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FUNDAMENTAL CONSIDERATIONS IN DETERMINING SIGNIFICANT
LEVELS OF RADIOACTIVE CONTAMINATION OF FOOD AND WATER
Prepared by

410846

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Division of Biology and Medicine
U. S. Atomic Energy Commission

The radioactivity of importan:e in sea water following an atomic

explosion at altitude near sea levei is principally due to fission products

from the bomb which, with other materials, condense into small particles and

fall into the sea. Some of this material will be retained in upper layers
of water in solution, in suspension, or associated with organic materials.

Radioactivity induced by the radiation from the bomb will be relatively un-

important, largely because of the extreme rapidity with which it is reduced
by radioactive decay.

Fish living and feeding in waters containing radioactive materials will
accumlate some of these materials in the various tissues of their bodies and

on exposed surfaces such as the skin and gills.

Observed levels of activity

in sea water are too low to produce any harmful effects on the fish or on
their food supply. In this connection, it may be observed that the levels of

radiation required to produce observable effects on lower forms of life are
generally much greater than for humans, and that the limits of radiation exposure considered acceptable for humans over periods of many years are much

lower than those which would be acceptable for short periods of time.

The best guide that we have available for limitation of radioactivity in
food and water is National Bureau of Standards Handbook 52, which contains

recommendations of the National Committee on Radiation Protection limiting the

quantities of radioactive material in the body.

The maximum permissible con-

centrations in water, expressed as microcuries per eram, recommended in Table 3

of this handbook are considered to be applicable also to food.

In setting these

concentrations, it is assumed that they apply to the entire water supply of the

individual (including the water contained in the food that he eats), and it is
assumed that these values may be maintained throughout the remainder of his life.
The figures given in Handbook 52, based largely on occupational exposure,
are considered adequate at the present time, since no one is exposed to radioactive materials at considerable fractions of these values throughout his
early life. The possibility of a general increase in environmental levels of
radioactivity from the widespread use of atomic energy for industrial purposes

has led to consideration of the desirability of using lower levels for lifetime
environmental exposure. These levels might be as low as one-tenth of those
acceptable for occupational exposure to radiation or to radioactive materials.

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