weighted average of the appropriate elemental mass attenuation coefficients. The second method

used was to directly measure the attenuation of 60 keV gamma rays from a 241

known thickness of soil

am source through a

The chemical analysis showed that the primary component of Enewetak soil is calcium carbonate
with calcium contributing approximately 30-40% by weight, oxygen approximately 40-50% by
weight, and carbon 10-12% by weight. There were a number of trace elements also identified; the
most significant was magnesium which contributed approximately 1-2% by weight. Several trace
elements such as sodium, strontium, chlorine and sulfur contributed a few tenths of a percent. The

other trace elements generally contributed less than a tenth of a percent, with only a few

exceptions. In one area on Mary both samples contained approximatey 4.5% iron. Iron also
contributed approximately 1% by weight in one area on Enewetak. For more than half the samples,
however, iron only contributed a few hundredths of a percent. Silicon and aluminum, which are two

primary components of continental soil, were present in only trace amounts in the Enewetak soil.

To help insure that no significant elements were missed in the chemical analysis, 20 samples were

analyzed through emission spectroscopy.

This analysis showed that nothing of significance was

missed in the chemical analysis. The soil samples were also analyzed for organie content. Although
the organic content varied from 0.5% to 25% by weight, most samples were in the range from 1% to

8% with an average of approximately 4% for all samples.

The in situ or wet soil mass attenuation coefficient for each of the 124 samples were obtained using
the elemental plus organic analysis combined with the in situ soil moisture measured at each
location with the nuclear moisture gauge. Elemental mass attenuation coefficients were based on
National Bureau of Standards (NBS) cross section data.* The mass attenuation coefficient for
organic material was estimated by using the value derived for cellulose. The results are summarized
in Figure B-22-4. The average value obtained was 0.333 + 0.12 em2/g. The average value for the
dry, organic free component was 0.365 em“/g compared to 0.37 em“/g for pure calcium carbonate.
Eleven of the samples sent for chemical analysis were split with half of the sample going to Las
Vegas for direct attenuation measurements. These samples were from 11 of the 12 locations on

Janet

where

sand-cone

comparisons

were

performed.

For

each

sample,

approximately 12 em in diameter by 2.5 em thick were filled with soil.

two

petri

dishes

Rocks greater than

approximately 1 em were not included. Otherwise, the samples were representative of the in situ

soil including organic material, roots and small aggregate. Soil was packed into the petri dish to
provide a density typical of the in situ densities which were measured at Enewetak--typically

1.4-1.6 g/em3, The volume of each petri dish was obtained by weighing the amount of water
required to fill the dish.
The attenuation of gamma rays of a given energy through a given medium is given by
N = Noes

p/p

py.

By measuring the net photopeak counts through an empty petri dish (Ng), the net photopeak counts

through the dish full of soil (N), the soil density within a given petri dish ( p ) and the soil thickness

(x), the soil mass attenuation coefficient (u/p) can be determined. Three independent
measurements were made for each of the 11 soil samples —- one with each of the petri dish samples
separately and one for both petri dishes stacked together. A115
Ci 241 am source was placed
approximately 50 em in front of a side-looking coaxial high purity germanium detector. Table

B-22-3 gives the average of the three measurements for each of the 11 samples. Also shown are the
results obtained from the soil sample analysis for each of the samples. As can be seen, the two
approachesyield results which agree quite well with each other.

In addition to the 11 Enewetak samples, three soil samples obtained near Las Vegas were also
analyzed in the same manner. The results for these samples are also shown in Table B-22-3. It can

be seen that the mass attenuation coefficient for Las Vegas soil is significantly different from that
for Enewetaksoil.

*Photon Cross Sections, Attenuation Coefficients, and Energy Absorption Coefficients from 10 keV

to 100 GeV (NSRDS-NBS29), 1969.

B-22-3

Select target paragraph3