germ plasm. For stated exposure conditions, the BEIR risk-estimate
of somatic effect predominate, relative to other effects of radiation. They
are therefore of primary concern in establishing protective criteria. Also,
the BEIR, 1972 report states that the rate of cancer induction is the only
somatic risk that needs to be considered. Consequently, in estimating the
risk to the Enewetak Atoll people from exposure to radiation, only cancer
induction has been considered,
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Induced cancer can be fatal or nonfatal. The risk guidelines listed
in Table 5-1 are estimated to apply equally to either fatal or nonfatal
effects:(BEIR, 1972) so that the total number of effects resulting from a
given dose would be twice the number of either. To calculate the number
of either effect, using the data of Table 5-1, find the product of (1) the
cancer incidence rate (Column 2), (2) the exposed population expressed as
millions, and (3) the average dose for an individual for each critical organ.

These products are then summed to obtain the total number of cases.

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The effects of the induced cancers, or even the cancers themselves,

may appear immediately or several decades after exposure (BEIR, 1972,
p- 91).

Since effects are not expected to show up in the earlier years

with the same frequency as in later years, and since the appropriate
frequency distribution is not known, the number of effects expected to
occur during the entire risk period are calculated instead of the number
of effects expected to occur in any one year. The guideline values given
in Table 5-1 are maximal] and the number of incidents of induced cancer
or fatalities may be as lowas zero.
5.3.2.2 Annual Dose Limits. The primary sources of recommendations
for radiation protection standards and guidance are the International
Commission on Radiological Protection (ICRP), the National Council on
Radiation Projection and Measurements (NCRP), and the Federal Radiation

Council (FRC). The standard-setting responsibilities of the FRC were
transferred to the Environmental Protection Agency (EPA) in 1969. The
recommendations of these groups are all compatible with each other.
These groups have recommended maximum permissible doses for
workers exposed to radiation, for individual members of the public, and
for a suitable sample of an exposed population.

In addition, they have

recommended dose rate limits for exposure of various critical organs.
These recommended dose rate limits are presented with the understanding

that radiation exposures should always be kept as low as can readily be

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