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CLEAxRW`*xATER <br /> C R O U P <br /> • Env:ronmentaf Services <br /> Alconox® soap bath and double rinsed with clean tap water prior to placement in each well to <br /> prevent possible water quality influence from exterior sources, and to prevent cross <br /> contamination Groundwater elevations were derived and are tied to previously established well <br /> surface elevation data (Table 1) <br /> Before sampling, each well was purged until water quality parameters had stabilized <br /> Stabilization occurred after approximately three wetted casing volumes had been removed Prior <br /> to purging, all wells were checked for the presence of light non-aqueous-phase liquids (LNAPL), <br /> none was observed to be present in any well Stabilization measurements of purged groundwater <br /> temperature, conductivity, and pH were made and recorded on Monitoring Well Data Sheets for <br /> each well Well stabilization data are included in Appendix A <br /> Following purging, each well was allowed to recharge to at least 80% of its static water level <br /> prior to sampling Groundwater samples were obtained from each well using disposable <br /> polyethylene bailers and decanted into clean laboratory supplied bottles Samples were labeled, <br /> documented on a chain-of-custody form, and placed on ice in a cooler for transport to the project <br /> laboratory Groundwater samples were analyzed by Kiff Analytical Labs, located in Davis <br /> California, a California State-certified laboratory, for concentrations of TPHg, BTEX and MTBE <br /> by EPA Method 8260B Groundwater samples collected for MNA data were delivered to <br /> CytoCulture Environmental Biotechnology Laboratories (CytoCulture) in Richmond, California <br /> All field work was conducted in accordance with Clearwater's Groundwater Monitoring and <br /> Sampling Field Procedures and Natural Attenuation Processes and Recommended Monitoring <br /> Guidelines included in this report as Appendix B <br /> ZB178C/4Q03 Monitoring Rpt 5 January 29,2004 <br />