by swimming upward. Because of the effect of gravity on particles, the soluble
and insoluble fractions would probably act as two independent systems as far
as concentration or dispersal processes are concerned.
In the waters of the open sea, the naturally-occurring trace elements zine,
cobalt, ruthenium, manganese, caesium, strontium, iodine, and possibly zirconjum and cerium are present for the most part in solution. The small amount

OF UPPER
: OF
OCLINE

COLLECTED 23
DAYS AFTER
SURFACE SHOT
—

“
Y,

5

COLLECTED 4 BAYS
AFTER OVER -WATER

jl--

SHOT

100

METERS

in solution plus colloid fraction from
and one from an over-water detonation

e over-water detonation, the total

he surface, decreased gradually at
face activity, and rose to a value
the upper edge of the thermocline.
t one-tenth of that at the surface.
rface was associated with particles,
f the activity was in the particulate
vity was associated with particles.
e matter at the surface is probably
he area contaminated with fallout
particulate activity at and in the
ue, to a large degree, to very small

hrough the thermocline because of
vould be present in fallout from the
> activity at the thermocline would
ynly approximately one-fourth that
illout area from the surface detonayn; thus the larger particles present
lepths below those sampled by the

ulate form are introduced into seasher because of their high solubility
sure as they sink through the water
xey may be precipitated as particles
in the sea or with accompanying
- inorganic particles. The particles,
i to be removed from the mixed
organisms tend to offset this effect

of natural iron occursin the colloidal and particulate form and may have associated with it a limited amount of manganese and zirconium. All the abovenamed elements except caesium, strontium and iodine, however, when introduced to the sea in fallout, would most probably be present in the particulate
form (36). The fallout elements strontium, caesium and iodine, which occur
mostly in the soluble form, were found in the least amount in plankton. In

contrast, the radioactive fission products with the least solubility, Zr® and
(‘el44, were present in plankton in the greatest amount (36, 7). LOWMAN (36)
reported that the non-fission-product radioelements zinc, cobalt, and iron were

present in plankton from one survey in approximately equal amounts of about:
24°% each and manganese at a level of less than one per cent. All of these
elements introduced as fallout would exist initially in the insoluble form.
The physical state of any given element in sea-water will depend upon
whether or not the solubility product of its least soluble compound has been
exceeded (2, 10), and precipitation will occur when it is exceeded. In order to
predict the form that a given radicelement will assume in sea-water, the ionic
activity of the compoundslikely to be present must be known. Very few data
are available concerning the activities of the ionic forms of the fission-product

elements in the sea. Limited information is available, however, for the neutron-

induced radicelements found in fallout from thermonuclear devices.
Precipitation of a radioelement in the sea will occur only when precipitation
of its stable element occurs normally or is induced by accompanying non-radioactive débris swept up into the fireball of the weapon at the time of detonation.
This débris at the Entwetok Test Site may be calcium compounds from the
islands and reefs, materials from nearby structures associated with the nuclear
devices or from the nuclear devices themselves, or salts from evaporated sea
water. Several of the abundant fission products belong to the rare-earth series,
and most of these elements are very insoluble in sea-water. In addition, seawater is probably naturally saturated with rare-earth elements, so that any

added material will be present in the particulate form (10).

Radioactive contamination may also occur in the sea in particulate form as
a result of another process which is neither precipitation nor coprecipitation,
but rather involves the adsorption of radioactive ions to organic detritus in the
sea water. This process may be distinguished from the adsorption of radioactive ions or particles on to microorganisms. Both organic detritus and
microorganisms have exposed polar groups with which transition elements
such as manganese, iron, cobalt, nickel, copper and zinc, and anions such as
zirconium, ruthenium, tungsten, neptunium, uranium, tellurium and molybdenum, may become complexed. A difference between organic detritus and
microorganismsis an increased tendency of the former to sink to the depth of
the sea, thus removing the radiocelements from the biosphere. However, for
the most part organic detritus probably sinks at a slower rate than particles
of calcium compounds, and would thus tend to be removed from the surface
waters at a slower rate than radioelements coprecipitated with calcium oxide
or scavenged by calcite.
117

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