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Mr. Maurice Benson - 3 - 1 July 2009 <br /> Defense Logistics Agency <br /> Key to the opposing views is the mobility of dieldrin under pumping conditions. DLA has relied <br /> on dieldrin concentration data from CPT-collected samples of groundwater from fine-grained <br /> materials before and after the pumping test and on assumptions that published behavioral <br /> characteristics will control the mobility-of dieldrin beneath the NWC area. As a result, DLA <br /> concludes that at least 40 groundwater extraction wells would be necessary to implement <br /> pump and treat. The State concludes that 40 wells would be excessive. The State's <br /> conclusion is based on groundwater extraction and monitoring well data collected during the <br /> 30-day pumping test performed on the upper aquifer zone beneath the NWC area. Also, the <br /> State notes that the plume behavior does not suggest that published behavior characteristics <br /> govern this plume's behavior. Specifically, dieldrin concentrations do not seem to decline as a <br /> function of distance according to a sorption isotherm. Instead, there is a sharp front where the <br /> plume just stops. This, together with evidence from the aquifer test showing the plume can be <br /> readily remobilized by pumping, justifies reconsidering the pump-and-treat alternative. <br /> Increasing the gradient by pumping at the toe of the plume may increase recovery at the <br /> leading edge of the plume. DLA continues to argue that the pump and treat remedy for <br /> dieldrin at the DDJC Tracy site is not feasible. <br /> Remediation of the NWC Area <br /> In this section, the State presents a path forward for remedy of the dieldrin plume in <br /> groundwater beneath the NWC Area. Details of this approach could be discussed during <br /> informal dispute resolution. <br /> The pump and treat alternative selected in the ROD applies to the NWC area. DLA is <br /> responsible for implementing the groundwater pump and treat alternative in the NWC area <br /> and proposing a system design in a revised Operable Unit 1 Pesticide Remedial Design <br /> document that requires an adequate number of extraction wells; the State believes that the <br /> number of wells proposed in the Draft and Draft Final FS is excessive. DLA will propose the <br /> number and placement of groundwater extraction wells and corrective action monitoring wells <br /> in the design document. Following acceptance of the design document by the State and the <br /> U.S. EPA, DLA will construct the system. <br /> DLA is responsible for operating the system until the aquifer cleanup level of 0.05 micrograms <br /> per liter(µg/L) has been met throughout the NWC area or until such time as all of the following <br /> conditions are met: <br /> 1) All feasible optimization efforts on the system, as designed and built, have been <br /> implemented such as pulsing, <br /> 2) The aquifer cleanup level for dieldrin of 0.05 µg/L has been achieved in the <br /> groundwater extraction wells, <br /> 3) Dieldrin mass removal rates in the extraction wells have decreased to asymptotically <br /> low levels, and <br /> 4) Dieldrin concentrations in the corrective action monitoring wells have not been reduced <br /> or have decreased to asymptotically low concentrations as a result of pumping <br /> groundwater extraction wells. <br />