62
of Table 26 showsthat the body burdens of **"Cs

and *°Coare notsignificantly different amongthe
various subdivisions by age and sex of the Rongelap resident population. The values given for the
children may be overestimates, because thecali-

brations were in terms of an adult-size phantom
only and the counting geometry is such that a
higher efficiency obtains for the children, especially the smaller ones.
Prior to 1962, the concentration of °°Sr in the

urine was used as a basisfor estimating °°Sr body
burdens. Subsequently, the ratio of °°Sr to Ca in
the urine has been used. On this basis the 1965

mean concentrations of 10.1 pCi **Sr/liter and
0.093 g Ca/liter correspond to a body burdenof
11.4 nCi. Data were not obtained on children in

1965. In previous years the urinary °°Sr to Ca
ratios in children have been about twice thatfor

adults. Urines for °°Sr analysis were not collected
in 1966.

rie

Comparison of the 1965 survey data with the

results from previous surveys (Figure 70) shows
that the mean levels of '*"Cs and *°Sr have re-

mained nearly constant since 1961, and that *°’Cs
is at about the 1958 level. Further comparison

with the 1954 and 1957 results indicates that the
activities now being seen are almost entirely due
to intake subsequentto the return of the Rongelap

population to their homeatoll in 1958.

If the ecological cycle were in equilibrium,it
would be expected that, by virtue of physical de-

cay, the specific activities of '*’Cs and *°Srin the
food and the corresponding body burdensofthese
radionuclides would have decreased about 9%
during the interim 1961 to 1965. Actually there
may have been a small decrease that is masked by
the unknownoverestimation errorin the children.

Even with a correction for this, the sustained levels
suggest that increasing amounts of the originally

contaminated materials are getting into the food
chain and thus maintainingthe specific activity at
the previous levels. This hypothesis is supported

by data obtained from E. Held, University of

Washington,”’ to the effect that soil and plantsurveys indicate that the ‘*’Cslevels in plants haveremained about the samesince 1961. There is no
ready explanation ofthe mechanism forthis. These
findings are to be contrasted with those cited be-

low for an Eskimo population.

Table 28 shows the relationship between *?’Cs
body burden andits excretion rate for those resi-

Table 28

Comparison of Body Burdens and Excretion Rates
L37 Cs

body

ICs

Subject

burden,

nCi/

Urine

No.

ni

liter

volume, |

day

day

508.9
405.6
484.8
971.2
575.0
732.7
525.5
773.3
1326.0
1047.0
1209.0

5.0
6.2
23.0
4.4
3.4
1.2
2.1
6.0
5.1
4.7
2.2

0.730
0.730
0.289
0.650
0.710
0.645
0.940
0.500
1.320
0.560
0.890

3.65
4.526
6.647
2.86
2.414
0.774
1.974
3.600
6.732
2.63
1.958

0.00717
O.O1LI5
0.01343
0.00294
0.00419
0.00105
0.00375
0.00387
0.00507
0.00251
0.00161

8
15
51
53
58
59
1!
20
27
40
41

50
73
835
843
928
932
94?
822
833
840
853
855

7289
1861.0
6448
419.8
491.4
5496
1058.0
69446
636.9
1455.0
8149
606.2

06
19.0
52
1.5
6.5
9.7
18.0
45
5.1
6.0
2.0
3.6

37g

1.800
0650
0.550
1.340
1.040
0.350
0.540
0.835
1.000
0.800
1.750
0.500

nCi/

1.08
12.35
2.86
2.01
6.76
3.395
9.72
3.758
5.10
4.80
3.50
1.80
Mean

Fraction/

0.00148
0.00663
0.00443
0.00478
0.01375
0.00617
0.00918
0.00540
0.00800
0.00329
0.00429
0.00296
0.00553

dents of Rongelap for whom individual urine

specimens were analyzed. An average of 0.553% of

the body burdenis excreted per day, the range being
0.105% to 1.375%. These values correspond to
turnoverhalf-times of 120 days, 660 days, and 50
days, respectively. Except for some of the very
slow turnoverrates, these values fall within the
ranges cited or reported for other populations, in
which the means were 75, 74, 87, 115, and 135
days.** Someof the lowest turnover rates in the

Rongelap population may be ascribed to uncertainties in the completeness of the urine collections. Thusit is to be expected that the '*’7Cs value
would fall to near-zero levels in a year ofliving in
a noncontaminated environment. Thatthis fall
does occuris shown bythe results with the Ebeye
population, who have been absent from Rongelap
for various times from 1 to 18 months.

Becauseit is not a gamma-ray emitter, °°Sr is
not detected by the whole-body counting method.
(Theoretically it might be possible to estimate °°Sr

Select target paragraph3