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Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients. / Peduru Hewa, Jeewani; Van Zwieten, Lukas; Zhu, Zhenke et al.
In: Soil Biology and Biochemistry, Vol. 160, 01.09.2021.

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Peduru Hewa, J, Van Zwieten, L, Zhu, Z, Ge, T, Guggenberger, G, Luo, Y & Xu, J 2021, 'Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients', Soil Biology and Biochemistry, vol. 160. https://doi.org/10.1016/j.soilbio.2021.108312

APA

Peduru Hewa, J., Van Zwieten, L., Zhu, Z., Ge, T., Guggenberger, G., Luo, Y., & Xu, J. (2021). Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients. Soil Biology and Biochemistry, 160. https://doi.org/10.1016/j.soilbio.2021.108312

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MLA

VancouverVancouver

Peduru Hewa J, Van Zwieten L, Zhu Z, Ge T, Guggenberger G, Luo Y et al. Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients. Soil Biology and Biochemistry. 2021 Sept 1;160. Epub 2021 Jun 1. doi: 10.1016/j.soilbio.2021.108312

Author

Peduru Hewa, Jeewani ; Van Zwieten, Lukas ; Zhu, Zhenke et al. / Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients. In: Soil Biology and Biochemistry. 2021 ; Vol. 160.

RIS

TY - JOUR

T1 - Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients

AU - Peduru Hewa, Jeewani

AU - Van Zwieten, Lukas

AU - Zhu, Zhenke

AU - Ge, Tida

AU - Guggenberger, Georg

AU - Luo, Yu

AU - Xu, Jianming

PY - 2021/9/1

Y1 - 2021/9/1

N2 - Iron (Fe) oxides regulate soil organic carbon (C) content via balancing C processes of stabilization and mineralization. However, abiotic and biotic mechanisms are involved in stabilization (e.g., by adsorption and/or coprecipitation) and decomposition (e.g., by shifting the microbial community) of paddy soil rich in iron oxides remains poorly understood. We examined the mineralization and stabilization of maize-straw-derived C (δ13C =5000‰), soil priming effects (PE), and soil microbial community structure in four paddy soils, along with Fe oxide concentrations gradient ranging from 13.7 to 55.8 g kg− 1 soil (Fe-13, Fe-25, Fe-42, and Fe-55). The paddy soil with the highest Fe content (Fe-55) stabilized 20.5 mg 13C kg− 1 soil of the maize-straw-derived C, being significantly greater (P < 0.05) than Fe-13 (5 mg 13C kg− 1 soil). The high C:Fe molar ratio of Fe-55 suggests the main pathway of stabilizing the maize-straw-derived C via co-precipitation as Fe-OM. Larger stabilization in Fe55 led to less CO2 emission from maize and SOM, e.g., Fe-55 had 12–16% lower straw mineralization and 8–11% lower PE than Fe-13 during the first 7 days of incubation. Random forest analysis further revealed that Proteobacteria and Actinobacteria (the keystone species, i.e., Gaiella) gave the largest contribution to maize-straw mineralization and PE, while microbial diversity and some microorganisms featured with filamentous hyphae contributed to C stabilization. This study confirmed that the concentration of Fe oxide in paddy soils plays a central role in C sequestration via biotic and abiotic processes, including i) modulation of microbial community diversity and composition, especially the abundance of fungi and Actinobacteria, and ii) physicochemical stabilization of maize-straw-derived C through the formation of Fe-OM complexes via co-precipitation.

AB - Iron (Fe) oxides regulate soil organic carbon (C) content via balancing C processes of stabilization and mineralization. However, abiotic and biotic mechanisms are involved in stabilization (e.g., by adsorption and/or coprecipitation) and decomposition (e.g., by shifting the microbial community) of paddy soil rich in iron oxides remains poorly understood. We examined the mineralization and stabilization of maize-straw-derived C (δ13C =5000‰), soil priming effects (PE), and soil microbial community structure in four paddy soils, along with Fe oxide concentrations gradient ranging from 13.7 to 55.8 g kg− 1 soil (Fe-13, Fe-25, Fe-42, and Fe-55). The paddy soil with the highest Fe content (Fe-55) stabilized 20.5 mg 13C kg− 1 soil of the maize-straw-derived C, being significantly greater (P < 0.05) than Fe-13 (5 mg 13C kg− 1 soil). The high C:Fe molar ratio of Fe-55 suggests the main pathway of stabilizing the maize-straw-derived C via co-precipitation as Fe-OM. Larger stabilization in Fe55 led to less CO2 emission from maize and SOM, e.g., Fe-55 had 12–16% lower straw mineralization and 8–11% lower PE than Fe-13 during the first 7 days of incubation. Random forest analysis further revealed that Proteobacteria and Actinobacteria (the keystone species, i.e., Gaiella) gave the largest contribution to maize-straw mineralization and PE, while microbial diversity and some microorganisms featured with filamentous hyphae contributed to C stabilization. This study confirmed that the concentration of Fe oxide in paddy soils plays a central role in C sequestration via biotic and abiotic processes, including i) modulation of microbial community diversity and composition, especially the abundance of fungi and Actinobacteria, and ii) physicochemical stabilization of maize-straw-derived C through the formation of Fe-OM complexes via co-precipitation.

KW - Fe-OM complexes Co-occurrence network O2PLS analysis 13C labeled Straw Priming effects Microbial community C accumulation

U2 - 10.1016/j.soilbio.2021.108312

DO - 10.1016/j.soilbio.2021.108312

M3 - Article

VL - 160

JO - Soil Biology and Biochemistry

JF - Soil Biology and Biochemistry

SN - 0038-0717

ER -