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ARCHIVED REPORTS_XR0002533
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0542014
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ARCHIVED REPORTS_XR0002533
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Last modified
1/16/2020 5:36:08 PM
Creation date
1/16/2020 4:34:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002533
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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' 03 May 2000 <br />' AGE-NC Project No 95-0184 <br /> Page 2 of 4 <br />' 22 COLLECTION OF GROUND WATER SAMPLES <br /> Water samples were collected from each purged well using new disposable bailers Each sample was <br />' transferred into 40-m1 EPA-approved VOA vials containing 0 5 ml 18% hydrochloric acid as a <br /> sample preservative The sample from MW-4 was also transferred into a 1-liter amber bottle without <br />' preservative The sample containers were labeled,placed in a chilled container and transported under <br /> chain-of-custody to McCampbell Analytical, Inc (MAI) in Pacheco, California, a California <br /> Department of Health Services (DHS)-certified analytical laboratory The samples were analyzed <br />' for <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) In accordance with EPA <br />' Method 5030/8015m, - <br /> • Volatile aromatic hydrocarbons benzene, toluene, ethylbenzene and xylenes (BTEX) with <br />' methyl tertiary-butyl ether(MTBE) In accordance with EPA Method 60218020, and <br /> • Volatile organic compounds and fuel oxygenates (di-isopropyl ether [DIPE], ethyl tertiary- <br /> butyl ether [ETBE], tertiary-amyl methyl ether [TAME] tertiary butanol [TBA] and MTBE) <br /> in accordance with EPA Method 8260 <br />' The 1-liter sample from MW-4 was also analyzed for total petroleum hydrocarbons quantified as <br /> diesel (TPH-d) in accordance with EPA Method 8015m <br /> 3 0. FINDINGS <br /> Ground water elevation and flow direction were calculated from field data, hydrocarbon-impact to <br /> ground water was inferred from laboratory analysis of the ground water samples <br /> 3 1 RELATIVE GROUND WATER ELEVATION AND GRADIENT <br />' The average depth to ground water at the site was 31 32 feet below the well casing tops during the <br /> February 2000 monitonng event Ground water elevation increased an average of 0 51 feet between <br /> November 1999 and February 2000 Ground water was approximately 23 6 feet above the screened <br /> interval In monitoring wells MW-1 and MW-3 Ground water was approximately 12 to 114 feet above <br /> the screened Interval In MW-4, VW-2B and VW5C, 8 5 feet above the screen In MW-7, 3 8 feet <br /> above the screen In VW-3 and 2 1 feet above the screen in VW-4 Ground water was within the <br /> screened interval of well VW-5B only Ground water elevations In deeper wells were similar to <br /> elevations calculated for the shallower wells at the site Vapor well VW-5 was installed at an angle <br /> of approximately 15° from vertical and therefore was not used for calculating the ground water <br /> Advanced GcoEniironmental,Inc <br />
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