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radiations while their shorter range beta particles will contribute a muchless biologically significant exposure to the skin.
Of the radionuclides that contribute to external radiation,

the most important single one is cesium 137. Its radioactive
half-life is approximately 30 years. Thus, it is possible for
cesium 137 to remain in our environment for long periods of
time without losing muchofits activity, although there can be
loss or reduction in availability of the material through normal

weathering processes.

Still cesium 137 does have a short

enoughhalf-life so that most of the radiations are released within the lifetime of a man.
All radioactive materials in fallout, except cesium 137, which

remain outside the body may be conveniently lumped together
to estimate their contribution to external exposures. These
usually are called “short-lived” even though some do havehalflives of upwards of one year.

In spite of the fact that nearly

all of the radiation exposure received from these short-lived
radionuclides is completed within a year after the radionu-

clides are created the total amount of exposure during the
year may be greater than that received from cesium 137 within
30 years.
Cesium 137 also is one of the two (carbon 14 is the other)

principal radionuclides deposited internally that irradiate

the whole body.

It is not a major source of the total whole

radiation dose except in such cases as that of Eskimos whose

diet is largely caribou or reindeer meat. The food chain
(liichen-caribou-Eskimo) reflects the relatively high surface

contamination of cesium 137 on the lichens.

The Data

The highest whole body exposures from nuclear weapons
tests ever reported by the United States were about 175 roentgens to 64 Marshallese following the March 1, 1954 surface
nuclear test detonation at the Pacific Proving Ground.’

This

situation resulted from a shifting of the winds so that the local
heavy fallout from this large yield surface burst occurred, in
part, across the islands instead of the open sea.
The Marshallese were evacuated, given medical treatment
and returned to their homeisland of Rongelap on June 29, 1957
after radiation levels had subsided to acceptable levels 5 (fig. 3).

From 1956 to 1962 about 24 children have been born —all
normal—and four persons have died from natural causes.®
(One of these had been on anotherisland and received 69 roent-

gens exposure.) Four deaths have occurred in the comparison
population of like size. There were, of course, noticeable
effects immediately after the irradiation such as nausea and
5

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