Soil organic matter turnover: Global implications from δ13C and δ15N signatures

The turnover and residence time of carbon (C) and nitrogen (N) in soil is a fundamental parameter reflecting the rates of soil organic matter (SOM) transformation and the contribution of soils to greenhouse gases fluxes. Based on the global database of the stable isotope composition of C (δ13C) and N (δ15N) depending on soil depth (171 profiles), we assessed С and N turnover and related them to climate, biome types and soil properties. The 13C and 15N discrimination between the litter horizon and mineral soil was evaluated to explain the key processes of litter transformation. The 13C and 15N discrimination by microbial utilization of litter and SOM, as well as the continuous increase of δ13C and δ15N with depth, enabled to assess C and N turnover within SOM. N turnover was two times faster than that of C, which reflects i) repeated N recycling by microorganisms accelerating N turnover, ii) C loss as CO2 and input of new C atoms to cycling, which reduces the C turnover within soil, and iii) generally slower turnover of N free persistent organic compounds (e.g. lignin, suberin, cellulose) compared to the N containing compounds (e.g. amino acids, ribonucleic acids). An increase in temperature and precipitation accelerated C and N turnover because: i) higher microbial activity and SOM decomposition rate, ii) larger soil moisture and fast diffusion of dissolved organics towards exoenzymes, iii) downward transport of 13C-enriched organic matter (e.g. sugars, amino acids), and iii) leaching of 15N-depleted nitrates from the topsoil into subsoil and losses from the whole soil profile. Temperature accelerates SOM turnover stronger than precipitation. The temperature increase by 10 °C accelerates the C and N turnover for 40 %. SOM turnover is boosted by decreasing C/N ratio because: i) SOM with a high C/N ratio originated from litter is converted to microbially-derived SOM in mineral soil characterized by a low C/N ratio; ii) litter with a low C/N ratio is decomposed faster than litter with a high C/N; iii) microbial carbon-use efficiency increases with N availability. The biome type affects SOM decomposition by i) climate: slower turnover under wet and cold conditions, and ii) by litter quality: faster utilization of leaves than needles. Thus, the fastest C turnover is common under evergreen forests and the lowest under mixed and coniferous ones, whereas temperature and C/N ratio are the main factors controlling SOM turnover. Concluding, the assessment of SOM turnover by δ13C and δ15N approach showed two times faster N turnover compared to C, and specifics of SOM turnover depending on the biomes as well as climate conditions. © 2023 Elsevier B.V.

Authors
Soldatova E. , Krasilnikov S. , Kuzyakov Y.
Publisher
Elsevier B.V.
Language
English
Status
Published
Number
169423
Volume
912
Year
2024
Organizations
  • 1 Center for Isotope Biogeochemistry, Institute of Environmental and Agricultural Biology (X-BIO), University of Tyumen, 6 Volodarskogo Street, Tyumen, 625003, Russian Federation
  • 2 Laboratory of Mass Transport, Geological Institute of the Russian Academy of Sciences, 7с1 Pyzhevskiy Pereulok, Moscow, 119017, Russian Federation
  • 3 Department of Land Surveying & Geo-Informatics, Research Centre for Deep Space Explorations, The Hong Kong Polytechnic University, ZN601, 6/F, Phase 8, 181 Chatham Road South, Kowloon, Hong Kong
  • 4 Department of Soil Science of Temperate Ecosystems, Department of Agricultural Soil Science, University of Goettingen, 2 Büsgenweg, Göttingen, 37077, Germany
  • 5 Peoples Friendship University of Russia (RUDN University), 6 Miklukho-Maklaya Street, Moscow, 117198, Russian Federation
  • 6 Institute of Environmental Sciences, Kazan Federal University, Kazan, 420049, Russian Federation
Keywords
Isotope fractionation; Isotopic approaches; Natural abundance; Soil depth profile; Stable isotopes; Turnover and recycling
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