9.6 + 0.22 was computed for this area.

(Refer to Tech Note 2.21 for more information on this

ratio). The other ratio used for Cape Mixan, 5.3 + 0.2, was the ratio used for Yuma cleanup. (The
cleanup ratio was different than the ratio used for characterization because more data were

available for the later effort.)

Using these ratios and the IMP data, TRU values were calculated.

To get a 0.25 hectare estimate,

the average of four IMP readings forming a square was calculated since the IMP field-of-view
includes most of the surface. Using original data no 0.25 hectare average was estimated with TRU
activity greater than 40 pCi/g but based on final data, one 0.25 hectare was estimated to have a
TRU activity of 41 pCi/g. The final isopleths for the final TRU values for Cape Mixan are shown on
Figure 7-107 on the map of Sally.
Characterization - Subsurface

Subsurface investigation, as described in Section 6.9, was conducted in five different parts of the
island - Kickapoo, Yuma, Hustead, Yoke and Cape Mixan. The results will be discussed more fully
later in this section. Figures 7-99 through 7-102 show the sampling locations for these five regions
and also give the highest TRU value in each profile.
Cleanup Activities

The pilot soil removal for the cleanup project was done in the Kickapoo area (Section 6.6). The
initial results from the characterization analysis showed three 0.25 hectare to have greater than 40
pCi/g average TRU activity. To better define the surface boundary exceeding 40 pCi/g, a 12.5 m
grid was surveyed and additional IMP measuremets were taken in February 1978 for the area in
Kickapoo that had TRU activity estimated to be greater than 40 pCi/g. Isopleths of TRU activity
exceeding the 40 pCi/g level are shown in Figure 7-103 for both 12.5 m and 25 m grids, along with
the boundary resulting from the kriged estimates done on the 50 m grid data. Because the isopleths

shown for the 25 m grid and the 12.5 m grid were not significantly different, the isopleth for the 25
m grid was used to outline the area where soil removal was necessary.

In addition to more IMP measurements, more surface soil samples were collected prior to any earth
moving activities. This was done to verify that the ratio first calculated for Kickapoo was

appropriate since the original number was based on one soi] sample location. The additional results
did justify using the 6.16 TRU to 24lAm ratio, and therefore the fine grid TRU values were
ealculated using this ratio.
The subsurface data collected earlier indicated that more than one "6-inch" lift would be necessary

in certain spots. Figure 7-103 also shows the outlines of subsurface contamination.

Before any soil lifts were made, the vegetation in the cleanup area was removed in mid-March 1978.

Surface soil samples were again collected and the TRU to 24lAm ratio verified. After this

vegetation removal activity, different methods for soil removal were tried to compare their

effectiveness. As a result of this experimentation, the soil was greatly disturbed. The area was then

measured by the IMP to determine how this disturbance affected the surface TRU activity. The
mean TRU concentrations before any soil disturbance was 146 pCi/g and after soil disturbance was
154 pCi/g; both ealeulations are based on data from the same sixteen locations. These results reflect

no significant change in surface TRU activity due to soil disturbance.

:

After the first actual soil lift was complete, IMP measurements on a 25 m grid were taken and more
surface and subsurface soil samples were collected during the first part of April 1978. The surface
soil samples again verified the initial ratio and the subsurface soil results corroborated earlier
results and also indicated another pocket of high activity along the northwest beach line. The IMP
data showed that the majority of the area with TRU activity estimated above 40 pCi/g initially was
still above 40 pCi/g.
After the next soil lift, very little soil was left at Kickapoo so that the surface was mainly beach
rock. Only IMP data were collected in June 1978, following this lift, and these results showed two
areas still with high TRU activity, the same two areas that had shownhigh subsurfaceactivity. One
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