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Management of Commercially Generated Radioactive Waste - U.S. ...

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5.83<br />

TABLE 5.5.8. 70-Year Whole-Body Dose Commitment to<br />

the Regional Population--Repository<br />

Breach by Faulting and Flooding<br />

Time <strong>of</strong> Event Man-rem<br />

Closure + 1,000 Years<br />

Spent Fuel 8.8 x 104<br />

Reprocessing waste 1.7 x 10 5<br />

Closure + 1,000,000 Years<br />

Spent Fuel 1.4 x 105(*)<br />

Reprocessing waste 2.8 x 104<br />

Closure + 1,000,000 Years<br />

Spent Fuel 7.1 x 104<br />

Reprocessing waste 1.0 x 104<br />

(*) The increase in dose between breaches at<br />

+1,000 and +100,000 years is due principally<br />

to the ingestion <strong>of</strong> 22 6 Ra from the<br />

decay chain <strong>of</strong> 2 38 pu.<br />

4 x 10- 11 /yr. The frequency that a high pressure aquifer exists with canister and surface<br />

access is 0.005 (DOE/ET-0028, Sec. 7.4.9). A total probability for release to the biosphere<br />

is 2 x 10-13 per year.<br />

Using the probability estimate <strong>of</strong> 2 x 10- 13 /yr and the largest number <strong>of</strong> health effects<br />

calculated, 140 (Table 5.5.8), the mathematical expectation <strong>of</strong> societal risk would be at most<br />

3 x 10-11/yr or 3 x 10 -7 health effects over 10,000 yr.(a)<br />

The population dose to the regional population from naturally occurring sources would<br />

amount to about 1.4 x 107 man-rem over the same time period. Even in the maximum case, that<br />

<strong>of</strong> 1.7 x 105 man-rem associated with release <strong>of</strong> radioactive material from nonsalt repositories,<br />

the doses are on the order <strong>of</strong> 1% <strong>of</strong> that from naturally occurring sources.<br />

One <strong>of</strong> the potential long-term effects <strong>of</strong> release <strong>of</strong> radionuclides to the river would<br />

include the movement <strong>of</strong> these radionuclides to the ocean, where accumulation in mollusks may<br />

occur resulting in another pathway to human exposure. It was assumed that the following<br />

dilution factors(b) were appropriate for concentrations <strong>of</strong> elements in an estuary; e.g.,<br />

concentration <strong>of</strong> cobalt nuclides in estuary water would be 0.01 <strong>of</strong> their concenrations in the<br />

river.<br />

(a) EPA commented that the calculation <strong>of</strong> probability was incorrect (see EPA Itr. comment<br />

#86; Vol. 3 App C. p 34). The EPA estimate <strong>of</strong> the probability <strong>of</strong> a faulting and water<br />

intrusion event was 4 x 10 -7 over a 10,000-year period compared to 2 x 10 - (2<br />

x 10- 13 /yr x 1 x 104 yr) used in this Statement. EPA concluded that once a fault<br />

intersected the repository that the probability <strong>of</strong> water intrusion in the long term<br />

would likely be one. DOE believes the EPA argument has merit, however using the EPA<br />

figures increases the societal risk to only 6 x 10 -5 over the 10,000 year period,<br />

which is still an insignificant societal risk.<br />

(b) Dilution factors are highly dependent on the specific river system and estuary <strong>of</strong><br />

interest. The dilution factors presented here were developed for movement <strong>of</strong> radionuclides<br />

from reactor effluent water at the Hanford Project in Eastern Washington via<br />

the Columbia River to Willapa Bay, Washington, where oysters are harvested.

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