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ARCHIVED REPORTS XR0000575
Environmental Health - Public
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EHD Program Facility Records by Street Name
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139
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3500 - Local Oversight Program
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PR0544169
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ARCHIVED REPORTS XR0000575
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Entry Properties
Last modified
2/22/2019 8:57:10 PM
Creation date
2/22/2019 4:04:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000575
RECORD_ID
PR0544169
PE
3528
FACILITY_ID
FA0006437
FACILITY_NAME
CHEVRON STATION #90557*** (INACT)
STREET_NUMBER
139
Direction
S
STREET_NAME
CENTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13730012
CURRENT_STATUS
02
SITE_LOCATION
139 S CENTER ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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WNg
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EHD - Public
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� r <br /> extend from the sand pack to the ground surface. The boring logs will show well <br /> construction details. <br /> The wells will be developed and sampled after completion. The development procedure <br /> for each well will consist of pumping or bailing water from the well until the water is <br /> visibly clear, the well goes dry, or until a maximum of ten casing volumes have been <br /> removed. After development, water levels are allowed to partially recover. <br /> Groundwater samples are then collected using a disposable teflon bailer, placed into <br /> appropriate EPA-approved containers, labeled, placed on ice, and transported to the <br /> laboratory accompanied by chain-of-custody documentation. <br /> A California State Licensed Surveyor will survey the newly installed wells. The well <br /> casings will be surveyed to the nearest 0.01 feet in elevation to a known benchmark. <br /> Organic Vapor Procedures <br /> Soil samples collected at continuously during drilling will be analyzed in the field for <br /> ionizable organic compounds using a photo-ionization detector(PID) with a 10.2 eV <br /> lamp or a flame ionization detector(FID). The test procedure will involve measuring <br /> approximately 30 grams from an undisturbed soil sample, placing this subsample in a <br /> sealed container (either a zip-lock bag or a mason jar). The container will be warmed for <br /> . approximately 20 minutes (in the sun), then the head-space within will be tested for total <br /> organic vapor, measured in parts per million as benzene (ppm; volume/volume). The <br /> instrument will be calibrated prior to drilling using a 100-ppm isobutylene standard (in <br /> air) and a sensitivity factor of 55, which relates the photo-ionization potential of benzene <br /> to that of isobutylene at 100 ppm. The results of the field-testing will be noted on the <br /> 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 samples collected will be analyzed for the presence of total petroleum <br /> hydrocarbons as gasoline (TPHg), benzene, toluene, ethyl benzene, xylenes (BTEX), and <br /> methyl tertiary butyl ether(MtBE) using EPA Method 8260. <br /> Collected groundwater samples will be analyzed for the presence of TPHg, BTEX <br /> compounds, and fuel oxygenates and lead scavengers including MtBE, tertiary butyl <br /> alcohol (TBA), di-isopropyl ether(DIPE), ethyl tertiary butyl ether(ELBE), tertiary amyl <br /> methyl ether(TAME), 1,2-dichloroethan, ethylene dibromide(EDB), ethanol and <br /> methanol using EPA method 8260. <br />
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