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page 2, 1112 Harding Way <br /> former dispenser island area from 20-90 feet bsg, though no analytical data has been <br /> submitted to SJC/EHD for soil samples collected deeper than 65 feet bsg. Review of soil <br /> analytical data submitted to SJC/EHD indicates that soil contamination was defined at less <br /> than 50 feet bsg near the former tank pit by boring SB-7. <br /> In the Addendum, ATC proposes screen interval depths of 20-40 feet bsg for the SVE <br /> wells and 60-62.5 feet bsg for the AS well. The proposed location of these wells is onsite <br /> between MW-2 and MW-3. A sand interval of varying thickness, located between 45-56 <br /> feet bsg, was reported on all boring logs except MW-3 and cone penetrometer boring <br /> CPT-1. The only boring logs completed at this site to a depth greater than 56 feet bsg are <br /> CPT-1, completed to 100 feet bsg, and SB-7 completed to 66 feet bsg. Both of these logs <br /> indicate the lithology at 60 feet bsg is clay, and that intervals labeled clay, stiff fine <br /> grained, clayey silt or silty clay extend from approximately 55-80 feet bsg. <br /> Groundwater contamination has been reported in all monitoring wells at this site. The <br /> highest concentrations are consistently reported in wells MW-2 and MW-5. One grab <br /> groundwater sample collected from CPT-1 at a depth of 78-80 feet bsg was non-detect for <br /> all constituents analyzed. This could indicate the vertical extent of the groundwater <br /> contamination is defined; a comprehensive site conceptual model is needed to further <br /> evaluate if this is a supportable conclusion. <br /> SJC/EHD does not approve the submitted CAP or Addendum at this time. Documented <br /> soil contamination at this site is concentrated from 10-35 feet bsg in the source area, and <br /> from 30-40 feet bsg up-to cross-gradient from the source area (MW-2, MW-5 and MW-6). <br /> Groundwater contamination exists across the site, and offsite in the up- and cross- <br /> gradient directions. SJC/EHD is concerned that air sparged into the clays at 60 feet bsg <br /> may not be effectively captured by the SVE wells screened to 40 feet bsg, which is also in <br /> an interval characterized by silts and clays that is above the sand interval at 55 feet bsg. <br /> Please proceed with preparation of a Work Plan to define the lateral extent of the <br /> groundwater contamination at this site. The Work Plan is due for submittal no later than <br /> October 20, 2006. A report of findings is due for submittal no later than 6 weeks following <br /> completion of the fieldwork, and must include a Site Conceptual Model (SCM). Include in <br /> the SCM current, detailed, scaled cross-sections, and calculations of contaminant mass <br /> remaining in both soil and groundwater at this site. <br /> If you have any questions please call Lori Duncan at (209) 468-0337. <br /> Donna Heran, REHS, Director <br /> Environmental Health Department <br /> Lori Duncan, Senior REHS Nuel C. Henderson, Jr., PG <br /> LOP/Site Mitigation Unit IV LOP/Site Mitigation Unit IV <br /> cc: James Barton, PG, CVRWQCB <br /> Jeanne Homsey, PG, ATC <br />