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

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4.81<br />

4.7.2 Environmental Impacts Related to Predisposal Operations for the<br />

Reprocessing Fuel Cycle<br />

<strong>Waste</strong> treatment operations required in the reprocessing fuel cycle were discussed in<br />

Sections 4.3.2 through 4.3.5 for fuel reprocessing plants (FRPs) and mixed-oxide fuel fabri-<br />

cation plants (MOX-FFPs). Potential waste storage requirements were discussed in Sec-<br />

tions 4.4.2 through 4.4.4. In this section we will summarize the environmental effects <strong>of</strong><br />

these waste management operations. The effects will be summarized for three different<br />

reference facilities: 1) a 2000 MTHM/yr FRP, 2) a 400 MTHM/yr MOX-FFP, and 3) a retriev-<br />

able waste storage facility (RWSF) that has capacity to store all the high-level and TRU<br />

wastes from FRPs and MOX-FFPs during the passage <strong>of</strong> 45,000 MTHM through the fuel cycle. An<br />

RWSF will be necessary only if reprocessing is initiated significantly before a repository<br />

is available.<br />

The environmental effects <strong>of</strong> waste treatment, storage, and transportation are summarized<br />

here for the example concepts defined in Sections 4.3, 4.4 and 4.5 for the reprocessing fuel<br />

cycle. The environmental effects <strong>of</strong> alternative concepts were also examined in DOE/ET-0029;<br />

only in the <strong>of</strong>f-gas case, where the results are significantly different from those <strong>of</strong> the<br />

example concepts, are the alternatives discussed here.<br />

The use <strong>of</strong> other than deep geologic repositories for disposal <strong>of</strong> the high-level waste<br />

could alter the number and type <strong>of</strong> waste management facilities required. As in the once-<br />

through cycle, additional transportation facilities such as ships and docking facilities<br />

would be required for disposal by the island, subseabed, or ice sheet disposal concepts.<br />

Use <strong>of</strong> the rock melting or well injection concepts to dispose <strong>of</strong> liquid waste would elimi-<br />

nate the need for high-level waste solidification and solidified high-level waste storage<br />

facilities but would probably require the addition <strong>of</strong> substantial liquid high-level waste<br />

storage facilities. Use <strong>of</strong> the space disposal concept would require additional chemical<br />

processing facilities and, perhaps, the addition <strong>of</strong> substantial liquid high-level waste<br />

storage facilities.<br />

4.7.2.1 Resource Commitments in Reprocessing Fuel Cycle <strong>Waste</strong> <strong>Management</strong><br />

Land use commitments for waste management facilities at the reference FRP are about<br />

19 ha compared to 60 ha for the production facilities. At the reference MOX-FFP, the waste<br />

management facilities occupy about 0.3 ha <strong>of</strong> the 6 ha required for the production<br />

facilities. An RWSF <strong>of</strong> the reference size would require 170 ha for buildings and storage<br />

areas.<br />

Water used during construction <strong>of</strong> waste management facilities amounts to about<br />

1.4 x 105 m 3 , 5.9 x 103 m 3 and 3.1 x 105 m 3 , for the FRP, MOX-FFP, and RWSF, respectively.<br />

If these quantities <strong>of</strong> water are withdrawn over the period <strong>of</strong> construction from a river such<br />

as R River, as described in the reference environment, the impact on downstream uses will<br />

be insignificant.<br />

Resources committed for construction and operation <strong>of</strong>-the waste management facilities<br />

are summarized in Table 4.7.5. Resources for construction and use <strong>of</strong> waste shipping

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