Based on more recent knowledge, changing criteria, and further FIDLER develop-

ment, the FIDLER may prove to be of greater value than was believed originally.

For example, if a "level of no concern" is set within the detection range of

the FIDLER, the number of samples subjected to radiochemistry could be substan-

tially reduced if the FIDLER were used and hence there would be a resultant
reduction in analytical costs.
Mound Sampling

Certain studies present unique sampling requirements such as those associated
with blow-sand mounds.
Blow-sand mounds may constitute as much as 20-30% of

a study area.

The mound may be considered as composed of layers which have

been intermittently deposited by wind.
The structure is complicated by the
dynamic nature of the mound in that deposition and removal are coexistent.

Many mounds have been created or altered by animal activities.

The mound may

be an accumulator of windblown radionuclides; a knowledge of associated concen-

trations is necessary to a calculation of inventory.

The location and concen-

tration of radionuclides within the mound and the proximity of radionuclides
to the root zone are also important.

The Soils Element submitted a procedure for mound sampling to NAEG in March,
1974.
The procedure was developed such that simple or complex missions could

be satisfied. Procedures were submitted by other Elements, and an integrated
version of the proposed methods was used in the summer of 1974 in a pilot
study titled Mound Study #1. Profile samples were obtained from a series of

mounds and adjacent desert pavement in Area 11 and assayed by Ge(Li) spectrometric techniques for 241lam to predict the distribution of plutonium within
the mound.
Figure 1 presents one typical pair of mound and desert pavement

profiles.

It will be noted that in this mound, the surface of the surrounding

desert pavement is below the desert pavement datum found under the mound,

possibly indicating erosion of the surrounding desert pavement during and

after mound formation.
Further, radioactivities below the desert pavement
datum within the mound and those in the desert pavement surrounding the mound
correlate very well below the 2 cm depth.
Based on the data obtained, two
possible explanations for the observed 24lam distribution are (1) that the
radioactivity was deposited prior to mound formation and (2) that the mound
may have dynamically moved in the direction of the sampling point covering an
already contaminated surface with additional contaminated material.
A second
point to note is the higher radioactivity associated with the mound than that
associated with the surrounding desert pavement.
Since the mounds are formed
from a relatively narrow range of particles, it can be assumed that 241am and

consequently plutonium is associated with soil particles which fall within
that range.

It was concluded from Mound Study #1 that mounds are an important sink for

radioactivity; hence, their contribution to inventory may be important.

A second study related to mound sampling (Mound Study #2) was initiated in FY
1976 to determine the contribution of plutonium and 24lam in the mound to
total inventory.
Sampling and analysis are progressing; results are not
available at this time.

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