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

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4.65<br />

spent fuel to an encapsulation or storage facility. Casks for barge shipment <strong>of</strong> spent fuel<br />

would probably be similar, if not identical, to those used for rail transport.<br />

Ship transport <strong>of</strong> spent fuel could be required if some <strong>of</strong> the alternatives to geologic<br />

disposal (e.g., island, subseabed, icesheet) described in Chapter 6 <strong>of</strong> this Statement are<br />

implemented. Casks for spent fuel transport by ship would probably require adaptation or<br />

modification <strong>of</strong> existing design. The design would likely vary somewhat depending on the<br />

specific disposal concept, but could be similar to those <strong>of</strong> existing casks.<br />

4.5.2 High-Level <strong>Waste</strong> Transport<br />

High-level waste transport is required in the example reprocessing cycle. Solidified<br />

high-level waste could be shipped in specially designed casks by truck, rail, barge, or<br />

ship, much the same as for spent fuel. Ship transport would be employed only if a disposal<br />

alternative involving transport across an ocean were implemented. Barge transport would<br />

likely be employed only if both the repository and the fuel reprocessing plant were located<br />

on or very near navigable waterways. Rail transport would likely be preferred to truck<br />

transport because <strong>of</strong> the greater capacity <strong>of</strong> the rail casks.<br />

We assume in this Statement that all transport <strong>of</strong> solidified high-level waste is by<br />

rail. Casks for such use have not been constructed but some have been designed (Perona and<br />

Blomeke 1972, Peterson and Rhoads 1977). These designs provide for transport <strong>of</strong> multiple<br />

waste canisters in a single cask and incorporate many features <strong>of</strong> spent fuel cask designs.<br />

The rail cask chosen as the basis for this study is a lead-filled double-walled stain-<br />

less steel cylinder weighing about 100 MT (220,000 lb) (Peterson and Rhoads 1972). Neutron<br />

shielding is furnished by a water jacket that surrounds the cask body. The cask will dissi-<br />

pate up to 50 kW <strong>of</strong> internally generated heat. High-level waste canisters are held in an<br />

aluminum insert that fits into the cask cavity. Different inserts can accommodate nine<br />

0.30-m dia (12-in.), thirteen 0.25-m dia (10-in.), twenty 0.20-m dia, or thirty-six 0.15-m<br />

dia (6-in.) waste canisters. Each <strong>of</strong> these configurations transports the same quantity <strong>of</strong><br />

waste. Thus, regardless <strong>of</strong> the canister heat generation limit imposed by disposal con-<br />

straints, the required number <strong>of</strong> shipments does not vary.<br />

The cask is transported on a special six-axle rail car. The gross shipping weight <strong>of</strong><br />

the loaded cask and rail car is about 350 MT (330,000 lb). Casks used for ship transport,<br />

in the event this is required by the choice <strong>of</strong> a disposal alternative, would require adapta-<br />

tion or modification <strong>of</strong> existing design.<br />

4.5.3 TRU <strong>Waste</strong> Transport<br />

Transport <strong>of</strong> TRU wastes is also required in the reprocessing cycle. These wastes are<br />

considered here in two categories: 1) fuel residues, which we assume to be packaged in spe-<br />

cial canisters; and 2) other solid wastes, which we assume to be packaged in steel drums or<br />

boxes (except for a small quantity in special canisters). Only truck and rail transport are<br />

considered.

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