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ARCHIVED REPORTS_XR0008439
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545864
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ARCHIVED REPORTS_XR0008439
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Last modified
7/21/2020 10:01:12 AM
Creation date
7/21/2020 9:50:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008439
RECORD_ID
PR0545864
PE
3528
FACILITY_ID
FA0004530
FACILITY_NAME
MARLOWE PROPERTY
STREET_NUMBER
4648
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95215
CURRENT_STATUS
02
SITE_LOCATION
4648 WATERLOO RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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I <br /> n Y <br /> 03 December 2004 <br /> . AGE-NC Project No 95-0104 <br /> IPage 2 of 4 <br /> I water sample was transferred Into three 40-m1 volatile organic analysis(VOA)vials containing 0 5 <br /> ml 18%hydrochloric acid as a sample preservative and into one 1-liter amber bottle without added <br /> preservative The samples were properly labeled,placed in a chilled container and transported under <br /> I chain of custody to McCampbell Analytical, Inc (MAI) a State of California Department of Health <br /> Services (DHS)-certified analytical laboratory The samples were analyzed for <br /> I • Total petroleum hydrocarbons quantified as gasoline (TPH-g) and diesel (TPH-d) In <br /> accordance with EPA Methods 503013550/8015-Modified, <br /> I • Benzene, toluene, ethylbenzene and total xylenes (BTEX) and methyl tertiary-butyl ether <br /> (MTBE) in accordance with EPA Method 8020, and <br /> • Fuel additives MTBE, di-isopropyl ether (DIPE), ethyl tertiary-butyl ether (ETBE), <br /> I tertiary-amyl methyl ether(TAME),tertiary butanol (TBA), 1,2-dichloro ethane (1,2-DCA) <br /> and ethylene dibromide (EDB) In accordance with EPA Method 8260B <br /> I <br /> 3.0. FINDINGS <br /> Ground water elevation, flow direction, and gradient were determined from field data collected on <br /> 27 September 2004, the contaminant impact to ground water was quantified from the laboratory <br /> Ianalytical data obtained from the sampling event <br /> 3 1 RELATIVE GROUND WATER ELEVATION AND GRADIENT <br /> The elevation of ground water in each monitored well was calculated by subtracting the depth to <br /> Iground water from the surveyed well casing elevations (Table 1) <br /> The depth to ground water ranged from 76 62 feet to 77 44 feet below the tops of the well casings <br /> Ground water elevations at the site ranged from 22 13 feet above mean sea level (MSL) in well <br /> MW-5 to 22 28 feet above MSL in well MW-6 <br /> The ground water flow direction on 27 September 2004 was inferred to be towards the north under <br /> an average gradient of 0 007 foot/foot Figure 3 illustrates the contoured ground water elevations <br /> 3 2 ANALYTICAL RESULTS OF GROUND WATER SAMPLES <br /> I1,2-DCA was detected in the water samples collected from MW-4, MW-Sand MW-6 at <br /> concentrations of 0 83 µg/1, 13 µg/1 and 1 7 gg/l,respectively TPH-g,BTEX and other fuel additives <br /> Advanced GeoEmironmental,Inc <br /> I <br />
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