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ARCHIVED REPORTS_XR0002661
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3500 - Local Oversight Program
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PR0545259
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ARCHIVED REPORTS_XR0002661
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Entry Properties
Last modified
1/31/2020 4:32:36 PM
Creation date
1/31/2020 3:23:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002661
RECORD_ID
PR0545259
PE
3528
FACILITY_ID
FA0004966
FACILITY_NAME
CHEVRON USA (INACT)
STREET_NUMBER
45
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
12707037
CURRENT_STATUS
02
SITE_LOCATION
45 E HARDING WAY
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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r September 18, 1996 <br /> Page 6 <br /> The vacuum radius of influence was estimated to be In excess of 25 feet, for Wells V-1 <br /> - through V-5 A subsequent vacuum radius of influence analysis was performed on <br /> Well MW-4,resulting in an estimated effective radius of 112 feet -During the SVE, <br /> program,`an estimated total of approximately 12,000 pounds (1,967 gallons) of petro- <br /> leum hydrocarbons were removed (Correctri,e Action Plan, PACIFIC, November 30, <br /> 1995) System operational data including influent concentrations, flow rates, and the <br /> operating time is presented in the table included in Attachment A <br /> The calculations for deterinirung TPPH-g mass in soil and groundwater utilized soil <br /> boring and analytical data to estimate the areal extent of the hydrocarbon plume Aver- <br /> age concentrations were applied to distinct cross sectional areas in order to arrive at the . <br /> total hydrocarbon mass both prior to and after SVE treatment Figures 3 through 5 <br /> depict soil conditions beneath the site prior to operation of the SVE system (November r <br /> 1990 - November 1992) .Figures 6 through 8 depict these conditions and show soil <br /> analytical data from soil borings and wells drilled after the operation of the SVE system <br /> ti <br /> Calculations for determining the TPPH'g mass in soil and groundwater before and after <br /> the operation of the SVE system are presented as Attachment A <br /> RESIDUAL PETROLEUM HYDROCARBONS IN SOIL <br /> Currently, residual petroleum hydrocarbons in soil occur below and northeast of the <br /> former UST cluster(installed in 1984) and adjacent product island The vertical and <br /> lateral extent of petroleum hydrocarbons in soil are shown on Figures 6 through 8 <br /> These hydrocarbon-affected soils occur in what can be described as two localized verti- <br /> cal soil columns Hydrocarbon-impacted soils in these two vertical soil columns occur <br /> from a depth of approximately 15 to 50 feet bgs The horizontal extent of hydrocarbon- , <br /> affected soils within these soil columns occur pnmanly within a range of 5 to 10 feet, <br /> with occasional thin zones that extend horizontally an additional 10 feet from the soil <br /> column These soil columns occur within vadose zone soils, soils within the capillary <br /> fringe and zone of groundwater fluctuation, and currently saturated soils Figures 6 <br /> through 8 depict these conditions and show soil analytical data from soil borings and <br /> wells drilled after the operation of the SVE system ' <br /> The location of the residual hydrocarbons in soils are charactenzed by soil bonngs , <br /> located in two areas These include Soil Bonngs SB-2 and SB-12 located in the north- <br /> ern portion of the UST complex and Borings SB-3 and SB-13 located adjacent to the <br /> western product island Hydrocarbons in these two areas are well defined and appear to <br /> be isolated based on data collected from several borings as shown on the geologic cross- <br /> sections (Figures 7 and 8) <br /> The concentration of the residual hydrocarbons in soils are characterized by the presence <br /> of the relatively high molecular weight compounds TPPH-g concentrations range in <br /> i concentration from,less than 10 to 10,000 ppm Benzene with few exceptions has not <br /> been detected <br /> 3201337B\CLOSLTREI <br />
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