CHAPTER 1 ~ THE PORTION OF ACTIVITY DEPOSITED
IN LOGAL FALLOUT
%In recent years there has been some concern that DCPA (and
1.
other) estimates of the fallout hazard that would be associated with

a nuclear war may be excessively high. The basis for this concern
was that the fallout models used in calculating this hazard were
thought to seriously over-predict the amount of the radioactivity

deposited in local fallout.

According to the discussions of Chapter i,

this concern is not justified.

Specifically,

the K-factor value of

2000 (R/hr)/(kt/sq mile), which has been in general usage, varies

from the figure of 1930 recommended in the report by the Subcommittee
by a small percentage.
2.
Past procedures for accounting for reduction in the ambient
radiation levels attributable to ground roughness (unevenness in

terrain features) have been either:
(1) in effect reducing the amount
of radioactivity (and consequently R/hr at any given time) assumed
to be associated with a particular weapon's fallout pattern; or
(2) assuming that personnel or other objects of interest, such as
crops or livestock, receive some protection because of this ground

roughness,

Although the net result of either method of treatment is

the same, logically the latter procedure is preferable since patently
ground roughness would have little if any effect on the amount of

activity deposited per unit area.

By accepting the recommendations

of Chapter 1, i.e., that a K-factor of 1930 be used in damage assessment models, then implicity, procedure Number 2 for accounting for
ground roughness effects is to be used.
This means, however, that when damage assessment of nuclear

radiation effects from a hypothetical attack on personnel or things in

the open is performed, an allowance for ground roughness protection
must be made.
Unless a specific evaluation of this ground roughness
for the condition of interest is available, an average PF of 4/3
should be assumed.

3.

The monitoring instruments of DCPA correctly read (assuming

proper calibration of course) the ambient dose rates, and no instrument
correction factor (as was necessary for older instrument designs) is

required.
(The test data on which the Subcommittee's recommendations
were based largely came from these old instruments and have been

adjusted, by using a multiplying factor of 4/3, to eliminate the
instrument response factor.)

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