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Annual Site Environmental Report for 1999<br />

99<br />

Table 5.6 Five-Year Tc Concentrations<br />

In Sediment<br />

99<br />

Tc (pCi/kg)<br />

1995 1996 1997 1998 1999<br />

Reference Locations<br />

Bayou Creek<br />

SS 20 516 100 334 810 ND<br />

little Bayou Creek<br />

SS 21 534 114 220 450 ND<br />

Massac Creek<br />

SS 28 624 174 332 210 ND<br />

Downstream Locations<br />

Bayou Creek<br />

SS 1 795 597 742 90730 ND<br />

little Bayou Creek<br />

SS 2 495 508 621 590 17850<br />

SS 27 560 4935 6042 3600 4005<br />

deer. Uranium-234 was found above detectable<br />

levels in two WKWMA deer. Uranium-235 was<br />

found above detectable levels in two WKWMA<br />

deer. Uranium-238 was found above detectable<br />

levels in one WKWMA deer. The concentrations<br />

of radionuclides detected were not significantly<br />

higher than background deer.<br />

Additional data is provided in Appendix C.<br />

Non-Routine Rabbit Sampling<br />

In deer bone, 237Np was found slightly<br />

above the detection leyel in one background<br />

deer. Strontium-90 was found above detection<br />

levels in two WKWMA deer. Thorium-230 was<br />

found above detection levels in three WKWMA<br />

deer and one background deer. Uranium-234<br />

was found above detection levels in four<br />

WKWMA deer. Uranium-235 was found above<br />

detection levels in one background deer.<br />

Uranium-238 was found above detection levels<br />

in two WKWMA deer. Although detectable<br />

levels of radionuclides were found none of the<br />

concentrations were significantly above<br />

background concentrations. In addition, the<br />

bone of deer are not consumed by humans and<br />

are not normally considered a source of human<br />

dose.<br />

In the deer liver, 237Np was found above the<br />

detection level in one WKWMAdeer. Thorium-<br />

230 was found above detection levels· i~· two<br />

WiKWMA deer. Although detectable, no<br />

significant concentrations of radionuclides were<br />

found.<br />

Table 5.7 Summary.of Radionuclldes<br />

Detected in Deer Samples In 1999<br />

Deer Sample<br />

#I Type<br />

1<br />

1<br />

I<br />

1 Dup<br />

1 Dup<br />

3<br />

2<br />

3<br />

3<br />

4<br />

5<br />

6<br />

6<br />

7<br />

7<br />

7<br />

7<br />

8<br />

8<br />

8<br />

Radionuclide<br />

WKWMADeer<br />

Bone Thorium - 230 .<br />

Bone Uranium - 234<br />

Liver Neptunium - 237<br />

Muscle Thorium - 230<br />

Muscle Uranium - 234<br />

Bone Thorium - 230<br />

Bone Uranium - 238<br />

Liver Thorium - 230<br />

Muscle Uranium - 235<br />

Muscle Uranium - 238<br />

Bone Uranium - 234<br />

Bone Uranium - 234<br />

Bone Uranium - 238<br />

Bone Strontium -90<br />

Liver Thorium - 230<br />

Muscle Thorium - 230<br />

Muscle Uranium - 234<br />

Bone Strontium -90<br />

Bone Thorium - 230<br />

Bone Uranium - 234<br />

Results<br />

(pCilg)<br />

0.29<br />

0.047<br />

0.009<br />

0.005<br />

0.012<br />

0.015<br />

0.008<br />

0.012<br />

0.006<br />

0.006<br />

0.022<br />

0.029<br />

0.012<br />

. 3.4<br />

0.017<br />

0.005<br />

0.02<br />

3.2<br />

0.03<br />

0.029<br />

In the deer muscle, which is normally<br />

considered to be edible to humans,· 231l'fh was<br />

found above detectable levels in two WKWMA<br />

9<br />

10<br />

Background Deer<br />

Bone Neptunium - 237<br />

Bone Thorium - 230<br />

Bone Uranium - 235<br />

0.013<br />

0.03<br />

0.018<br />

Radiological Environmental Surveillance<br />

5-7

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