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ARCHIVED REPORTS_XR0004485
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2900 - Site Mitigation Program
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PR0541913
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ARCHIVED REPORTS_XR0004485
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Last modified
2/13/2020 5:53:29 PM
Creation date
2/13/2020 1:54:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004485
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 I <br /> I2003 4"' Quarter Groundwater Report <br /> • Frontier Transportation - <br />' February 11, 2004 <br /> Page 4 � <br /> �C <br /> includes the third quarter 2003 sampling episode Groundwater analysis for TPH-d will continue <br />' to be performed for the site <br />' Historical groundwater monitoring results have identified TPH-g concentrations above <br /> to <br /> 15000 gg/L in MW-1andfW-3 only Maximum dissolved TPH-g concentrations were <br /> identified in March 1998 as 42,000 gg/L in MW-3, which was the shallowest recorded <br />' groundwater depth in that well Since then, dissolved TPH-g concentrations attenuated to a low <br /> of 100 gg/L The Iast groundwater sample collected from MW-3 prior to abandonment detected <br /> dissolved TPH-g as 9,750 gg/L Dissolved TPH-g concentrations in MW-1 have attenuated from <br />' 1,800 gg/L in August 1996 and remained under 50 gg/L since January 2000 <br /> Groundwater collected in December 2003 from fourteen groundwater monitoring wells <br />' identified dissolved TPH-g concentrations exclusively in MW-3R as 984 gg/L using EPA <br /> method 8015 modified The previous episode performed in October 2003 identified 431 gg/L as <br /> TPH-g in MW-3R All other monitoring wells identified no detectable concentrations (<50 <br />' gg/L) of dissolved TPH-g from the fourth quarter 2003 sampling episode Please see Figure 4 <br /> for recent dissolved TPH-g isoconcentration map <br /> Historically no de tabcentri��s`gf dissolved BTEX were identified in <br /> monitoring wells MW-5, W- , MW-7, MW-8, W-9, MW-10, and MW-11_since�nitial -1 <br /> groundwater testing began in each well Monitoring wells MW- , -2, and MW-4 have hev,er 5- ��,� <br /> remained non detect since at least July of 1999 Only monitoring well MW-3, which wasp, <br /> replaced by MW-3R, contained dissolved BTEX from every groundwater sampling episode <br /> Detectable concentrations of dissolved BTEX were identified exclusively in monitoring <br /> well MW-3R for the groundwater samples collected in December 2003 Analytical results for <br />' MW-3R demonstrated an increase in BTEX from 60 2 gg/L in October 2003 to 2216 gg/L in <br /> December 2003 No detectable concentrations of dissolved BTEX were identified in the <br /> groundwater samples collected in December 2003 from the remaining thirteen monitoring wells <br />' using EPA method 8020 See Figure 5 for the recent dissolved BTEX Iso concentration Map 3tC7 <br /> ytp ETBt �' t� l� 6tiir �Arn� 1y1fU. y}' rnVK, <br /> MTBE was the only oxygenate identified in groundwater using EPA method 8260 from l a <br /> the fourth quarter 2003 sampling episode Monitoring well MW-1 identified dissolved MTBE <br /> concentrations at 75 gg/L, a decrease from the maximum 5,800 gg/L identified in October 2002 <br /> Dissolved MTBE was also identified in June 2002 as 230 gg/L The depth to groundwater in <br />' MW-1 was recorded as its lowest level (10 75') in June and October 2002, which coincides with <br /> the observance of increasing dissolved MTBE concentrations between those episodes <br /> Monitoring well MW-3 identified a maximum dissolved MTBE concentration of 29,400 gg/L in <br /> 1 1 <br />
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