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

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3.28<br />

nuclides radium-226 ( 226 Ra) and radon-222 ( 222 Rn) as well as 31 other radionuclides.<br />

Other radionuclides decay directly to stable nuclides. The most significant <strong>of</strong> the primo-<br />

radial radionuclides in terms <strong>of</strong> dose is potassium-40 ( 4 0 K). Aside from a small contribu-<br />

tion to dose by rubidium-87 ( 87 Rb), the remainder <strong>of</strong> the primordial radionuclides, including<br />

plutonium-244 (244Pu), occur in extremely small amounts and make no significant contribution<br />

to dose. Doses resulting from these primordial radionuclides are discussed below.<br />

External Gamma Radiation. The significant contributors to dose to people from outside<br />

<strong>of</strong> their bodies are 40K and the decay products <strong>of</strong> the 238U and 23 2 Th series. The principal<br />

determinant <strong>of</strong> outdoor terrestrial radiation at a given location is the soil concentration<br />

<strong>of</strong> natural radionuclides. In addition to soil composition, the radiation outdoors varies<br />

depending on the moisture content <strong>of</strong> the soil, the presence and amount <strong>of</strong> snow cover, and<br />

on the radionuclide concentration in the atmosphere which itself is quite variable.<br />

Indoors, the level <strong>of</strong> radiation is modified by the degree <strong>of</strong> shielding provided by the<br />

building materials against the outdoor radiation, and the amount <strong>of</strong> radiation originating<br />

from radionuclides in the building materials. Variations in outdoor radiation will be par-<br />

tially reflected indoors and, in addition, the contribution from radon decay products will<br />

depend on the room air ventilation rate. Each <strong>of</strong> these factors can play an important role<br />

in determining the exposure received by the population.<br />

The overall population-weighted dose rate in the United States from external terres-<br />

trial radiation is estimated to be 28 mrem/yr. Moreover, variability in external terres-<br />

trial radiation is larger than that for other natural sources <strong>of</strong> human exposure. This<br />

variation in dose rate is characterized by nominal external terrestrial dose rates to the<br />

whole body <strong>of</strong> 15, 30, and 55 mrem/yr for the Atlantic and Gulf Coastal Plains, for the<br />

majority <strong>of</strong> the United States, and for an undetermined area along the Rocky Mountains,<br />

respectively.<br />

Internally Deposited Radionuclides. While all natural radionuclides may add to inter-<br />

nal (inside the body) radiation doses, only a few are found to be significant contributors.<br />

These include 3 H, 14C, 40 K, and 226 Ra and 228 Ra and their decay products. Within the United<br />

States, all <strong>of</strong> these are relatively uniformly distributed so that their levels in foods and<br />

water do not vary appreciably with geographic location. In the United States widespread<br />

food processing and widespread transportation <strong>of</strong> foods and people have an additional<br />

"averaging" effect on radionuclide contents <strong>of</strong> diets throughout all geographic areas.<br />

The'average total internal whole-body dose rate <strong>of</strong> about 22 mrem/yr is dominated by<br />

about 20 mrem/yr from 40K.(a) Dose rates to specific organs from internally deposited<br />

radionuclides are about 30 mrem/yr to the gonads and other s<strong>of</strong>t tissues, 60 mrem/yr to bone<br />

(a) Potassium is an essential element in the body and is physiologically controlled, hence<br />

variations in dietary composition will have little effect on body content or radiation<br />

dose received. The same is largely true for the cosmogenic radionuclides 3 H and 14 C.

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