l2

Table 3

Comparison of Shipboard and Laboratory Analyses for MFP
d/min/g Ash
Sample No.

Type

TANEY

HASL

547
548

Tuna [ - Skin
- White Muscle

0.2
94

Oto.5
3.640.6

549
550
553

- Red Muscle
- Bone
Tune II - Skin

132
6.2
7

3.40.6
1.1t0.5
0,5t0.5

568

- White Muscle

69

2.30.6

554
555

- Red Muscle
- Bone

-2.4

3.50.5
1.4+0.5

63

Shark - Cartilage

45

11¢0.5

158
567

Shark - Cartilage
Remora - Entire

5
18

8t1.2
16+6.4

,

Although the activity level was too low for accurate radiochemical analysis, the
Sr?9 level in the edible portion was shown to be less than 2 percent of the permissible
level for this isotope. This estimate of hazard is of course based on the fish as the
only food intake.
|
The results obtained on individual tissues of fish taken on Troll upon analysis at
the Applied Fisheries Laboratory are shown in Appendix]. The Troll fish collection
included 19 flying fish, 6 shark, 3 yellowfin tuna and reef fishes from Truk, Guam,
Douglas Reef and Okinawa. Invertebrates and algae were also collected with the reef
fishes and on four occasions from floating objects at sea.

Values in d/min/g(wet) for samples of these organisms and for comparable

samples from other areas are also included in Appendix J. No correction has been
made for potassium. The following conclusions were drawn from these data:
l.

Values for plankton, fish, invertebrates and algae were usually several to

many times greater than comparable samples from Puget Sound, an area considered
to be free of fission product contamination,
Zz. The contamination was considerably less than at Bikini or Eniwetok, usually
by a factor of 10 to 20 or greater.
3.

Of the reef collections, the highest average values were obtained at Guam, the

lowest at Okinawa, with Douglas Reef (Parece Vela) and Truk intermediate.
HN nee ce

Probe Measurements

No significant measurements were made with the probe, since the activity levels
encountered were generally below the sensitivity of the instrument. In addition, operational difficulties allowed use of the probe for only small portions of the track. These
flaws in the experimental model can be corrected, and it is felt that the probe would be

of considerable value in assessing sea water activity shortly after a detonation.
Probe operations were complicated by the possibility of tangling if two cables
were over the side at the same time. Therefore, the probe had to be brought on deck
at each station and tow. This extra handling plus the relative fragility of the conducting
cable required considerable time and resulted in many cable failures.
Five men were required for the operation: one officer in phone contact with the
bridge and engine room regulated course and speed to keep the probe clear of the

Select target paragraph3