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ARCHIVED REPORTS XR0001087
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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3500 - Local Oversight Program
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PR0544230
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ARCHIVED REPORTS XR0001087
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Entry Properties
Last modified
3/5/2019 8:33:56 PM
Creation date
3/5/2019 3:58:12 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001087
RECORD_ID
PR0544230
PE
3528
FACILITY_ID
FA0003829
FACILITY_NAME
VANCO TRUCK-AUTO PLAZA
STREET_NUMBER
1033
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16323041
CURRENT_STATUS
02
SITE_LOCATION
1033 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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ti <br /> 13 June 2005 , <br /> AGE-NC Project No 02-0962 <br /> IPage 2 of 4 <br /> dedicated tubing after allowing the well to achieve a minimum 80%recovery of the pre-purge water <br /> volume The samples from each well were transferred Into three 40-milliliter(ml) volatile organic <br /> analysis(VOA)vials containing 0 5 ml 18%hydrochloric acid solution as a sample preservative,and <br /> into one 1-liter amber bottle without preservative The samples were labeled with the monitoring <br /> well designation, date, time of sampling, and the sampler's initials and transported in a chilled <br /> container under chain of custody to Cal Tech Environmental Laboratories (CTEL), a State of , <br /> I California Department of Health Services (DHS)-certified analytical laboratory, for analysis The <br /> samples were analyzed for r <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 1,2- <br /> Idichloroethane (1,2-DCA) in accordance with EPA Method 8260B <br /> 3.0. FII - DIINGS <br /> 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 19 55 feet (MW-1) to 19 80 feet (MW-2) below the tops of the well casings <br /> Ground water elevation at the site averaged approximately 7 73 feet below mean sea level (MSL), <br /> indicating an increase in ground water elevation of 2 20 feet since the last ground water monitoring <br /> event in November 2004 <br /> During the March 2005 ground water monitoring event, ground water was Inferred to be flowing <br /> toward the north-northwest under a nearly flat gradient of approximately 0 0003 foot/foot (ft/ft) <br /> Ground water elevations were within the screened intervals of the wells,indicating that the wells are <br /> properly screened to yield samples representative of shallow ground water conditions `Figure 3 <br /> illustrates the contoured ground water elevation as measured on 02 March 2005 <br /> I <br /> Advanced GeoEnvnronmentat,Inc <br /> I , <br />
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