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

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Oak Ridge Reservation Fig. 5.30. Flux of total mercury in the White Oak Creek watershed, November 2009. Fig. 5.31. Flux of total mercury in Bethel Valley reaches of White Oak Creek, November 2009. 5-58 Oak Ridge National Laboratory
Annual Site Environmental Report Monitoring results for 2009 indicated that mercury concentrations at all instream locations were below the Tennessee water quality criterion for recreational use, 51 ng/L (parts per trillion), with a few stream reaches showing higher mercury concentrations and/or fluxes than the rest (Fig. 5.28 and Fig. 5.30). These areas of interest included Outfall 211 and the area downstream from that outfall in White Oak Creek; a particular reach of Fifth Creek; and White Oak Creek downstream of its confluence with Fifth Creek (Fig. 5.29 and Fig. 5.31). Methylmercury values were typically less than 1% of the total mercury concentrations and fluxes monitored in the same locations. Dissolved methylmercury was only detected at a few of the monitoring locations; overall much less methylmercury than total mercury, both in dissolved and undissolved analyses, was detected. For 2010, WQPP mercury investigative efforts will focus on one or more of the areas of interest that were identified in the 2009 monitoring. A subset of the 2009 characterization-monitoring protocol will also be conducted in 2010, to maintain ongoing data on the presence of mercury in the White Oak Creek watershed. 5.5.6 Ambient Dry and Wet Weather Monitoring In 2009, the ORNL WQPP included an objective to characterize water quality at some of the same instream locations where biological communities (fish and benthic macroinvertebrates) are monitored. These locations, where both biological and water quality data were collected, are referred to in the WQPP as integration points. Monitoring sites included seven integration points within or downstream of industrialized areas and four water quality reference locations upstream of the majority of process and stormwater discharges from those industrialized areas (see Fig. 5.32). The purpose of generating a Fig. 5.32. Locations of ambient water quality monitoring integration points and reference locations at ORNL. Oak Ridge National Laboratory 5-59
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Oak Ridge Reservation Annual Site E
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Oak Ridge Reservation 3. East Tenne
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Oak Ridge Reservation 5.3.2 Clean A
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Figures Figure Page 1.1. Location o
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Oak Ridge Reservation 3.30. Results
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1. Introduction to the Oak Ridge Re
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Discharge Point Outfall 512 (Ground
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Uranium isotopes Annual Site Enviro
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Oak Ridge Reservation Source ID 7-4
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Oak Ridge Reservation 7-6 Dose Tabl
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Oak Ridge Reservation concentration
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Oak Ridge Reservation 7.1.3 Current
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Appendix A. Errata
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Appendix B. Glossary
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Oak Ridge Reservation biota — The
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Oak Ridge Reservation committed dos
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Oak Ridge Reservation hectare — A
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Oak Ridge Reservation quality facto
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Oak Ridge Reservation total dissolv
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Appendix C. Climate Overview for th
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C-8 Appendix C. Climate Overview fo
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Oak Ridge Reservation for winds fro
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Table D.1. Reference standards for
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TDEC and EPA Drinking Water Standar
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Chemical TDEC and EPA Drinking Wate
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Appendix E. National Pollutant Disc
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Appendix F. Radiation This appendix
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F.2.2 Non-ionizing Radiation Annual
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F.5.10 Dose from Consumer Products
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The ED from swimming in water conta
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Appendix G. Chemicals This appendix
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Table G.1. Chemical reference doses
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BW = body weight (70 kg), and Annua
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