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ARCHIVED REPORTS XR0009151
EnvironmentalHealth
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3500 - Local Oversight Program
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ARCHIVED REPORTS XR0009151
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Last modified
7/29/2019 11:07:07 AM
Creation date
7/29/2019 10:54:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009151
RECORD_ID
PR0544705
PE
3526
FACILITY_ID
FA0003754
FACILITY_NAME
CALIFORNIA FUELS
STREET_NUMBER
3147
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
17512003
CURRENT_STATUS
02
SITE_LOCATION
3147 S EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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23 March 2001 <br /> AGE-NC Project No 97-0301 <br /> Page 9of11 <br /> MW-7,located approximately 35 feet east of the former UST area at depths of 30 and 40 feet <br /> ' bsg TPH-g concentrations increased with depth at MW-7(Table 1,Figure 8) The lateral and <br /> vertical extent of impacted soil has not been defined northeast, east and southeast of MW-7 <br /> • Low concentrations of BTEX were detected in borings MW-5 and MW-7 in soil as deep as <br /> ' 70 feet bsg Laterally,the BTEX-impacted soil plume has not been fully defined northeast <br /> and southeast of MW-7 BTEX-impacted soil extends to 70 feet bsg,beyond which BTEX <br /> ' concentrations sharply decline <br /> • 1,2-DCA was detected in the 30-foot sample collected from boring MW-7 <br /> ' 0 Generally, the TPH-g/TPH-dBTEX plume beneath the former UST area extends to at least <br /> 40 feet bsg, however it appears the contaminants detected at depths in excess of 70 feet bsg <br /> and contaminants detected at MW-7 could have originated from another source due to the <br /> ' increasing concentrations with depth at MW-7 and due to an Intermediate interval of non <br /> detect soil samples collected at 45, 55 and 60 from MW-1 and P-1 The approximate models <br /> are shown in cross sectional views A A', B-B'and C C'in Figures 6, 7 and S, respectively <br /> ' 0 The results of the microbial enumeration and physicochemical analysis indicated that <br /> hydrocarbon-degrading microorganisms were detected as high as 25,000 CFU per gram The <br /> laboratory indicated that the physicochemical conditions at the site were well within the <br /> range necessary to support microbial growth and bioremedial activity <br /> ' Based on the guide How to Evaluate Alternative Cleanup Technologies For UST Sates <br /> (October 1994) published by the United States Environmental Protection Agency (EPA) <br /> Office of USTs, intrinsic permeability values between the magnitude of 10' and 10-$ are <br /> t generally_adequate for soli vapor extraction (SVE) technology (Exhibit ITS Intrinsic <br /> Permeability And SVE Effectiveness) with respect to gasoline-impacted sites Based on <br /> Information gained through laboratory analysis, the average permeability (hydraulic <br /> ' conductivity) at the site was between 5 x 10' cm/sec (MW-5 at 25 feet bsg) and 2 x 10' <br /> cm/sec(MW-5 at 45 feet bsg), hydraulic conductivity is converted to intrinsic permeability <br /> utilizing the conversion factor of 102 x 10' cm/sec which yields Intrinsic permeability <br /> ' values between 5 1 x 10" cm2 and 2 04 x 10-11 cm2 The laboratory analysis Indicated <br /> permeability conditions at the site should be marginal to Ineffective for SVE and IAS <br /> technology <br /> The implications from the December 2000 ground water monitoring event are as follows <br /> ' The ground water elevation at the site was within the screened Intervals of wells MW-1, <br /> MW-2, MW-3, MW-4, MW-6 and MW-7 which yield samples fully representative of <br /> ' shallow ground water conditions, ground water elevation was approximately 50 feet above <br /> the screened Interval of MW-5 and yields a sample representative of deeper water conditions <br /> Advanced GeoEnvironmental,Inc <br /> I <br />
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