O. Ugedal et al., SOURCES OF VARIATION IN RADIOCESIUM LEVELS BETWEEN INDIVIDUAL FISH FROM A CHERNOBYL CONTAMINATED NORWEGIAN LAKE, Journal of Applied Ecology, 32(2), 1995, pp. 352-361
1. We evaluate sources of individual variation in Cs-137 Of Arctic cha
rr (Salvelinus alpinus) and brown trout (Salmo trutta) from a Norwegia
n lake contaminated by fall-out from the Chernobyl accident. Samples w
ere collected on 14 occasions between July 1986 and October 1989. 2. T
he relationship between Cs-137 concentration, and fish weight, age and
growth rate, changed with time. In 1986 the Cs-137 concentration in A
rctic charr was negatively correlated with age and positively correlat
ed with growth rate. Later, after a transition period, Cs-137 concentr
ation in Arctic charr became positively correlated with weight and age
, and negatively correlated with growth rate. The timing of this chang
e was associated with changes in prey relative to fish radioactivity.
3. From September 1987 and throughout the study, the increase in Cs-13
7 concentration with fish weight could be described by a power-functio
n with weight exponents of 0.39 and 0.11 for Arctic charr and brown tr
out, respectively. We could detect no diet changes with size in brown
trout, while Arctic charr showed a diet shift from zooplankton to zoob
enthos with increasing age and weight. This diet shift probably accoun
ted for the larger increase in Cs-137 concentration with weight in cha
rr than trout. 4. Variation in fish weight accounted for 29 and 11% of
the individual variation in Cs-137 concentration in Arctic charr and
brown trout, respectively. Most of the variation in caesium concentrat
ions can be attributed to size independent factors, of which individua
l variation in diet composition is suggested to be the most important
one. 5. Frequency distributions of Cs-137 concentration in fish were p
ositively skewed, leptokurtic and differed significantly from the norm
al distribution, but not from the log-normal distribution. Individual
variation in caesium concentration was rather large, and larger in Arc
tic charr than in brown trout, probably because of a wider niche utili
zation by Arctic charr than by brown trout. These large individual var
iations necessitate large sample sizes if representative values of Cs-
137 concentration for the populations shall be obtained.