Soil recalcitrant but not labile organic nitrogen mineralization contributes to microbial nitrogen immobilization and plant nitrogen uptake

Author:

Chen Shending123ORCID,Elrys Ahmed S.1456ORCID,Yang Wenyan12,Du Siwen2,He Mengqiu2,Cai Zucong2,Zhang Jinbo1246,Müller Christoph367ORCID

Affiliation:

1. School of Breeding and Multiplication Hainan University Sanya China

2. School of Geography Nanjing Normal University Nanjing China

3. Institute of Plant Ecology Justus‐Liebig University Giessen Giessen Germany

4. College of Tropical Agriculture and Forestry Hainan University Haikou China

5. Soil Science Department, Faculty of Agriculture Zagazig University Zagazig Egypt

6. Liebig Centre for Agroecology and Climate Impact Research Justus Liebig University Giessen Germany

7. School of Biology and Environmental Science and Earth Institute University College Dublin Dublin Ireland

Abstract

AbstractSoil organic nitrogen (N) mineralization not only supports ecosystem productivity but also weakens carbon and N accumulation in soils. Recalcitrant (mainly mineral‐associated organic matter) and labile (mainly particulate organic matter) organic materials differ dramatically in nature. Yet, the patterns and drivers of recalcitrant (MNrec) and labile (MNlab) organic N mineralization rates and their consequences on ecosystem N retention are still unclear. By collecting MNrec (299 observations) and MNlab (299 observations) from 57 15N tracing studies, we found that soil pH and total N were the master factors controlling MNrec and MNlab, respectively. This was consistent with the significantly higher rates of MNrec in alkaline soils and of MNlab in natural ecosystems. Interestingly, our analysis revealed that MNrec directly stimulated microbial N immobilization and plant N uptake, while MNlab stimulated the soil gross autotrophic nitrification which discouraged ammonium immobilization and accelerated nitrate production. We also noted that MNrec was more efficient at lower precipitation and higher temperatures due to increased soil pH. In contrast, MNlab was more efficient at higher precipitation and lower temperatures due to increased soil total N. Overall, we suggest that increasing MNrec may lead to a conservative N cycle, improving the ecosystem services and functions, while increasing MNlab may stimulate the potential risk of soil N loss.

Funder

National Natural Science Foundation of China

China Scholarship Council

Publisher

Wiley

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