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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 />

Analytical results for the K-31/K-33 area that<br />

exceeded screening levels in samples collected in 2009<br />

are given in Table 3.26. Analytical results from these<br />

samples were used to provide information for<br />

determining if chromium or other metals are present in<br />

storm water discharges in quantities that exceed the<br />

Tennessee Water Quality Criteria. In addition, the total<br />

amount of chromium and other metals in combined storm<br />

water and groundwater discharges to receiving waters<br />

could be determined.<br />

Chromium was detected in the discharge from storm water outfall 590 at a level of 8.1µg/L<br />

(Table 3.26). This exceeds the screening level for chromium, which is 8 µg/L. No previous analytical data<br />

is available for this outfall. Outfall 590 receives discharges from the former location of the K-861 cooling<br />

tower and associated facilities. Including the K-861 cooling tower, there were a total of five cooling<br />

towers that were constructed of either treated redwood or Douglas fir to dissipate the heat from the<br />

recirculating cooling water system to the environment. A chromate/zinc/phosphate treatment was used for<br />

corrosion control. In the 1960s, a Martreat treatment was used to control biological fouling in the cooling<br />

towers. That process reportedly produced copper fluorides, copper chromate, zinc arsenate, and zinc<br />

chromate. The cooling towers were demolished as part of the Cooling Tower Demolition Project, which<br />

was conducted in 1996–1998.<br />

Copper was detected in the discharge from storm water outfall 710 at a level of 10.2 µg/L<br />

(Table 3.26). This exceeds the screening level for copper, which is 7 µg/L. Copper has not been detected<br />

at levels above screening criteria in sampling performed in 2006 and 2007. Outfall 710 receives storm<br />

water discharges from Building K-33, a portion of Building K-31, the former location of the K-792<br />

switchyard, and the K-1065 waste storage facilities. All storm water runoff from Buildings K-31 and K-<br />

33 that enter this drainage system pass through oil skimmer K-897-N before discharging through outfall<br />

710. Buildings K-31 and K-33 are currently inactive. A decision on the final disposition of the buildings<br />

will be made in the future. The K-1065 facility remains active, but no discharges from the facility to the<br />

environment have been reported. The K-792 Electrical Switchyard transferred electrical power to the<br />

K-33 cascade operations. A series of French drains were installed underneath the gravel bed of the<br />

switchyard when it was constructed in 1954. An oil skimmer for storm water runoff was installed in 1981.<br />

All of the equipment has been removed from this switchyard, and it is no longer active.<br />

3.5.1.9 Sampling of the K-702-A Slough<br />

A portion of the Powerhouse area drains to Poplar Creek through the K-702-A slough. This flume is<br />

connected to Poplar Creek by underground piping. Discharges from the Powerhouse area into the<br />

K-702-A slough currently consist almost entirely of storm water runoff.<br />

The K-702-A slough receives storm water runoff from the K-700 Powerhouse and associated area.<br />

The Powerhouse generated and distributed electrical power for <strong>Oak</strong> <strong>Ridge</strong> Gaseous Diffusion Plant<br />

operations using fossil fuel fired steam generating facilities. Several storm water outfalls carry storm<br />

water runoff from the general Powerhouse area to the slough. The slough also receives discharges from<br />

the K-720 Fly Ash Pile, which was historically utilized for disposal of fly ash generated by the coal-fired<br />

boilers in the K-700 Powerhouse. Discharges from the K-720 Coal Ash Pile enter the slough via<br />

outfall 992.<br />

Arsenic and selenium have been detected in historical sampling events conducted at outfall 992. Also,<br />

the discharge from outfall 992 has been observed to have a very low pH on several occasions. Runoff<br />

from the K-720 Fly Ash Pile is believed to be the primary contributor of arsenic and selenium to the<br />

discharge from outfall 992. It is also believed to be the source of the low pH discharges from this outfall.<br />

In 1994, the K-720 Fly Ash Pile area was covered with soil and seeded. In 2008, the drainage channel for<br />

runoff from the K-720 area was lined with rip-rap in an effort to prevent the discharge of low-pH runoff<br />

from the ash pile. Elevated levels of arsenic or selenium have not been noted in the K-702-A slough.<br />

3-52 East Tennessee Technology Park<br />

Table 3.26. Storm water results from<br />

K-31/K-33 sampling exceeding<br />

screening levels<br />

Storm water<br />

outfall<br />

Chromium<br />

(µg/L)<br />

590 8.1<br />

Copper<br />

(µg/L)<br />

710 10.2

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