The turnover of radioactive caesium was studied experimentally and the
oretically in a forested catchment that was covered by snow during the
wet deposition of radioactive nuclides from the Chernobyl accident. T
he study spans from 1 week before to 8 years after the deposition even
t. A fraction of the catchment is covered by a mire (16%). From the ed
ge of the mire a stream channel runs to the outlet of the catchment. T
wo phases of decreasing activity concentration in the stream water wer
e found in addition to a positive influence of runoff on the activity
concentration in the stream. The half-lives for Cs-137 in the stream w
ater corresponding to the early and the later phase were estimated by
non-linear regression to be 6.5 days and 4 years, respectively. During
the first phase, which corresponded to the initial snow melt in 1986,
6.8% of the deposition was lost from the catchment, whereas the slow
secondary loss during the following 8 years was 1.8%. The main contrib
ution to the yearly discharge of Cs-137 occurred during spring and aut
umn when the areal contribution to saturated surface runoff was highes
t. The remaining deposition in soil a few years after the fallout was
significantly lower in the mire than in the surrounding forest. By usi
ng the calculated activity concentration of Cs-137 in the stream water
together with the remaining deposition in the different biotopes and
information on stream flow for the catchment it was concluded that the
loss originated from the mire. During the initial phase 44% of the de
position was lost from the mire, and during the following years the ye
arly loss was 30% from the fraction that constantly undergoes saturate
d surface runoff and 2% from the drier fractions of the mire. Until th
e end of the study it was not possible to demonstrate any loss from th
e recharge areas (podzol and cambisol soils), which means that physica
l decay will govern the decrease in activity in these areas. (C) 1997
Elsevier Science B.V.