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2900 - Site Mitigation Program
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PR0528359
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Last modified
5/8/2020 3:20:07 PM
Creation date
5/8/2020 2:48:23 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0528359
PE
2950
FACILITY_ID
FA0019146
FACILITY_NAME
SHELL OIL PRODUCTS US
STREET_NUMBER
3725
Direction
N
STREET_NAME
TRACY
STREET_TYPE
BLVD
City
TRACY
Zip
95304
APN
21217030
CURRENT_STATUS
02
SITE_LOCATION
3725 N TRACY BLVD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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-- PROPOSED WORK PLAN FOR PRETANK CLOSURE SITE ASSESSMENT <br /> Shell Service Station <br /> 3725 Tracy Boulevard, Tracy California <br /> Delta Project No. 40-0-012 <br /> Pale 7 <br /> .1 Exploratory Soit Borings <br /> A total of ten soil borings will be advanced within the property boundaries of the site (Figure 2). <br /> Four soil borings will be advanced adjacent to the existing underground storage tank location. Four <br /> soil borings will be advanced in the vicinity of the proposed new tank location, and two other soil <br /> borings will be located adjacent to the dispensing line locations. <br /> All soil borings will be advanced using 7.5- or 8-inch-diameter hollow-stem augers. Samples will <br /> be collected with a California modified split-spoon sampler. Appendix C describes the drilling and <br /> V sampling techniques to be used. Soil samples will be collected at vertical intervals of 5.0 feet. Soils <br /> - will be screened with a PID as described in Appendix C to determine organic vapor content. Borings <br /> will be advanced to a minimum depth of 20 feet, or until soil screening indicates three consecutive <br /> LI soil samples contain nondetectable levels of organic vapors. A soil sample containing organic vapor <br /> levels comparable to background levels will be considered to contain nondetectable levels of organic <br /> vapors. A sample will be submitted for laboratory analysis to verify the field determination. <br /> 3.2 Soil SAmiple Collection and Scrgening <br /> L' <br /> A California modified split-barrel sampler will be used to extract the soil samples from the soil <br /> borings. Three 6-inch brass tubes will be inserted into the California sampler to retain the soil <br /> w� sample. Upon retrieval, one brass tube will be capped, packaged, and placed in an ice chest at 4°C <br /> for shipment to the laboratory. The soils in the second brass tube will be extracted and placed in a <br /> t sealed jar until completion of the drilling activities. The samples placed in jars will be brought to <br /> !� room temperature, and the headspace of each jar will be screened for total organic vapors utilizing <br /> a portable photoionization detector equipped with a 10.2 eV lamp calibrated to benzene for direct <br /> t reading in parts per million. Refer to Appendix C for sampling and screening methods. <br /> 3.3 Chemical Analysis <br /> Based on results of soil sample screening, soil samples will be selected for chemical analysis. Soil <br /> samples will be analyzed for TPH by EPA Method 8015. Those samples with TPH concentrations <br /> exceeding 100 ppm will be analyzed for BTEX by EPA Method 8020. <br /> 4.0 SCHEDULE <br /> Delta will proceed with the work outlined in this work plan as soon as approval is obtained. A drill <br /> crew will be mobilized to drill the proposed borings within 2 weeks of approval of this plan. <br /> Laboratory analysis of soil samples generally requires 3 weeks. A summary report of our results will <br /> be prepared within 3 weeks after laboratory results are received. <br /> 1 <br /> r <br />
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