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. 2315 El Dorado, Stockton <br /> Page 2 <br /> The two sets of monitoring wells proposed furthest from the site on Hampton and Adam Street <br /> MW-9,MW-109, MW-209, and MW-11,MW-111,MW-2110,respectively,are not approved These <br /> three proposed wells are located at 140 feet, 310 feet, and 280 feet from MW-3,which is the well <br /> with the historically highest levels of contamination EHD does not believe that sentinel wells at <br /> these distances are necessary at this time given the information currently available <br /> I <br /> The inferred groundwater flow direction has been consistently to the east EHD approves the <br /> proposed location for the installation of MW-10,MW-110,and MW-210 duster east of the site, and j <br /> the locations for the installation of MW-7,MW-107,MW-207 cluster north of the site, and MW-12, <br /> MW-112,MW-212 cluster south of the site Instead of installing these 9 monitoring wells in 9 <br /> separate borings in 3 locations,EHD strongly recommends that you consider installing 3 multi- <br /> chambered wells (MCW)instead The casing of an MCW is capable of housing up to 7 different <br /> discrete screen sections of varying lengths The number of wells needed could be reduced by <br /> incorporating three screen sections equivalent to the three proposed monitoring wells per MCW <br /> Since the screen sections of a MCW are typically built on site,EHD also recommends obtaining a <br /> continuous core from the boring in order to provide the exact geological information for discrete <br /> screen section construction Submit a brief work plan addendum reducing the above-discussed 9 <br /> monitoring wells to 3 MCWs if you agree to these recommendations <br /> EHD requires the following conditions be met <br /> 1) EPA Method 8260 must be used to analyze groundwater samples from all new wells <br /> for 5 oxygenates, 1,2-DCA,EDB, and ethanol <br /> 2) Collect additional VOAs of samples from all impacted monitoring wells Effort <br /> must be made to lower the detection limits Previous detection limits of analysers <br /> for M7IBE and other oxygenates were often set at level as high as 250, 500, even <br /> 5,000 µg/l Primary Maximum Contaminant Level(MCL) for MTBE in drinking <br /> water established by California Department of Health Services is 13 }ig/l,and the <br /> Secondary MCL is 5 µg/l <br /> 3) The geological / hydrological model should be refined with the new acquired data <br /> 4) Implement approved portion of the work plan by November 17, 2002 Submit a <br /> report of findings to EHD by January 17, 2003 <br /> 5) EHD strongly recommends that use of hollow stem auger to complete the <br /> installation of monitoring wells and collect soil samples be attempted before going <br /> to mud rotary <br /> Portions of the work plan not approved may be implemented at a later time if justified based on <br /> concentrations detected or migration of the contamination A work plan addendum stating reasons <br /> and data sufficient to approve and implement these portions of the work plan may be submitted to <br /> EHD at such time <br /> Donna Heran,REHS,Director <br /> Environmental Health Department <br /> '_1C.P. W'' <br /> Jeffrey ong, Senior REHS Nuel C Henderson,Jr,RG <br /> LOP/Site Mitigation Unit IV LOP/ Site Mitigation Unit IV <br /> Cc RWQCB, Central Valley Region—Marty Hartzell <br /> Cc Geological Technics,Inc -Raynold I Kablanow <br />