School of Water and Environment, Chang'an University, Xi'an 710054, China; National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China.
National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China.
J Environ Sci (China). 2023 Apr;126:113-122. doi: 10.1016/j.jes.2022.05.018. Epub 2022 May 21.
Scorodite (FeAsO·HO) is a common arsenic-bearing (As-bearing) iron mineral in near-surface environments that could immobilize or store As in a bound state. In flooded soils, microbe induced Fe(III) or As(V) reduction can increase the mobility and bioavailability of As. Additionally, humic substances can act as electron shuttles to promote this process. The dynamics of As release and diversity of putative As(V)-reducing bacteria during scorodite reduction have yet to be investigated in detail in flooded soils. Here, the microbial reductive dissolution of scorodite was conducted in an flooded soil in the presence of anthraquinone-2,6-disulfonate (AQDS). Anaeromyxobacter, Dechloromonas, Geothrix, Geobacter, Ideonella, and Zoogloea were found to be the dominant indigenous bacteria during Fe(III) and As(V) reduction. AQDS increased the relative abundance of dominant species, but did not change the diversity and microbial community of the systems with scorodite. Among these bacteria, Geobacter exhibited the greatest increase and was the dominant Fe(III)- and As(V)-reducing bacteria during the incubation with AQDS and scorodite. AQDS promoted both Fe(III) and As(V) reduction, and over 80% of released As(V) was microbially transformed to As(III). The increases in the abundance of arrA gene and putative arrA sequences of Geobacter were higher with AQDS than without AQDS. As a result, the addition of AQDS promoted microbial Fe(III) and As(V) release and reduction from As-bearing iron minerals into the environment. These results contribute to exploration of the transformation of As from As-bearing iron minerals under anaerobic conditions, thus providing insights into the bioremediation of As-contaminated soil.
羟砷铁矿(FeAsO·HO)是近地表环境中常见的含砷(As)铁矿物,可将砷固定或呈束缚态存储。在淹水土壤中,微生物诱导的 Fe(III)或 As(V)还原会增加砷的迁移性和生物可利用性。此外,腐殖质可以作为电子穿梭体来促进这一过程。在淹水土壤中,羟砷铁矿还原过程中砷的释放动态和潜在的 As(V)还原细菌的多样性尚未得到详细研究。在此,在蒽醌-2,6-二磺酸钠(AQDS)存在的情况下,在淹水土壤中进行了羟砷铁矿的微生物还原溶解实验。在 Fe(III)和 As(V)还原过程中,发现 Anaeromyxobacter、Dechloromonas、Geothrix、Geobacter、Ideonella 和 Zoogloea 是主要的土著细菌。AQDS 增加了优势种的相对丰度,但没有改变有和没有羟砷铁矿存在时系统的多样性和微生物群落。在这些细菌中,Geobacter 的增加幅度最大,并且是在含有 AQDS 和羟砷铁矿的孵育过程中占主导地位的 Fe(III)和 As(V)还原菌。AQDS 促进了 Fe(III)和 As(V)的还原,超过 80%释放的 As(V)被微生物转化为 As(III)。与没有 AQDS 相比,AQDS 增加了 Geobacter 中 arrA 基因和潜在 arrA 序列的丰度。因此,AQDS 的添加促进了微生物从含砷铁矿物中释放和还原 Fe(III)和 As(V)进入环境。这些结果有助于探索在厌氧条件下含砷铁矿物中砷的转化,从而为受砷污染土壤的生物修复提供了新的思路。