Radiological Concerns

The primary radiological problems are the result of residual fission and activation products in the
terrestrial environment.

They have been identified by previous environmental surveys as follows:

1) Exe

ternal radiation levels significantly higher on some islands in an atoll compared to levels on lightly

contaminated islands.
2) Fission and activation product radioactivity in certain terrestrial food trems
now growing on islands of these atolls and the possibility thac unacceptable levels of these radionuclides
may appeat in foods, plants and animals newly introduced into these atolls.
3) Radioactivity in the
ground water, a possible source of drinking water and water for irrigation.
4) Pluronium and americiuim
{socopes in the surface soil,
These factors are illustrated by data in Tables 1 through 4 taken from
previous radiological survey reports.
.

Table 1.

Gamma Radiation Rates in Bikini Acoll™

Island

Bikini
Weathered areas
Close to shore

Island center
Hot spots

Eneu

Nam

Outer edge

Island center

N.E. corner

Bokantuak, Iomelan,
Rojkere, Eonjebi
Aerokoj-Emenman complex:

Aerokoj, Aerokojlol
Bikdrin, Lele

Eneman

East Eneman

West Eneman

Enidrik

East Enidrik

West Enidrik

(mR /br)
Exposure rate
Range
-010-,120
-010-.030
-020-.040

137

-010-, 330

60¢9,*?'cs

-010-,030

-110-, 330
-003-.010

ek

-001-,010
-006-.010

wk
we

"001.570

-001-+.010

-020-,570

,003~.235

-003+,030

Lukoj

Oroken

2015-.045

Bokdrolul

~020-,050

010.035

Bokbata

Aomen-Lroij complex:

wh

‘010~.030

Aomen

-005~.020

Odrik, Lrotj

.010~.040

Lomi lik
*

;060~. 200

-060-.136

Bokaetoktok

C83,

.015-.150

-010-,235

Jelere

-

Major contributors
T3/ Cg

-050-.,080
.080~. 120+

~002-.010

—

.020~. 330

.

Gc, 125g, 102m,

600, 1255, 102m,

“

6069, 125g, 102m,

wh

ek

we

6005, 376
%o9, 12555

Saad

See ref, 9.

;

No soil sample or field spectra measurements.

In some cases, che predicted doses and dose commitments derived from survey information for Bikini

and Enewetak Atolls approach or even exceed national and international radiation protection standards for

certaio living and dietary patterns.
Corrective actions or restrictions must be placed on use of these
atolls and their resources to assure that the applicable radiation standards are not exceeded,
Herein
lies the primary justification for the continuing environmental followup surveys sponsored by ERDA.
Environmental Monitoring
The most important sources of exposure to people living on Rongelap and to future

residents of Bikini

and Enewetak Atolls are from internal deposition of radicisotopes from certain elements in the human

diet, and from the long term occupancy of islands having external radiation dose rates higher than
natural background. Aside from periodic re-evaluations to establish trends in external dose rate
reduction, external radiation monitoring will assume less significance, compared to monitoring of che

food chain, as time passes.

At present, annual visits are being made to identify and collect repre-

sentative samples of local diets for laboratory analysis and dose commitment updates.
New locally
grown food items are becoming available in small quantities on Bikini Island as a result of the experimental agricultural practices of a small group of caretaker families living there.
Neither Bikini Atoll,
where radiological cleanup has been completed, nor Enewetak Atoll where clean up has not yet begun,
have a subsistence agriculture resource in being which is sufficient to suppore the anticipated populations which will one day live there (though such crops are currently being developed or planned).

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