Gs-1357

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Zn-68
$1-90 ¢ G001)
RETURN TO RONGELAP
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OPERATION REOWING

of the Cs'* ’g K in the entire Marshallese popula-

tion suggests that the Cs**’ level, like the K’" level.
is proportional to the lean body weight.
The mean Cs'** body burden of the Rongelap
adult males (14.7 mypC/kg) was 300 times the

mean of that of the medical team carrying out the

study(9.048). The levei of Cs'* in the world-wide

population in July 1961 appears to have declined
from the maximum level observed in 1959. The

average value for Cs'"* measured in BNL person-

nel, for example, declined from 59 puC’g Kin

f J sr-90 1 0055:
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20-658
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rium with the levels of Cs'* in the diet (although
this is a difficult point to ascertain). The uniformity

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June 1960 to 30 in December 1961. The body
burdens of the Marshallese will. of course. also be
affected bv this world-wide fallout as well as by
the fallout released in the series of tests carried out

by the USSR in October 1961. As the accumula-

2.2

0.3

0.4

95

0.6

0.7

tion is gradual both in the environment, as world-

The levels of radioactive contamination ap-

wide fallout settles out. and in the human body,
via the ingestive route, it will be a number of
months before a clear picture emerges. However,
after the moratorium of 3 vears, during which
time the Cs'** levels had an opportunity to stabilize, it will be clear what the direct results are of
that particularseries oftests.

sex apparently do not influence significantly the
deposition of these radionuclides. Wide variations

weight of the Marshallese does not differ significantly between the exposed and unexposed groups.
nor doesit differ on the basis of sex or age. How-

pee

Figure 58. Estimated bodyburden of isotopes in Rongelap
people at various times since 1954. Values obtained either
by gamma spectroscopy or by radiochemical urine
analyses.

peared to bé about the samefor juveniles as for
adults. for men as for women. Factors of age and
in the level of contamination appear among individuals of all groups, as might be expected when
the source of the contamination is via ingestion.

Even with a fairly limited diet, individual tastes

maydictate great differences in the food consumed.

As for the time course of the contamination in
the population as a whole, it is necessary to consider each radioisotope individually, as to source

of supply and discrimination of the soil, plant and
animal life, and the human bodyfor each isotope.
The mean Cs'"* body burden of the Rongelap
adult males is 14.7 muC/kg as compared to 14.1
in 1959. Thus, no significant change has occurred
in the past 2 years. These Cs'** body burdens of
the Marshallese result from the relatively high
dietary intake through foodstuffs produced in the
Marshallese environment. Theyreflect the level

of residual fallout on the island, and also the higher

uptake and retention of Cs'* by food plants grown

in a K-deficientsoil. It appears that the bodyburden of Cs‘** has reached an approximate equilib-

The mean Zn” concentration per kg body

ever, the mean was generallyslightly higher among
adults than in juveniles, and higher among aduit

males than adult females. In the period 1959-1961
the value of Zn*’ body burden dropped bya factor
of 6. The value of Zn*’ in male adult Marshallese
dropped from 9.9 muC/kg bodyweight in 1959 to
1.51 in 1961. No clear reason emerges as the basis
for this drop, although it is possible that dietary

variation may be responsible.It is known that the
source of Zn*”’ in these people is from fish. which

selectively concentrate this element. Theretore. it

is possible that the decrease in Zn”? levels noted
mavbe due to the fact that the people are eating
more canned meats in place of fresh fish. If the

Zn”' intake in the diet had decreased radically

during that period, the observed fall in the level
of internally-deposited Zn" would be consistent
with the effective half-life of Zn”’, which is =120
days.'* The evidence that could be obtained on
this subject is insufficient to make anv conclusive
statement, however.

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