The study site comprises temporary and permanent grassland in areas in cent
ral and northern Sweden which were strongly affected by the Chernobyl fallo
ut in 1986. The aim of the study was to investigate the vertical migration
of radiocaesium from 1987 to 1995 in undisturbed soil profiles under field
conditions, as related to soil type and texture. The sampled sites differ i
n soil types and textures, i.e. six cultivated or semi-natural mineral soil
s (Dystrochrept, Haploboroll, Udorthents, Cryorthent and Haplocryod) and tw
o cultivated organic soils (Sulfihemists). The ground deposition of Cs-137
ranged from 14 to 184 kBq m-(2) (average 82). Cs-137-activities were measur
ed in cm-sliced, 25-cm-deep soil cores and in soil horizons of the entire s
oil profiles down to 0.7-1.0 m depth. The soil cores were collected on two
or three occasions between 1987 and 1995, and migration rates were calculat
ed based on the median depths. Grass samples were taken from the same locat
ions to measure the amount of Cs-137 transferred from soil to grass.
After eight years, most (50-92%) of the Cs-137 fallout was still present in
the upper 5 cm (median depth 2.3-5.1 cm), although considerable amounts ha
d migrated to deeper soil layers. Downward migration was most pronounced in
the organic soils and in the podzol where Cs-137 was found to about 50 cm
depth. Migration rates were in the range of 0.5-1.0 cm year(-1) for the fir
st year and thereafter 0.2-0.6 cm year(-1). The transfer of Cs-137 to grass
was highest in two gravely sandy loam soils in the mountain region, interm
ediate in two organic soils, and lowest in soils from the river and coastal
areas. (C) 1999 Elsevier Science Ltd. All rights reserved.