#4. <br /> equipment that can provide quantitative or semi- <br /> quantitative analysis of VOCs during advancement of the <br /> 40 borings, so subsequent borings can be adjusted to <br /> characterize any release areas that may be identified <br /> during investigation. Alternatively, if CANG suspects <br /> VOCs have been encountered based on field screening <br /> readings,the sample could be analyzed on an <br /> accelerated turnaround at a fixed-base laboratory. <br /> 2 <br />
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