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CrtologualTeckxuslxc Page 2 <br /> ' 3`4 Quarter 2005 Groundwater Momtonng Report <br /> Project No 507 2 <br /> October 31,2005 <br /> 1 <br /> Since there is uncertainty regarding the soil profile at the site, due to the 5-foot sampling <br /> ' interval, GTI proposed performing several continuous core bonngs GTI developed our <br /> March 7, 2005 "Site Characterization Work Plan" that includes three continuous core borings <br /> ' to determine the presence of sand/silt layers in the core contaminant area SJC PHS/EHD <br /> issued an April 15, 2005 correspondence that requested additional information and denied <br /> approval of the work plan We submitted a May 16, 2005 work plan addendum and SJC <br /> ' PHS/EHD approved the work plan in their June 21, 2005 letter However, in a letter dated <br /> June 27, 2005, SJC PHS/EHD stated that the Regional Water Quality Control Board-Central <br /> Valley Region (RWQCB) must approve any additional infection work so the site <br /> ' characterization and remediation work is on hold pending concurrence from the RWQCB <br /> GTI's Project Geologist Mr Joseph Angulo contacted Mr James Barton of the RWQCB <br /> ' regarding their requirements for ozone/peroxide infection Mr Barton confirmed that a <br /> bench scale (laboratory) pilot study would be acceptable to determine if the proposed <br /> infection would cause deleterious effects to groundwater He directed that a work plan for <br /> ' the bench scale pilot test be submitted for his review GTI submitted our August 8, 2003 <br /> "Ozone Sparging SECOR Benchscale Test" work plan for RWQCB consideration The <br /> RWQCB responded in a September 8, 2005 letter requesting additional information GTI <br /> submitted an October 25, 2005 work plan addendum addressing the RWQCB and we are <br /> currently awaiting a response <br /> 1.0 GROUNDWATER MONITORING <br /> ' 1.1 Hydrogeology of Site <br /> ' The geology of the site is predominately clays and sandy clays with lesser amounts of inter- <br /> bedded silts and sands The average groundwater elevation was —10 51 feet below msl on <br /> August 19, 2005, which corresponds to approximately 16 feet below grade surface (bgs) <br />' This average elevation represents a decrease of 159 feet since the May 27, 2005 monitoring <br /> event Groundwater gradient for this monitoring event was 0 003 ft/ft flowing N48'E The <br /> site consistently exhibits a flat groundwater gradient <br />' The gradient direction for the August 2005 monitoring event is shown in Figure 2, and the <br /> historical groundwater directions and gradients are shown in Figure 3, Groundwater Gradient <br />' Rose Diagram The groundwater elevation data are summarized in Table 1, Appendix A <br /> Table 5 provides a summary of monitoring well construction <br /> The groundwater gradient is relatively flat and the direction of groundwater flow has varied <br /> during the course of the investigation As evident in Figure 3, groundwater exhibited a strong <br /> bifurcated flow regime in 2000, trending predominantly to the southwest or north-northeast at <br /> approximately 180-degree direction reversal Since the installation of wells MW-7 and MW- <br /> 1 <br />