3C Radionuclides in Biota
Günter Kanisch
vTI, Johann Heinrich von Thünen-Institute, Germany
3C.1 Introduction
The biota of the Baltic Sea received the most
significant contribution to their radionuclide
levels following the Chernobyl accident in
1986, predominantly in the form of 137 Cs and
134 Cs. The ratio 134 Cs/ 137 Cs in Baltic biota
agreed very well with that of the Chernobyl
fallout. High trophic level species, including
predators such as cod and pike, showed the
highest 137 Cs levels, but there was some delay
in reaching their maximum values after 1986,
when compared to trends in seawater. In the
long-term, 137 Cs time trends in biota closely
follow the trends in seawater.
Levels of radionuclides in marine biota are
linked to the corresponding levels in seawater
and sediments, via accumulation through
food chains. The complexity of food chains
increases with the trophic level of the species
considered. Fish, the biota type in the Baltic
Sea most important for human consumption,
accumulate most of their radionuclides from
food, not from water. Within the existing box
model (see Chapter 4), which is also used
for describing activity concentrations in biota,
however, the simpler concentration factor
concept is applied. This relates the biota
activity concentrations directly to those of
seawater, which is the simplest approximation
to a food chain sub-model. Concentration
factors specific to the different model boxes
are derived from measured data. Results
of model predictions based on estimated
concentration factors are included in the
following summary where appropriate.
In this report, the evaluation of biota data
is restricted to fish and the bladder wrack
Fucus vesiculosus, which is a well established
biological indicator for radionuclides.
3C.2 Material
The number of biota samples collected
annually by the MORS-PRO group decreased
slightly through the sampling period 1999-
2006 from about 120 initially to about 90
ultimately. Over the whole period the numbers
of samples collected were 615 for fish, 126
for Fucus vesiculosus, and 102 for benthic
animals.
Fish flesh samples were measured from the
marine species : herring (138), cod (166) and
whiting (3), of the round fish; and flounder (68)
and plaice (24), of the flat fish.
Fish flesh sample numbers were measured
from the freshwater species : Pike (48) and
perch (6).
Additionally 45 herring samples were analysed
examining their “edible parts” (fish without
head and entrails).
The main artificial radionuclides measured
in biota during the assessment period were:
137 Cs, 90 Sr, 239 24 °Pu and 241 Am in fish, and "Tc
in Fucus vesiculosus.
3C.3 Use of a box model
for comparison with measured data
Trends for the activity values of 137 Cs and
90 Sr may be also simulated by using the
box model described briefly in Chapter 4.
Because 137 Cs showed a sharp peak in
seawater concentrations in 1986 (HELCOM
1995), a small sub-model for fish is included
in the model, which allows the fish to take up
and excrete the activity with an appropriate
biological half-life (250 days), thereby
transforming the sharp seawater peak into a
smooth increase in fish and a slightly delayed
decrease after the peak.
Concentration factors updated from the
MORS-PRO database are required for this
purpose. The results of the consequent
estimations are included in the next section.
3C.4 Results and discussion
3C.4.1 Concentration factors
Because of area-dependent significant