wAbstract
@To determine the dominant processes controlling nitrogen (N)
dynamics in soils and increase insights into soil N cycling from
nitrogen isotope (Β15N) data, patterns of 15N
enrichment in soil profiles were compiled from studies on tropical,
temperate, and boreal systems. The maximum 15N enrichment
between litter and deeper soil layers varied strongly with mycorrhizal
fungal association, averaging 9.6}0.4ρ in ectomycorrhizal systems
and 4.6}0.5ρ in arbuscular mycorrhizal systems. The 15N
enrichment varied little with mean annual temperature, precipitation,
or nitrification rates. One main factor controlling 15N
in soil profiles, fractionation against 15N during
N transfer by mycorrhizal fungi to host plants, leads to 15N-depleted
plant litter at the soil surface and 15N-enriched nitrogen
of fungal origin at depth. The preferential preservation of 15N-enriched
compounds during decomposition and stabilization is a second important
factor. A third mechanism, N loss during nitrification and denitrification,
may account for late 15N enrichments with depth in
less N-limited forests and may account for soil profiles where
maximum Β15N is at intermediate depths. Mixing among
soil horizons should also decrease differences among soil horizons.
We suggest that dynamic models of isotope distributions within
soil profiles that can incorporate multiple processes could provide
additional information about the history of nitrogen movements
and transformations at a site.
Keywords: Nitrogen isotopes; Soil horizons; Isotopic fractionation;
Modeling; Mycorrhizal fungi; Soil mixing; Denitrificationx
Introduction
Methods
@Analytical and computational solutions of 15N
enrichment patterns in soil profiles
Results
Discussion
@Climate
@Nitrification and denitrification
@Mycorrhizal fractionation
@Fractionation during decomposition
@Soil fauna, soil foodwebs, bioturbation, and disturbance
@Synthesizing the processes influencing soil Β15N into
a conceptual model
Conclusion
Acknowledgments
References