The leveling device (not shown in the schematic) consists of polyethylene tubing extended
from the bottom of the column to a Y-tube above the paper pulp in the column. This prevents

the column from running dry during the collection period.
3
3.1

PREPARATION AND ANALYSIS OF COLLECTOR
Preparation

The ion-exchange column is packed with a triple filter consisting of paper pulp, anion exchange resin, and cation exchange resin. The paper pulp is Whatman No. 41 filter paper blended
in a Waring blender with distilled water. The anion exchange resin, IRA 400 Amberlite resin,
is used throughout this paper. This resin is prepared by an aqueous and nonaqueous extraction
of the commercial product followed by conversion to the chloride form and thorough washing
with distilled water. Dowex 50 x 16 is used as the cation exchange resin. This resin is treated
by an aqueous and nonaqueous extraction, converted to the hydrogen form, and washed with
distilled water.
A glass wool plug is added to the bottom of each column and cation exchange resin, anion

exchange resin, and paper pulp are added in this order. Approximately 3 in. or 50 ml of wet

settled resin and 1 in. of paper pulp are packed into an ion-exchange columnfilled with distilled water. Care is taken to prevent the formation of air pockets.
3.2

Care of Collector
During dry periods the funnel is rinsed and policed every three days. At the end of the

exposure period, any residue on the funnel is washed into the column with water.
3.3

Analysis

cm

The total activity may be determined by ashing the paper pulp and resin, individual isotopes may be eluted, or the three absorbents may be separated for gamma spectral analysis

and later chemical analysis. The data for total beta activity in this report was obtained by

ashing the absorbents and counting the residue. The Sr®, Sr®®, and Ba? data were obtained
by chemical separation! of these isotopes from the ash.

4

FALLOUT IN NEW YORK CITY (JUNE TO DECEMBER 1957)
Table 1 summarizes the Sr®, Sr®®, and Ba™° activities found in fallout in New York City

from June to December 1957 by the ion-exchange fallout collection system. The total beta

activity level, counted approximately 14 days after the end of each sampling month, decreased

from a high of 163 mc/sq miin July to a low of 46.4 mc/sq mi in November. A rise in activity
to 81 mc/sq mi occurred in December, probably due to the announced Russiantests in
November.

5

EFFICIENCY OF COLLECTION UNIT
The efficiency of the ion exchange fallout collection unit was measured by the following

methods:

1. Per cent of activity in effluent: The effluent from the collector during the monthly exposure was retained in a covered polyethylene pail. This solution was evaporated and the

residue analyzed for total beta activity. In all cases the activity found was less than 5 per cent
of the total activity of each unit. No marked discrimination of isotopes was found in the ef-

fluent.
2. Collector comparison: During the six month period, duplicate units of the following
description were exposed side by side: (1) funnel and column containing the three filtering

media, (2) funnel and column containing no filtering medium, and (3) open-potcollectors.

Figure 2 gives the total beta activity for each collection device plotted against the counting
date. Each point represents the collection from a month. From these data it is evident that the
funnel and resin column method of collecting fallout is equivalent to the pot method. Table 2

357

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