46,

Shinn, J. H., and L. R. Anspaugh. 1975. “Resuspension -- New
Results in Predicting the Vertical Dust Flux." In: Radioecology
of Plutonium and Other Transuranics in Desert Environments.

M. G. White and P. B. Dunaway (Eds.).
47.

4a,

Stannard, J. N.

1973.

Report NVO-153.

"Plutonium In The Environment."

FOLIAR AND ROOT PATHWAYS OF PLUTONIUM
CONTAMINATION OF VEGETATION

pp. 207-215.
In:

Uranium, Plutonium, Transplutonic Elements.
(H. C. Hodge, Jd. N.
Stannard and J. B. Hirsh (Eds.). Springer Verlag, New York, N.Y.

R. C. Dahlman*
and

-Tamura, T.
1974. “Distribution and Characterization of Plutonium
in Soils from the Nevada Test Site." In:
The Dynamics of Plutonium

K. W. McLeod**

in Desert Environments. P. B. Dunaway and M. G. White (Eds.}.
Report NVO-142. pp. 29-42.

49.

Tamura, T.

1975.

“Distribution and Characterization of Plutonium

50.

Tamura, T.

1976.

"Physical and Chemical Characteristics of

in Soils from the Nevada Test Site."

J. Environ. Quality 4:

Plutonium in Existing Contaminated Soils and Sediments."
Transuranium Nuclides in the Environment.

51.
52.

Report LA 4756.

Volehok, H. L., R.- Knuth, and M. T. Kleiman.

in the Neighborhood of Rocky Flats, Colorado:

Particles."
Doe

In:

IAEA, Vienna. pp. 213-229.

Volchok, H. L. 1971. "Resuspension of *°’Pu in the Vicinity of

Rocky Flats."

1972.

Report HASL-246.

“Plutonium

Airborne Respirable

Wallace, A., and BE. M. Romney.
1975.
"Feasibility and Alternate
Procedures for Decontamination and Post-Treatment Management of

Pu-Contaminated Areas in Nevada." In: The Radioecology of
Plutonium and Other Transuranics in Desert Environments. M. G,
White and P. B. Dunaway (Eds.). Report NVO 153. pp. 251-337.
ak

ABSTRACT

350-355.

weapons
Plutonium enters the terrestrial environment from testing of nuclear
depends on
and from nuclear technologies, Assimilation of Pu by vegetation
Pu sources in
source term characteristics and mode of exposure to different
facilities,
the environment. For Pu released to the atmosphere from fRuclear
for most of the
direct deposition of airborne particles on foliage accounts
Assimtlation of Pu via the roots
incipient contamination of vegetation.
lower by at
generally yields Pu concentrations in edible tissues that are
humans will depend
least an order of magnitude; however, lifetime exposure of
These concepts
increasingly on the entry of Pu into foods by the root pathway.
environments at
are confirmed from information obtained from contaminated
for ingestion of
Savannah River and Oak Ridge, Radiologic doses calculated
airborne Pu on
Pu-contaminated vegetables show that direct deposition of
than those for Pu assimisurfaces yields doses that are a factor of ten higher
tated into the plants by roots.

Whicker, F. W., ©. A. Little, and T. F. Winser.
1973.
"Plutonium
Behavior in the Terrestrial Environs of the Rocky Flats Installation.”

INTRODUCTION

In: Environmental Surveillance Around Nuclear Installations.
Vol. II. TIARA, Vienna. pp. 89-103.
5D.

Wildung, R. E., H. Drucker, and F. H. F. Au.
1977.
"The Relationship of Microbial Proceses to the Fate of Transuranic Elements in
Soil." Presented at the Nevada Applied Ecology Group Symposium on
The Dynamics of Transuranics in Terrestrial and Aquatic Environments,

Gatlinburg, TN, October 5-7, 1976.

(This Report).

ADDITIONAL REFERENCE
Plant Panel.

1975.

Workshop on Environmental Research, Seattle,

Washington, November 12-14.

U. S. ERDA 76/134.

fallout from atmoEnvironmental plutonium (Pu) originates from two sources:
facilities.
spheric nuclear testing and emissions from nuclear fuel cycle
extensive weapons
Fallout from nuclear testing will likely decrease unless
from the nuclear
testing in the atmosphere is resumed, but future emissions
potential radiological
fuel cycle may increase as a result of Pu recycling. The
in the environment
toxicity and long half-life of Pu dictate that its behavior
be thoroughly understood.

, Oak Ridge, TN
*Environmental Sciences Division, Oak Ridge National Laboratory

**kSavannah River Ecology Laboratory, Aiken, SC

302
303

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