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

Publikation: Beitrag in FachzeitschriftArtikelForschungPeer-Review

Autoren

  • Peduruhewa H. Jeewani
  • Lukas Van Zwieten
  • Zhenke Zhu
  • Tida Ge
  • Georg Guggenberger
  • Yu Luo
  • Jianming Xu

Organisationseinheiten

Externe Organisationen

  • Zhejiang University
  • Labuduwa
  • NSW Department of Primary Industries
  • Institute of Subtropical Agriculture, Chinese Academy of Sciences
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Details

OriginalspracheEnglisch
Aufsatznummer108312
FachzeitschriftSoil Biology and Biochemistry
Jahrgang160
Frühes Online-Datum1 Juni 2021
PublikationsstatusVeröffentlicht - Sept. 2021

Abstract

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 co-precipitation) 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 Fe-55 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.

ASJC Scopus Sachgebiete

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Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients. / Jeewani, Peduruhewa H.; Van Zwieten, Lukas; Zhu, Zhenke et al.
in: Soil Biology and Biochemistry, Jahrgang 160, 108312, 09.2021.

Publikation: Beitrag in FachzeitschriftArtikelForschungPeer-Review

Jeewani PH, 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 Sep;160:108312. Epub 2021 Jun 1. doi: 10.1016/j.soilbio.2021.108312
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title = "Abiotic and biotic regulation on carbon mineralization and stabilization in paddy soils along iron oxide gradients",
abstract = "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 co-precipitation) 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 Fe-55 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.",
keywords = "C labeled Straw, C accumulation, Co-occurrence network, Fe-OM complexes, Microbial community, O2PLS analysis, Priming effects",
author = "Jeewani, {Peduruhewa H.} and {Van Zwieten}, Lukas and Zhenke Zhu and Tida Ge and Georg Guggenberger and Yu Luo and Jianming Xu",
note = "Funding Information: This study was supported by the National Science Foundation of China ( 41671233 ) and Zhejiang Outstanding Youth Fund ( R19D010005 ). ",
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language = "English",
volume = "160",
journal = "Soil Biology and Biochemistry",
issn = "0038-0717",
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Download

TY - JOUR

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

AU - Jeewani, Peduruhewa H.

AU - Van Zwieten, Lukas

AU - Zhu, Zhenke

AU - Ge, Tida

AU - Guggenberger, Georg

AU - Luo, Yu

AU - Xu, Jianming

N1 - Funding Information: This study was supported by the National Science Foundation of China ( 41671233 ) and Zhejiang Outstanding Youth Fund ( R19D010005 ).

PY - 2021/9

Y1 - 2021/9

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 co-precipitation) 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 Fe-55 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 co-precipitation) 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 Fe-55 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 - C labeled Straw

KW - C accumulation

KW - Co-occurrence network

KW - Fe-OM complexes

KW - Microbial community

KW - O2PLS analysis

KW - Priming effects

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U2 - 10.1016/j.soilbio.2021.108312

DO - 10.1016/j.soilbio.2021.108312

M3 - Article

AN - SCOPUS:85107765503

VL - 160

JO - Soil Biology and Biochemistry

JF - Soil Biology and Biochemistry

SN - 0038-0717

M1 - 108312

ER -

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