Stabilization of organic matter in temperate soils: mechanisms and their relevance under different soil conditions – a review

European Journal of Soil Science - Tập 57 Số 4 - Trang 426-445 - 2006
Margit von Lützow1, Ingrid Kögel‐Knabner1, Paula Fernandes1, Egbert Matzner1, Georg Guggenberger1, Bernd Marschner1, Heinz Flessa1
1a Lehrstuhl für Bodenkunde, Technische Universität München, Wissenschaftszentrum Weihenstephan, 85350 Freising, b Institut für Allgemeine und Spezielle Zoologie – Tierökologie, Justus Liebig Universität, Heinrich-Buff-Ring 26–32, 35392 Gießen, c Lehrstuhl für Bodenökologie, Universität Bayreuth, 95440 Bayreuth, d Institut für Bodenkunde und Pflanzenernährung, Universität Halle, Weidenplan 14, 06108 Halle, e Geographisches Institut, Ruhr-Universität, 44780 Bochum , and f Institut für Bodenkunde und Waldernährung, Universität Göttingen, Büsgenweg 2, 37077 Göttingen, Germany

Tóm tắt

Summary

Mechanisms for C stabilization in soils have received much interest recently due to their relevance in the global C cycle. Here we review the mechanisms that are currently, but often contradictorily or inconsistently, considered to contribute to organic matter (OM) protection against decomposition in temperate soils: (i) selective preservation due to recalcitrance of OM, including plant litter, rhizodeposits, microbial products, humic polymers, and charred OM; (ii) spatial inaccessibility of OM against decomposer organisms due to occlusion, intercalation, hydrophobicity and encapsulation; and (iii) stabilization by interaction with mineral surfaces (Fe‐, Al‐, Mn‐oxides, phyllosilicates) and metal ions. Our goal is to assess the relevance of these mechanisms to the formation of soil OM during different stages of decomposition and under different soil conditions. The view that OM stabilization is dominated by the selective preservation of recalcitrant organic components that accumulate in proportion to their chemical properties can no longer be accepted. In contrast, our analysis of mechanisms shows that: (i) the soil biotic community is able to disintegrate any OM of natural origin; (ii) molecular recalcitrance of OM is relative, rather than absolute; (iii) recalcitrance is only important during early decomposition and in active surface soils; while (iv) during late decomposition and in the subsoil, the relevance of spatial inaccessibility and organo‐mineral interactions for SOM stabilization increases. We conclude that major difficulties in the understanding and prediction of SOM dynamics originate from the simultaneous operation of several mechanisms. We discuss knowledge gaps and promising directions of future research.

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