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Page 5 <br /> January 30, 1992 <br /> Job No 400511-SA <br /> of 99 feet with 30 feet of screen The construction details of the new wells are summarized in Table A. <br />' The locations of all wells are shown on the Site Plan Showing Lines of Cross Sections, Figure 2 <br />' 4.1 Borehole Advancement and Soil Sampling <br /> The groundwater monitoring and vapor extraction wells were drilled on September 23 through <br /> October 16, 1991 by Pierson Drilling of Modesto, California under the supervision of a DERS field <br /> geologist The boreholes were drilled using 8-inch O D hollow-stem augers All bits, drill rods, and <br /> augers were steam-cleaned prior to use Soil samples were collected from the borings using a 15-foot <br /> x 2 5-inch I D split-barrel sampler The split-barrel was advanced into the undisturbed soil beyond the <br />' tip of the auger to collect soil samples The sampling of the boreholes was conducted at 5-foot intervals <br /> starting with a sample collected at 5 to 6 5-feet below the ground surface Prior to each sampling, the <br /> samplers were thoroughly washed and rinsed to avoid cross-contaminating the samples The soil <br /> samples collected from the boreholes were selected for analysis based on headspace Organic Vapor <br /> Meter (OVM) readings as described in Appendix A OVM values are presented on the well logs The <br /> boreholes were logged and all soil samples were visually classified (ASTM D-2487-85) The well logs <br /> are attached m Appendix B Soil cuttings from the borings were placed on visqueen, covered with <br /> t r visqueen, and stored on-site inside a fenced enclosure for security Soil samples from each borehole <br /> were submitted to the State of California-licensed laboratory, Trace Analysis Laboratory, Inc <br /> (Hayward), for total petroleum hydrocarbons as gasoline (TPHg) analysis by the DHS method, and <br />' benzene, toluene, xylenes, and ethylbenzene (BTXE) by EPA Method 8020 Routine chain-of-custody <br /> procedures were employed <br /> 4.2 Monitoring Well Installation <br />' The four monitoring wells, MW-27, MW-28, MW-29, and MW-30 were constructed with threaded aded flush <br />' joint 2-inch diameter, schedule 40 PVC screen and riser pipe(see Well Logs,Appendix B) A summary <br /> of the well construction details for all the new wells at the site is presented in Table A The wells were <br /> finished with traffic boxes set in a 2-foot diameter circular concrete pad The traffic boxes were <br />' typically set about an inch above the existing ground surface to help divert surface water away from the <br /> well Each well is equipped with a locking, watertight, expanding cap The new monitoring wells were <br /> developed by hand bailing and surging until the groundwater contained minor particulate turbidity The <br /> water extracted during well development was contained in drums and stored on-site inside the fence <br /> for later recycling Based on laboratory results, noncontamirnated water will be disposed on-site or by <br /> discharge permit and contaminated water will be recycled at a licensed facility <br /> 4005111 Rev 1 c3' Du Pont Environmental Remediation Services <br /> Pnnted on Re tied Pa Per <br />