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

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6.78<br />

food chains and ultimate consumption <strong>of</strong> seafood and radiation exposures to man. Although<br />

there is some question as to the applicability <strong>of</strong> these models to the subseabed disposal<br />

option, the following summary <strong>of</strong> results using these models is presented until such time as<br />

better estimates <strong>of</strong> radiation exposures to man from subseabed disposal are available.<br />

The individual doses resulting from the consumption <strong>of</strong> surface fish, deep-ocean fish,<br />

or plankton are expected to be well below the maximum permissible levels. External indi-<br />

vidual doses(a) from contamination <strong>of</strong> coastal sediments are expected to be fractions <strong>of</strong><br />

the ICRP dose limit for both skin and whole body irradiation. The largest annual internal<br />

population doses to the whole body and bone due to the consumption <strong>of</strong> surface fish would be<br />

about 4 x 104 and 105 man-rems, respectively. The largest annual external population<br />

doses from contaminated sediments would be about 103 to 10 man-rems for both skin and<br />

whole body. These large population doses would occur during the early stages <strong>of</strong><br />

postemplacement and would decrease during the later stages.<br />

As an attempt to provide a further yardstick against which to compare the results <strong>of</strong><br />

the calculations, Table 6.1.15 gives the concentrations <strong>of</strong> nuclides predicted by the<br />

modeling, as well as the natural activity in seawater.<br />

6.1.4.6 Cost Analysis<br />

An estimate <strong>of</strong> capital, operating, and decommissiong costs for subseabed disposal has<br />

been made for both spent fuel disposal and HLW disposal (Bechtel 1979a). Both are based on<br />

penetrometer emplacement. All estimated costs are in January 1978 dollars.<br />

TABLE 6.1.15. Levels Of Natural And <strong>Waste</strong>s Radionuclides In Seawater<br />

Max Widespread Surface Water<br />

Conc. Predicted From Postulated<br />

Natural Activity In <strong>Waste</strong> Disposal Operation,<br />

Nuclide Seawater, Ci/cm 3 Ci/cm 3 (No Containment)<br />

Actinides<br />

Pb-210 (1 - 9) x 10-11 2 x 10-15<br />

Pb-210 1 x 10-10 2 x 10-15<br />

Ra-226 1 x 10-10 2 x 10-15<br />

Th-230 (0.6 - 14) x 10-13 2 x 10-1 7<br />

Th-234 1 x 10-9 1 x 10-15<br />

U-234 1 x 10-9 1 x 10-15<br />

U-238 1 x 10-9 4 x 10-15<br />

Pu-239<br />

1 x 10-12<br />

Fission Products<br />

H-3 2 x 10-10 1 x 10-12<br />

Sr-90<br />

4 x 10-10<br />

1-129 3 x 10-11 3 x 10-1 4<br />

Cs-137<br />

6 x 10-10<br />

(a) Based on world population

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