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Soil C and N availability determine the priming effect: microbial N mining and stoichiometric decomposition theories

Ruirui ChenState Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008 ChinaMehmet ŞenbayramInstitute of Applied Plant Nutrition Georg‐August University Goettingen Goettingen 37075 GermanySergey BlagodatskyInstitute for Plant Production and Agroecology in the Tropics and Subtropics, University of Hohenheim, Stuttgart, 70593 GermanyOlga MyachinaInstitute of General and Inorganic Chemistry Tashkent 100170 UzbekistanKlaus DittertInstitute of Plant Nutrition and Soil Science Christian‐Albrecht University Kiel Kiel 24118 GermanyXiangui LinState Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008 ChinaEvgenia V. BlagodatskayaInstitute of Physicochemical and Biological Problems in Soil Science Russian Academy of Sciences Institutskaya 2 Pushchino 142290 RussiaYakov KuzyakovDepartment of Agricultural Soil Science Georg‐August University of Göttingen Göttingen 37077 Germany
2013en
ABI

Annotatsiya

The increasing input of anthropogenically derived nitrogen (N) to ecosystems raises a crucial question: how does available N modify the decomposer community and thus affects the mineralization of soil organic matter (SOM). Moreover, N input modifies the priming effect (PE), that is, the effect of fresh organics on the microbial decomposition of SOM. We studied the interactive effects of C and N on SOM mineralization (by natural (13) C labelling adding C4 -sucrose or C4 -maize straw to C3 -soil) in relation to microbial growth kinetics and to the activities of five hydrolytic enzymes. This encompasses the groups of parameters governing two mechanisms of priming effects - microbial N mining and stoichiometric decomposition theories. In sole C treatments, positive PE was accompanied by a decrease in specific microbial growth rates, confirming a greater contribution of K-strategists to the decomposition of native SOM. Sucrose addition with N significantly accelerated mineralization of native SOM, whereas mineral N added with plant residues accelerated decomposition of plant residues. This supports the microbial mining theory in terms of N limitation. Sucrose addition with N was accompanied by accelerated microbial growth, increased activities of β-glucosidase and cellobiohydrolase, and decreased activities of xylanase and leucine amino peptidase. This indicated an increased contribution of r-strategists to the PE and to decomposition of cellulose but the decreased hemicellulolytic and proteolytic activities. Thus, the acceleration of the C cycle was primed by exogenous organic C and was controlled by N. This confirms the stoichiometric decomposition theory. Both K- and r-strategists were beneficial for priming effects, with an increasing contribution of K-selected species under N limitation. Thus, the priming phenomenon described in 'microbial N mining' theory can be ascribed to K-strategists. In contrast, 'stoichiometric decomposition' theory, that is, accelerated OM mineralization due to balanced microbial growth, is explained by domination of r-strategists.

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