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�f <br /> WASHINGTON TE PHONE(206)285-2400 <br /> OREGON x <br /> CALIFORNIA 12 Tp FAX(206)283-8036 <br /> DAHONEVADA g 123 N TAME OIL C � o <br /> B 4 1 <br /> 66 5 TS 2737 WEST COMMODORE WAY SEATTLE,WA 98199-1233 <br /> PRODUCTS TQM PO BOX 24447 SEATTLE,WA 98124-0447 <br /> TIME TESTED E November 14, 2001 <br /> Mr Harlin Knoll <br /> San Joaquin County Public Health Services <br /> Environmental Health Division <br /> P O Box 2009 <br /> Stockton, California 95201 <br /> RE Submittal of"Quarterly Monitoring Report, July- September 2001"for <br /> Jackpot Food Mart, 14000 E Highway 88, Lockeford, California (Property No 04-049) <br /> Dear Mr Knoll, <br /> At the request of the San Joaquin County Public Health Services Environmental Health Division (PHSIEHD), <br /> an environmental Investigation was implemented at the subject site in December 1994 to evaluate the extent <br /> of hydrocarbon-impacted soils and to determine whether or not groundwater had been impacted A total of <br /> four monitoring wells were installed during this Investigation In July 1996, six additional monitoring wells were <br /> installed on and off of the subject site to assist in defining the extent of groundwater Impacts and quarterly <br /> monitoring was implemented In August and September 1999, SECOR installed a vapor extraction/air <br /> sparging system at the subject site to remediate hydrocarbon-impacted soils and groundwater System <br /> operation began December 13, 1999 <br /> Please find enclosed SECOR's "Quarterly Monitoring Report, July - September 2001" dated November 12, <br /> 2001 This document presents analytical results and field observations collected during Third Quarter 2001 <br /> groundwater sampling, and discusses the efficiency of the remediation system currently in operation <br /> Third Quarter 2001 Groundwater Sampling Results <br /> On August 20, 2001, groundwater samples were collected from MW-2 through MW-10 at the subject site by <br /> a representative of SECOR Prior to purging, the depth to water In all wells (MW-1 through MW-10) was <br /> measured to evaluate elevation, flow direction, and gradient As noted in the attached report, groundwater <br /> with a southwesterly flow direction and a gradient of 0 02 ft/ft was encountered in the wells at depths of <br /> 68 90 feet to 76 94 feet below ground surface Approximately 0 52 feet of free product was encountered in <br /> MWA The locations of the wells are identified on Figure 2 of the attached report <br /> Since the April 2001 sampling event, groundwater elevation increased in MWA by 0 91 feet and in MW-3 by <br /> 0 67 feet while it decreased in the remaining wells by 0 94 feet to 3 96 feet These changes resulted in an <br /> overall average decrease in groundwater elevation of 145 feet across the site Changes in groundwater <br /> elevation are most likely a result of seasonal variation and operation of the remediation system <br /> Groundwater gradient and flow direction remained consistent with previously collected data Table 1 in the <br /> attached report summarizes historical groundwater elevation data <br /> TPH-g and BTEX were not identified in the groundwater samples submitted from MW-2 thorough MW-10 <br /> Analyses identified 1 1 ppb MTBE in the sample collected from MW-4, however none of the other samples <br /> contained detectable concentrations of MTBE No sample was collected from MWA, as It contained free <br /> product Table 2, Table 3, and Figure 3 in the attached report summarize groundwater analytical data and <br /> . laboratory reports are included as Attachment 2 <br /> The highest concentrations of hydrocarbons appear to remain onsite in the vicinity of the pump islands (MW- <br /> 1) When compared to the April 2001 sampling event, hydrocarbon concentrations decreased in MWA (as <br /> shown by a decrease in free product thickness)while they remained relatively unchanged In the remainder of <br /> the wells Changes In hydrocarbon concentrations are most likely a result of groundwater elevation <br />