from the Bikini people.
patterns also allow us

These
to extrapolate

other reasonable patterns.

Note

as the external dose assessment is
concerned,

cases 5 and 6 are identical.

Because the expected living patterns

that the cases also include assump-

are most likely to differ between

tions on the food production and

the various age groups,

consumption plans of

tion data has been compiled (Table 2).

population.

This

the returning

information is

age distribu-

These data were obtained from the

only required for the internal dose

1974 census taken on Kili Island

assessment via the specific food

of the 784 persons who claim land

chains, and hence is not pertinent

rights on Bikini Island.?

to the external dose calculations.

geographical living patterns,

The cases are based upon the

The
also

shown in Table 2, were assumed to be

assumption that the people will

similar to those expected for the

reside on either Bikini or Eneu

returning Enewetak people.

Island in accordance with the

Even though the gamma-ray

Preliminary Bikini Atoll Master

exposure rates vary widely,

Plan.?

necessary,

For purposes of this report,

it is

for the purpose of

the

the cases are primarily directed

external dose calculations,

toward assessing the external dose

derive the most reasonable values of

associated with various options for

the mean exposure rates for each

housing locations on the two islands.

specific geographical area under

The first case is based on the

consideration (Table 3).

assumption that the people will

exposure rates for specific areas

live only on Eneu Island.

on Bikini Tsland were obtained by

The

to

The mean

remaining cases assume residence

weighting the mean exposure rates

on Bikini Island at different

within each contour interval (Fig.

village sites with various remedial

4) by the area within the contour.

actions being taken to reduce the

Since the exposure rates on Eneu

exposure rates.

Island are relatively uniform,

Thus,

cases 2

through 4 assume the residences

the mean exposure rates were chosen

are situated along the lagoon road

by inspection of Fig.

on Bikini Island (areas 1 and 2 in

the survey did not include the other

Fig.

islands of

7), while cases 5 and 6 assume

5.

Because

the atoll, we had

to

the people will live within the

rely on data from previous surveys

interior

to estimate how much of

portions

of

the

shown as area 3 in Fig.

island,

7.

As far

the

total

population dose was contributed by

Select target paragraph3