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

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E.6<br />

support the RSS position (Brown 1976). The EPA, in its formal review <strong>of</strong> the RSS study, disagreed<br />

with several aspects <strong>of</strong> the RSS health effects model, including the 0.2 dose rate<br />

effectiveness factor, and concluded that the RSS central estimate <strong>of</strong> late somatic effects<br />

"may be underestimated by a factor <strong>of</strong> 2 to 10" (EPA 1976).<br />

Finally, the RSS acknowledges in its lower-bound estimate the possibility that a<br />

threshold for cancer induction may exist. While a threshold for primary radiation effects<br />

at the molecular level is considered unlikely on theoretical grounds, the mechanisms by<br />

which such effects become expressed as cancers are not understood, and available data in no<br />

way preclude the possibility <strong>of</strong> a threshold for these expressed effects. The RSS calculates<br />

its lower-bound estimate assuming a 10- or 25-rem threshold dose, either <strong>of</strong> which is larger<br />

than most doses predicted to occur to an individual from CWM activities.<br />

The most recent and most thoroughly documented estimates <strong>of</strong> cancer risk from radiation<br />

exposure are those contained in the 1977 UNSCEAR Report. These values are listed in<br />

Table E.1.1. The UNSCEAR Report cautions that these values are". . . derived essentially<br />

from mortalities induced at doses in excess <strong>of</strong> 100 rad. The value appropriate to the much<br />

lower dose levels involved in occupational exposure, and even more so in environmental expo-<br />

sures to radiation, may well be substantially less; . . ." (p. 414). Also shown in<br />

Table E.1.1 are the risk estimates adopted in the 1977 Recommendations <strong>of</strong> the International<br />

Commission on Radiological Protection (ICRP 1977), which were based primarily on the UNSCEAR<br />

Report.

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