9.8 + 0.5 x 10°

3

?

mCi/km”.

We eagerly

to adequately

await completion of the soil analyses

of

test

the applicability

this model in its present

form.

Dose Assessment

The 1O-,

30-,

S0-,

Bikini Atoll.

and 70-year

Samples collected dur-

integral doses are listed in Table 6

ing January 1977 will indicate whether

for consumption of Bikini cistern

the present dose assessment based

water and in Tables 7 and 8 for con-

upon observed concentrations in June

sumption of Bikini and Eneu ground-

1975 is acceptable or whether the

water,

1975 concentrations might have been

respectively.

The doses are

calculated using an average daily

higher than normal due to possible

intake of 2 litres of water and using

contamination resulting from the

a sum of the average radionuclide

initial drilling operations.

concentrations for the soluble and

The resuits for the 30-year inte-

particulate phases listed in Tables

gral dose in the tables can be used

2, 4, and 5.

for comparison and discussion.

We have further assumed

The

that the only loss of radionuclides

whole-body dose for all three water

from the water is due to radioactive

Sources is contributed almost entirely

decay.

by

If the water concentrations

L3fa

For both cistern and

increase with time relative to the

groundwater

1975 concentrations or if they

mately 4

decrease more rapidly

marrow dose than Malo, and both 90.

than assumed

Ose contributes approxi-

to 5 times more of

the bone-

{rom radioactive decay because of more

and Iolo. are approximately

rapid environmental turnover,

of magnitude more significant

then

239,240

the long-term integrated doses would
be affected accordingly.

port

than

Pu.

The 30-year integral doses pre-

Therefore,

the dynamics of radionuclide

two orders

trans-

dicted from consumption of Bikini

in the groundwater reservoirs

cistern water are 1.7 mrem for

the

and the mechanism of nuclide con-

whole body and 11

tamination in the cistern water must

marrow.

be understood before final Long-term

0.5 rem for a member of

dose evaluations can be made.

tion,

or 15 rem in 30 years.

Fore,

the whole-body and bone-marrow

As was previously mentioned,

we

mrem for

the bone

The annual federal puide is
the populaThere-

doses resulting from consumption

are continuing groundwater studies at
~18-

Select target paragraph3