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ARCHIVED REPORTS_XR0001974
Environmental Health - Public
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ARCHIVED REPORTS_XR0001974
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Last modified
1/30/2020 6:45:00 PM
Creation date
1/30/2020 2:22:19 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001974
RECORD_ID
PR0545246
PE
3528
FACILITY_ID
FA0003611
FACILITY_NAME
PARKWOODS GAS & FOOD
STREET_NUMBER
1612
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
APN
07728002
CURRENT_STATUS
02
SITE_LOCATION
1612 W HAMMER LN
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Ms Mary Meays Project 0805-109 01 <br /> August 15, 1994 <br /> Page 2 <br /> SITE GEOLOGY <br /> Based on previous soil characterization sediments underlying the site appear to consist <br /> primarily of silt with some clay and silt with fine- to medium-grained sand The <br /> interpreted subsurface conditions are shown on geologic cross-section A-A' and <br /> section B-B' (see Figures 3 and 4, respectively) The trace of the geologic cross-sections <br /> is included on Figure 2 <br /> VAPOR EXTRACTION TEST <br /> On March 3, 1992, the previous consultant conducted a soil vapor extraction test (SVET) <br /> to evaluate the feasibility of using soil vapor extraction to remediate vadose zone soil at <br /> the site Appendix A contains a copy of the previous consultant's SVET report. <br /> The previous consultant utilized the vacuum and distance measurements obtained during <br /> the SVET to estimate an effective radius of influence for the site. The previous consultant <br /> estimate that a wellhead flow rate of 80 cubic feet per minute (cfm) will result in an <br /> effective radius of influence of approximately 30 feet for one vapor extraction well <br /> • PRELIMINARY EVALUATION OF REMEDIAL ALTERNATIVES <br /> Based on the size of the site, the extent and concentrations of the hydrocarbons in soil, <br /> the minima impact to groundwater, and the type of soil present at the site, in situ <br /> bioremediation, chemical neutralization, and slurry wall containment are not technically <br /> or economically feasible remedial options The following feasible options are presented <br /> Soil Remediation <br /> Excavation Vadose soil with residual hydrocarbons occurs in the vicinity of the <br /> underground storage tanks (USTs) and extends toward the southern dispenser island <br /> Capillary fringe soil 1s affected Excavation as a remedial alternative will require removal <br /> of the USTs If this alternative is selected, soil removed by excavation cannot be treated <br /> on site due to lack of available space and site constraints, therefore, the soil must be <br /> hauled to an appropriate landfill for treatment and disposal Additionally, because <br /> petroleum hydrocarbons were detected in soil samples collected to groundwater <br /> (approximately 40 feet below surface grade) near the USTs, it is not feasible to excavate <br /> all petroleum hydrocarbons impacted due to excavation equipment limitations <br /> SAC/pj"8OW8051090 1bm-94 mam 4 <br />
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