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Final Release LLNL Site 300 (USDOE) <br /> remediation thus far, its aggressive treatment strategy for the future, and the continued <br /> monitoring of site contaminant plumes, ATSDR scientists have concluded that exposure to Site <br /> 300 contaminants in the future is unlikely. Using current data, and provided that no new <br /> contaminant source develops and migrates off-site,potential residential developments near Site <br /> 300 will be unaffected by contamination originating at Site 300. <br /> The Pit 6 landfill was capped in 1997 to prevent rainwater from infiltrating the landfill and <br /> leaching additional contaminants into the groundwater. Contaminated groundwater plumes from <br /> the Pit 6 OU are not predicted to migrate off-site (LLNL 2000). ATSDR scientists have <br /> concluded that in the future, residents of the CSVRA will not be exposed to contamination from <br /> the Pit 6 landfill. <br /> Soil and Sediment <br /> Background <br /> LLNL has been monitoring surface soil near LLNL Site 300 since 1971. Soil sampling is <br /> conducted at 14 locations at Site 300 as part of a continuing LLNL monitoring program designed <br /> to measure any changes in environmental levels of radioactivity (LLNL 2001). Each of these <br /> locations is situated near firing tables and other areas of potential soil contamination. Soil <br /> samples were analyzed for gamma-emitting radiation and for beryllium. Plutonium analysis was <br /> discontinued for soil samples from Site 300 because since sampling began, plutonium levels have <br /> consistently been at background levels (i.e.,levels expected from global fallout) (LLNL 2001). <br /> Soil and sediment samples are also collected and analyzed for VOCs, HE compounds,uranium, <br /> PCBs, metals, tritium,perchlorate, general minerals and nutrients as part of the CERCLA <br /> investigations. <br /> There are no perennial streams at or near Site 300; therefore, no sediment sampling locations <br /> have been established. Overland flow occurs intermittently and often at relatively high flow rates, <br /> as in a storm; therefore sediment does not accumulate. For this reason,LLNL deemed sediment <br /> sampling at Site 300 unwarranted. <br /> Contaminants of Concern <br /> Although soil contamination exists on Site 300, particularly around the firing tables in the <br /> EFA/WFA and from surface spills throughout the site (see Table 3), there has been no evidence <br /> of off-site contaminated soil. Because access to Site 300 is limited, there is no exposure of the <br /> public to contaminated soil from Site 300. There are no contaminants of concern in the off-site <br /> soil and sediment. <br /> Surface Water <br /> Background <br /> As stated, no perennial streams exist on or near Site 300. After heavy rains, surface runoff occurs <br /> through ravines,primarily Elk Ravine, and intermittent stream channels. Runoff that does not <br /> infiltrate the ground eventually discharges into Corral Hollow Creek. Corral Hollow Creek is an <br /> 17 <br />