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

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6.92<br />

Occupational casualties from the nonpolar activities are expected to occur at rates typi-<br />

cal <strong>of</strong> the industrial activities that would be involved, and to be independent <strong>of</strong> both the<br />

nuclear and polar aspects <strong>of</strong> the remainder <strong>of</strong> the system. Operations are routinely carried<br />

out with nuclear systems and in the polar regions with safety comparable to that experienced<br />

in more familar environments. In all likelihood, the required large-scale activities could<br />

also be performed safely, with the polar conditions being reflected in higher program costs<br />

rather than in decreased safety.<br />

Accidents in processing and handling the waste material could occur before the material<br />

reaches the embarkation facility. Impacts resulting from such accidents are common to virtu-<br />

ally all <strong>of</strong> the alternative disposal options. Other impacts would be virtually identical to<br />

those <strong>of</strong> the subseabed disposal option because in both cases the material would be trans-<br />

ported to a coastal location.<br />

Nonradiological health effects for activities that would occur on the ice sheet under<br />

abnormal conditions have not been studied extensively. Occupational impacts would occur, but<br />

as stated above, it is not expected that polar conditions will significantly alter the level<br />

<strong>of</strong> effects anticipated. Non-occupational effects would be even less significant, reflecting<br />

the lack <strong>of</strong> human activity on the ice sheets.<br />

Natural System Impacts<br />

Quantitative estimates <strong>of</strong> the radiological impact <strong>of</strong> ice sheet disposal on the ecosystem<br />

are not available. These impacts are expected to be small because there are very few living<br />

organisms in the polar regions, except along the coastline. Nonradiological ecological im-<br />

pacts at the disposal site are difficult to characterize because <strong>of</strong> a lack <strong>of</strong> understanding<br />

<strong>of</strong> the processes occurring in polar environments. The present understanding <strong>of</strong> impacts on the<br />

glacial ice mass or the dry barren valleys <strong>of</strong> Antarctica is limited. The effect <strong>of</strong> the heat<br />

that would be produced by the wastes on the ice or the potential geologic host media remains<br />

unclear.<br />

Air impacts would result from the combustion products <strong>of</strong> over-ice transport vehicles,<br />

supporL aircraft, and fuel consumed for heating the facilities at the various sites. At<br />

present, the effects <strong>of</strong> these products are not considered a major problem.<br />

Few, if any, ecological impacts are expected near the disposal sites because the plant<br />

and animal life are confined mostly to the coastal areas. Access routes and air traffic<br />

lanes could be made to avoid as much as possible the feeding, nesting, and mating spots <strong>of</strong><br />

the birds and animals that inhabit the coastal areas. Fuel spills, equipment emissions, and<br />

general transportation support activities could lead to some localized impacts along the<br />

transportation disposal corridors. Few, if any, other impacts on water are expected, except<br />

for a marginal increase in temperature <strong>of</strong> the water that would be used for once-through cool-<br />

ing <strong>of</strong> canisters during sea transport. The only other water uses would be for consumption by<br />

the 200 operating personnel, which would be obtained by melting the ice.

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