PRIVACY ACT MATERIAL REMOVED

food and water(see Appendix 9C). Otherinternally

Table 3

Estimated Body Burden (uCi) of Rongelap People?
Activity
at day |

—

‘Activity
at day 82

89Sr
140Ba

16 - 2.2
0.34- 2.7

0.19
0.021

131] (in thyroid gland)
103Ru
Ca

6.4 -11.2
0 - 0.013
0 - 0.019

0.0
0.0

Rare earth group

Fissile material

0

O

9

- 1.2

- 0.016 (ug)

0.03

0.0

cal analyses of urine samples, beginning 15 days

post exposure,for ®9Sr, 14°Ba, 131], the rare earth

group, and fissile material. As expected, the
Rongelap people had the highest body burdens.
By 6 months, beta activity in the urine samples
was barely detectable. Table 3 shows the main
isotopes foundat day 1 (extrapolated values) and
at day 82. The agreement between the findingsat
the two laboratories is close considering the techniques available at that time. Levels in the AilingNae group were about one-half and in the Americans about one-quarterthe levels in the Rongelap
group. Only isotopes of iodine, strontium, barium,
and a few rare earth elements were absorbed to
any significant degree. In the Rongelap group,at
day 1, 99Sr and 13!I were near the maximum per-

missible levels, and the estimated total amount of

radioactive material in the gastrointestinal tract
was about 3 mCi; whetherthis had anyrelation to
the early gastrointestinal symptoms is not known.?
Radiological monitoring of personne! and environment at Rongelap and otheratolls in subsequent
years is discussed in Section VI.

absorbed isotopes (see Table 3) were not thought
to be significantly absorbed by the thyroid and
probably contributed little to the dose to that
gland. Conversely, the radioiodines contributed
only slightly to the whole-body radiation dose.
During the early period after the fallout, radioiodine was recognized as possibly its most hazardous constituent, but the estimated dose to the
gland of 100 to 150 rads was not considered sufficient to cause later development of thyroid ab-

normalities. No acute effects were noted in anyof

the people that could be related to the internal
absorption of radioiodines or other radioisotopes.
Contamination of the skin resulting in extensive
beta burns in the neck region in 70%of the people
(see Figure 2) probably did not contribute to the
thyroid dose because of the low energy of the beta
radiation. Possibly slight absorption of radioiodines throughthe skin occurred.
Whenthe people returned to Rongelap to live
in 1957, no radioactive isotopes of iodine remained
(except possibly very slight amountsof 12°), and
the principal remaining isotopes (137Cs, 9°Sr),
which were absorbedto low levels in the people,
probably did not contribute to any significant

degree to the thyroid dose.®
When thyroid lesions began developing in the
Rongelap children in 1963, the dose to the thvroid
of the Rongelap people was reevaluated by
James.?6 His estimates of the gammadose agreed
approximately with the previous estimate of 175

5. Thyroid Dosimetry

The fallout produced several possible sources of
radiation exposure to the thyroid gland. The gamma radiation resulted in thyroid doses of 175 rads
in the Rongelap people, 69 rads in the Ailingnae
people, and 14 rads in the Utirik group. Iodine
isotopes are producedinrelatively high yields by
the fission process. Someare too short-lived to be
of consequence, but 131], 132], 133], and 155] are

sufficiently long-lived to cause a considerable dose
to the thyroid following internal absorption and
concentration in that gland, and these were absorbed both via inhalation and via ingestion in

Figure 2. Beta burns (March 29, 1954).

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