plutonium not only to the inhalation

-burden from cistern or ground water

pathway but to the ingestion path-

ingestion than do New Yorkers.

way as well.

assume here, of course, that Bikini

Bennett has recently published

We

Island water is the only available

data on fallout 239,240, in 1972

source for the present population.

dietary components in New York that

It follows that urine levels in the

included a mean tap water concentra-

Bikini population would exceed those

tion of 0.3 f£Ci/liter from 1973.

in a New York population even if

Other data appropriate for compara-

drinking water were the only pathway

tive purposes are fallout levels in

involved and each of the other path-

untreated surface water of the Great

ways contributed a similar level of

Lakes , 1044

plutonium at Bikini and New York.

These data are sum-~

marized in Table 2, along with the
mean and range of plutonium concen-

Dietary Intake

trations in cistern and ground water
from Bikini Island.

Assuming that

Terrestrial Food Pathway — The

water consumption rates for individ-

diet for the people on Bikini Island

uals at Bikini and New York are

consists of foods imported from the

similar, we see that Bikinians

United States and foods grown on

experience a higher plutonium body

Bikini Atoll.

Table 2.

The imported foods,

Comparison of plutonium concentrations in water of Bikini Island with
those in several U.S. sources.
239,240, FCi/liter
Mean
Range

Location

Data from
Ref. No.

Bikini (1975)
Cistern water

1?

8-29

9

Ground water

44

6-122

9

New York (1973)

City tap water

0.3

3

Great Lakes (1973)
Superior

0.63

10

Michigan

0.73

10

Huron

0.63

10

Erie

0.17

_ 10

Ontario

0.25

11

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