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wells, depth to water measurements were obtained prior to pumping, prior to termination <br /> • of pumping and five days after termination of pumping at a rates commencing at 8 9 gpm <br /> and subsequently decreased to 4 gpm and 2 gpm Charts developed from these varied <br /> pump rates were created for each well and indicate that pumping MW 10 at 2 gpm <br /> effected Sanchez wells MW2, MW3, MW6A, MW6B, MW7A, MW7B, MW8A and <br /> MW8B, with Iittle or no effect on Sanchez wells MW4, MW5, MW9A, MW9B and <br /> Country Club Food and Fuel wells MWI, MW2, MW3 and MW4, see Table 3 and Charts <br /> — Appendix D From April 1, 2005 through November 29, 2005 313,921 gallons of <br /> gasoline contaminated groundwater were pumped from MW1O removing 7 gallons of <br /> gasoline range hydrocarbons This water was batched treated through the carbon/aeration <br /> system and stored in the Baker Tank and then discharged to the sanitary sewer once <br /> laboratory analysis indicated that sewer discharge parameters were met, see Table 4 and <br /> Appendix C, Sewer Discharge Reports <br /> The most recent sample event (October 20, 2005) continues to show a reduction in TPHg <br /> in the groundwater Comparing TPHg concentrations prior to over-excavation of the <br /> UST area (MWIO/R1A and RIB) show concentration reduction from 54,000 ug/L <br /> (November 2002 at RIA) to 18,000 ug/L (July 2004 at MW I O) to the most recent 8,000 <br /> ug/L (October 2005 at MW10) Similar reductions are evident in wells 6A and SA Well <br /> 6A contained 19,000 ug/L TPHg in November 2002, 16,000 ug/L in July 2004 and <br /> currently contains 5,200 ug/L (October 2005) Although MW8A was not installed prior <br /> to the over-excavation, destroyed well MWI was in close proximity MWI contained <br /> 34,000 ug/L in November 2002, MW8A contained 16,000 ug/L in July 2004 and <br /> . currently contains 2,700 ug/L (October 2005) <br /> Pumping from MW 10 has shown to capture the gasoline range hydrocarbon groundwater <br /> plume A Corrective Action Plan (CAP) should be developed that incorporates the <br /> groundwater pumping from MW 10 as the primary remediation strategy for this site <br /> TIME FRAME <br /> February, 2006 1" Quarter 2006 monitoring and sampling To be coordinated with <br /> AGE for same time DTW and sampling <br /> February 2006 Submittal of Corrective Action Plan (CAP) <br /> LIMITATIONS <br /> The discussion presented in this report is based on the following <br /> I The observations and data collected by field personnel <br /> 2 The results of laboratory analyses performed by a state certified analytical laboratory <br /> 3 Our understanding of the regulations of San Joaquin County and State of California <br /> 12 Sanchez QM 4th 2005 <br />