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2900 - Site Mitigation Program
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PR0523552
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COMPLIANCE INFO
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Last modified
5/27/2021 2:33:36 AM
Creation date
5/26/2021 4:29:52 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0523552
PE
2950
FACILITY_ID
FA0015902
FACILITY_NAME
76 STATION #255417
STREET_NUMBER
1700
Direction
E
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
22802002
CURRENT_STATUS
02
SITE_LOCATION
1700 E YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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S E C O R <br /> ATTACHMENT A <br /> FIELD AND LABORATORY PROCEDURES <br /> EXPLORATORY DRILLING <br /> Soil borings will be drilled to maximum depth of 50 feet bgs using direct push drilling equipment. <br /> The borings will be logged by a geologist using the Unified Soil Classification System and <br /> standard geologic techniques. Soil samples for logging from the borings will be collected <br /> continuously. All soil samples for chemical analysis will be retained in brass liners, capped with <br /> Teflon squares and plastic end caps, and sealed in clean zip-lock bags. The samples will be <br /> placed on ice for transport to the laboratory accompanied by chain-of-custody documentation. <br /> All down-hole drilling and sampling equipment will be steam-cleaned following the completion of <br /> the soil boring. Down-hole sampling equipment will be washed in an alconox solution between <br /> samples. <br /> ORGANIC VAPOR PROCEDURES <br /> Soil samples collected during drilling and redevelopment will be analyzed in the field for ionizable <br /> organic compounds using a photo-ionization detector (PID) with a 10.2 eV lamp or a flame <br /> ionization detector (FID). The test procedure will involve measuring approximately 30 grams <br /> from an undisturbed soil sample, placing this subsample in a sealed container (either a zip-lock <br /> bag or a mason jar). The container will be warmed for approximately 20 minutes (in the sun), <br /> then the head-space within will be tested for total organic vapor, measured in parts per million as <br /> benzene (ppm; volume/volume). The instrument will be calibrated prior to drilling using a <br /> 100-ppm isobutylene standard (in air) and a sensitivity factor of 55, which relates the photo- <br /> ionization potential of benzene to that of isobutylene at 100 ppm. The results of the field-testing <br /> will be noted on the boring logs. PID and FID readings are useful for indicating relative levels of <br /> contamination, but cannot be used to evaluate hydrocarbon levels with the confidence of <br /> laboratory analyses. <br /> LABORATORY PROCEDURES <br /> Selected soil and groundwater samples will be analyzed for TPHg, BTEX, and fuel oxygenates <br /> by EPA Method 8260. <br /> SOIL CUTTINGS AND RINSATE/PURGE WATER <br /> Soil cuttings generated during drilling operations will be temporarily stored on-site in a secure <br /> location pending characterization and disposal. Soil cuttings will be removed by an approved <br /> disposal contractor to an appropriate disposal facility. Water generated during equipment <br /> cleaning and sampling will be temporarily stored in DOT-approved 55-gallon drums pending <br /> transport by an approved disposal contractor to an appropriate disposal or treatment facility. <br /> Drummed soil cuttings and rinsate water will be temporarily stored on-site for approximately 4 to <br /> 6 weeks. <br />
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