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ARCHIVED REPORTS XR0001089
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3500 - Local Oversight Program
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PR0544230
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ARCHIVED REPORTS XR0001089
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Last modified
3/5/2019 8:08:47 PM
Creation date
3/5/2019 3:59:08 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001089
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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I SS <br /> 11 <br /> y ! <br /> i" 11 November 2004 <br /> AGE-NC Protect No 02-0962 <br /> i Page 12 of 14 <br /> l 1 <br /> r, <br /> 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 /> i ranging from surface grade to approximately 30 feet bsg underlies the assessed portion of the <br /> property(vadose zone&HU 1) Beneath the clayey silt layer is a fine-grained layer consisting of silty <br /> i sand to'fine sand (HU2),which is encountered approximately from 30 feet bsg to 38 feet bsg HU2 <br /> has the characteristics of an aquifer, or the water table <br /> Beneath the silty sand to sand layer are alternating layers of stiff, fine-grained soils and sandy soils <br /> i The stiff fine grained layers act as confining layers,retarding the vertical migration of contaminants <br /> The sandy layers act as migratory flow units allowing contaminants to vertically and laterally migrate <br /> ifrom the source A geologic cross section is provided on Figure 4 <br /> During site assessment activities in July and August 2004, saturated soil or the capillary fringe was <br />' first encountered at approximately 25 feet to 30 feet below bsg Based on information from quarterly <br /> monitoring events performed by AGE at the adjacent Nomellini Construction Company, ground <br /> water flow is generally toward the north to northeast However,this maybe greatly modified by local <br /> recharge and discharge patterns <br /> Site assessment activities to date defined two areas where soil is impacted by concentrations of <br />' petroleum hydrocarbons The maximum petroleum hydrocarbon concentrations(110 mg/kg TPH-d) <br /> were detected adjacent to the former piping sample location P13, at 15 feet bsg in soil probe boring <br /> B3 (Figure 2) Petroleum hydrocarbons were also detected at a concentration of 12 mg/kg in the soil <br />' sample collected from boring B7 at 30 feet bsg, adjacent to piping sample P7 Soil samples collected <br /> at 60 and 90 feet bsg from boring CPT1 were impacted by petroleum hydrocarbons TPH-g was <br /> detected at concentrations of 2 1 mg/kg(CPT 1-60) and 6 3 mg/kg(CPT 1-90), TPH-d was detected <br /> at a concentration of 110 mg/kg in CPT 1-90 <br />' Site assessment activities to date defined an area where ground water is impacted by high <br /> concentrations of petroleum hydrocarbons The highest petroleum-hydrocarbon concentrations, up <br /> to 2,200,000 µg11 TPH-d,were detected in grab ground water samples adjacent to the former piping <br />' sample location P13 Petroleum hydrocarbons, up to 190,000 µg/l, were detected in grab ground <br /> water samples j ust north of dispenser D 1(Fzgure 2) MTBE was detected in minor concentrations just <br /> north of dispenser sample D7 Ground water,was not impacted below 35 feet bsg Ground water <br /> samples collected from the ground water monitoring wells defined the dissolved plume at the <br /> northern edge of the dispenser islands <br />' Based on AGE's interpretation of the available data,the initial release(s)of petroleum hydrocarbons <br /> . occurred from the former,dispensers and associated piping prior to their removal in 2003 Once <br />' Advanced GeoEnvironmental <br />
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