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ARCHIVED REPORTS_XR0008720
Environmental Health - Public
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WATERLOO
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2900 - Site Mitigation Program
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PR0537118
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ARCHIVED REPORTS_XR0008720
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Last modified
7/7/2020 9:57:05 AM
Creation date
7/7/2020 9:33:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008720
RECORD_ID
PR0537118
PE
2957
FACILITY_ID
FA0021303
FACILITY_NAME
WATERLOO FOOD & FUEL
STREET_NUMBER
3032
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95205
CURRENT_STATUS
01
SITE_LOCATION
3032 WATERLOO RD
QC Status
Approved
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EHD - Public
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W�j <br /> • 25 January 2005 <br /> AGE-NC Project No 99-0559 <br /> Page 3 of 10 <br /> 2 2 COLLECTION AND ANALYSIS OF GROUND WATER SAMPLES <br /> Prior to ground water sampling,the ground water level In each well was measured to ensure that the <br /> well achieved a minimum of 80 percent recharge Following depth measurement, ground water <br /> samples were collected from well chambers well chambers 5B, SC, 5D, 5E, 6B, 6C, 6E, 7B and 7E <br /> utilizing 3/8-inch diameter polyethylene tubing The sample collected from chamber 7D was <br /> collected In the same manor but without purging the chamber prior to sampling The ground water <br /> samples were transferred Into three 40-milliliter(ml)EPA-approved volatile organic analysis(VOA) <br /> vials containing 0 5 ml 18%hydrochloric acid as a sample preservative,care was taken to ensure that <br /> visible air bubbles were not present In the vials after filling and capping Ground water sample <br /> containers were properly labeled, placed In a chilled container and transported under chain of <br /> custody protocol to Cal Tech Environmental Laboratories (CTEL), a California Department of <br /> Health Services-certified laboratory, for analysis The ground water samples were analyzed for the <br /> following <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) in accordance with EPA <br /> Method 8015 Modified, and <br /> • Benzene, toluene, ethylbenzene and xylene (BTEX) and the fuel additives tertiary butanol <br /> (TBA), dl-isopropyl ether (DIPE), ethyl tertiary-butyl ether (ETBE), tertiary-amyl methyl <br /> ether (TAME), methyl tertiary-butyl ether (MTBE), 1,2-dlbromoethane (EDB) and <br /> 1,2-dlchloroethane (1,2-DCA) In accordance with EPA Method 8260B <br /> 2 3 GROUND WATER ELEVATION AND GRADIENT <br /> The elevation of ground water In each monitoring well at the time of the monitoring event was <br /> calculated by subtracting the depth to ground water from the surveyed casing elevation, current and <br /> historical ground water elevation results are provided in Table 1 Each ground water elevation Is <br /> grouped according to the HU on the assumption that the elevation will reflect hydrostatic conditions <br /> within the designated HUs <br /> HU1 and HU2 The depth to ground water In monitoring wells MW-1 through MW-3 was affected <br /> by the presence of free petroleum product and the level of ground water In well MW-4 was below <br /> the casing, these wells were considered dry The depth to ground water measured In wells MW-5A <br /> through MW-7A ranged between 63 91 and 64 09 feet below the top of casing (btoc) The ground <br /> water elevation was calculated between 38 56 feet(MW-6) and 39 49 feet(MW-5)below mean sea <br /> level(MSL),the ground water elevation decreased an average of 0 8 feet since the September 2004 <br /> monitoring event In the multi-level wells The top of the ground water table remained within the <br /> Advanced 4,e0Lnv1r0nmcnt21,Inc <br />
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