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

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Response<br />

54<br />

RADIOLOGICAL ISSUES<br />

EPA contends that the risk factors attributed to the EPA in the second paragraph on<br />

draft p. E.3 have been superseded by more recently derived numbers, and a more extensive<br />

consideration <strong>of</strong> the various risk factors that have been suggested by the EPA, and by<br />

others, could have been included. In any case, the more recent EPA numbers would not have<br />

led to different conclusions with regard to the range <strong>of</strong> values employed in the Statement,<br />

as summarized in draft Table E.2 (draft p. E.6).<br />

Draft pp. E.3 and E.5<br />

Issue<br />

EPA's dissatisfaction with the health effects estimates in the Reactor Safety Study<br />

(RSS) is documented in Reference 53, draft Appendix E. Recent literature has done nothing<br />

to dispel our belief that the use <strong>of</strong> a dose rate reduction factor is ill-advised as is the<br />

minimal plateau duration (30 years) used in the RSS.<br />

The UNSCEAR 1977 Report suggests (except for leukemia) a 50-yr expression period unless<br />

the period has been shown to be shorter or longer for a specific cancer (Reference 2, draft<br />

Appendix E, par. 12, page 363).<br />

In particular, the two major human cancers associated with radiation, lung and breast,<br />

are considered to elevate risk for the duration <strong>of</strong> lifespan following exposure (C. E. Land,<br />

and J. D. Norman, "The Latent Periods <strong>of</strong> Radiogenic Cancers Occurring Among Japanese A-Bomb<br />

Survivors," Late Biological Effects <strong>of</strong> Ionizing Radiation, 1, IAEA, Vienna, pp. 29-47,<br />

1978; V. E. Archer, E. P. Radford and 0. Axelson, "Radon Daughter Cancer in Man: Factors<br />

in Exposure-Response Relationships," Health Physics Society Annual Meeting, June 1978).<br />

The dose reduction factor in the RSS report appears to be derived from an analysis by<br />

Mays, et al. considering ten sets <strong>of</strong> animal data from nine studies. If an additional two<br />

studies (that happen to show a reverse effect) are included in the analysis, the dose reduc-<br />

tion factor becomes 1.7 + 0.20 reported by Mays, et al. As UNSCEAR 1977 points out, most<br />

<strong>of</strong> the existing animal carcinogenesis data comes from observations at doses above 50 rads<br />

and that each tumor-model system has peculiarities which prevent generalization across mul-<br />

tiple organ systems and cancers. See Reference 53 <strong>of</strong> this appendix for comments on the dose<br />

reduction factor in the RSS.<br />

As has been pointed out by Crump, et al. (K. S. Crump, D. G. Hoel, C. H. Langle, and<br />

R. Peto, "Fundamental Carcinogenic Processes and Their Implications for Low Dose Risk Asses-<br />

sment," Cancer Res., 36, pp. 2983-2979, 1976): "It is likely that the error in the accept-<br />

able dose associated with a simple linear extrapolation will be made less than those<br />

associated with species extrapolation to man from the laboratory animal data. The BEIR<br />

Report (Reference 16) recommended linear extrapolation on pragmatic grounds. The theoret-<br />

ical conclusions <strong>of</strong> the present paper are that linear extrapolation to low-dose levels is

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