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

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E.1<br />

APPENDIX E<br />

RADIOLOGICALLY RELATED HEALTH EFFECTS<br />

The radiation dose to man from ingestion, inhalation, or external exposure to specified<br />

quantities <strong>of</strong> radionuclides can be calculated with reasonable confidence. Estimates <strong>of</strong> the<br />

amounts <strong>of</strong> radioactive material that may be released from Commercial <strong>Waste</strong> <strong>Management</strong> (CWM)<br />

operations, however, and fractions reaching man via various environmental pathways are not<br />

as well defined. The relationship <strong>of</strong> dose to so-called "health effects" is even less well<br />

defined. Thus, estimates <strong>of</strong> "health effects" that may result from radiation exposure con-<br />

sequent to CWM activities can derive only from a chain <strong>of</strong> estimates <strong>of</strong> varying uncertainty.<br />

The usual practice in making these estimates is that if an error is to be made, it will be<br />

made in a way intended to overprotect the individual. As a result, if the chain <strong>of</strong> esti-<br />

mates is long, there may be considerable conservatism in the final value.<br />

Because expected releases <strong>of</strong> radioactive materials are small, and the radiation dose<br />

to any individual is small, the effects considered are long-delayed somatic and genetic<br />

effects; these will occur, if at all, in a very small fraction <strong>of</strong> the persons exposed.<br />

Except as a consequence <strong>of</strong> the unusually severe accident involving larger doses, no possi-<br />

bility exists for an acute radiation effect. The effects that must be considered are<br />

1) cancers that may result from whole body exposures, and more specifically, from<br />

radioactive materials deposited in lung, bone, and thyroid; and 2) genetic effects that are<br />

reflected in future generations because <strong>of</strong> exposure <strong>of</strong> the germ cells.<br />

Knowledge <strong>of</strong> these delayed effects <strong>of</strong> low doses <strong>of</strong> radiation is necessarily indirect.<br />

This is because their incidence is too low to be observed against the much higher background<br />

incidence <strong>of</strong> similar effects from other causes. Thus, for example, it is not possible to<br />

attribute any specific number <strong>of</strong> human lung cancers to the plutonium present in everyone's<br />

lungs from weapons-test fallout, because lung cancers are known to be caused by other mate-<br />

rials present in much more hazardous concentrations, and because lung cancers occurred<br />

before there was any plutonium. Even in controlled studies with experimental animals, one<br />

reaches a low incidence <strong>of</strong> effect that cannot be distinguished from the level <strong>of</strong> effect in<br />

unexposed animals, at exposure levels far higher than those predicted to result from CWM<br />

activities. Hence, one can only estimate a relationship between health effect and radiation<br />

dose, basing this estimate upon observations made at very much higher exposure levels, where<br />

effects have been observed in man, and carefully studied animal experiments. In this con-<br />

text the National Council on Radiation Protection and Measurements has said (NCRP 1975):<br />

"The NCRP wishes to caution governmental policy-making agencies <strong>of</strong> the unreasonableness <strong>of</strong><br />

interpreting or assuming 'upper limit' estimates <strong>of</strong> carcinogenic risks at low radiation

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