B= rate of intake of '%7Cs (picocuries per day)
a«= iological mean time (days),

Ar=absorstion factor, assumed to be 1.0.

With biological mean time expressed as a
function of age, equation (8) becomes: |
B=0.018 R (xi+e-%)

(9)

where:

x=age (vears)
Equation (9) may be used, for example, to
estimate the average body burdens of cesium437 in the U.S. population from milk consumption. The US. Public Health Service pasteurazed milk retwork results for 1963 and 1964
averaged 114 and 109 pCi/liter, respectively

(20, 21).

These data indicate that the average level of

cesiuin-137 in U.S. milk supplies has decreased
slowly over the past 2 years. Considering the
smal! change in these levels, it can be assumed °
that the various age groups in the population

<r in equilibrium with the cesium-137levels in
milk they consume for the portion of their
body burden due to milk intake, and their average body burdens for 1964 may be determined
from an average value of daily cesium-137
intake.

If it is assumed that milk ingestion for males

less than 1 year of age resulted in an average

intak. of 55 pCi/day during 1964, and using
the s,ormalization factors in table 2 to estimate
milk consumption by other age groups in the
population, estimated body burdens may be
determined from equation (9). The resulting
values are shown in figure 7.
r

4 Beteten

The dos: to males less than 1 year of age from
at-home milk consumption, using equation (5),
is about 0.002 rad or 2.0 millirads in 1964. The
poini should be stressed that these estimates
apply only to that portion of the cesium-137
body bura-na of the U.S. population due to milk
consumpt.on at home. The contribution to body

burden and whole body dose from milk con-

sumption outside the home and from other
items of the diet arc additive.
December i965

oo

WeMALE

et

1.
Cy

A

%

—t.

2

Wi

a

_t

»-

=

B= body sarden (nanocuries)

s-

where:

CU

(8)
AVERADE CESAIMH1TT BODY BURDEN INU. $, POPULATION (nime--ntes!

B=RT, Adit!

Figure 7. Estimated cesium-137 body burdens from
milk consumption for U.S. population in 1964

For cesium-137 in U.S. milk supplies, estimates of cesium-137 body burden in figure %
indicate that males 15 to 20 years of age had
the highest Jevels; those less than 1 year of age,

male and female, had the lowest levels; and

females of all ages had a lower average level

than males of the same age.
Sunmary

The observations of biological half-time for
cesium-137 in man indicate that half-time is a
function of age. The average biological halftimes for cesium-187 from birth through adult
life vary by a factor of about 10. A simple
mathematical expression has been presented
which relates half-time of retention of cesium—
137 and age. Though the model]is crude, it has
utility in predictions of doses and body burdens
from cesium-137 for various ages within an exposed population. Additional measurements of
cesium-137 retention are needed, particularly
for younger age groups, to further refine the
model and to improve prediction capability.
More data are also needed for the elderly.
The combination of changes in half-time and
body weight results in a dose variation, for a
given cesium-137 intake, from birth through

adult life, of a factor of about two. The addi-

tion of assumptions regarding patterns of milk
intake as a function of age and resultant cesium-137intake leads to a different distribution
' of dose with age than is foundfora fixed intake

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