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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 />

3.5.1.6 Monitoring of K-1006 Sump<br />

3-48 East Tennessee Technology Park<br />

Fig. 3.33. PCB results at manhole 13074A.<br />

The Building K-1006 basement sump is a 30 inch diameter by 36 inch deep concrete structure. It is<br />

located in the northeast corner basement of the K-1006 laboratory building (Fig. 3.22) beneath the interior<br />

stairwell. The sump receives groundwater flow that is periodically pumped to the sanitary sewer system<br />

by a float-controlled pump. The Baseline <strong>Environmental</strong> Assessment Report (BEAR) for the K-1006<br />

Material and Chemistry Laboratory, K/EM-543/R1, states that the sump located in the northeast corner of<br />

the basement accumulates rain water from a drain in the concrete floor area adjacent to the outside door of<br />

the basement. Discharge from this sump was believed to be routed to storm drain 100. It used to also<br />

receive water from steam condensate and a sink drain in the room C 107. The sink drain has been<br />

removed from service. The sump had not previously been recorded as part of the sump registration<br />

program that was conducted in the mid 1990’s, and it had never been assigned an identification number.<br />

The sump was registered in 2008 and was designated as sump S-073A.<br />

In May 2007, sediment present in the bottom of the sump was sampled. This sampling was performed<br />

under CERCLA to determine if the sump met the requirements of the Zone 2 Record of Decision.<br />

Samples of the solids were found to exceed applicable remediation levels for the radium/thorium decay<br />

series (41.64 pCi/g), PCB-1254 (23,000 mg/kg), and U-238 (116 pCi/g). Due to these exceedances of<br />

remediation levels, the sump did not meet the applicable CERCLA requirements, and remediation of the<br />

sediments in the sump was required.<br />

In January 2009, water samples from the sump were obtained while the sediment was still in the sump<br />

to determine if any contaminants of concern were being discharged from the sump. The samples were<br />

analyzed for gross alpha, gross beta, VOCs, metals, isotopic uranium and thorium. The analytical results<br />

from this water sampling effort that exceeded screening levels are presented in Table 3.23.<br />

In February 2009, a dye test was performed to verify whether the sump discharges to the<br />

environment, and if it does, whether it discharges to the storm drain system, the sanitary sewer system, or<br />

into the soil. Several floor drains in the basement of K-1006 appeared to drain into the sump. These floor<br />

drains were also tested to verify whether or not the floor drains are connected to the sump. A drain at the<br />

foot of an external stairwell was also thought to drain into the sump, so it was also dye tested. The dye<br />

test indicated that the sump was connected to the sanitary sewer system. The floor drain at the north end<br />

of the basement was found to discharge to the sump. A floor drain located near the exit door of the<br />

basement was found to be plugged. Additionally, it was found that the drain located at the foot of the<br />

external stairs was also connected to the sump. This drain appears to be the major contributor of water to<br />

the sump.

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