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

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5.35<br />

Contaminated assemblies are first cleaned, then sealed in a canister; damaged assemblies<br />

are returned to their casks, transferred to the overpack cell, and encased in canisters and<br />

appropriately sized overpack canisters. The canisters are then transported to the<br />

canistered waste shaft and lowered into the repository. All spent fuel handling is done<br />

remotely.<br />

The spent fuel canisters are received at subsurface transfer stations where shielded<br />

transporters remotely remove the canisters from the transfer stations for delivery to an<br />

emplacement room.<br />

In addition to the thermal restrictions discussed in Section 5.3.1.1, room capacity is<br />

limited by the minimum allowable hole spacing <strong>of</strong> 1.8 m (6 ft) center to center. This is a<br />

mechanical limit that prevents weakening <strong>of</strong> the floor by holes spaced too closely together.<br />

The conceptual repositories in salt and shale emplace both PWR and BWR canisters in holes,<br />

while repositories in granite and basalt emplace PWR canisters in holes and BWR canisters<br />

in trenches. Trenches allow the relatively low heat-generating BWR canisters to be spaced<br />

more closely together (trenches are not economical for the higher heat-generating PWR can-<br />

isters). The trenches run the length <strong>of</strong> emplacement rooms and contain steel racks to main-<br />

tain the canisters in an upright position. They are backfilled after emplacement sleeves<br />

are installed.<br />

Table 5.3.3 lists the contents <strong>of</strong> the conceptual spent fuel repositories in salt,<br />

granite, shale, and basalt formations at the end <strong>of</strong> emplacement.<br />

TABLE 5.3.3. Contents <strong>of</strong> the Conceptual Spent Fuel Repositories When Full<br />

PWR BWR Total<br />

Canisters MTHM Canisters MTHM MTHM<br />

Salt 68,200 31,500 104,000 19,600 51,100<br />

Granite 162,700 75,100 246,300 46,500 121,600<br />

Shale 86,300 39,800 131,000 24,700 64,500<br />

Basalt 162,700 75,100 246,300 46,500 121,600<br />

Two separate repository design concepts were also developed for the limited quantities<br />

<strong>of</strong> spent fuel, 10,000 MTHM and 48,000 MTHM, produced in the two cases (Cases 1 and 2 in<br />

Section 3.2.2) where the nuclear industry is assumed to be severely constrained. Surface<br />

facilities are reduced in size and capacity for these reduced requirements and the mined<br />

area is reduced in proportion to the quantity <strong>of</strong> spent fuel sent to disposal.<br />

5.3.1.5 Retrievability<br />

Actions necessary to remove emplaced wastes from a geologic repository depend on the<br />

period <strong>of</strong> repository operations during which removal takes place. Initially, wastes are<br />

emplaced in holes lined with steel sleeves and sealed with removable concrete plugs. The<br />

sleeves and plugs ensure the canisters remain accessible and minimize corrosion or other<br />

damage. During this period the wastes are considered readily retrievable in that they are<br />

removable from the repository at about the same rate and with about the same effort as for

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