Urinary excretion of radionuclides @ P. S. Harris ET AL.

1000

I

estimates of intakes in 1954** are presented here (Table
5). Urine samples were counted on numerous days to

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check for consistency of the decay rate.****** The count

rate data reported here were specifically from 30 March

1954. Count rates from '*'I in the pooled urine samples

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obtained from adult Marshallese on March 16 and 17 on
Rongelap were nearly identical: about 70 counts per
second (c s ') per 500 mL obtained on 30 March 1954.

The count rate from the pooled sample of Rongelapese

on Sifo Island, Ailinginae Atoll, at the time of the Bravo
test was 33cs ! per 500 mL, about one-half of the value

for the adults exposed on Rongelap.****Ss

The count rate in a pooled urine sample from the

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!

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1

§ 10 2030 50 7080 9095

!

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99

99.999.99

Cumulative Percent

Fig. 3. Empirical cumulative probability distributions of urine
volumes obtained from Rongelap and Ailinginae groups by the
Health and Safety Laboratory (HASL AEC-NYOO)(see Table 4
for a summary ofthe data).

1600

T_T

TTT

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samples, about 20 counts per second per 500 mL,*****85§

though when adjusted to the approximate 1 L per day

urinary excretion of the Americans, the count rate per

'’Cs on Rongerik compared to Ailinginae (see Table7,

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on an equal volumeof urine as that for the Marshallese
samples, was less than one-third of that of the Rongelap

24-h excretion was 40 cs ', higher than on Ailinginae.
This is explained by the two-fold higher deposition of

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Simonet al. 2010b).

The intakes of '*'I originally estimated in 1954 by

Harris** were 2.1 MBq (56 pCi) for the Rongelapese
and 0.65 MBq (17.5 mwCi) for the Rongerik group.

Revised estimates by Harris" that included minorrevi-

sions for detector efficiency were 2.8 MBq for the
Rongelap group, 1.3 MBq for the Ailinginae group, and
0.78 MBq for the Rongerik group (Table 5).

1

Comparison of estimates of intake of radioiodines
A comparison of adult male and female average

intakes of '*'T for Marshallese exposed on Rongelap and
01

«1

1

5 10 2030

50

7080 9095

99

99.9 99.99

Cumulative Percent

Fig. 4. Empirical cumulative probability distributions of urine
volumes obtained from two Los Alamos Scientific Laboratory
(LASL) samplings of American military weather observers on
Rongerik (see Table 4 for a summary ofthe data).

the tropics that occurs as a consequence of perspiration and
insensible water losses through the skin due to high humidity and temperatures. It is known that urine volumes in
humid, tropical climates are typically much smaller than

Ailinginae to Bravo fallout is made in Table 6 from
estimates derived by Harris in 1954** and later modi-

fied,’* Lessard et al. (1985), and Simon et al. (2010b).

Similarly, a comparison of estimates of intake for American military weather observers exposed to Bravo fallout
on Rongerik is made in Table 6 from estimates presented
by Harris in 1954,** Goetz et al. (1987), and Simonetal.

(2010b).

Average estimates of intakes of '*'T among adults,

depending on the assessment, ranged from 2.8 to 3.5

more temperate climates (Elebute 1973; Latham 1997); see

the Appendix of Simon et al. (2010b) for a detailed
discussion of that phenomenon. For these reasons, we
believe that the relatively small volumes obtained from the

Table 5. Original and revised estimates of intakes (MBq) of ‘I

by Harris.*

Sampled group

Marshallese were, on average, reasonable.

LA316R and LA317R
LA318A
LA319S

'S'T count rates and estimates of intake

Gamma-ray count rates per 500 mL from each ofthe

four pooled urine samples (Table 3) and the related

a ¢é

nr” is not reported.

Original estimates

Revised estimates

2.1
0.65
nt

2.8
0.78
1.3

(**)

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