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Citelogical recknlcsInc. Page 5 <br /> ' Additional Site Characterization and <br /> 3rd Quarter Groundwater Monitoring <br /> Project No.989.2 <br /> October 31,2002 <br /> ' The detection limits for these compounds are listed in the data table, Table 2 of Appendix <br /> A. A Chain of Custody was completed.for all samples collected and tracked to ensure <br /> ' sample integrity. Laboratory data sheets are included in Appendix D. <br /> The laboratory data were submitted electronically to GeoTracker as required under AB2886 <br /> on September 6, 2002. The confirmation number for the electronic submittal is <br /> ' 5128278017. <br /> 2.3 Groundwater Investigation <br /> 2.3.1 Groundwater Sampling Procedure <br /> Del-Tech Geotechnical Support personnel mobilized to the site on three separate occasions <br /> during this quarter. On August 19, 2002, Del-Tech personal arrived on site and developed <br /> the four new monitoring wells. On August 22, 2002, Del-Tech personal arrived on site, <br /> opened the four new monitoring wells and measured the depth to water with an electrically <br /> actuated sounding tape. On September 26, 2002, Del-Tech personal arrived on site, opened <br /> ' the original six monitoring wells (MW-1 through MW-6) and measured the depth to water <br /> with an electrically actuated sounding tape. The water level reading was recorded to an <br /> accuracy of 0.01 foot. No floating product was observed during this sampling event. <br /> ' Stagnant water in the well casing was purged using a dedicated Waterra pump. The rate of <br /> well purging was monitored. The well was purged of at least three casing volumes and until <br /> the groundwater, parameters (temperature, conductivity and pH) had stabilized (Appendix <br /> C) indicating that water representative of actual aquifer conditions was entering the well. <br /> Groundwater parameter stabilization was characterized by three successive readings within <br /> 10%. Oxidation-Reduction Potential (ORP) was recorded during the sampling event. The <br /> ' ORP and groundwater parameters are included as Table 3. <br /> Before a sample was collected, the well's water level was allowed to recharge to at least <br /> ' 80% of its initial level. All water removed from the monitoring well and not used as a <br /> sample was placed in a 55 gallon DOT approved container that is properly labeled and <br /> temporarily stored on-site. <br /> A dedicated Waterra pump was used to collect each sample. Pump cleanliness was assured <br /> by collecting a bailer blank (pouring distilled water through the pump and collecting it in a <br /> VOA vial) prior to collecting the analytical sample. <br /> Extreme care was exercised while collecting samples to prevent agitation of the water <br /> contained in the Waterra pump. With minimal sample aeration, water samples were <br /> transferred from the pump into 40-m1 VOA vials preserved with hydrochloric acid. All <br /> samples were checked for headspace bubbles, labeled, inserted into foam holders and placed <br /> into a cooled ice chest for transport to the laboratory. <br /> The sampling technician wore disposable gloves while collecting all samples. <br /> A chain of custody document, listing all samples collected and their intended analyses, <br /> ' accompanied the samples from field to the laboratory, thereby providing a means to track <br /> the movement of and ensure the integrity of the samples. <br />