CHAPTER 1 - THE PORTION OF ACTIVITY DEPOSITED
IN LOCAL FALLOUT
1. In recent years there has been some concern that DCPA (and
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 1,
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 £
the same, logically the latter procedure is preferable since patent,

ground roughness would have little if any effect on
activity deposited per unit area.
By accepting the
of Chapter 1, i.e., that a K-factor of 1930 be used
ment models, then implicity, procedure Number 2 for

ground roughness effects is to be used,

the amount of
recommendations
in damage assessaccounting for

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.)

II-5

Select target paragraph3