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.
Guangdong-Hong Kong-Macao Joint Laboratory for Environmental Pollution and Control, Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou 510640, China.
ISME J. 2024 Jan 8;18(1). doi: 10.1093/ismejo/wrae110.
Arsenate [As(V)] reduction is a major cause of arsenic (As) release from soils, which threatens more than 200 million people worldwide. While heterotrophic As(V) reduction has been investigated extensively, the mechanism of chemolithotrophic As(V) reduction is less studied. Since As is frequently found as a sulfidic mineral in the environment, microbial mediated sulfur oxidation coupled to As(V) reduction (SOAsR), a chemolithotrophic process, may be more favorable in sites impacted by oligotrophic mining (e.g. As-contaminated mine tailings). While SOAsR is thermodynamically favorable, knowledge regarding this biogeochemical process is still limited. The current study suggested that SOAsR was a more prevalent process than heterotrophic As(V) reduction in oligotrophic sites, such as mine tailings. The water-soluble reduced sulfur concentration was predicted to be one of the major geochemical parameters that had a substantial impact on SOAsR potentials. A combination of DNA stable isotope probing and metagenome binning revealed members of the genera Sulfuricella, Ramlibacter, and Sulfuritalea as sulfur oxidizing As(V)-reducing bacteria (SOAsRB) in mine tailings. Genome mining further expanded the list of potential SOAsRB to diverse phylogenetic lineages such as members associated with Burkholderiaceae and Rhodocyclaceae. Metagenome analysis using multiple tailing samples across southern China confirmed that the putative SOAsRB were the dominant As(V) reducers in these sites. Together, the current findings expand our knowledge regarding the chemolithotrophic As(V) reduction process, which may be harnessed to facilitate future remediation practices in mine tailings.
砷酸盐[As(V)]还原是土壤中砷释放的主要原因,这威胁到全球超过 2 亿人的生命健康。虽然已经对异养 As(V)还原进行了广泛的研究,但对化学自养 As(V)还原的机制研究较少。由于砷在环境中经常以硫化物矿物的形式存在,微生物介导的硫氧化耦合砷酸盐还原(SOAsR),一种化学自养过程,可能在受贫营养采矿影响的地点(例如含砷尾矿)更有利。虽然 SOAsR 在热力学上是有利的,但关于这一生物地球化学过程的知识仍然有限。目前的研究表明,在贫营养区,如尾矿库,SOAsR 比异养 As(V)还原更为普遍。水溶性还原态硫浓度被预测为对 SOAsR 潜力有重大影响的主要地球化学参数之一。DNA 稳定同位素探针和宏基因组分箱组合的结果表明,硫氧化砷酸盐还原菌(SOAsRB)主要属于 Sulfuricella、Ramlibacter 和 Sulfuritalea 属。基因组挖掘进一步扩展了潜在 SOAsRB 的名单,包括与伯克霍尔德氏菌科和红环菌科相关的成员。对来自中国南方多个尾矿库的多个尾矿样本进行的宏基因组分析证实,假定的 SOAsRB 是这些地点中主要的 As(V)还原剂。总的来说,目前的研究结果扩展了我们对化学自养 As(V)还原过程的认识,这可能有助于未来在尾矿库中进行修复实践。