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Geosyntec <br /> consultants <br /> 3.2 RATIONALE <br /> In order to determine the data needs for this Work Plan, an analysis of the chemical and <br /> stratigraphic data was performed to develop a current understanding of the off-site <br /> subsurface area. To conduct the analysis existing information was compiled for the <br /> downgradient groundwater area (east of the site and Pacific Avenue) including boring <br /> logs, cone penetration testing logs, membrane-interface probe logs, well construction <br /> details, cross sections, laboratory data, groundwater elevation data, and aquifer <br /> parameter data. <br /> In addition to the analysis of chemical and stratigraphic data, a two-dimensional <br /> groundwater flow model prepared. The flow model was used to assess the performance <br /> of the GWETS and to provide any recommendations for system optimization. As <br /> discussed in Section 2.2.1.1, the flow model was used to adjust the extraction rates of <br /> individual wells to in an effort to achieve capture of VOCs in the A- and B-Zones <br /> downgradient of the site. Prior to these system adjustments, it is unclear if the GWETS <br /> achieved complete capture of the site impacts. Some additional investigation work is <br /> proposed in the Work Plan in response to the results of the flow model. <br /> In conjunction with the flow model, the analysis of chemical and stratigraphic data <br /> generally confirmed the hydrogeology as discussed in Section 2.1.2 with the following <br /> data gaps or qualifications: <br /> • There is a scarcity of subsurface data in the area between Pacific and Inglewood <br /> Avenues with regards to the transition between the A- and B-hydrostratigraphic <br /> units and for identifying the base of the B-Zone. As described above, an <br /> anomalous, water,bearing sand interval is found east of Pacific Avenue within <br /> the inferred depth range of the A/B-Zone. The A/B-Zone in other areas of the <br /> site has been conceived as an aquitard; however, the more permeable character <br /> of this sand interval could facilitate the continued migration of the A-Zone <br /> impacts into the B-Zone. <br /> • In general, the existing B-Zone wells are inconsistent in regards to their screen <br /> intervals. Wells classified as B-Zone are generally constructed with a 20-foot <br /> screen interval; however, the screen intervals range between 81 and 147 feet bgs <br /> (66 to 136 feet below msl). This variation in the B-Zone well screen intervals <br /> must be considered when evaluating GWETS performance and the extent of <br /> COPC impacts. <br /> Pre-Design Investigation Work Plan 11 18.05.12 <br />