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1 <br /> Well Installation Report <br /> X506 Pacific Avenue, Stockton California{CAo No 5-Oo7o71 _. EAl Project No 1232 <br />' A Mini Rae Photo-Ionization Detector PID calibrated against an isobut le <br /> . (PID) g y ne gas standard was <br /> used on the soil contained in the second tube from the bottom of the shoe, at each sampling <br />' interval within the borings, to determine if volatile hydrocarbon vapors were emanating directly <br /> from the soil Each sample was placed in an airtight "Ziploc" plastic bag The soil samples <br /> were allowed to sit in the bags for a minimum of five minutes and then the headspace in the <br /> bags was analyzed using the PID The results of this field-testing are recorded on the boring <br /> logs (see Appendix B) <br />' 22 Monitoring Well Construction <br /> The wells were constructed of two-inch inside diameter flush threaded Schedule 40 polyvinyl <br /> chloride well casing All casing materials were steam cleaned prior to installation The ground <br /> water monitoring wells were designed with a slotted section (0 010-inch x 1-inch slots) The <br /> annular space between the borehole wall and well casing was backfilled with grade 92 <br /> Monterey sand to about two feet above the slotted section An approximate three-foot thick <br /> layer of hydrated bentonite chips was placed on top of the sand pack and the borings grouted to <br /> the surface using a cement slurry Flush mounted traffic grates were placed on all wells <br /> Appendix D contains the specific well construction details for each well <br /> Although minor layers of silt and clay exist between 85 and 105 feet bgs, neither well MW-23 <br /> SID nor MW-24 SID contained a good 5-foot aquitard within this interval (see Appendix B) <br /> After discussing the ltthology in well MW-23 S/D with Marty Hartzell it was his opinion that <br /> two well casings should still be installed to attempt to determine if the ground water at 85 and <br /> 105 feet is in the same aquifer and if contamination is present at both levels Similar lithologic <br /> conditions were observed in well MW-24 S/D Therefore, using the same logic, two well <br /> casings were also installed in this well <br /> 23 Equipment Cleaning Protocol <br /> All augers were steam cleaned prior to drilling each boring/well The sampler was <br /> disassembled and decontaminated prior to each sampling using the following procedure <br /> • All excess soil was scraped off the sampler parts <br /> • The sampler was washed in a solution ofAlconox detergent and tap water <br />' • The sampler was rinsed with tap water <br /> 2.4 Effluent Management <br /> All effluent generated during drilling and equipment decontamination activities was sealed in <br /> labeled 55-gallon drums The drums remained on the Site pending the results of the analytical <br /> testing, at which time the effluent was transported to an approved disposal or recycling facility <br /> by Belshire Environmental Copies of the manifests documenting proper handling of the <br /> effluent are available upon request <br /> B{IAh 1212RU121 3 <br /> ,ENVIRONMENTAL AUDIT, INC <br />