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1 - paducah environmental information center

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Paducah Site.<br />

(also known as an acute test) were conducted for<br />

Outfalls 015, 017, and 019, and longer term 6- or<br />

7-day toxicity tests (also known as a chronic test)<br />

were conducted for Outfall, 001. For the acute<br />

toxicity test data, the 48-hour LC so (concentration<br />

that is lethal to 50% of ,the· test organisms) was<br />

determined and Ithe acute toxicity unit (TU a) was<br />

calculated l (TU a<br />

= lOOILC so )' For the chronic<br />

toxicity tesrdata, the 25% inhibition concentration<br />

(IC25, that concentration causing a 25%<br />

reduction in fathead minnow growth<br />

Ceriodaphnia reproduction compared to a<br />

control) was determined and the chronic toxicity<br />

unit (TV c ) was calculated (TVc = 100IlC25). The<br />

TV a and TV c are compliance endpoints in the<br />

KPDES permit. For permitting purposes,<br />

KDOW has determined that Little Bayou and<br />

Bayou creeks have a low-flow zero; thus a TV ><br />

1.0 would be considered a noncompliance and<br />

an indicator of potential instream toxicity. A TV<br />

~ 1.2 is considered a significant noncompliance.<br />

During 1999, five toxicity exceedences<br />

were noted at KPDES Outfall 017. Details are<br />

provided in Sections 2 and 7· of this ASER.<br />

Terrestrial Wildlife<br />

Annual Deer Harvest<br />

found elevated in the muscle of background<br />

(Tables 8.4 and 8.5).<br />

In summary, there were no unusual<br />

findings in the 1999 deer data. When comparing<br />

Paducah Site deer data to the reference· deer data,<br />

the results were not substantially different. The<br />

data from future sampling events will continue to<br />

be assessed to identify any potential trends.<br />

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

Non-Routine Rabbit Sampling<br />

At the request of KDFWR, rabbit sampling<br />

was conducted in 1999. Muscle and fat tissue<br />

from seven rabbits collected at WKWMA were<br />

sampled for radionuclides (Section 5), PCBs,<br />

. and inorganic elements. No PCBs were detected<br />

in any samples. Copper, aluminium, iron,<br />

manganese, and zinc were detected in several<br />

muscle samples and barium was detected in one<br />

muscle sample. No regulatory standards exist by<br />

which to compare these results.<br />

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

The deer population in WKWMA is<br />

sampled annually to determine levels. of<br />

radionuclides (Section· 5), PCBs, and inorganic<br />

elements that might be attributed to past plant<br />

practices.. There were eight deer harvested from<br />

WiKWMA and two deer harvested from the<br />

BWMA to. serve as reference samples. There<br />

were no PCBs detected in the fat tissue, muscle,<br />

or liver samples of any of the ten deer harvested.<br />

Of the inorganics detected, all results for the<br />

WKWMA deer were comparable to the<br />

reference deer except for the presence of small<br />

amounts of barium, nickel; and copper in the<br />

liver of some WKWMA deer. Silver was found to<br />

be elevated in the muscle of a WKWMA deer and<br />

nickel was found elevated in another WKWMA<br />

deer. Beryllium, iron, vanadium, and zinc Were<br />

8-8<br />

Nonradiological Environmental Surveillance

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