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

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4.3 WASTE TREATMENT AND PACKAGING<br />

4.17<br />

This section addresses the treatment and packaging <strong>of</strong> high-level (including spent<br />

fuel), TRU, and gaseous wastes resulting from the once-through and the reprocessing cycles.<br />

The principal source <strong>of</strong> the information contained herein is DOE/ET-0028, Technology for Com-<br />

mercial <strong>Radioactive</strong> <strong>Waste</strong> <strong>Management</strong> (DOE 1979), which was prepared in support <strong>of</strong> this<br />

Statement.(a) The processes described here are not necessarily optimized but are represen-<br />

tative <strong>of</strong> currently available technology.<br />

The treated waste form and container each provide a barrier to release <strong>of</strong> radionuclides<br />

after disposal. The functions <strong>of</strong> the treated waste forms and containers are discussed in<br />

more detail in Section 5.1.2.<br />

4.3.1 Spent Fuel Treatment and Packaging in Once-Through Cycle<br />

In the once-through fuel cycle, the spent fuel is considered to be waste and is treated<br />

to prepare it for disposal. Treatment processes that have been examined range from simply<br />

1) packaging the intact spent fuel assemblies to 2) chopping the fuel assemblies to expose<br />

the fuel, utilizing a process called voloxidation to remove a portion <strong>of</strong> the volatile radio-<br />

nuclides, dissolving the fuel in nitric acid and finally converting the solution to a solid<br />

by calcination and vitrification.<br />

Encapsulation <strong>of</strong> intact spent fuel assemblies for geologic disposal is the example pro-<br />

cess assumed in this Statement for the once-through fuel cycle. Three other treatment<br />

methods are also described to illustrate the range <strong>of</strong> treatment alternatives available.<br />

4.3.1.1 Encapsulate Intact Assembly (Example Method)<br />

A detailed description <strong>of</strong> the example encapsulation process is contained in DOE/ET-0028<br />

(Section 5.7.3). A similar process is described in ONWI-39 (Appendix C). In both <strong>of</strong> these<br />

process concepts the intact fuel assemblies are placed in steel canisters that are then<br />

backfilled with helium and welded closed. A flow diagram for the process is shown in<br />

Figure 4.3.1.<br />

The canister and filler materials included in the studies discussed here are only a few<br />

<strong>of</strong> the potentially applicable materials. Canister materials being considered by DOE include<br />

a variety <strong>of</strong> metal alloys, ceramics, carbides, forms <strong>of</strong> carbon, glasses, and cements; poten-<br />

tial filler (stabilizer) materials include a variety <strong>of</strong> gases, castable solids, and granular<br />

(a) Additional once-through cycle concepts were discussed later in "An Assessment <strong>of</strong> LWR<br />

Spent Fuel Disposal Options," ONWI-39 (ONWI 1979); this report also contains information<br />

on a reprocessing case which is somewhat different in waste treatment philosophy than<br />

that presented in DOE/ET-0028. Other recent descriptions <strong>of</strong> reprocessing waste treatment<br />

operations are contained in "Design Integration Study, Spent LWR Fuel Recycle Complex,<br />

Conceptual Design, Case A-1, Separated Streams," DP-CFP-78-121 (SRL 1978) and<br />

"Design Integration Study, Spent LWR Fuel Recycle Complex, Conceptual Design, Coprocessing<br />

Case A-2," DP-CFP-121-79 (Harries et al. 1979). Various methods <strong>of</strong> waste treatment<br />

and packaging for both fuel cycles are also addressed in "Technical Support <strong>of</strong> Standards<br />

for High-Level <strong>Radioactive</strong> <strong>Waste</strong> <strong>Management</strong>, Volume B, Engineering Controls,"<br />

EPA 520/4-79-007B (EPA 1977).

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