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

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6.42<br />

Radiological Impacts. During presealing operations, waste in solution or slurry form<br />

would be introduced directly into the repository cavity. Various operations in this charging<br />

phase could lead to release <strong>of</strong> radioactive material into the environment.<br />

Under normal operating conditions, the casing in the emplacement well should prevent con-<br />

tact <strong>of</strong> radioactive waste with any aquifers that would overlie the disposal cavity. During<br />

waste charging, however, it would be possible that some radioactivity could migrate out <strong>of</strong><br />

the cavity and into the surrounding rock. This possibility would be reduced if the cavity<br />

were maintained approximately at atmospheric pressure. Under these conditions, the tendency<br />

<strong>of</strong> water under hydrostatic pressure to flow into the cavity would minimize the importance <strong>of</strong><br />

this transport mechanism. Nevertheless, it would be possible for radioactive material to<br />

reach man through such migration into the surrounding rock and onto the biosphere.<br />

Operational impacts would vary somewhat, depending on which version <strong>of</strong> the rock melting<br />

concept is considered. If liquid HLW were emplaced directly into a cavity from the proces-<br />

sing facility, there would be no impacts due to transportation <strong>of</strong> the waste. If solid waste<br />

were slurried into the repository, impacts <strong>of</strong> waste transportation from the reprocessing<br />

plant to the repository would have to be considered. However, such transportation would have<br />

no different environmental effects than would the shipping <strong>of</strong> such wastes to any other type<br />

<strong>of</strong> repository.<br />

Treatment <strong>of</strong> HLLW prior to emplacement might be required to enhance the compatibility <strong>of</strong><br />

the liquid with the rock in which the cavity would be located. This additional treatment<br />

step would increase the probability <strong>of</strong> occupational and population exposures to radiation.<br />

Handling and treatment <strong>of</strong> solidified HLW would also increase the probability <strong>of</strong> radiation ex-<br />

posure; risk analysis would take into account the details <strong>of</strong> the required handling and treat-<br />

ment procedures.<br />

A summary <strong>of</strong> potential radiological health impacts was prepared for the rock melting con-<br />

cept (Bechtel 1979a). This study projected the short-term occupational impacts for a single<br />

rock melting cavity, which are presented in Table 6.1.8. For a 5,000 MTHM/yr throughput, it<br />

is estimated that three rock melting cavities would be required and that the impacts would be<br />

linear (Bechtel 1979a). Occupational impacts prior to the waste reaching the repository,<br />

nonoccupational impacts, and impacts from abnormal conditions were also postulated in this<br />

study. For this analysis, the consequence <strong>of</strong> impacts under abnormal conditions was found to<br />

be comparable to, or slightly less than, those <strong>of</strong> the other options. This study, however, did<br />

not include any probability analysis and consequently total radiological impacts under<br />

abnormal conditions have not been quantitatively determined.<br />

Nonradiological Impacts. The underground portion <strong>of</strong> rock melt repositories would proba-<br />

bly be constructed using conventional mining and drilling techniques. Health impacts would<br />

be those typical <strong>of</strong> any analogous construction project, and would be somewhat dependent on<br />

the method chosen (whether the cavity were created by mining, underreaming, explosive spring-<br />

ing, etc.).

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