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Stable isotopes were used to study sulfur dynamics in forest soils of the Czech Republic (Central Europe), one of the most polluted regions in the world. δ 34 S ratios were determined in vertical soil profiles in 18 small forested catchments covering a wide range of pollution levels from 8.8 to 78.8 kg of S ha - 1 yr - 1 . All sites exhibited an increase in δ 34 S ratios from topsoil to mineral soil, regardless of the distance from major point sources of atmospheric pollution. Of these 18 sites, 15 sites were characterized by a smooth positive isotope signal with the highest δ 34 S in the deepest level sampled. The remaining three sites had a δ 34 S maximum in the second deepest horizon. With increasing soil depth, the positive δ 34 S signals accompanied a negative S concentration gradient. Our findings constrain the relative roles of various mechanisms of sulfur isotope redistribution in the soil depth profile. Even at extremely high atmospheric deposition (>70 kg of S ha - 1 yr - 1 ) sulfur appears to be cycled through an organic S pool in the forest soil.
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Novák et al. (1996) studied this question.
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