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WORK PLANS FILE 2
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3500 - Local Oversight Program
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PR0544591
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WORK PLANS FILE 2
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Last modified
6/21/2019 7:22:35 PM
Creation date
6/21/2019 11:39:16 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
RECORD_ID
PR0544591
PE
3526
FACILITY_ID
FA0005220
FACILITY_NAME
CHEVRON #9-4054
STREET_NUMBER
2103
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204
APN
12308029
CURRENT_STATUS
02
SITE_LOCATION
2103 COUNTRY CLUB BLVD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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«� <br /> probe should begin within 10 minutes of purging. Leak testing should be performed <br /> concurrently with sampling as described above. To begin sampling, open the valve on <br /> the Summa canister. As the canister fills, observe the pressure gauge on the flow <br /> controller to ensure that the vacuum in the canister is decreasing over time. If the flow <br /> controller is working correctly, the planned sampling completion time will be reached <br /> when the pressure has decreased to 5 in Hg. Note that low permeability soils <br /> characterized by low soil vapor flow rates may require sampling to cease before the <br /> canister pressure has decreased to 5 in Hg. <br /> Quality control (QC) of soil vapor samples must be addressed through the collection of <br /> field blanks and field duplicates, and the transport trip blanks. A field blank should be <br /> collected at the site during sampling activities from a certified air source (supplied by the <br /> laboratory). At least one trip blank should be obtained from the analytical laboratory for <br /> each sampling day (event). The trip blank contains laboratory grade ultra pure air and is <br /> intended to provide evidence of contaminants entering the sample containers during <br /> handling and shipping. <br /> At least one duplicate sample should be obtained each day of sampling, or from at least <br /> 10 % of the samples obtained. A duplicate sample should be collected by using a splitter <br /> located upgradient of the flow controller, with separate sampling tubes connecting the <br /> splitter to two Summa®canisters. The flow controller must be set such that the flow rate <br /> from the sampling probe is < 200 mL/min; this will double the required sampling time <br /> since two canisters are being filled simultaneously. <br /> After collection, canisters must not be chilled since contaminants may condense in the <br /> canister at low temperatures. Make certain that all samples are correctly and clearly <br /> labeled. Follow standard chain-of-custody procedures, including noting the final canister <br /> vacuums and serial numbers of the canisters and flow controllers. See Section III A for <br /> canister maximum holding time information. Document all procedures, sampling times, <br /> conditions, problems, etc. Although the California EPA (2003) guidance recommends <br /> against using air freight for shipping,air shipment of canisters is acceptable. <br /> IV. Analytical techniques <br /> The analytical methods used are specific to the components analyzed. Also, the level of <br /> quantification required can vary between components. For example, fixed gases such as <br /> 02, CO2, N2, and CH4 may have less stringent quantification requirements than those for <br /> VOCs (e.g., benzene). Before sampling and analysis begins, refer to applicable state <br /> and/or regional regulations to ensure that all requirements are complied with in sampling <br /> and analysis, including any requirement for state certification of the analytical laboratory. <br /> Ensure consistency of analytical methods between sampling events, as this can help <br /> reduce uncertainties in data results and interpretation. The use of field monitoring <br /> devices such as a PID is not recommended for analyzing soil vapor sample <br /> concentrations. <br /> ETC Soil Vapor Sampling Technical Toolkit 22 <br /> Version 1.4, September 7,2005 <br />
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