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

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<strong>Annual</strong> <strong>Site</strong> <strong>Environmental</strong> Report<br />

concentration data for iron exhibiting a statistically significant increasing trend. It is likely that these<br />

metals are sorbed onto suspended solids in the samples contributing to the exceedance of the reference<br />

standards. Other metals were detected at low concentrations in groundwater samples collected from<br />

Northwestern Discharge Area in 2009 and results are provided in the 2009 <strong>Environmental</strong> Monitoring<br />

Results (<strong>DOE</strong> 2009). Detection limits for several undetected semi-volatile organic compounds (atrazine,<br />

benzo(a)pyrene, hexachlorobenzene, and pentachlorophenol) exceeded reference standards. Diethyl<br />

phthalate was detected at a low, estimated concentration in a sample collected from well 535. Plastic well<br />

casing materials used in the construction of the well may explain the presence of the phthalate in the<br />

sample. Toluene was also detected at low, estimated concentrations in samples collected from well 535 in<br />

2009.<br />

Southern Discharge Area Exit Pathway Results<br />

Monitoring point S-01 was sampled by UT-Battelle in March 2009, but no samples were collected<br />

during the dry season sampling event (August 2009) because the monitoring point was dry. Monitoring<br />

point S-02 was sampled in March and August 2009.<br />

No radiological parameters exceeded reference standards at either monitoring point; however, low<br />

concentrations of 214 Bi and 214 Pb were detected in the sample collected from S-01, and gross alpha and<br />

beta were detected in samples collected from S-02.<br />

Concentrations reported for iron, aluminum, manganese, and lead concentrations exceeded reference<br />

standards at S-02 during 2009. It is likely that these metals are sorbed onto suspended solids in the<br />

groundwater samples collected contributing to the exceedance of the reference standards. Other metals<br />

were detected at low concentrations in groundwater samples collected from Southern Discharge Area in<br />

2009; these results can be viewed in the 2009 <strong>Environmental</strong> Monitoring Results (<strong>DOE</strong> 2009).<br />

Detection limits for several undetected semi-volatile organic compounds (atrazine, benzo(a)pyrene,<br />

hexachlorobenzene, and pentachlorophenol) exceeded reference standards. Acetone was detected in a<br />

blank sample associated with samples collected from S-02. Subsequent to collection of the 2009<br />

groundwater samples, acetone was found to be present in the deionized water used in preparing blank<br />

samples. This source of deionized water is no longer used for blank samples or for decontamination of<br />

sampling equipment.<br />

5.6.2.2 Active <strong>Site</strong>s Monitoring<br />

5.6.2.2.1 Active <strong>Site</strong>s Monitoring—HFIR<br />

Surveillance monitoring of the HFIR site detected a subsurface release of 3 H from a process waste<br />

drain in the autumn of 2000. At that time, reactor systems were shut down so that the release site could be<br />

identified and repaired. The process waste drain was found to be the source of the release and was<br />

repaired, ending the release of the 3 H to the subsurface. From 2000–2007, monitoring of HFIR-site wells<br />

and subsurface drains was conducted to determine the size and scope of the 3 H plume that was created by<br />

the release. This groundwater monitoring approach was conducted by the UT-Battelle Research Reactor<br />

Division (RRD). The main mass of the 3 H plume was observed to move from the release area to the<br />

south-southeast toward a tributary to Melton Branch and Melton Branch, itself. RRD discontinued routine<br />

monitoring in 2007 based on a history of zero detectable subsurface releases of 3 H from the process waste<br />

drain and observations of steep downward trends in 3 H concentration reductions in samples collected<br />

from monitoring sites down gradient of the release site. The expectation is that 3 H concentrations should<br />

continue to decrease with the possibility of additional precipitation-driven concentration spikes or<br />

drought-induced 3 H concentration stagnation. Although RRD has ceased monitoring the 3 H plume, 3 H<br />

monitoring at HFIR has continued under the auspices of the ORNL Radiological Monitoring Plan. Please<br />

refer to Sect. 5.5 for results of 2009 3 H monitoring at HFIR. All wells used in the RRD groundwater<br />

monitoring program are being maintained for future use as needed.<br />

<strong>Oak</strong> <strong>Ridge</strong> National Laboratory 5-79

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