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

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5.40<br />

sealed in an appropriately sized overpack canister. RH-TRU waste in 55-gal drums is shipped<br />

to the repository by truck, arriving in shielded Type B overpacks (see Section 4.5.3.2 for<br />

Type B overpack definition). The overpacks are lifted by crane from the truck bed to<br />

shielded transfer cells for remote removal <strong>of</strong> the drums. The drums are placed three each<br />

into steel drum-pack canisters which are sealed with a welded lid. The drum-pack is trans-<br />

ported to the canistered waste shaft and lowered into the repository.<br />

CH-TRU waste arrives at the repository on pallets <strong>of</strong> twelve 55-gallon drums stacked two<br />

by three by two drums high or in steel boxes measuring 1.2 x 1.8 x 1.8 m (4 x 6 x 6 ft),<br />

roughly equivalent in size to the pallet <strong>of</strong> drums. The CH-TRU is shipped by truck in spec-<br />

ial cargo carriers (see Section 4.5) loaded with three pallets or boxes <strong>of</strong> waste. The pal-<br />

lets and boxes are unloaded from the cargo carrier using shielded forklifts, inspected for<br />

damage and repaired if necessary, transported to the CH-TRU waste shaft and lowered into the<br />

repository.<br />

<strong>Waste</strong>s are received at subsurface transfer stations that form integral structures with<br />

the shafts. Shielded transporters remotely remove the containers from the transfer sta-<br />

tions for delivery to an emplacement area.<br />

At the conceptual repositories in salt and shale formations, HLW canisters are lowered<br />

into vertical holes in the emplacement rooms in accordance with the same minimum hole spac-<br />

ing (1.8 m) described for spent fuel canisters in the once-through fuel cycle repositories<br />

and with an allowable thermal density calculated specifically for the HLW's characteristics.<br />

In these formations, RH-TRU waste is also emplaced in drilled holes; however the minimum<br />

hole spacing is increased to 2.3 m as a result <strong>of</strong> the larger-hole diameters necessary for<br />

the 0.76-m-diameter canisters.<br />

The conceptual repositories in granite and basalt formations emplace HLW in vertical<br />

holes as described for the salt and shale repositories. However, RH-TRU canisters are<br />

lowered into trenches running the length <strong>of</strong> the rooms. The canisters are held upright in a<br />

single row by storage racks that allow a minimum spacing <strong>of</strong> 1 m center-to-center.<br />

Shielded forklifts stack the CH-TRU waste pallets and boxes two high along the walls<br />

<strong>of</strong> CH-TRU waste emplacement rooms.<br />

Table 5.3.7 lists the contents based on the example treatment processes described in<br />

Section 4.3 <strong>of</strong> conceptual repositories located in salt, granite, shale, and basalt forma-<br />

tions at the end <strong>of</strong> operations. Because <strong>of</strong> the differences in thermal criteria the capaci-<br />

ties <strong>of</strong> different rock media vary. For the conceptual repositories illustrated here, the<br />

relative quantities <strong>of</strong> high-level waste and TRU wastes are different on an MTHM-equivalent<br />

basis. This is because the five-year cooling hold up for the HLW resulted in a dispropor-<br />

tionately larger quantity <strong>of</strong> TRU waste being emplaced. Subsequent repositories would fill<br />

up with more nearly equivalent amounts <strong>of</strong> HLW and TRU wastes. The capacities when equiva-<br />

lent quantities <strong>of</strong> HLW and TRU wastes are emplaced are also shown.

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