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_ _M�rs. <br /> zzac <br /> xF - T- _ :,n, FORM <br /> k"v° <br /> ME <br /> a <br /> hydraulic conductivity from Freeze and Cherry, 1979, represent the medium-range of marine <br /> clay sediments. <br /> Tabla 1. King Island Resort Groundwater Elevation Data, April 15, 1391. <br /> YELL I.D. WELL ELEVATION' DEPTH TO WATER GR6UN6WATER` <br /> ELEVATION <br /> MW1 . -17.76 2.30 -20.06 <br /> MW2 -11.64 1.64 -13.28 <br /> MW3 -7.22 4.87 -12.09 <br /> MW4 -12.09 1.93 -14.02 <br /> M, 5L 2.52 -11.76------ <br /> • MSL Elevation is based on assumption that arbitrary datum is <br /> 10 feet below mean s9a level (Terminous Quad). <br /> �. Subsequent to monitoring, each well was purged by extracting appro;,imately 4 well volumes. <br /> ~ While purging,the groundwater parameters(temperature,conductivity;and pH)were monitored <br /> .�— <br /> and allowed to stabilize before water samples were collected. The sample:were transported to <br /> and analyzed by state-certified Applied Analytical Environmental Laboratories in -remont, <br /> California. <br /> 5.3 Laboratory Analysis - Soil <br /> One sample from each boring, the sample collected directly above groundwater, was submitted <br /> to state-certified Applied Analytical Environmental Laboratories for analysis. Analyses included <br /> BTEX using EPA method 8020, and TPHG and TPHD by modified EPA methods 8015. <br /> Laboratory results indicate that soil samples analyzed from monitoring wells NM 1, MW3, <br /> MW4, and MW5 contained nondetectable concentrations of BTEX, and TPHG and TPHD. <br /> Only :monitoring well MW2 contained detectable concentrations of toluene and total xylenes in <br /> concentrations of 0.014 and 0.027 mg/kg, respectively. The laboratory reports and chain-of- <br /> custody documents are included in Appendix Il. Laboratory results are summarized in Table <br /> Kinq Used Resort-387 S <br /> R061581.wp <br />