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d, <br /> U liy ENVIRONMENTAL HEALTH DEPARTMENT <br /> pQ <br /> SAN JOAQUIN COUNTY <br /> Donna K Heran,R E H S Unit Supervisors <br />' h Director 304 East Weber Avenue, Third Floor Carl Borgman,R E H S <br /> Al Olsen,R E H S Stockton, California 95202-2708 Mike Huggins,R E H S,R D I <br /> c �p • Program Manager Douglas W Wilson,R E H S <br /> q[i FP�`� Laurie A Cotulla,R E H S Telephone (209) 468-3420 Margaret Lagono,R E H S <br /> Program Manager Fax (209)464-0138 Robert McClelion,RE H S <br /> Mark Barcellos,R E H S <br />' PAUL SUPPLE <br /> ARCO PRODUCTS COMPANY QAN 2 U 2004 <br />' P 0 BOX 6549 <br /> MORAGA CA 94570 <br />' RE ARCO <br /> 225 Cherokee Lane <br /> Lodi, CA <br /> San Joaquin County Environmental Health Department(EHD) has reviewed Work Plan <br /> for Sod and Groundwater Assessment dated 13 January 2004, prepared by URS <br /> Corporation for the above referenced site The work plan was prepared in response to <br /> the EHD directive letter dated 17 November 2003 to investigate the 1,2-dichloroethane <br /> (1,2-DCA) detected in ground water samples collected from the three on-site ground <br /> water monitoring wells at concentrations as high as 26 micrograms per liter (µg/l) The <br /> City of Lodi has a well within 1000 feet of the site that must be protected from this <br /> contaminant <br /> 1 URS proposes to advance four soil borings to collect soil and grab groundwater samples <br /> to assess for the lateral extent of 1,2-DCA Based on the data obtained from these <br /> borings, URS will design an on-site deep groundwater monitoring well and up to four off- <br /> site shallow groundwater monitoring wells if needed URS proposes to collect soil <br /> samples at 10-foot intervals and grab groundwater samples from first ground water <br /> EHD approves the work plan with the following conditions <br /> Soil samples collected in the saturated zone shout - <br /> d be taken at 5 foot intervals to <br /> adequately characterize the hydrogeological framework controlling the <br /> distribution and migration of the dissolved contaminant and to properly set well <br /> screens, <br /> • Well screens for all proposed wells should be set in a coarse-grained interval as <br /> verified by soil samples, <br /> • Care must be taken setting the shallow wells The boring log for MWA indicates <br /> wet sand at 65 feet below surface grade (bsg), dry clayey silt at 70 feet bgs, and <br /> dry sand at 75 feet bsg This suggests the possibility that first groundwater may <br /> be perched and that MW-1 may be providing a vertical conduit to the underlying <br /> sand MW-2 and MW-3 were also terminated at 75 feet bsg, but soil samples <br /> were not collected below 70 feet bsg The sand interval immediately underlying <br /> the existing monitoring wells should also be characterized and assessed onsite <br /> and off-site, <br />' • A shallow well between the potential source area and the municipal well should <br /> be set regardless of the analytical results of the grab ground water sample to act <br />