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ARCHIVED REPORTS_XR0002534
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0542014
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ARCHIVED REPORTS_XR0002534
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Last modified
1/16/2020 5:37:00 PM
Creation date
1/16/2020 4:35:16 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002534
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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. 31 January 2000 <br /> AGE-NC Project No 95-0184 <br />' Page 2 of 4 <br /> t <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% hydrochlonc acid as a E <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 xc lenes, BTEX) with <br /> methyl ternary-butyl ether (MTBE) in accordance with EPA Method 602/8020 and <br /> I • Volatile organic compounds and fuel oxygenates (di-isopropyl ether [DIFF], ethyl tertiary- <br /> butyl ether [ETBE], tertiary-amyl methyl ether [TAME] tertiary butanol [TBA] and MTBE) <br /> In accordance with EPA Method 8260 <br /> i <br />' The sample from MW-4 was also analyzed for total petroleum hydrocarbons quantified as diesel <br /> (TPH-d) in accordance with EPA Method 8015m <br />' 30 FINDINGS <br /> 3 1 RELATIVE GROUND WATER ELEVATION AND GRADIENT <br /> i <br /> The average depth to ground water at the site was 31 80 feet below the well casing tops during the <br />' Nox ember 1999 monitoring eN ent Ground water elevation decreased an average of 1 34 feet <br /> between August and November 1999, Ground water was approximately 22 to 23 feet above the <br /> screened interval in monitonng wells MW-1, MW-2 and MW-3 Ground water was approximately <br /> I13 feet above the screened interval in MW-4, VW-2B and VW5C, 7 9 feet above the screen in MW-, <br /> 7, 3 5 feet above the screen in VW-3 and 1 6 feet above the screen In VW-4 Ground water was <br /> v.ithin the screened interval of well VW-513 only Ground water elevations in deeper wells were <br /> slightly lower than elevations calculated for the shallower wells at the site Vapor well VW-5 was <br /> installed at an angle of approximately 15° from vertical and therefore was not used for calculating <br /> the ground water elevation and flow direction Measurable free product was not encountered at the <br /> site during the November 1999 monitoring event <br /> For hydraulic gradient determination, the wells were divided into two data sets, MW-1, MW-2 and <br /> E <br /> 4d),ancid CIUEmir.ental laic <br />
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