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ARCHIVED REPORTS XR0004137
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544300
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ARCHIVED REPORTS XR0004137
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Last modified
4/2/2019 3:58:52 PM
Creation date
4/2/2019 3:51:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004137
RECORD_ID
PR0544300
PE
3528
FACILITY_ID
FA0003855
FACILITY_NAME
TESORO (SHELL) 68153
STREET_NUMBER
2448
Direction
W
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
05814001
CURRENT_STATUS
02
SITE_LOCATION
2448 W KETTLEMAN LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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' 10 METHODS AND PROCEDURES <br /> 1.1 Soi] 3am�iing acid Contamination,Reduction <br /> Soil borings and soil sampling was performed under the direction of a Delta geologist The soil borings <br /> will be advanced using a truck-mounted hollow-stem auger drill rig <br /> ' To reduce the chances of cross contamination between boreholes, all downhole drilling equipment will <br /> be steam-cleaned between each soil boring To reduce cross contamination between samples, the <br />' split-barrel sampler is washed in a soap solution and double rinsed between each sampling event <br /> iSoil sampling conducted in accordance with ASTM 1586-84, will use a 2-inch outside-diameter <br /> split-barrel sampler or a 2-inch inside-diameter split-barrel California-type sampler driven into the soil <br />' by a 140-pound weight falling 30 inches After an initial set of 6 inches, the number of blows required <br /> to drive the sampler an additional 12 inches, known as penetration resistance, or the "N" value The "N" <br />' value is used as an empirical measure of the relative density of cohesionless soils and the consistency of <br /> cohesive soils The sampler is lined with three brass sample tubes, each 6 inches long and the <br /> outside-diameter equal to the inside-diameter of the sampler <br /> Upon recovery, a portion of the soil sample is placed into a plastic bag and sealed for later screening with <br /> a photoionization detector (PID) as described in Section 1 3 A representative portion of the soil sample <br /> will be used for classification and description The soil sample collected in the leading brass tubes within <br /> the California-type sampler will be labeled, sealed, and stored on ice for transport to the laboratory <br /> 1.2 Soil Classification <br />' As the samples are obtained in the field, they will be classified in accordance with the Unified Soil <br /> Classification System Representative portions of the samples will be retained for further examination <br /> t and for verification of the field classification Logs of the borings indicating the depth and identification <br /> of the various strata, the "N" value, and pertinent information regarding the method of maintaining and <br />' advancing the borehole will be made <br />' 1.3 Soil-Sample Screenin /hNu Portable Photoionization Detector Method <br /> After the soil samples in the plastic bags are warmed to approximate ambient temperature, the organic <br />' vapors within the headspace of the soil sample bars will be screened with a portable PID equipped with <br /> a 10 2 eV lamp calibrated to benzene The sample bag will be opened and the detector probe <br /> unmediatgly placed within the headspace of the bag The highest observed reading will be recorded <br /> RPTo66 TA <br />
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