in Tables 16 and 17 by weighting by

of Bikini and Enewetak data on bird

sample size and by assuming that

muscle and liver, we are listing in

detection limit values ("less than"

Table 20 the Pu concentrations from

numbers) were actual concentration

the Enewetak Radiological Survey. >>

values.

The 10-, 30-, 50-, .and 70-yr inte-

Table 18 lists the final

radionuclide concentrations that were

gral doses resulting from ingestion of

used along with the estimate of fish

marine foods are given in Table 21.

ingested per day (600 g/da) to calcu-

Strontium-90 contributes the largest

late the radionuclide intake via the

fraction of the bone marrow dose (70

marine food chain (pCi/da).

to 80%), 13766 contributes approxi-

The table

also includes the concentration of

mately 20%, while 600, and 239,240,

some radionuclides in fish used in the

contribute about 64 of the total.

1973 Enewetak assessment.

whole body dose from the marine path-

The

way is 50 mrem for the integrated

The species of birds that are
readily caught and included in the

30-yr dose and 66 mrem for the 50-yr

diet are marine feeders, mostly

integrated dose.

-species of terns.

The bone marrow

doses are 200 mrem and 290 mrem for

Therefore, the

radionuclide concentrations in their

the 30-yr and 50-yr integral doses,

muscle tissue are similar to that in

respectively.

the marine diet.

are small relative to those from other

For this reason,

These integral doses

birds and bird eggs are considered

pathways.

part of the marine diet for the pur-

contributes a relatively significant
239,240,
fraction of the total
u intake,

poses of dose calculation.

No birds

Although the marine pathway

or bird eggs were collected in June
Table 18.

1975, so the data used to evaluate
this part of the marine food chain
come from previously published
|
8,31,32
reports
and are summarized in
Table 19.

Average weighted® radianuclide concentrations in
fish and clams at Bikini
Atoll.
Concentration,

The final concentration

pCi/g Wet Weight

data used for dose assessment listed
in Table 20 were derived assuming that
six times more bird muscle is consumed

Species

6006

1376,

0c,

Tish

1.51

0.14

0,076

0.0028

Clams

2.06

0.011

0.0060

0.0072

than liver and that the wet-to-dry

ratio is 0.33 for muscle and liver and
0.25 for eggs.

Because of the absence

of Pu concentration data on birds and

bird eggs on Bikini and the similarity

'Enewetak Atoll 1972 Dose Assessment

Fish

2.0

0.39

0.075

—

“Weighted by number of fish or clams
in the sample.

-27-

5009911

239, 2405,

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