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ARCHIVED REPORTS_XR0008829
Environmental Health - Public
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EHD Program Facility Records by Street Name
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12 (STATE ROUTE 12)
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13889
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3500 - Local Oversight Program
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PR0545719
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ARCHIVED REPORTS_XR0008829
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Entry Properties
Last modified
11/19/2024 3:45:50 PM
Creation date
6/3/2020 11:26:46 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008829
RECORD_ID
PR0545719
PE
3528
FACILITY_ID
FA0005335
FACILITY_NAME
CHARLES JACOBS
STREET_NUMBER
13889
Direction
W
STREET_NAME
STATE ROUTE 12
City
LODI
Zip
95240
CURRENT_STATUS
02
SITE_LOCATION
13889 W HWY 12
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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LSauers
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EHD - Public
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I <br /> 1001 February 2006 <br /> AGE-NC Project No 00-0697 <br />' Page 2 of 4 <br /> allowing the wells to achieve a minimum 80%recovery of the pre-purge water volume Each water <br /> sample was transferred into three laboratory-supplied, 40-milliliter (ml) volatile organic analysis <br /> (VOA)vials containing 0 5 ml 18%hydrochloric acid solution as a sample preservative,and into one <br /> 1-liter amber bottle without preservative After collection,the samples were properly labeled,placed <br /> in a chilled container, and transported under chain of custody to Cal Tech Environmental <br /> Laboratories(CTEL),a State of California Department of Health Services(DHS)-certified analytical <br /> laboratory, for analysis The samples were analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline and diesel (TPH-g and TPH-d, <br /> respectively) in accordance with EPA Method 8015M, and <br /> • Benzene,toluene,ethylbenzene,and total xylenes(BTEX)and fuel additives methyl tertiary- <br /> butyl ether(MTBE), tertiary-butyl alcohol (TBA), di-isopropyl ether(DIPE), ethyl tertiary- <br /> butyl ether (ETBE), tertiary-amyl methyl ether (TAME), 1,2-dibromoethane (EDB), and <br /> 1,2-dichloroethane (1,2-DCA) in accordance with EPA Method 8260B <br /> I <br /> 3.0. FINDINGS <br /> 1 • Ground water elevation and flow direction were inferred from field data, hydrocarbon impact to <br /> ground water was quantified by laboratory analysis of the ground water samples <br /> 3 1 GROUND WATER GRADIENT AND FLOW DIRECTION <br /> The elevation of ground water in each of the monitoring wells was calculated by subtracting the <br /> depths to ground water from the surveyed relative casing elevations (Table 1) Depths to ground <br /> water ranged from 5 02 feet(MW-4)to 6 35 feet(MW-1)below the tops of the well casings Ground <br /> water elevation at the site ranged from 17 78 feet (MW-4) to 18 I5 feet (MW-1) below mean sea <br /> level (MSL), and averaged approximately 18 02 feet below MSL, indicating a decrease in ground <br /> water elevation of approximately 0 45 feet since the last monitoring event in August 2005 During <br /> this monitoring event, the ground water levels in all the wells were below the tops of the well <br /> screens <br /> During the November 2005 ground water monitoring event, ground water at the site was inferred to <br /> be flowing toward the west-northwest under a hydraulic gradient of approximately 0 007 foot/foot <br /> (ft/ft) Figure 3 illustrates the contoured ground water elevations as measured on 16 November 2005 <br /> • <br /> lAdvanced GeoEnvironmental,Inc <br /> I � <br />
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