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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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I_0 METHODS <br /> LL—Soil .SamItlingand.0 nt minati n Reduction <br /> Soil borings and soil sampling will be performed under the direction of a Delta engineer or geologist. <br /> The soil borings will be advanced using a truck-mounted drill rig utilizing hollow-stem augers. <br /> To reduce the chances of cross-contamination between boreholes, all downhole drilling equipment <br /> will be cleaned between borings. To reduce cross-contamination between samples, the spit-barrel <br /> sampler will be washed in a soap solution and double-rinsed between each sampling event. <br /> Soil sampling .will be done in accordance with ASTM I586-84. Using the procedure, a two-inch <br /> outside diameter split-barrel sampler or a two-inch inside diameter California-type sampler is driven <br /> into the soil by a 140-pound weight failing 30 inches. After an initial set of 6 inches, the number <br /> of blows required to drive the sampler an additional 12 inches is known as penetration resistance, or <br /> the "N" value. The N value is used as an empirical measure of the relative density of cohesionless <br /> soils and the consistency of cohesive soils. <br /> Upon recovery, a portion of the soil sample will be placed into a glass jar and sealed for later <br /> screening with a portable photoionization detector. Another portion of the soil sample will be used <br /> for classification and description. That part of the soil sample collected in brass tubes within the <br /> California-type sampler will be stored at approximately 4°C for transport to the laboratory. <br /> 1,2 Soil Classification <br /> As the samples are obtained in the filed, they will be classified by a geologist/engineer in accordance <br /> .with ASTM: D2488-84. Representative portions of the samples will then be returned to the <br /> laboratory for further examination and for verification of the field classification. Logs of the borings <br /> indicating the depth and identification of the various strata the N value water-level information, <br /> and pertinent information regarding the method of maintaining and advancing the borehole will be <br /> made. <br /> 1.3 Soil Sample Screening/Portable Photoionization Detector Method <br /> After soil sample jars have been brought to room temperature, the headspace vapors of the soil <br /> sample jars will be screened with a portable photoionization detector equipped with a 10.2 eV lamp <br /> calibrated to benzene for direct reading in parts per million(ppm). The sample jar lid will be opened <br /> and the probe immediately placed within the headspace of the jar. The highest observed reading will <br /> be recorded. <br /> 1.4 Monitoring Well Gravel Pack and Slot Size Selection <br /> The size of the gravel pack that will be placed adjacent to the well screen will be determined by the <br /> project manager based on an estimation of the distribution of grain size in the formation which is <br />
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