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ARCHIVED REPORTS XR0002680
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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HARDING
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3500 - Local Oversight Program
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PR0544424
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ARCHIVED REPORTS XR0002680
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Entry Properties
Last modified
5/6/2019 11:59:15 AM
Creation date
5/6/2019 11:27:25 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002680
RECORD_ID
PR0544424
PE
3529
FACILITY_ID
FA0005099
FACILITY_NAME
HESS DUBOIS CLEANERS
STREET_NUMBER
300
Direction
W
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95203
CURRENT_STATUS
02
SITE_LOCATION
300 W HARDING WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Ir <br />} fl Y.1• J Y.- �'-'-• l �' . 1 h- .11 , aa.f 4 1 - <br /> March 2002 I -4 <br /> la . :AGE-NC.P`roject No.-95'0114 <br /> Page 2 of-4 <br /> 2.2. - COLLECTION OF GROUND WATER SAMPLES <br /> Ground wafer samples were.collected froth.each well using new disposable bailers. Following <br /> recovery of at least 80% of'the-pre-purge "casing water,volume..Immediately upon retrieval; the <br /> 'samples were transferred into 40-;ml EPA=approved'VOA vials containing 0.5 ml of hydrochloric <br /> acid.(18%) as-a sample preservative, and were labeled. The samples were transported,in a chilled <br /> container under chain-of-custody to,Cal Tech Environmental Laboratories,Inc(Cal.Tech_)of -Orange, <br /> . . a State of California Department of Health Services(DHS)-certified laboratory(#2424).The samples <br /> were analyzed for: <br /> • Volatile organic compounds(VOCs) specifically fuel additives methanol,ethanol,ethylene <br /> dibromide(EDB), I,2-dichloroethane(1,2-DCA),tertiary butanol(TBA);di-isopropyl ether ' <br /> (DIPE);ethyl-tert butyl ether(ETBE), tert amyl methyl ether(TAME), and confirmation of: <br /> ' MTBE bEPA Method 8260 Modified and <br /> • Total petroleum hydrocarbons quantified as gasoline and stoddard solvents.(TPH-g/ss) by, <br /> EPA Method 8015 Modified. " <br /> 3.0. FINDINGS <br /> Ground water flow direction and gradient were inferred from the field data. The current distribution <br /> of dissolved petroleum hydrocarbons and dissolved chlorinated hydrocarbons was assessed from <br /> laboratory analytical results of the soil and ground water samples. <br /> .3.1. . GROUND WATER GRADIENT AND.DIRECTION ' <br /> The groundwater elevations were calculated by subtracting the measured depth'to'ground water from <br /> ;the surveyed casing elevations-(Table 1). Ground water elevation s*were plotted and'contoured on <br /> scaled site map." <br /> ;During the February 2002.ground water monitoring event, the depth to ground water at the site <br /> I ,1 ganged from 22:57 to 24:19 feef below tops of the well casings.The ground water gradient and flow <br /> direction was toward the northeast with a gradient of approximately 0.002 from well-MW-1 toward <br /> well NiW-10. Ground water elevation data are summarized in Table t..The contoured ground"water <br /> elevation for the ground water monitoring`event is depictcAin Figure 3. <br /> Wells MW-3R, MW-4 and MW-5:are screened between'30-and 50 feet bsg; wells MW-6-through. <br /> MW'10 are screened between 25 and"45'6r 50 feet.bsg. Ground water is more than,6 feet above the, ` <br /> ,, ,Advanced GeoEnvironmental,Inc, i <br />
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