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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 />

Table 3.23. Analytical results exceeding screening levels from water samples collected<br />

at sump S-073A before sediment removal<br />

Location<br />

Before sediment<br />

removal<br />

After sediment<br />

removal<br />

Cadmium<br />

(µg/L)<br />

Copper<br />

(µg/L)<br />

Lead<br />

(µg/L)<br />

Nickel<br />

(µg/L)<br />

Silver<br />

(µg/L)<br />

Zinc<br />

(µg/L)<br />

Mercury<br />

(µg/L)<br />

Gross<br />

alpha<br />

(pCi/L)<br />

PCB-<br />

1254<br />

(µg/L)<br />

PCB-<br />

1260<br />

(µg/L)<br />

9.5 114 105 54.6 2.5 263 2 19.8 1.2 NA<br />

1.18 15 8.76 NA NA NA 0.189 NA 0.46 0.31<br />

Personnel from the City of <strong>Oak</strong> <strong>Ridge</strong> who are involved with the management of the sanitary sewer<br />

system were notified about the results of the dye testing effort. Because of the levels of some<br />

contaminants in the tested water, city personnel requested an estimate of the quantity of the discharge<br />

from the sump into the sanitary sewer system. In February 2009, flow monitoring equipment was placed<br />

in the sump to determine how much water the sump was discharging. Data were collected from February<br />

2009 through the first week of May 2009. It was found that the sump did not discharge during periods of<br />

dry weather. The discharge rate of the sump was found to be directly related to the amount of rainfall that<br />

occurred. The sump was found to discharge approximately 6–8 gallons of water per 0.1 inch of rainfall.<br />

The flow monitoring equipment was removed from the sump in August 2009.<br />

Removal of the solids in the bottom of the sump was initiated in March 2009. The water present in<br />

the sump at the time the solids were to be removed was pumped into 5-gallon containers using a<br />

peristaltic pump. After all free water was removed from the sump, the solids were removed using a small<br />

hand-held shovel and placed into 5-gallon waste containers. Grout was added to the solids, hydrated with<br />

water from the sump, and allowed to set. Excess water was returned to the sump. The solidified material<br />

was turned over to Waste Management personnel for disposal at Energy Solutions.<br />

After the sediments were removed, the sump was allowed to discharge for a period of approximately<br />

2 months before additional water samples were collected. This was done to allow the sump adequate time<br />

to discharge and refill several times. The water in the sump was sampled in June 2009. The levels of some<br />

of the contaminants that had exceeded screening levels before the solids were removed were found to<br />

have dropped below screening levels after the solids were removed. However, several of the contaminants<br />

remained above screening levels. The analytical results from this water sampling effort that exceeded<br />

screening levels are presented in Table 3.23.<br />

It has been determined that sump S-073A will remain in place until the demolition of the K-1006<br />

building occurs.<br />

3.5.1.7 Monitoring of Runoff from K-1070-B Burial Ground<br />

The K-1070-B Burial Ground (Fig. 3.22) covers approximately 3.7 acres and has an average depth of<br />

30 ft. This burial ground was opened in the early 1950s when the amount of equipment, materials, and<br />

parts reached a level that made warehouse storage impractical. The burial ground grew outward from the<br />

side of the hill south of Mitchell Branch. As waste was added and covered, the elevation became level<br />

with the K-1300 complex to the south. The unit is estimated to have been in operation from 1950 through<br />

the mid-1970s. Technological advances in barrier, compressor, and coolant systems resulted in plant<br />

improvement programs that generated large quantities of obsolete machinery, equipment, materials, and<br />

parts for disposal. Also, a former disposal site located near the junction of Highways 95 and 58 that was<br />

jointly used by the Y-12 National Security Complex, <strong>Oak</strong> <strong>Ridge</strong> National Laboratory (formerly X-10),<br />

and ETTP was cleaned up in the 1960s. At least ten tractor-trailer loads of materials were brought to<br />

K-1070-B for disposal. These materials included ferrules, seal parts, radioactive green/yellow<br />

compounds, stators, and contaminated valves. Operation of K-1070-B continued until the opening of the<br />

K-1070-C/D Burial Ground in the mid-1970s. The K-1070-B Old Burial Ground was closed by covering<br />

the site with soil, seeding with fescue, and planting black locust trees.<br />

East Tennessee Technology Park 3-49

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