化学
砷酸盐
环境化学
腐植酸
亚砷酸盐
砷
溶解
黄腐酸
土壤水分
氧化还原
有机质
无机化学
分数(化学)
电子转移
土壤污染
修正案
自行车
金属
甲烷厌氧氧化
甲烷
溶解有机碳
污染
土壤有机质
遗传算法
电子供体
作者
Yu Zhang,Yu Chen,Fengjie Liu,Yves Plancherel,Andreas Kappler,Lina Zou,Olubukola Oluranti Babalola,Ayansina Segun Ayangbenro,Xianjin Tang
标识
DOI:10.1021/acs.est.5c12983
摘要
Arsenic (As) contamination in paddy soils threatens global food security because microbial reduction of arsenate (As(V)) to mobile arsenite (As(III)) drives As mobilization. Methane (CH4)-dependent As(V) reduction (M-AsR) is a key route coupling CH4 cycling to As release, yet how structurally distinct soil organic matter (SOM) fractions regulate this pathway remains poorly understood. Here we show that an aromatic, quinone-rich humic acid fraction enhances electron transfer and promotes coupling of CH4 oxidation to As(V) reduction, accelerating iron (Fe)-As mineral dissolution and increasing As(III) release by ∼1.5-fold. Accordingly, copy numbers of NC10-targeted pmoA, ANME-2d-targeted mcrA, and arrA increased by 116.6%, 126.5%, and ∼2.4-fold, respectively. In contrast, a carboxyl-rich fulvic fraction promoted acetate accumulation, thereby making CH4-driven metabolism thermodynamically unfavorable. NC10-targeted pmoA and ANME-2d-targeted mcrA signals consequently decreased by 95.3% and 89.6%, respectively, and M-AsR was largely blocked, with the CH4-driven As(III) component increasing by only 47.9%. Crucially, humic acid acts as an electron shuttle linking CH4 oxidation and As(V) reduction, while fulvic acid disrupts this coupling process via acetate accumulation, highlighting the need for molecular-level SOM characterization to predict As risks in flooded soils.
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