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Role of the Regulatory Agencies <br /> As part of the Federal Facility Agreement for DOE/LLNL Site 300,the U.S.EPA and the State <br /> of California DTSC and RWQCB provide guidance to DOE/LLNL on the investigation and <br /> remediation of contaminants at the GSA. Specifically, the three regulatory agencies review and <br /> comment on all CERCLA compliance reports prepared by DOE/LLNL,provide applicable or rel- <br /> evant and appropriate requirements (ARARs) for the site, review and evaluate remedial technolo- <br /> gies and alternatives, participate in the selection of the final remedy, and provide oversight and <br /> enforcement of state and federal environmental regulations. In addition, the regulatory agencies <br /> monitor and review public acceptance of the proposed remedy. In doing so, the regulatory agen- <br /> cies will actively participate at the public meeting in the Crystal Room at the Tracy Inn for the GSA <br /> on April 24, 1996. <br /> Site Background <br /> The GSA is composed of a cluster of eleven DTSC,and RWQCB in June 1992. Since then, <br /> buildings that were constructed in the late 1950s all remedial investigations have been conducted <br /> to support Site 300 activities. Undetermined under the guidance of these regulatory agen- <br /> quantities of solvents containing trichloroeth- cies. To determine the extent of contamination <br /> ylene (TCE), a suspected human carcinogen, in the GSA, DOE/LLNL drilled 75 boreholes <br /> and other volatile organic compounds (VOCs) to collect soil samples. Ninety-eight ground <br /> were released to the ground as a result of past water monitor wells have been installed for <br /> activities in the craft shops,equipment fabrica- water-level measurements and water sample <br /> tion and repair facilities in the GSA and are collection. <br /> present in the soil/rock and ground water in the Geologic and hydrogeologic data were col- <br /> area. For purposes of discussion,the GSA has lected and field parameters were measured dur- <br /> been divided into two subareas: the central GSA ing the drilling and installation of monitor wells <br /> and eastern GSA, based on.differences in hy- to characterize the subsurface properties of the <br /> drogeology, contaminant source areas, and the GSA. As shown in Figure 4, the central GSA <br /> location of ground water VOC plumes. Two is underlain by a shallow water-bearing zone <br /> primary release sites were identified: 1)a former (aquifer). This shallow water-bearing zone is <br /> dry well area located in the central GSA near underlain by a thick, low-permeability layer <br /> Building 875, and 2) the debris burial trench (also referred to as an aquitard) that, where <br /> area located in the eastern GSA. Four other present, prevents downward migration of wa- <br /> release sites have also been identified in the ter to the regional aquifer in this area. In the <br /> GSA including a decommissioned drum stor- eastern GSA, the aquitard is not present, and <br /> age rack, a steam cleaning/sink area, and two the shallow water-bearing zone directly over- <br /> former dry wells. lies the regional aquifer. <br /> In 1982, DOE/LLNL discovered the con- <br /> tamination at the site and began an investiga- Extent of Soil and Ground Water <br /> tion under the guidance of the RWQCB. The Contamination <br /> Site 300 Experimental Test Facility was placed The remedial investigation determined that <br /> on the EPA National Priority List in August VOC releases in the GSA had affected ground <br /> 1990, and DOE entered into a Federal Facility <br /> Fater in both the shallow water-bearing zone <br /> Agreement with the U.S. EPA Region IX, <br /> 4 <br />