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Nitrogen, organic carbon and sulphur cycling in terrestrial ecosystems: linking nitrogen saturation to carbon limitation of soil microbial processes
Authors:Ji?í Kopá?ek  Bernard J Cosby  Christopher D Evans  Jakub Hru?ka  Filip Moldan  Filip Oulehle  Hana ?antr??ková  Karolina Tahovská  Richard F Wright
Institution:1. Biology Centre AS CR, Institute of Hydrobiology, Na Sádkách 7, 37005, ?eské Budějovice, Czech Republic
2. Centre for Ecology and Hydrology, Deiniol Road, Bangor, LL57 2UW, UK
3. Department of Environmental Science, University of Virginia, Charlottesville, VA, 22904, USA
4. Czech Geological Survey, Klárov 3, 11821, Prague 1, Czech Republic
5. IVL Swedish Environmental Research Institute, Box 53021, 40014, Gothenburg, Sweden
6. Department of Ecosystem Biology, University of South Bohemia, Brani?ovská 31, 37005, ?eské Budějovice, Czech Republic
7. Norwegian Institute for Water Research, Gaustadalleen 21, 0349, Oslo, Norway
Abstract:Elevated and chronic nitrogen (N) deposition to N-limited terrestrial ecosystems can lead to ‘N saturation’, with resultant ecosystem damage and leaching of nitrate (NO3 ?) to surface waters. Present-day N deposition, however, is often a poor predictor of NO3 ? leaching, and the pathway of the ecosystem transition from N-limited to N-saturated remains incompletely understood. The dynamics of N cycling are intimately linked to the associated carbon (C) and sulphur (S) cycles. We hypothesize that N saturation is associated with shifts in the microbial community, manifest by a decrease in the fungi-to-bacteria ratio and a transition from N to C limitation. Three mechanisms could lead to lower amount of bioavailable dissolved organic C (DOC) for the microbial community and to C limitation of N-rich systems: (1) Increased abundance of N for plant uptake, causing lower C allocation to plant roots; (2) chemical suppression of DOC solubility by soil acidification; and (3) enhanced mineralisation of DOC due to increased abundance of electron acceptors in the form of ${{\text{SO}}_{ 4}}^{ 2-}$ SO 4 2 ? and NO3 ? in anoxic soil micro-sites. Here we consider each of these mechanisms, the extent to which their hypothesised impacts are consistent with observations from intensively-monitored sites, and the potential to improve biogeochemical models by incorporating mechanistic links to the C and S cycles.
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