Jiangsu Key Laboratory for Organic Waste Utilization, Jiangsu Collaborative Innovation Center for Solid Organic Waste Resource Utilization, College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing, 210095, China.
School of Environmental and Chemical Engineering, Shanghai University, Shanghai, 200444, China.
Environ Pollut. 2019 Apr;247:736-744. doi: 10.1016/j.envpol.2019.01.043. Epub 2019 Jan 22.
The bioavailability of the metalloid arsenic (As) in paddy soil is controlled by microbial cycling of As and other elements such as iron (Fe) and sulfur (S), which are strongly influenced by water management in paddy fields. In this study, we evaluated how water management affects As bioavailability by growing rice plants in a geogenic As-contaminated soil. We determined As speciation in soil porewater and the diversity of the associated microbial community. Continuous flooding enhanced the release of Fe and As and increased arsenite (As(III)) and methylated As species concentrations in the rice grain compared with aerobic treatment. Total inorganic and organic As in the grain was 84% and 81% lower, respectively, in the aerobic treatment compared with the continuous flooding treatment. The amounts of Fe(III)-reducing bacteria (FeRB) increased in the flooded rhizosphere soil. The abundance of FeRB in the soil correlated with the dissolution of Fe and As. Among the As-transformation genes quantified, the aioA gene for As(III) oxidation and arsM gene for As(III) methylation were most abundant. The arsM copy number correlated positively with the levels of dsrB (dissimilatory (bi) sulfite reductase β-subunit), suggesting that dissimilatory sulfate-reducing bacteria (SRB) may play an important role in dimethylarsenate (DMAs(V)) production in soil. Our results show that decreased populations of rhizosphere FeRB and SRB contributed to a lower bioavailability of As, and decreased production of methylated arsenicals under oxic conditions.
土壤中类金属砷(As)的生物可给性受 As 与铁(Fe)和硫(S)等元素的微生物循环控制,而这些元素受稻田水分管理的强烈影响。在这项研究中,我们通过在受地质成因污染的土壤中种植水稻来评估水分管理如何影响 As 的生物可给性。我们测定了土壤孔隙水中的 As 形态和相关微生物群落的多样性。与有氧处理相比,连续淹水会促进 Fe 和 As 的释放,并增加水稻籽粒中亚砷酸盐(As(III))和甲基化 As 浓度。与连续淹水相比,有氧处理使水稻籽粒中总无机和有机 As 分别降低了 84%和 81%。在淹水的根际土壤中,Fe(III)-还原菌(FeRB)的数量增加。土壤中 FeRB 的丰度与 Fe 和 As 的溶解有关。在所定量的 As 转化基因中,用于 As(III)氧化的 aioA 基因和用于 As(III)甲基化的 arsM 基因最为丰富。arsM 拷贝数与 dsrB(异化(生物)亚硫酸盐还原酶β-亚基)呈正相关,这表明异化硫酸盐还原菌(SRB)可能在土壤中二甲基砷酸盐(DMAs(V))的产生中发挥重要作用。我们的结果表明,根际 FeRB 和 SRB 种群减少导致 As 的生物可给性降低,在有氧条件下减少了甲基化砷的生成。