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Contrasting response of organic carbon mineralisation to iron oxide addition under conditions of low and high microbial biomass in anoxic paddy soil

Li, Yuhong ; Shahbaz, Muhammad LU ; Zhu, Zhenke ; Chen, Anlei ; Nannipieri, Paolo ; Li, Baozhen ; Deng, Yangwu ; Wu, Jinshui and Ge, Tida (2021) In Biology and Fertility of Soils 57(1). p.117-129
Abstract
In contrast to what is observed in aerobic uplands, microbial biomass and the presence of electron acceptors, such as iron oxides, play a crucial role in regulating soil organic C (SOC) mineralisation in paddy soils. However, the related underlying mechanisms are still poorly explored. We conducted an anaerobic incubation study to investigate changes in CO2 emissions from SOC and acetate (13C-labeleld) in response to iron oxide (ferrihydrite and goethite) addition in chloroform-fumigated and unfumigated paddy soils. The iron oxides, as electron acceptors, increased CO2 emissions from SOC with stronger impact under ferrihydrite than goethite addition. However, the acetate addition, as a preferable C source for reducing microbes, decreased... (More)
In contrast to what is observed in aerobic uplands, microbial biomass and the presence of electron acceptors, such as iron oxides, play a crucial role in regulating soil organic C (SOC) mineralisation in paddy soils. However, the related underlying mechanisms are still poorly explored. We conducted an anaerobic incubation study to investigate changes in CO2 emissions from SOC and acetate (13C-labeleld) in response to iron oxide (ferrihydrite and goethite) addition in chloroform-fumigated and unfumigated paddy soils. The iron oxides, as electron acceptors, increased CO2 emissions from SOC with stronger impact under ferrihydrite than goethite addition. However, the acetate addition, as a preferable C source for reducing microbes, decreased SOC mineralisation and caused a negative priming effect. CO2 emission from both acetate and SOC was affected by microbial biomass change. In the acetate-treated soil, goethite in the fumigated soil (i.e. high microbial biomass) increased CO2 emissions from acetate, providing electron acceptors, and decreased CO2 emissions from SOC. Ferrihydrite accepted electrons and adsorbed acetate, resulting in a slight decline in CO2 emission from acetate. However, in the fumigated soil (i.e. low microbial biomass), both iron oxide additions reduced CO2 emissions from acetate and SOC and likely the dominant role of both iron oxides shifted from being electron acceptors to being adsorbents, thus limiting acetate accessibility to microorganisms. The results suggest that microbial biomass is a key driver in shifting the effects of iron oxides on organic C mineralisation in anaerobic paddy soils. (Less)
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author
; ; ; ; ; ; ; and
organization
publishing date
type
Contribution to journal
publication status
published
subject
keywords
Acetate, Anaerobic mineralisation, Iron oxides, Microbial biomass, Rice paddy soil, Soil organic C
in
Biology and Fertility of Soils
volume
57
issue
1
pages
117 - 129
publisher
Springer
external identifiers
  • scopus:85091351702
ISSN
1432-0789
DOI
10.1007/s00374-020-01510-8
language
English
LU publication?
yes
id
a75ef3a0-ac83-463b-90f0-bb33113baab9
date added to LUP
2020-09-24 11:45:12
date last changed
2023-02-21 11:31:11
@article{a75ef3a0-ac83-463b-90f0-bb33113baab9,
  abstract     = {{In contrast to what is observed in aerobic uplands, microbial biomass and the presence of electron acceptors, such as iron oxides, play a crucial role in regulating soil organic C (SOC) mineralisation in paddy soils. However, the related underlying mechanisms are still poorly explored. We conducted an anaerobic incubation study to investigate changes in CO2 emissions from SOC and acetate (13C-labeleld) in response to iron oxide (ferrihydrite and goethite) addition in chloroform-fumigated and unfumigated paddy soils. The iron oxides, as electron acceptors, increased CO2 emissions from SOC with stronger impact under ferrihydrite than goethite addition. However, the acetate addition, as a preferable C source for reducing microbes, decreased SOC mineralisation and caused a negative priming effect. CO2 emission from both acetate and SOC was affected by microbial biomass change. In the acetate-treated soil, goethite in the fumigated soil (i.e. high microbial biomass) increased CO2 emissions from acetate, providing electron acceptors, and decreased CO2 emissions from SOC. Ferrihydrite accepted electrons and adsorbed acetate, resulting in a slight decline in CO2 emission from acetate. However, in the fumigated soil (i.e. low microbial biomass), both iron oxide additions reduced CO2 emissions from acetate and SOC and likely the dominant role of both iron oxides shifted from being electron acceptors to being adsorbents, thus limiting acetate accessibility to microorganisms. The results suggest that microbial biomass is a key driver in shifting the effects of iron oxides on organic C mineralisation in anaerobic paddy soils.}},
  author       = {{Li, Yuhong and Shahbaz, Muhammad and Zhu, Zhenke and Chen, Anlei and Nannipieri, Paolo and Li, Baozhen and Deng, Yangwu and Wu, Jinshui and Ge, Tida}},
  issn         = {{1432-0789}},
  keywords     = {{Acetate; Anaerobic mineralisation; Iron oxides; Microbial biomass; Rice paddy soil; Soil organic C}},
  language     = {{eng}},
  number       = {{1}},
  pages        = {{117--129}},
  publisher    = {{Springer}},
  series       = {{Biology and Fertility of Soils}},
  title        = {{Contrasting response of organic carbon mineralisation to iron oxide addition under conditions of low and high microbial biomass in anoxic paddy soil}},
  url          = {{http://dx.doi.org/10.1007/s00374-020-01510-8}},
  doi          = {{10.1007/s00374-020-01510-8}},
  volume       = {{57}},
  year         = {{2021}},
}