X.

RADIOLOGICAL MONITORING OF PERSONNEL AND ENVIRONMENT

Radiological monitoring of personnel and environment of the islands
affected by the 1954 fallout accident is reviewed in detail in Appendix II
(Dose Assessment) and in the 20-year report (1). The findings will only be
briefly summarized here.
A.

Background

The medical team assumed responsibility for the personnel monitoring of
the Rongelap and Utirik people in 1954 and for that of the Bikini people

returning to live on their home island in 1969.

In 1978, both environmental

and personnel monitoring responsibilities were transferred from the Medical Department to the Safety and Environmental Protection Division of this Laboratory.
Numerous radiological surveys for environmental contamination have been

carried out on Rongelap, Utirik, Bikini, and Enewetak (210-225). These
studies have provided important information on the movements of radionuclides
through marine and terrestrial life to man and have aided in the evaluation of
the body burdens of radionuclides in the inhabitants of these islands.

B.

Methods

Methodology for personnel monitoring has been discussed in detail in pre-

vious reports (8,18,22). Personnel monitoring has consisted of regular
radiochemical analyses of urine specimens from inhabitants along with wholebody gamma spectrographic analyses

for gamma emitters with special shielding

arrangements (first a 21l-ton steel room and later a "shadow-shield" bed and
chair arrangement of lead bricks).
C.

Results and Comments
1.

Rongelap and Utirik

The radionuclides absorbed at the time of the fallout from consumption

of contaminated food and water and inhalation are tabulated for the Rongelap
people in Table 2 of Appendix II. Only radioiodines were absorbed to above acceptable levels. The full impact of the thyroid injury resulting from absorption of radionuclides of iodine was not appreciated until much later when development of thyroid nodules and stunting of growth in some of the children
occurred. As discussed in Appendix II, the dose calculations for the thyroid
have been subject to many uncertainties and can only be considered approxi-

mate. The absorption of radionuclides other than iodine has not resulted in
any detectable injury, and the doses to the target tissues from these radio-

nuclides are thought to have been quite low though no precise doses have been
calculated.

By six months, radiochemical urine analyses revealed barely detectable
levels of radionuclides in the Rongelap people. When they returned to their

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