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ARCHIVED REPORTS_XR0010151
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PR0545688
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ARCHIVED REPORTS_XR0010151
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Last modified
5/21/2020 4:11:37 PM
Creation date
5/21/2020 10:11:26 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010151
RECORD_ID
PR0545688
PE
3528
FACILITY_ID
FA0003634
FACILITY_NAME
CANTEEN CORPORATION
STREET_NUMBER
1500
Direction
N
STREET_NAME
SHAW
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
14326008
CURRENT_STATUS
02
SITE_LOCATION
1500 N SHAW RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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technology for the impacted soil and groundwater at this site The results of the Enhanced <br /> • Bioremediation pilot test study indicated that both oxygen and nutrient augmentation are feasible <br /> treatment technologies for the impacted soil and groundwater at this site <br /> Based on the pilot test results, air sparge/soil vapor extraction was selected as the most effective <br /> treatment technology for this site A conceptual design of the treatment system, technology <br /> implementation workplan, and proposed monitoring and reporting guidelines are included in this <br /> CAP report <br /> 2.0 Assessment of the Impacts <br />' Results of the soil and groundwater sampling conducted during the assessment portion of the <br /> project indicate that the horizontal extent of the hydrocarbon impact from the UST release has <br /> been delineated The vertical extent of the hydrocarbon impact is the underlying groundwater <br /> aquifer <br /> 2.1 Contaminant Characteristics <br /> The soil stratigraphy across the site is depicted in Cross Section (Figure 3) Cross Section A-A' <br /> (Figure 4) extends from monitoring well MW-6 (north) to MW-9 (south) and includes wells <br /> screened in the shallow and deep aquifers Cross Section B-B' (Figure 5) extends from <br /> monitoring well MW-7 (southwest) to MW-1 (northeast) and includes wells screened in the <br /> shallow and deep aquifers In general, shallow subsurface soil at the site consists of interbedded <br /> units of fine-grained (silt) deposits and coarse-grained (sand) deposits Based on the soil boring <br /> logs, relatively fine-grained soil consisting of silt and clay was encountered from surface to <br /> approximately 60 feet bgs These fine-grained soils appeared to be underlain primarily by <br /> deposits consisting of clayey to silty sand and sand to a depth of approximately 116 feet bgs A <br /> stiff silt layer was encountered from about 116 to 118 feet bgs The silt layer was underlain by <br />' silty sand and sand Soil boring and well construction details are presented in Appendix A <br /> A Soil Boring Location Map presented as Figure 6 shows the location of soil borings installed at <br /> the site and summarizes the analytical results Concentrations of adsorbed-phase hydrocarbons <br /> detected in the soil were compared to the EPA Region 9 DRGs The soil samples collected from <br /> the south and southeast walls of the UST excavation at depths between 14 and 19 feet below <br /> I ground surface (bgs) exceeded the Industrial PRGs for benzene (1 5 mg/kg), toluene (520 <br /> mg/kg), and xylenes (210 mg/kg) The benzene PRG was also exceeded in borings SB-2 (46 feet <br /> bgs) and SB-13D (46 5 feet bgs) TPH-G concentrations detected in these soil samples ranged <br /> from 10 3 to 17,600 mg/kg Soil analytical data are summarized in Table 1 <br /> 2.2 Hydrogeologic Characteristics <br /> IInterpretation of the monitoring well gauging data indicates that there is a south to southwesterly <br /> hydraulic gradient across the site (Figure 7) A review of the groundwater level data at the two <br /> cluster well points (MW-3, MW-3A, MW-3D and MW-13, MW-13A, N4W-13B) indicates that <br /> the shallow aquifer appears to be at least partially isolated from the deeper aquifer Water level <br /> data from monitoring well MW-13B, screened in the deep aquifer, shows a consistently lower <br /> IEGUL,q�o <br /> 'T <br /> ® U <br /> ACES+ <br />
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