' Groundwater Investigation,Monitor Well Destruction and Installation,and Interim Remediation Pucrip Test Report
<br /> Boyett Petroleum,419 S.Main SL,Manteca,CA
<br /> January 30,2004
<br /> Page 15
<br /> treated by filtration through coconut shell granulated activated carbon canisters prior to discharge to the
<br /> ' City sanitary sewer system.
<br /> .Pour water samples were collected during the pump test: two at the beginning and two at the end. !
<br /> Samples were collected from the influent port before the first carbon canister and from the discharge port
<br /> ' after the final carbon canister following on-site treatment. All groundwater sample containers were
<br /> sealed, labeled, and placed in a cooler chilled with ice and delivered under chain-of-custody procedures to
<br /> Argon for analyses. The samples were analyzed using U.S. EPA and California-approved methods.
<br /> 5.3 LABORATORY ANALYSES
<br /> The groundwater samples collected during the pump test were analyzed for BTEX and selected gasoline
<br /> ' oxygenates/additives by EPA Method 8260B, and TPH-G by Method 8015B. The selected
<br /> oxygenates/additives included MTBE, EtOH, TBA, DIPE, ETBE, TAME, 1,2-DCA, and EDB. The
<br /> analytical methods and analytical detection limits are presented in Table 7, below.
<br /> ' Table 7 ump Test Laboratory Analytical Results November 18 and 21, 2003
<br /> Constituent: Benzene Toluene Ethyl Total Benzene Xylenes TPH-i MTBE Other Oxygenates
<br /> Detection Limit: 0.5 0.5 0.5 1.0 50 0.5 0.5-5.0
<br /> Sample 1D µg/L µ€/L Ag/l µ!'/L µg/L µ/'IL "g/L*
<br /> 3761E-In-11/18/03 <0.5 <0.5 Q.5 <1.0 <50 360 0.8 TAME
<br /> 3761E-Out-11/18/03 <0.5 <0.5 <0.5 <1.0 <50 <0.5 <0,5-5.0
<br /> ' 3761B-In-11/21/03 <0.5 <0.5 <0.5 <1.0 <50 870 1.2 TAME
<br /> 3761 B-Out-11/21/03 <0.5 <0.5 <0.5 <1.0 <50 <0.5 <0.5-5.0
<br /> *=See laboratory reports in Appendix F for actual laboratory reported detection limits.
<br /> Other Oxygenates=MTBE,TBA,DI PE,ETBE,TAME,1,2-DCA,and EDB
<br /> Unit Conversions: lig/l_=micrograms per liter= parts per billion(ppb)
<br /> ' Laboratory analytical results for the groundwater sample collected from the influent port on November
<br /> 18, 2003, indicate that TPH-G, BTEX, and gasoline oxygenates/additives, with the exception of MTBE
<br /> ' and TAME, were not detected at or above the laboratory reported detection limits; MTBE and TAME
<br /> were detected at concentrations of 360 µg/L and 0.8 µg/L, respectively. Laboratory analytical results for
<br /> the groundwater sample collected from the influent port on November 21, 2003, indicate that TPH-G,
<br /> BTEX, and gasoline oxygenates/additives, with the exception of MTBE and TAME, were not detected at
<br />' or above the laboratory reported detection limits; MTBE and TAME were detected at concentrations of
<br /> 870 tig/L and 1.2 }tg/L, respectively. Laboratory analytical results indicate that petroleum hydrocarbon
<br /> constituents were not detected at or above the laboratory reported detection limits in either of the
<br />' groundwater samples collected from the discharge port. Laboratory analytical results indicate that the
<br /> treated groundwater met the requirements of the IWDP prior to discharge to the City sanitary sewer.
<br /> 5.4 DISCUSSION
<br /> Graphs in Appendix C show the response of the pumped well, MW-11, and the observation wells, MW-9 and
<br /> EW-1, to the pumping rate of 8.7 gallons per minute {gpm) used during the pump test. Water level responses
<br /> i
<br /> to the drawdown at MWA 1 were observed at both observation wells. Unfortunately, the transducer at MW-9
<br /> . malfunctioned late in the active pumping period At the end of the three-day active pumping period, the pump
<br /> was turned off and water level responses to the recovery were observed at MW-11 and EW-1 for a period of
<br />' three days.
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<br />' �� CONDOR
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