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

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6.180<br />

factory performance <strong>of</strong> the island concept, while possible, is less certain because <strong>of</strong> an<br />

incomplete understanding <strong>of</strong> island hydrologic systems.<br />

Maintenance <strong>of</strong> isolation for the requisite period under ice sheet conditions appears<br />

to be sufficiently questionable as to preclude this option from further consideration on the<br />

basis <strong>of</strong> this standard <strong>of</strong> judgement. If not tethered, the packages would descend to the<br />

ice-rock interface where the waste form packages could be pulverized by ice motion, and<br />

waste subsequently transported to the ocean by water potentially present at the interface.<br />

If tethered, ice sheet erosion or sublimation (possible within a 10,000-year period given<br />

historical climatic fluctuation) could expose waste to the surface environment.<br />

The waste-rock matrix <strong>of</strong> the rock melt concept would potentially be exposed to severe<br />

hydrothermal alteration and leaching conditions late in the cooling phase when hot water may<br />

be present at the periphery <strong>of</strong> the rock-waste mass. This could result in transfer <strong>of</strong> waste<br />

to ground water. However if the surrounding geologic and hydrologic conditions were suit-<br />

able, migration <strong>of</strong> waste to the accessible environment might be limited to acceptably low<br />

levels. On the other hand, thermomechanical disruption <strong>of</strong> the surrounding geology by the<br />

rock melt process might allow rapid transfer <strong>of</strong> contaminated ground water to surface aqui-<br />

fers, especially if promoted by thermal gradients from decay heat. While there is currently<br />

insufficient evidence to eliminate rock melt from further consideration on the basis <strong>of</strong> this<br />

standard <strong>of</strong> judgement, satisfactory performance appears highly uncertain. Furthermore a<br />

method for resolving this uncertainty does not appear to be available.<br />

The host rock is the primary isolation mechanism for the shale-grout version <strong>of</strong> well<br />

injection. Assuming a suitably stable formation <strong>of</strong> adequate sorptive potential, preliminary<br />

calculations (Section 6.1.6) indicate that the likelihood <strong>of</strong> unacceptable quantities <strong>of</strong><br />

radionuclides reaching accessible ground water is small. For dilute acid injection, assum-<br />

ing the site has suitable bounding formations, it also appears that there would be a low<br />

probability <strong>of</strong> unacceptable quantities <strong>of</strong> radioisotopes reaching accessible aquifers. How-<br />

ever, prediction <strong>of</strong> acceptable long-term performance <strong>of</strong> well injection will require thorough<br />

characterization and understanding <strong>of</strong> the host formations and surrounding geology. It is<br />

highly uncertain at this time how this could be accomplished.<br />

The transmutation concept may not require repositories providing 10,000-year isolation<br />

if all long-lived isotopes are eliminated. However, the 10,000-year isolation standard is<br />

not applicable to the transmutation process per se.<br />

The space disposal concept appears to have most merit with respect to isolation. It<br />

has been calculated that a stable orbit would provide a minimum <strong>of</strong> 1 million years<br />

isolation.<br />

In conclusion, it appears that all concepts with the exception <strong>of</strong> ice sheet, rock melt,<br />

and well injection have the potential <strong>of</strong> meeting the 10,000-year standard for acceptable<br />

waste isolation.

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