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ARCHIVED REPORTS_XR0004483
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2900 - Site Mitigation Program
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PR0541913
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ARCHIVED REPORTS_XR0004483
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Last modified
2/13/2020 5:28:57 PM
Creation date
2/13/2020 1:53:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004483
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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SJGOV\sballwahn
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EHD - Public
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Report of Findings <br /> Frontier Transportation - <br /> March 12, 2004 <br /> Page 4 <br /> identified in the shallow soil from MW-15 at 10' b as 1 310 and at 15' b as 24Q <br /> lnrtP.�was g � µmg g µg/kg- S5 if <br /> MW-16 detected 132 µg/kg as MTBE at 15' bg MTBE was encountered in MW-17 at 15' bg �� <br /> and 20' bg at 101 µg/kg and 22 µg/kg MW-18 identified MTBE as 957 µg/kg at 10' bg and 45 <br /> µg/kg at 15' bg No MTBE was detected at 5' bg MTBE was identified at depth in MW-15 as <br /> 10 6 µg/kg exclusively at 35' bg, the depth of the second encountered groundwater in MW-15 <br /> In each well, the MTBE levels attenuated to non-detect or less than 22 µg/kg below 20' bg See <br /> Table 1 for Soil Sample Results and Appendix B for Laboratory Analytical Reports <br /> TPH-gas was detected at 10' bg exclusively in MW-15 and MW-18 at 1 7 mg/kg and 12 <br /> mg/kg, respectively No detectable concentrations of BTEX, lead scavengers, or other <br /> oxygenates were identified in any of theXsoil samples collected and analyzed JPl*4 Ja4 <br /> 3� ♦� <br /> Groundwater monitoring will be conducted in the next quarterly sampling event to be <br /> performed in March 2004 The groundwater samples will be analyzed for TPH-g, BTEX, and <br /> I MTBE, TBA, DIPE, ETBE, TAME, 1,2-DCA and TBA using EPA methods 8015M and 8260B <br /> as requested by the PHS/EHD Results will be presented in the 2004 First Quarter Groundwater <br /> Report <br /> 5.0) CONCLUSIONS <br /> Based on soil sample results from monitoring wells MW-15 through MW-18, it is <br /> concluded that MTBE has impacted the subsurface soil along the capillary fringe and within the <br /> saturated zone of first encountered groundwater The depth of detectable MTBE concentrationso}S <br /> coincides with the depth to groundwater beneath the site The location of monitoring wells MW- <br /> 15 through MW-18 is approximately 130 feet west from the former UST location This supports <br /> that MTBE spread laterally in the soil via the groundwater gradient The MTBE can be adsorbed <br /> by the soil and act as a continuing source of MTBE contamination to groundwater _ <br /> I <br /> f 6.0) RECOMMENDATIONS <br /> Monitoring wells MW-15, MW-16, MW-17 and MW-18 identified elevated MTBE <br /> concentrations in soil approximately 130 away from the former UST area It is recommended <br /> that the impacted soil should be excavated to prevent the elevated MTBE in soil from acting as a ` - <br /> continual source to groundwater contamination <br /> IMonitoring wells MW-15 through MW-18 will be incorporated in future groundwater <br /> monitoring episodes Further groundwater analysis will provide information as to whether <br /> further delineation on the extent of MTBE impacted groundwater beneath the site is warranted _ <br /> 0 <br />
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