Sererce ae)

in adults and 22 nCi in children, about 6 and 11%
respectively of the maximuin permissible lifetime
body-burden levels for the populationatlarge,i.e.,
Ye the ICRP valuc.' Analyses of bone samples
from several autopsies during the past 20 years

~*
",
* <*
+ -

local nuclear testing Program and also from world.

wide fallout, and to be concentrated by marine.

2

eer

Ife, particularly fish. The estimated body burdens _
for the Marshallese tested (Tabie 43) are higher
than those found for Japanese bomb survivors and
for others tested, but they are not more than oe
gave estimated “Sr body burdens similar to those
of the maximum permissible levels for non-occu- ~
obtained from urinalysis (see Figure 57). 17Cs
bedy burdens also reached their peak in abou ~~ pationally exposed individuals estimated with the
total] body as the critical organ. The values are
1965, at nearly 0.7 wCi (25% of the permissible
level for the general population), The body burslightly higher in females than in males, and sig. *
dens of the Utirik peaple were considerably below
nificantly higher in older persons. >*Fe emits phothese of the Rongelapese. Vable 42 shows that the
. tons of very low energy, and, sinceit is incorporated
stiinated bone marrow doses of Rengelap people
into the hemoglobin of the red cells, ic results ia
from internal and external sources (both natural
- relatively title irradiation of nucleated cells, Some
and riah-made radioactivity) were considerably
blood samples from the 1974 surveyare also Deing
reduced by 1974, and presenty data also for Cuirik
analyzed for +*Fe,
‘
and Tikini.*
‘Vhe coconut crab was banned fram the diet an ‘+ ©. PERSONNEL MONITORING AT BIKINI _
Rongelap because of its bigh level of radioactivity,

but about 2 years ago the ban was lifted on the
In 1946, before Operation Crossroads, the resisouthern islands ofthe atoll because the radioac- "3, dents were evacuated fromBikini. After stays at
tivity had decreased sullicicniy (see Table 40), <¢ Rongerik and at Kwajalein which proved unsatis447 factory, they were relocated on Kili Island in the
southern Marshalls, which also proved unsatisfacB. Fe BODY BURDENS IN RONGELAPESE
tory. The Eniwetok peuple were relocated at
Ujeclang Atoll, to the west, afier their evacuation,
In 1971 blood samples from 62 Rongelap resiAfter the 1958 moratorium on atmospheric nudents were analyzed** forFe, and their body
burdens were estimated by the method of Beasley
clear testing, numerous radiological surveys were
et al.52e was known to be present in the Mar.
done on Bikini and later on Eniwetok Atoll.}71-174
shall Ishands in fairly high levels as a result of the
In 1967 the principal isotopes contributing to the
gammaradiation field on Bikini and Eneu Islands
*Mir. KR. Fairchild at UNL cak ulated the bone marcow duse
Bor tha: 1007 4 alata.
“The Fe analyses were carried out by TM. Keasley and

BOE. Del atthe Gaisersity of alinglog School of Fisheries,
Seullhe,
“Table '3

Average Body Burdens of ?"Fein Rongelapess, 197 10
Aue
Alales

1-20
tL. 4
wld
Va-a54
yy t—trh
>t
1-20
2-54
bo-42
455
o4-61

>t

Na, of

Birnples

:

;
.
:
:

'
'

Badly burden,

pha

Out
ONS
Uol
O38
O43
G.48
0.25
U.54
0.435
0.66
0.37

0.06

were FCs, Co, 1255b, and Eu; slight amounts

of Py were also found, Considerable variation was
acen in the contamination of individualislands
comprising the atolls of Bikini and Eniwetok since
different tests had been conducted on various ones,
The contamination of Rongelap and Uuirik was
more uniform, being due largely to fallout from a
single detonation, Bravo,
In 1968 an ad foe committce reviewed the sur-

vey results for Bikini and decided that Eneu and
Bikini Islands were safe for hubitation, with cerain mcasures recommended to reduce ex posure

(sce Appendix 13). In 1969 about 30 people started
work on Bikini Atoll (living on Eneu), and in 1971
several Bikini familics moved back to Bikini Islaid
self, which now has about 50 Bikini people plus
a few administrators and construction workers,
Annual monitoring of personnel has been carried
out since 1969. In 1974 radiochemical analvses
were done on urine (sce Table 37 and Appendix
12) and other sainples, whole-body gamma spec.
troscopy was carried out on personnel living on

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