RET,A ee

period of time. The detection efficiency of cellulose

nitrate film is not quite as high as that of nuclear

emulsions because the etching process reaches only
those particles which penetrate the top surface of the
filn (away from the bone). Since the films were 3 p

thick and the etching process removed 1-2 p», a few

tracks were missed, On the other hand, this penetration effect should increase resolution (particularly

with thicker films) by etching only those alpha tracks
which are more perpendicular to the plane of the
film.
In summary, the cellulose nitrate method provides
an alternative to autoradiography with nuclear emulsions. It does not require darkroom facilities. The
alpha tracks are enlarged and more easily detectable.
Background fogging is eliminated. At the expense of
some decrease in efficiency one should be able to obtain better resolution than with emulsions.
REFERENCES

ite onary ert Re

1. Fleischer, R. L., Price, P. B. and Walker, R. M. Ann. Rev.

Nucl. Sct. 15, 1 (1965).
2. Benton, E. V. U.S. Naval Radiological Defense Laboratory
Report USNRDL-TR-14 (1968).
3. Becker, K. Health Phys. 16, 113 (1969).
4. Rosenthal, M. W., Marshal, J. H. and Lindenbaum, A.
Diagnosis

and

Treatment

of Deposited Radionuctides,

Symp. Richland, Washington, May 15-17, 1967. Excerpta
Medica Foundation, Amsterdam, 1968, pp. 73-80.

Fic. 2—A serially etched cellulose nitrate autoradiograph
of trabecular bone from mouse, injected with O1yCi ionic
™Pu, which shows surface alpha tracks. 100 X.

THE CONCENTRATION OF RADIUM, THORIUM, AND URANIUM
BY TROPICAL ALGAE

wee

oe

fae ine

D.N. Edgington, S. A. Gordon,* MI. M. Thommes, and L. R. Almedovart
Samples of twenty species of marine algae collected between
1961 and 1968 in Puerto Rico have been analyzed for total
Organic material, protein nitrogen, calcium, radium, thorium,
and uranium. The results suggest that the concentration of
radium, thorium, or uranium by these organisms may be controlled by two mechanisms: (1) ion-exchange or coprecipitation of the ion with the calcium carbonate matrix, or (2) complex formation with either the protein nitrogen or some other
component of the organic fraction.
Concentration of radium (and possibly thorium) appears to
occur by both mechanisms, the dominant one being dependent
upon the division. For the Rhodophyceae and the highly calcified Chlorophyceae it is the former, and for the Phaeophycea the latter. Concentration of uranium occurs by the
first mechanism. This difference in behavior is consistent with
the chemical forms of the ions of these elements in seawater.
* Biological and Medical Resarch Division.
¢ Department of Marine Biology, University of Puerto
Rico.

INTRODUCTION

To predict the consequences of the accidental re-

lease of radionuclides from nuclear power plants it is
necessary to understand the mechanisms by which
stable elements are concentrated and transported
within the ecosystem. Nuclear power plants, by necessity, are located close to large bodies of water for
cooling purposes. Hence, aquatic organisms are

among the first most likely to be affected by radionuclide release. Also, data on their natural levels of ra-

dieactivity would be useful as reference indices.
While some information is available on the concentration of various elements and radionuclides from

fallout in marine organisms,‘1-8) little is known concerning their distribution within species, between species, and as a function of collection site. In 1961, before the nuclear reactor “Bonus” at Punta Jiquero

Select target paragraph3