2.2.9 Co® Field Calibration. Exposures were made with @ well calibrated 4a, 200-curie
Co® source that had an effective energy of 1.2 Mev. The source consisted of two cylindrical
Co® pellets with a total height of 1.58 inches and a diameter of 0.39 inch. The pellets were gold

plated and sealed in two concentric monel capsules.

The source capsule was stored in a lead pig

and was forced up a monel metal tube by compressed air for use.
nel capsules and tube was 0.33 inch.

The total thickness of the mo-

Instruments were exposed on a horizontal wooden platform

3 inches belowthe level of the raised source and 2 feet above the lead pig.
The source was calibrated on site using Victoreen r-chambers that had 5~mm lucite caps.
These chambers were calibrated at NBS for use at 22C and 760 mm of pressure. Corrections
for pressure and temperature differences were applied to chamber readingsat the timeof calibration. Corrections for decay of the source were applied to calibration curves after the calibration was completed.

A 200-curie Co™ calibration curve for exposure rate versus distance is shown in Figure 2.6.
Calibrations for Shots Lacrosse and Cherokee were made using an 80-curie Co™ source of simiTABLE 2.4
Station
Series

STATION CONSTRUCTION

Material

ena

Diameter

Wall
Thickness

Height Above
Surface

inch

inch

ft

ramos)

Depth Below
Surface
ft

210.0

Aluminum

3

0.25

3

_

210.27!
10.30!
a .

Steel

8

0.45

2.5

6

210.23!
210.34!

Steel

8

0.45

2

1

213.0

Steel

4

0.30

4

4

113.0

Steel

3

0.25

5

—_

212.0

lar design used as a collimated source (Reference 3).

Cherokee because of capsule rupture.

This source was discarded after Shot

2.3 DATA REQUIREMENTS
To accomplish Project 2.1 objectives, gamma-radiation measurements were required at
surveyed distances from ground zero for each of six high-yield thermonuclear devices detonated
at Bikini Atoll.

It was necessary that these measurements should permit discrimination between

initial- and residual-gammaradiation so that a true measure of initial-gamma radiation could be
made.

Measurements of the residual-gamma exposure rate and decay rate were required at known
times for stations instrumented in a contaminated field, and after all shots to allow extrapolation
of residual-exposure measurements to times other than recovery time. For those stations at
which initial-gamma data were recorded, residual-field gamma exposure rate measurements
were required to allow for correction of the initial data to account for the effect of the residual-

gammafield.
The initial exposure values are accurate to within 30 percent. This figure is based on an
overall 20-percent accuracy of the NBS dosimeter for initial-gamma measurements in the energy
range from 115 kev to 10 Mev and in the exposure range from 1 to 50,000 r (Reference 3). The
variations in wall thickness and other possible station-shielding errors in shielding corrections
amounted to about 15 percent. The error in mutual shielding effects among the instruments as
21

Select target paragraph3