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DOE/ORO/2327 Oak Ridge Reservation Annual Site Environmental ...

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<strong>Oak</strong> <strong>Ridge</strong> <strong>Reservation</strong><br />

Fig. 4.28. Locations of biological monitoring reference sites in relation to the <strong>Oak</strong><br />

<strong>Ridge</strong> Y-12 National Security Complex.<br />

4.5.9.1 Bioaccumulation Studies<br />

Mercury and PCB levels in fish from East Fork Poplar Creek (EFPC) have been historically elevated<br />

relative to fish in uncontaminated reference streams. Fish in EFPC are monitored regularly for mercury<br />

and PCBs to assess spatial and temporal trends in bioaccumulation associated with ongoing remedial<br />

activities and Y-12 Complex operations.<br />

As part of this monitoring effort, redbreast sunfish (Lepomis auritus) and rock bass (Ambloplites<br />

rupestris) are collected twice a year from five sites throughout the length of EFPC and are analyzed for<br />

tissue concentrations of mercury (twice yearly) and PCBs (annually). Mercury concentrations remained<br />

much higher during 2009 in fish from East Fork Poplar Creek than in fish from reference streams.<br />

Elevated mercury concentrations in fish from the upper reaches of EFPC indicate that the Y-12 Complex<br />

remains a continuing source of mercury to fish in the stream. Although waterborne mercury<br />

concentrations in the upper reaches of EFPC decreased substantially following the 2005 start-up of a<br />

treatment system on a mercury-contaminated spring (Fig. 4.29), mercury concentrations in fish have not<br />

yet decreased in response and were significantly higher in 2009 than in recent years. Mean concentrations<br />

of PCBs in fish at EFK 23.4 (the site where PCBs in fish are highest) continued to be much lower in 2009<br />

than peak concentrations observed in the mid 1990s (Fig. 4.30).<br />

4.5.9.2 Benthic Invertebrate Surveys<br />

Benthic macroinvertebrate communities were monitored at three sites in East Fork Poplar Creek and<br />

at two reference streams in the spring of 2009. The macroinvertebrate communities at EFK 23.4 and<br />

EFK 24.4 remained degraded as compared with reference communities, especially in the richness of<br />

pollution-sensitive taxa (i.e., EPT taxa richness; Fig. 4.31). Of note is a similar recent trend of reductions<br />

4-56 The Y-12 National Security Complex

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