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, Guangdong Institute of Eco-environmental Science and Technology, Guangdong Academy of Sciences, Guangzhou, 510650, China.
State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang, 550081, China.
Environ Geochem Health. 2021 Mar;43(3):1305-1317. doi: 10.1007/s10653-020-00725-w. Epub 2020 Sep 25.
Fe(II)-oxidizing bacteria (FeOB) are important catalysts for iron cycling in iron-rich marine, groundwater, and freshwater environments. However, few studies have reported the distribution and diversity of these bacteria in flooded paddy soils. This study investigates the microbial structure and diversity of microaerophilic Fe(II)-oxidizing bacteria (mFeOB) and their possible role in Fe(II) oxidation in iron-rich paddy soils. Using enrichment experiments that employed serial transfers, the changes in microaerophilic microbial community were examined via 16S rRNA gene high-throughput sequencing. During enrichments, the Fe(II) oxidation rate decreased as transfers increased, and the maximum rate of Fe(II) oxidation was observed in the first transfer (0.197 mM day). Results from X-ray diffraction of minerals and scanning electron microscopy of the cell-mineral aggregates revealed that cell surfaces in all transfers were partly covered with amorphous iron oxide formed by FeOB. After four transfers, the phyla of Proteobacteria had a dominant presence that reached up to 95%. Compared with the original soil, the relative abundances of Cupriavidus, Massilia, Pseudomonas, Ralstonia, Sphingomonas, and Variovorax increased in FeS gradient tubes and became dominant genera after transfers. Cupriavidus, Pseudomonas, and Ralstonia have been identified as FeOB previously. Furthermore, the structure of the microbial community tended to be stable as transfers increased, indicating that other bacterial species might perform important roles in Fe(II) oxidation. These results suggest the potential involvement of mFeOB and these other microorganisms in the Fe(II)-oxidizing process of soils. It will be helpful for future studies to consider their role in related biogeochemical processes, such as transformation of organic matters and heavy metals.
亚铁氧化菌(FeOB)是富含铁的海洋、地下水和淡水中铁循环的重要催化剂。然而,很少有研究报道这些细菌在淹水稻田中的分布和多样性。本研究调查了富铁稻田中微好氧亚铁氧化菌(mFeOB)的微生物结构和多样性及其在亚铁氧化中的可能作用。通过采用连续传代的富集实验,通过 16S rRNA 基因高通量测序研究了微好氧微生物群落的变化。在富集过程中,随着传代次数的增加,微好氧微生物群落的 Fe(II)氧化速率降低,在第一次传代(0.197 mM day)时观察到最大的 Fe(II)氧化速率。矿物的 X 射线衍射和细胞-矿物聚集体的扫描电子显微镜结果表明,所有传代物的细胞表面部分被 FeOB 形成的无定形氧化铁覆盖。经过四次传代后,变形菌门的丰度达到 95%。与原始土壤相比,在 FeS 梯度管中,Cupriavidus、Massilia、Pseudomonas、Ralstonia、Sphingomonas 和 Variovorax 的相对丰度增加,并在传代后成为优势属。Cupriavidus、Pseudomonas 和 Ralstonia 以前被鉴定为 FeOB。此外,随着传代次数的增加,微生物群落的结构趋于稳定,表明其他细菌可能在 Fe(II)氧化过程中发挥重要作用。这些结果表明 mFeOB 和这些其他微生物可能参与土壤中的 Fe(II)氧化过程。考虑到它们在相关生物地球化学过程(如有机物和重金属的转化)中的作用,这将有助于未来的研究。