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ARCHIVED REPORTS_XR0004471
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0541913
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ARCHIVED REPORTS_XR0004471
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Last modified
2/13/2020 5:12:49 PM
Creation date
2/13/2020 1:41:37 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004471
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 /> 20033 rd Quarter Groundwater Report <br /> . Frontier Transportation <br /> November 14, 2003 <br /> Page 4 <br /> identified in March 1998 as 42,000 µg/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 µg/L The last groundwater sample collected from MW-3 prior to abandonment detected <br /> I dissolved TPH-g as 9,750 p.g/L Dissolved TPH-g concentrations in MW-1 have attenuated from <br /> 1,800 µg/L in August 1996 and remained under 50 µg/L since January 2000 <br /> 14 <br /> Groundwater collected in October 2003 from ten groundwater monitoring wells <br /> identified dissolved TPH-g concentrations exclusively in MW-3R as 431 µg/L using EPA <br /> method 8015 modified The previous episode performed in June 2003 identified 668 µg/L as <br /> I TPH-g in MW-3R All other monitoring wells identified no detectable concentrations (c50 <br /> µg/L) of dissolved TPH-g from the third quarter 2003 sampling episode Please see Figure 4 for <br /> recent dissolved TPH-g isoconcentration map _. <br /> Historically no de ctabe�t, <br /> ntration f dissolved BTEX were identified in <br /> monitoringwells MW-5 MW-6 MWW-9 MW 10 and MW-11 since initial <br /> groundwater testing began in each well Monitoring wells -2, and MW-4 haver� „�],� <br /> remained non detect sii ce at least July of 1999 Only monitoring well MW-3, which was n rngralj 1,043 <br /> replaced by MW-3R, con ainecdissolved BTEX from every groundwater sampling episode �'�"�'v <br /> Detectable concentrations of dissolved BTEXw �e�ei�de tified exclusively in monitoring <br />' well MW-3R for the groundwater samples collected ince 03 Analytical results for MW-3R <br /> demonstrated a decrease in BTEX from 94 8 µg/L in June 2003 to 60 2 µg/L in October 2003 <br /> No detectable concentrations of dissolved BTEX were identified in the groundwater samples <br /> collected in October 2003 from the remaining thirteen monitoring wells using EPA method 8020 >7 , <br /> See Figure 5 for the recent dissolved BTEX Isoconcentration Map �d G <br /> MTBE was the only oxygenate identified in groundwater using EPA method 8260 from <br />' the third quarter 2003 sampling episode Monitoring well MW-1 identified dissolved MTBE <br /> concentrations at 8 4 µglL,a decrease from the maximum 5,800 µg/L identified in October 2002 <br />' Dissolved MTBE was also identified in June 2002 as 230 µg/L The depth to groundwater in —' x, 16 401 t' <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 1J 1 <br />' Monitoring well MW-3 identified a maximum dissolved MTBE concentration of 29,400 µg/L in p D14� <br /> March 1998"Replacement well MW-3R identified a maximum dissolved MTBE concentration <br />' as 5,500 pg/L in January 2003 Third quarter 2003 groundwater analysis from MW-3R identified <br /> dissolved MTBE at 2,300 p,g/LAThe third quarter 2003 groundwater sampling identified <br /> dissolved MTBE at 23 µg/L from MW-14 No detectable concentrations of other oxygenates <br />' were identified from groundwater sample analysis of the monitoring wells sampled using EPA <br /> V-)-V11 <br />
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