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I <br /> Quarterly Monitoring Report .January 2001 <br /> Canepa s Car Wash(P-ic1hc Avenue) <br /> Page-2 <br /> gasoline (TPH-G), and methyl tertiary-butyl ether (MTBE) were present at the former location of the fuel <br /> dispenser Islands <br /> Prior to granting approval of installation of the new SVE system, the Underground Storage Tank Clean-Up <br /> Fund indicated the need for additional investigation Condor subsequently conducted the installation and <br /> sampling of two soil borings adJacentto the SVE well array The investigation Included soil vapor screening <br /> using a Simulprobe sampling device in soil vapor collection mode The results indicated high <br /> concentrations of volatile organic compounds were present in the soil vapor at the site The laboratory <br /> analytical results of the soil and groundwater samples collected during the investigation are presented in <br /> Report — Soil and Groundwater Investigatzon, dated June 12, 1998 Operation of the SVE system has <br /> continued since its initiation on March 15, 1999 <br /> Due to a directive from the Underground Storage Tank Cleanup Fund (USTCF), laboratory analyses of <br /> groundwater samples for gasoline oxygenates/additives by EPA Method 8260 were discontinued <br /> beginning with the October 1999 quarterly groundwater monitoring event The USTCF indicated that <br /> analysis by EPA Method 8260 is not warranted based on historical groundwater laboratory analytical <br /> results Commencing with the October 1999 quarterly groundwater monitoring event, labotatory analyses <br /> of groundwater samples for gasoline oxygenates/additives are limited to MTBE using EPA Method 8020 <br /> or 8021B <br /> 3 0 QUARTERLY GROUNDWATER MONITORING —JANUARY 2001 <br /> • On January 9 and 10, 2001 a Condor representative collected groundwater samples from the eight <br /> monitor wells at the site (see Figure 2, Appendix A, for well locations) The sampling order was as <br /> follows MW-1, MW-3, MW-2, MW-8, MW-7, MW-5, MWA, and MW-6 <br /> 3 1 GROUNDWATER MONITORING OBSERVATIONS AND PARAMETERS <br /> The static water level in each well was measured to the nearest 0 01-foot with a battery-operated, flat <br /> tape, water-level meter A clean, single-use, polypiopylene, disposable bailei was lowered into each well <br /> to check for floating product, petroleum odors, and sheen Floating product was not obseived in any of <br /> the monitor wells dtriirig the groundwater sampling Sheen was noted in the samples from MW-2 and <br /> MW-3 The surface of the groundwater table was above the top of the well screens, however Olfactory <br /> obscivations wet <br /> Stiong petroleum hydrocatbon odors detected in the gioundwater samples collected from MW-1, <br /> MW-2, and MW-3 <br /> • A moderate petroleum hydrocarbon odoi detected in the gioundwater sample collected from MW-4 <br /> • A slight petroleum hydrocarbon odor detected in the groundwater sample collected from MW-7 <br /> + Petroleum hydrocarbon odors were not noted in any of the other groundwater samples <br /> All of the monitor wells were purged with Redr-Flow submersible purnps which were decontaminated <br /> P1101 tU LEW APPIVY1111dtely thlCr, Well CaJlllg VOILIniej of Water weic purged IAoi t each will (SCC ilii <br /> Gioundwatet Monitoting Field Forms in Appendix B) The purged water fionn each well was d]SLlnaiged <br /> to the washwatet mixing pit <br /> 3 2 GROUNDWATER SAMPLING <br /> • The gioundwater simples were collected by filling two 40-milliliter glass vials with groundwatet directly <br /> Ifiom the pump discharge tubing at a reduced tate The sample containers were labeled, placed in a cooler <br /> *1k N&W_ <br /> %.J* CONDOR <br />