the highest concentration of radionuclides in the skeleton (over 90% of the body burden
of the pigs), with the liver and colon containing the second highest levels of activity, and
all other tissues having some measurable contamination. The iodine-131 content of
human urine and the observation of bone-seeking fall-out nuclides in the human urine
samples and the animal skeletal tissue samples focus the concern for internal radiation
doses on the thyroid, skeleton, and bone marrow.

| TABLE 3. Estimated Early Body Burdens of Radionuclides in the Rongelap Population
7 in Kbg (pCi)
Radionuclide
Sr-89
Ba-140
"Rare Earths”
]-131
(in thyroid)
Ru-103
Ca-45

Estimated Activity,
59-81 (1.6-2.2)
13-100 (0.34-2.7)
00-44 (0-1.2)
240-410 (6.4-11.2)
0-0.48 (0-0.013)
0-0.70 (0-0.019)

“Fissile Material”

0-0.016 pg

s Source: Conard et al., 1980.

Most radioiodine absorbed into the body is excreted within two days, therefore, urine
samples, especially pooled urine samples, are an ineffective means for estimating theinitial

iodine intake. From the one pooled sample collected on day 15 after the Bravo
detonation, it was apparent that there was someintake of iodine-131, but, a sample at this
date cannot accountdirectly for short-lived nuclides that might have contributed to thyroid
dose. Although good anatomical models did not exist in 1954 for the thyroids of the
children exposed, the early estimates of the thyroid doses probably were fairly accurate.
Webase this conclusion on the fact that the electron dose to the glandtypically is the

dominant component, and that it can be calculated with good precision given a good
estimate of gland mass. The masses of the thyroids of individual Marshallese residents
were not well-known, but estimates were available for children elsewhere who were of

similar ages to those exposed ontheislands. The earliest estimates of thyroid doses were
1.5 Gy (150 rad) for the Rongelap population and 0.5 Gy (50 rad) for the servicemen
22

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