Electron accepting capacity of soil dissolved organic matter increases while electron donating capacity decreases along a temperature gradient

• Rising temperature enhances soil DOM’s EAC while reducing its EDC. • Γ and Δ increases weaken DOM’s pollutant redox control efficacy. • Aromaticity and phenolic content drive DOM’s redox response to warming. • Temperature indirectly affects DOM’s ETC by altering soil and plant litter properties. The electron transfer of soil-derived dissolved organic matter (DOM) plays a key role in the biogeochemical redox processes of redox-active substances. Yet the effect of temperature on soil DOM’s electron transfer capacity (ETC) remains poorly unexplored. This study investigates the temperature response of the ETC of soil DOM through an examination of soils collected from sites along a temperature gradient with 400 mm of annual precipitation in China. Our results demonstrate that increasing temperature enhances soil DOM’s electron-accepting capacity (EAC) while reducing its electron-donating capacity (EDC). For every 1 °C increase, EAC rises by 0.034 mmol e − (g soil DOM) −1 while EDC decreases by 0.014 mmol e − (g soil DOM) −1 . This reduces the efficiency of electron transfer to redox-active substances, potentially weakening soil DOM’s role in biogeochemical redox processes under warming conditions. The influence of temperature on soil DOM’s ETC was achieved indirectly through modulating soil properties and plant litter composition affecting the traits of soil DOM. These findings provide crucial insights for predicting soil DOM’s response to climate warming.

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Publication Details

Journal
Geoderma
Published
2025-10-01
DOI
https://doi.org/10.1016/j.geoderma.2025.117541
Primary Topic
Microbial Fuel Cells and Bioremediation
Type
article
Field-Weighted Citation Impact
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article

Electron accepting capacity of soil dissolved organic matter increases while electron donating capacity decreases along a temperature gradient

Wenbing Tan, Shuwen Hu, Yufu Jia, Guoan Wang et al.
Geoderma
Microbial Fuel Cells and Bioremediation
article

Electron accepting capacity of soil dissolved organic matter increases while electron donating capacity decreases along a temperature gradient

Wenbing Tan, Shuwen Hu, Yufu Jia, Guoan Wang, Yiman Gao, Shuhan Wang, Li Li, Zixun Chen
article en

Abstract

• Rising temperature enhances soil DOM’s EAC while reducing its EDC. • Γ and Δ increases weaken DOM’s pollutant redox control efficacy. • Aromaticity and phenolic content drive DOM’s redox response to warming. • Temperature indirectly affects DOM’s ETC by altering soil and plant litter properties. The electron transfer of soil-derived dissolved organic matter (DOM) plays a key role in the biogeochemical redox processes of redox-active substances. Yet the effect of temperature on soil DOM’s electron transfer capacity (ETC) remains poorly unexplored. This study investigates the temperature response of the ETC of soil DOM through an examination of soils collected from sites along a temperature gradient with 400 mm of annual precipitation in China. Our results demonstrate that increasing temperature enhances soil DOM’s electron-accepting capacity (EAC) while reducing its electron-donating capacity (EDC). For every 1 °C increase, EAC rises by 0.034 mmol e − (g soil DOM) −1 while EDC decreases by 0.014 mmol e − (g soil DOM) −1 . This reduces the efficiency of electron transfer to redox-active substances, potentially weakening soil DOM’s role in biogeochemical redox processes under warming conditions. The influence of temperature on soil DOM’s ETC was achieved indirectly through modulating soil properties and plant litter composition affecting the traits of soil DOM. These findings provide crucial insights for predicting soil DOM’s response to climate warming.

GeodermaVol. 462
Beijing Normal University (CN), Chinese Academy of Forestry (CN), Institute of Desertification Studies (CN), Chinese Research Academy of Environmental Sciences (CN), China Agricultural University (CN)
Openalex Percentile: Top 74%
Microbial Fuel Cells and Bioremediation
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