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