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Carbon and nitrogen recycling from microbial necromass to cope with C:N stoichiometric imbalance by priming. / Cui, Jun; Zhu, Zhenke; Xu, Xingliang et al.
In: Soil Biology and Biochemistry, Vol. 142, 107720, 01.03.2020.

Research output: Contribution to journalArticlepeer-review

HarvardHarvard

Cui, J, Zhu, Z, Xu, X, Liu, S, Jones, DL, Kuzyakov, Y, Shibistova, O, Wu, J & Ge, T 2020, 'Carbon and nitrogen recycling from microbial necromass to cope with C:N stoichiometric imbalance by priming', Soil Biology and Biochemistry, vol. 142, 107720. https://doi.org/10.1016/j.soilbio.2020.107720

APA

Cui, J., Zhu, Z., Xu, X., Liu, S., Jones, D. L., Kuzyakov, Y., Shibistova, O., Wu, J., & Ge, T. (2020). Carbon and nitrogen recycling from microbial necromass to cope with C:N stoichiometric imbalance by priming. Soil Biology and Biochemistry, 142, Article 107720. https://doi.org/10.1016/j.soilbio.2020.107720

CBE

Cui J, Zhu Z, Xu X, Liu S, Jones DL, Kuzyakov Y, Shibistova O, Wu J, Ge T. 2020. Carbon and nitrogen recycling from microbial necromass to cope with C:N stoichiometric imbalance by priming. Soil Biology and Biochemistry. 142:Article 107720. https://doi.org/10.1016/j.soilbio.2020.107720

MLA

VancouverVancouver

Cui J, Zhu Z, Xu X, Liu S, Jones DL, Kuzyakov Y et al. Carbon and nitrogen recycling from microbial necromass to cope with C:N stoichiometric imbalance by priming. Soil Biology and Biochemistry. 2020 Mar 1;142:107720. Epub 2020 Jan 17. doi: 10.1016/j.soilbio.2020.107720

Author

Cui, Jun ; Zhu, Zhenke ; Xu, Xingliang et al. / Carbon and nitrogen recycling from microbial necromass to cope with C:N stoichiometric imbalance by priming. In: Soil Biology and Biochemistry. 2020 ; Vol. 142.

RIS

TY - JOUR

T1 - Carbon and nitrogen recycling from microbial necromass to cope with C:N stoichiometric imbalance by priming

AU - Cui, Jun

AU - Zhu, Zhenke

AU - Xu, Xingliang

AU - Liu, Shoulong

AU - Jones, Davey L.

AU - Kuzyakov, Yakov

AU - Shibistova, Olga

AU - Wu, Jinshui

AU - Ge, Tida

N1 - Validated without post-print. Added without post-print and no response to repeated requests for version.

PY - 2020/3/1

Y1 - 2020/3/1

N2 - The impact of increasing amounts of labile C input on priming effects (PE) on soil organic matter (SOM) mineralization remains unclear, particularly under anoxic conditions and under high C input common in microbial hotspots. PE and their mechanisms were investigated by a 60-day incubation of three flooded paddy soils amended with13C-labeled glucose equivalent to 50–500% of microbial biomass C (MBC). PE (14–55% of unamended soil) peaked at moderate glucose addition rates (i.e., 50–300% of MBC). Glucose addition above 300% of MBC suppressed SOM mineralization but intensified microbial N acquisition, which contradicted the common PE mechanism of accelerating SOM decomposition for N-supply (frequently termed as “N mining”). Particularly at glucose input rate higher than 3 g kg−1 (i.e., 300–500% of MBC), mineral N content dropped on day 2 close to zero (1.1–2.5 mg N kg−1) because of microbial N immobilization. To cope with the N limitation, microorganisms greatly increased N-acetyl glucosaminidase and leucine aminopeptidase activities, while SOM decomposition decreased. Several discrete peaks of glucose-derived CO2 (contributing >80% to total CO2) were observed between days 13–30 under high glucose input (300–500% of MBC), concurrently with CH4 peaks.Such CO2 dynamics was distinct from the common exponential decay pattern, implicating the recycling and mineralization of 13C-enriched microbial necromass driven by glucose addition. Therefore, N recycling from necromass was hypothesized as a major mechanism to alleviate microbial N deficiency without SOM priming under excess labile C input. Compound-specific 13C-PLFA confirmed the redistribution of glucose-derived C among microbial groups, i.e., necromass recycling. Following glucose input, more than 4/5 of total 13C-PLFA was in the gram-negative and some non-specific bacteria, suggesting these microorganisms as r-strategists capable of rapidly utilizing the most labile C. However, their 13C-PLFA content decreased by 70% after 60 days, probably as a result of death of these r-strategists. On the contrary, the 13C-PLFA in gram-positive bacteria, actinomycetes and fungi (K-strategists) was initially minimal but increased by 0.5–5 folds between days 2 and 60. Consequently, the necromass of dead r-strategists provided a high-quality C–N source to the K-strategists. We conclude that under severe C excess, N recycling from necromass is a much more efficient microbial strategy to cover the acute N demand than N acquisition from the recalcitrant SOM.

AB - The impact of increasing amounts of labile C input on priming effects (PE) on soil organic matter (SOM) mineralization remains unclear, particularly under anoxic conditions and under high C input common in microbial hotspots. PE and their mechanisms were investigated by a 60-day incubation of three flooded paddy soils amended with13C-labeled glucose equivalent to 50–500% of microbial biomass C (MBC). PE (14–55% of unamended soil) peaked at moderate glucose addition rates (i.e., 50–300% of MBC). Glucose addition above 300% of MBC suppressed SOM mineralization but intensified microbial N acquisition, which contradicted the common PE mechanism of accelerating SOM decomposition for N-supply (frequently termed as “N mining”). Particularly at glucose input rate higher than 3 g kg−1 (i.e., 300–500% of MBC), mineral N content dropped on day 2 close to zero (1.1–2.5 mg N kg−1) because of microbial N immobilization. To cope with the N limitation, microorganisms greatly increased N-acetyl glucosaminidase and leucine aminopeptidase activities, while SOM decomposition decreased. Several discrete peaks of glucose-derived CO2 (contributing >80% to total CO2) were observed between days 13–30 under high glucose input (300–500% of MBC), concurrently with CH4 peaks.Such CO2 dynamics was distinct from the common exponential decay pattern, implicating the recycling and mineralization of 13C-enriched microbial necromass driven by glucose addition. Therefore, N recycling from necromass was hypothesized as a major mechanism to alleviate microbial N deficiency without SOM priming under excess labile C input. Compound-specific 13C-PLFA confirmed the redistribution of glucose-derived C among microbial groups, i.e., necromass recycling. Following glucose input, more than 4/5 of total 13C-PLFA was in the gram-negative and some non-specific bacteria, suggesting these microorganisms as r-strategists capable of rapidly utilizing the most labile C. However, their 13C-PLFA content decreased by 70% after 60 days, probably as a result of death of these r-strategists. On the contrary, the 13C-PLFA in gram-positive bacteria, actinomycetes and fungi (K-strategists) was initially minimal but increased by 0.5–5 folds between days 2 and 60. Consequently, the necromass of dead r-strategists provided a high-quality C–N source to the K-strategists. We conclude that under severe C excess, N recycling from necromass is a much more efficient microbial strategy to cover the acute N demand than N acquisition from the recalcitrant SOM.

KW - Soil carbon

KW - Priming effects

KW - Glucose mineralization

KW - Compound-specific C-13-PLFA analysis

KW - Necromass recycling

KW - Stoichiometric imbalance

U2 - 10.1016/j.soilbio.2020.107720

DO - 10.1016/j.soilbio.2020.107720

M3 - Article

VL - 142

JO - Soil Biology and Biochemistry

JF - Soil Biology and Biochemistry

SN - 0038-0717

M1 - 107720

ER -