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ARCHIVED REPORTS_XR0002547
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2900 - Site Mitigation Program
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PR0542014
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ARCHIVED REPORTS_XR0002547
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Last modified
1/16/2020 6:19:40 PM
Creation date
1/16/2020 4:43:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002547
RECORD_ID
PR0542014
PE
2960
FACILITY_ID
FA0023306
FACILITY_NAME
LARRYS AUTO REPAIR
STREET_NUMBER
308
Direction
N
STREET_NAME
GRANT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
01
SITE_LOCATION
308 N GRANT ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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28 May 2003 <br /> AGE-NC Project No 95-0184 <br /> IPage 2 of 5 <br /> 22 COLLECTION OF GROUND WATER SAMPLES <br /> Water samples were collected from MW-1 through MW-4 with a hose bailer while dedicated <br /> disposable plastic bailers were used to sample the remaining wells after allowing the wells to achieve <br /> a minimum 80% recovery of the pre-purge water volume Each water sample was transferred into <br /> laboratory-supplied 40-m1 VOA vials containing 0 5 ml 18% hydrochloric acid as a sample <br /> I preservative, the sample from MW-4 was also transferred into a 1-liter amber bottle without <br /> preservative After collection, the samples were properly labeled, placed in a chilled container and <br /> transported under chain-of-custody to Cal Tech Environmental Laboratories (CTEL), a California <br /> Department of Health Services(DHS)-certified analytical laboratory for analysis The samples were <br /> analyzed for <br /> Y <br /> I • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> Method 8015M, <br /> • Volatile organic compounds (VOCs), including benzene, toluene, ethylbenzene and total <br /> rxylenes (BTEX) with fuel oxygenates, including di-isopropyl ether (DIPE), ethyl tertiary- <br /> butyl ether(ETBE),methyl tert butyl ether(MTBE),ternary-amyl methyl ether(TAME)and <br />'. tertiary butyl alcohol (TBA) in accordance with EPA method 826013 Full Scan <br /> In addition, ground water sample MW-4 was analyzed for diesel (TPH-d) In accordance with EPA <br /> IMethod 8015M <br />' 3.0. FINDINGS <br /> Ground water elevation and flow direction were inferred from field data Hydrocarbon-impact to <br />' ground water was quantified by laboratory analysis of the ground water samples <br />' 3 1 GROUND WATER GRADIENT AND FLOW DIRECTION <br />' The elevation of ground water in each well was calculated by subtracting the depth to ground water <br /> from the surveyed casing elevations (Table 1) Depths to ground water ranged from 34 68 feet to <br /> 35 28 feet below the tops of the well casings The ground water levels are as high as approximately <br />' 20 feet above the screened intervals of MW-1 through MW-4 Ground water elevations at the site <br /> ranged from 22 03 feet (MW-3) to 22 54 feet (VW-5C) below mean sea level (MSL) <br />' The ground water appears to flow generally northeast across much of the site at a hydraulic gradient <br /> of approximately 0 003 ft/ft(Figure 2), however, in the northwestern portion of the site the inferred <br /> ground water gradient was 0 006 ft/ft i <br /> Advanced CeoEnvironmental,Inc <br /> ' �r <br />
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