EXPERIMENTAL CONDITIONS

Probably one of the more significant factors affecting reported plant root
uptake of plutonium has been the highly artificial conditions under which
many of the experiments have been carried out. The uptake-translocation
experiments have frequently involved highly unusual conditions such as one
plant per 1 to 10 grams of soil along with growth and uptake periods of
several days to several weeks using seedlings.
Such experiments subject
the soil to intensive extraction of nutrients and all other elements,
including the transuranics.
In addition, such intensive short term cropping precludes growing the crops to maturity, thus excluding significant
plant parts such as grain, etc.
Generally, at the time such work was
carried out, there were very good reasons for performing the experiments
in the manner chosen. Caution must be taken in application of data
obtained from these experiments to more usual soil-plant systems.
It
should not be implied that such data are applicable to agricultural
systems.
For example, a review of the literature by Lipton and Goldin
(1976) led them to conclude that "plant concentration factors for plutonium are in the order of 10-4," However, most of the articles referred
to were reports of work where very high and unusual soil to plane ratios
were employed.
It will be shown later in this discussion that the concentration ratios are not in the order of 10-4, but range over many orders
of magnitude.
[t is most important that extrapolations not be made from
specialized plant root uptake experiments to field conditions which govern
introduction of plutonium and other transuranics into food chains via this
pathway.

Table 1.

Plutonium concentration ratios for plants grown in potted soil

(from Piant Panel, 1976).

Plant

Ladino clover

Range of CR's

Conditions

\

10°° to 10°"

In 120 kg of NTS soil;

70 nCi g~' soil; CR's

increased by seven times
in 5 years.

Alfalfa

10° to 10°

Straw

.
10_° to 10°

Barley

Grain

10° to 103

Soybean
Forage

Bean

In 3 kg of NTS soil; 0.6

-,
.
10_" to 10°

In 3 kg of NTS soil; 5 nCi
g-' soil; highest CR's
involve chelate treatment.

107

NTS soil; high-fired Pu

10 ® to lo *

Barley
Grain

Leaf

Grain

Leaf

> R

nci g™' soil; highest
CR's involve chelate
treatment.

omney

.
~

10

-s

oxide; 10 to 50 nCi g@! soil

Wheat
MAGNITUDE OF ROOT UPTAKE AND TRANSLOCATION

Rapporteur

’ Schulz
10° to 10 °

Pu-chloride and Pu-nitrate

10 > to 10 3

Pu-nitrate (77"Pu and

10 ® to 10 3

(77%pu at 0.5 wCt g?)

Barley
A Workshop on Environmental Research for Transuranic Elements was held at
Seattle, Washington, ih 1975. A group charged to discuss plant uptake of
transuranium elements was designated the Plant Panel and will be referenced
in this paper as "Plant Panel (1976)." The Panel listed data (Table 1) on
plant uptake where plants were grown in containers and efforts were made to
exclude foliar contamination.
The concentration ratios (plutonium in plant/

plutonium in soil) ranged from 10-8 to 10-3.

In addition to the plutonium

concentration ratios, the Panel also summarized data on americium concentration ratios (Table 2).
Here the range of concentration ratios was even
larger than that of the plutonium CR's.
The range of concentration ratios
reported wag 10-7? to 10+. These experiments were also carried out in containers and attempts were made to exclude foliar contamination. The most
striking feature of both the plutonium and americium concentration ratios
was the enormous range reported; that is, for root uptake and translocation,
and excluding foliar contamination, the range was 5 orders of magnitude for
plutonium and 8 orders of magnitude for the americium uptake.

322

Leaf and sten

Grain

10°”

239Pu) 10 ci gs},

Wildung

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