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ARCHIVED REPORTS_XR0004478
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2900 - Site Mitigation Program
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PR0541913
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ARCHIVED REPORTS_XR0004478
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Last modified
2/13/2020 5:31:19 PM
Creation date
2/13/2020 1:50:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004478
RECORD_ID
PR0541913
PE
2960
FACILITY_ID
FA0024043
FACILITY_NAME
FRONTIER TRANSPORTATION FACILITY
STREET_NUMBER
425
STREET_NAME
LARCH
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21220009
CURRENT_STATUS
01
SITE_LOCATION
425 LARCH RD
P_LOCATION
03
QC Status
Approved
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EHD - Public
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i <br />' D <br /> • 20052 d Quarter Groundwater Report <br />' Frontier Transportation, Inc. <br /> August 5, 2005 <br /> Page 6 <br />' never identified MTBE during previous sampling events The elevated dissolved MTBE <br /> concentrations are limited to the shallow monitoring wells only See Figure 13 for the recent <br /> shallow well MTBE Isoconcentration Map <br /> Beginning in March 2004, all groundwater samples collected were analyzed for v�-p` <br /> 1 oxygenates ETBE, TAME, TBA, DIPE, 1,2-DCA and EDB using EPA method 8260 No �'y 8 <br /> detectable concentrations of analyzed oxygenates were identified in June 2005 The reporting <br /> Iimit for DIPS, ETBE and TAME was 0 50 µg/L and for TBA it was 20 pg/L See Appendix B 1 J0 <br />' for laboratory analytical results <br /> 5.0) WASTE MANAGEMENT <br />' Any free product,purged groundwater, and decontamination water generated from the <br /> site dunng sampling activities will be stored in sealed 55-gallon drums for a period not to exceed <br />' 90 days Stored wastes will be profiled for hazardous constituents and characterized as Non- <br /> Hazardous, California Hazardous, or RCRA Hazardous, as appropriate Any transportation of <br /> waste will be under appropriate marufest <br /> 6.0 CONCLUSIONS AND RECOMMENDATIONS <br /> tBased on groundwater sample analysis results, the dissolved MTBE plume appears to be 0 Gam ' <br /> significantly expanding to the west as identified in MW-9 No detectable to low-level <br /> concentrations (below CDHS primary MCLs) of dissolved TPH-g and BTEX were identified in <br />' the 9 sampled monitoring wells at the site However, the id nhfific tion of elevated levels of CIIAO <br /> dissolved MTBE in MW-1, MW-3R, MW-9, and MW-174mlcates that lateral migration of <br />' MTBE is occurring beneath the site <br /> BEA recommends that specifications for soil vapor extraction and groundwater sparging <br />' and a cost-benefit analysis of alternative remediation be prepared as soon as possible based upon <br /> the significant expansion of MTBE to the west BEA further recommends that quarterly <br /> groundwater monitoring continue at the site until constant or decreasing dissolved MTBE <br />' concentrations are observed Further, migration of MTBE indicates that the source area may <br /> need to be re-excavated to prevent additional migration Groundwatcr samples will be analyzed <br /> for TPH-g using EPA method 8015m and for oxygenates and BTEX using EPA method 8260 in <br /> 1 all future monitoring episodes as directed by the PHS/EHD Should dissolved MTBE <br /> concentrations continue to be above EPA primary MCLs beneath the site, then groundwater <br />' remediation/treatment may be warranted <br /> i <br /> 1 <br /> i <br /> 1 <br />
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