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ARCHIVED REPORTS XR0001091
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3500 - Local Oversight Program
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PR0544230
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ARCHIVED REPORTS XR0001091
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Last modified
3/5/2019 8:42:39 PM
Creation date
3/5/2019 3:59:49 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001091
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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1 . 30 March 2004 <br /> AGE-NC Project No 02-0962 <br />' Page 5 of 7 <br /> 4 3 HYDROCARBON-IMPACTED GROUND WATER <br /> 1 <br /> Grab ground water samples collected from six of the seven soil borings on 30 and 31 October 2003 , <br /> were analyzed for the petroleum hydrocarbon products listed in Section 3 2 The following target <br /> analytes were detected <br /> • TPH-g and TPH-d were detected in ground water samples collected from bonngs B2 and B4, <br />' at maximum concentrations of 190,000 micrograms per liter(µg/1)TPH-g and 2,200,000µg/1 <br /> (TPH-d) in boring B4 Laboratory chromatograms show the TPH-g concentrations were <br />' detected within the diesel-range spectrum, Indicating that the TPH-g may actually be <br /> degraded diesel fuel <br /> • MTBE was detected in ground water samples collected from boring B5 at a concentration <br />' of 15 µg/1 <br /> No other target analytes were detected at or above laboratory detection limits in the samples <br />' analyzed Analytical results from ground water samples are summarized in Table 2 The lateral <br /> distribution of TPH-d impacted groundwater is depicted in Figure 3A The laboratory report(CTEL <br /> Project No CT214-0311002), quality assurance and quality control (QA/QC) report and chain-of- <br /> custody forms are included in Appendix B ` <br /> 5 0 SITE CONCEPTUAL MODEL <br /> Based on the data collected to date from the soil boring installation and sampling, AGE has <br /> developed a site conceptual model for the release,migration and distribution of the contaminants in <br /> the subsurface as described below <br /> The site surface is essentially flat land that Is developed into a truck and auto plaza(Figure 2) The <br /> majority of the ground surface is covered by an asphalt or concrete cap In general, a clayey silt layer <br /> ranging from surface grade to approximately 20 feet bsg underlies the assessed portion of the <br /> property(Unit 1) Beneath the clayey silt layer is a fine-grained layer consisting of silty sand to fine <br /> sand (Unit 2); which is encountered at approximately 20 feet bsg and whose vertical extent in not <br /> yet known The informal unit 2 has the characteristics of the an aquifer, or the water table Geologic <br /> cross sections are provided as Figures 4 through 10 <br /> During site assessment activities in October of 2003;ground water was encountered approximately , <br /> I' 19 45 feet to 26 3 feet below bsg Based on Information from quarterly monitoring events performed <br /> by AGE at the adjacent Nomellmi Construction Company, ground water flow is generally toward <br /> the north to northeast However, this may be greatly modified by local recharge and discharge <br /> . patterns <br /> Advanced GeoE nviron mental,Inc <br /> I ' <br />
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