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Humic and Fulvic Acid Fractions Differentially Regulate Methane-Dependent Arsenate Reduction in Paddy Soils
Yu Zhang1,2,3, Yun Chen2, Fengjie Liu3
1Key Laboratory of Development and Application of Rural Renewable Energy, Biogas Institute of Ministry of Agriculture and Rural Affairs, Chengdu 610041, China.
Soil organic matter fractions critically influence arsenic mobilization in paddy soils. Humic acids accelerate arsenic release by enhancing methane oxidation coupled to arsenate reduction, while fulvic acids inhibit this process.
Area of Science:
- Environmental Science
- Soil Science
- Microbiology
Background:
- Arsenic contamination in paddy soils poses a significant threat to global food security.
- Microbial reduction of arsenate (As(V)) to mobile arsenite (As(III)) is a primary driver of arsenic mobilization.
- Methane (CH4)-dependent As(V) reduction (M-AsR) links methane cycling to arsenic release, but the role of soil organic matter (SOM) is unclear.
Purpose of the Study:
- To investigate how structurally distinct soil organic matter (SOM) fractions regulate the methane (CH4)-dependent arsenate (As(V)) reduction (M-AsR) pathway.
- To elucidate the mechanisms by which humic and fulvic acids influence electron transfer and arsenic mobilization in paddy soils.
Main Methods:
- Experimental analysis of two distinct SOM fractions: aromatic, quinone-rich humic acid and carboxyl-rich fulvic acid.
- Quantification of arsenic species (As(III) and As(V)) and microbial gene abundance (pmoA, mcrA, arrA) under different SOM treatments.
- Thermodynamic assessment of methane-driven metabolism.
Main Results:
- Humic acid enhanced electron transfer, promoting CH4 oxidation coupled to As(V) reduction, leading to a ~1.5-fold increase in As(III) release.
- Fulvic acid promoted acetate accumulation, thermodynamically hindering CH4-driven metabolism and largely blocking M-AsR, with only a 47.9% increase in CH4-driven As(III).
- Humic acid acted as an electron shuttle, while fulvic acid disrupted the coupling via acetate accumulation.
Conclusions:
- Soil organic matter structure significantly controls arsenic mobilization pathways in paddy soils.
- Humic acids facilitate arsenic release by enhancing microbial methane oxidation and arsenate reduction.
- Molecular-level characterization of SOM is crucial for predicting arsenic risks in flooded agricultural systems.
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