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Most isolated nitrate-reducing Fe(II)-oxidizing microorganisms are mixotrophic, meaning that Fe(II) is chemically oxidized by nitrite that forms during heterotrophic denitrification, and it is debated to which extent Fe(II) is enzymatically oxidized. One exception is the chemolithoautotrophic enrichment culture KS, a consortium consisting of a dominant Fe(II) oxidizer, sp., and less abundant heterotrophic strains (e.g., sp., sp.). Currently, this is the only nitrate-reducing Fe(II)-oxidizing culture for which autotrophic growth has been demonstrated convincingly for many transfers over more than 2 decades. We used 16S rRNA gene amplicon sequencing and physiological growth experiments to analyze the community composition and dynamics of culture KS with various electron donors and acceptors. Under autotrophic conditions, an operational taxonomic unit (OTU) related to known microaerophilic Fe(II) oxidizers within the family dominated culture KS. With acetate as an electron donor, most 16S rRNA gene sequences were affiliated with sp. sp. not only was able to oxidize Fe(II) under autotrophic and mixotrophic conditions but also survived over several transfers of the culture on only acetate, although it then lost the ability to oxidize Fe(II). spp. became and remained dominant when culture KS was cultivated for only one transfer under heterotrophic conditions, even when conditions were reverted back to autotrophic in the next transfer. This study showed a dynamic microbial community in culture KS that responded to changing substrate conditions, opening up questions regarding carbon cross-feeding, metabolic flexibility of the individual strains in KS, and the mechanism of Fe(II) oxidation by a microaerophile in the absence of O Nitrate-reducing Fe(II)-oxidizing microorganisms are present in aquifers, soils, and marine and freshwater sediments. Most nitrate-reducing Fe(II) oxidizers known are mixotrophic, meaning that they need organic carbon to continuously oxidize Fe(II) and grow. In these microbes, Fe(II) was suggested to be chemically oxidized by nitrite that forms during heterotrophic denitrification, and it remains unclear whether or to what extent Fe(II) is enzymatically oxidized. In contrast, the enrichment culture KS was shown to oxidize Fe(II) autotrophically coupled to nitrate reduction. This culture contains the designated Fe(II) oxidizer sp. and several heterotrophic strains (e.g., sp.). We showed that culture KS is able to metabolize Fe(II) and a variety of organic substrates and is able to adapt to dynamic environmental conditions. When the community composition changed and became the dominant community member, Fe(II) was still oxidized by sp., even when culture KS was cultivated with acetate/nitrate [Fe(II) free] before being switched back to Fe(II)/nitrate.
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http://dx.doi.org/10.1128/AEM.02173-17 | DOI Listing |
Water Res
September 2025
State Key Laboratory of Soil Pollution Control and Safety, Department of Environmental Science, Zhejiang University, Hangzhou 310058, China; Future Environment Laboratory, Innovation Center of Yangtze River Delta, Zhejiang University, Jiaxing 314100, China. Electronic address:
Accelerating the rate-limiting surface Fe(III)/Fe(II) redox cycling is pivotal for efficient iron-mediated Fenton-like decontamination, yet conventional reductants (e.g., toxic hydroxylamine, thiosulfate) suffer from secondary toxicity, self-quenching, and heavy metal leaching.
View Article and Find Full Text PDFWater Res
August 2025
State Key Laboratory of Water Pollution Control and Green Resource Recycling, College of Environmental Science and Engineering, Tongji University, Shanghai 200092, China; Shanghai Institute of Pollution Control and Ecological Security, Shanghai 200092, China. Electronic address:
Anaerobic co-digestion of sulfur-containing organic wastes with waste-activated sludge containing iron-phosphorus compounds (FePs) was recently suggested as an environment-friendly strategy to promote phosphate release, energy recovery, and hydrogen sulfide (HS) control. Nevertheless, the mechanistic coupling between FePs speciation and the concurrent transformation of carbon, sulfur, iron, and phosphorus within this system remains to be fully elucidated. To address this knowledge gap, methionine, a typical hydrolysis product of sulfur-containing organics, and five FePs prevalent in sludge (ferric-phosphate tetrahydrate (FePO⋅4HO), ferric-phosphate dihydrate (FePO⋅2HO), vivianite (Fe(PO)·8HO), phosphate coprecipitated with Fe(III) (COP-P), and phosphate adsorption on hydrous ferric oxide (HFO-P)) were selected to elucidate C-S-Fe-P transformations in this study.
View Article and Find Full Text PDFMicrobiol Spectr
September 2025
Department of Biological Sciences, Molecular and Computational Biology Section, University of Southern California, Los Angeles, California, USA.
expresses three ferritins that store acquired iron by oxidizing soluble Fe(II) to insoluble Fe(III), which can accumulate and later be utilized in cellular processes. Although bacterioferritin (Bfr) and ferritin (FtnA) sequester more Fe(III) atoms per multimeric complex, the abundance of the DNA-binding protein from starved cells (Dps), coupled with its preference for hydrogen peroxide as an oxidant in its ferroxidase activity, makes it a fundamental component in iron homeostasis and long-term stationary phase (LTSP) survival. To investigate the temporal role and mechanisms of action of Dps in parallel with the other ferritins, growth yield, survival, competitive fitness, and siderophore assays were performed under different conditions of iron availability.
View Article and Find Full Text PDFWater Res
August 2025
Key Laboratory of Groundwater Resources and Environment, Ministry of Education, Jilin University, Changchun 130021, China; Jilin Provincial Key Laboratory of Water Resources and Environment, Jilin University, Changchun 130021, China; National and Local Joint Engineering Laboratory for Petrochemical
In-situ chemical oxidation (ISCO) based on Fe(II)-activated O is a promising approach for groundwater remediation; however, its efficiency is often limited by the low oxygen content in subsurface environments and insufficient generation of reactive oxygen species (ROS). In this study, a novel ISCO technology was developed by integrating a tripolyphosphate (TPP)-enhanced Fe(II)/O advanced oxidation system with aeration to promote ROS generation and enhance remediation performance. Two-dimensional sand tank experiments were conducted to evaluate the effectiveness of this approach in remediating p-Nitrophenol (PNP) contaminated groundwater.
View Article and Find Full Text PDFNucleic Acids Res
August 2025
Department of Chemistry, Hong Kong Baptist University, Kowloon Tong, Hong Kong SAR, China.
N 6-Methyladenosine (m6A) is a prevalent post-transcriptional modification in eukaryotic messenger RNA. Two cancer-linked human Fe(II) and 2-oxoglutarate (2OG)-dependent oxygenases, the fat mass and obesity associated-protein (FTO), and AlkB human homolog 5 (ALKBH5) catalyse m6A methyl group oxidation. While ALKBH5 has consistently been reported to catalyse m6A demethylation, there are conflicting reports concerning the FTO products.
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