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Magnetite nanoparticles are metastable biogeobatteries in consecutive redox cycles driven by microbial Fe oxidation and reduction

Published online by Cambridge University Press:  25 September 2024

T. Bayer
Affiliation:
Geomicrobiology Group, Department of Geosciences, University of Tuebingen, Schnarrenbergstrasse 94-96, 72076 Tuebingen, Germany
N. Jakus
Affiliation:
Geomicrobiology Group, Department of Geosciences, University of Tuebingen, Schnarrenbergstrasse 94-96, 72076 Tuebingen, Germany Current address: Environmental Microbiology Laboratory, École Polytechnique Fédérale de Lausanne, CE1 644, Lausanne CH 1015, Switzerland
A. Kappler
Affiliation:
Geomicrobiology Group, Department of Geosciences, University of Tuebingen, Schnarrenbergstrasse 94-96, 72076 Tuebingen, Germany Cluster of Excellence: EXC 2124: Controlling Microbes to Fight Infection, Auf der Morgenstelle 28D, 72076 Tuebingen, Germany
J. M. Byrne*
Affiliation:
School of Earth Sciences, University of Bristol, Queens Road BS8 1RJ, Bristol, UK
*
Corresponding author: James M. Byrne; Email: james.byrne@bristol.ac.uk
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Abstract

Iron (Fe) minerals play a crucial role in biogeochemical cycles due to their ubiquity in nature, high adsorption capacity and redox activity towards many other elements. Mixed-valent Fe minerals are unique since they contain Fe(II) and Fe(III). For example, magnetite (Fe(II)Fe(III)2O4) nanoparticles (MNPs) can affect the availability and mobility of nutrients and contaminants. This is due to the high surface area to volume ratio and the presence of Fe(II) and Fe(III), allowing redox transformation of (in‑)organic contaminants. Recent studies have shown that magnetite can serve as an electron source and sink for Fe(II)-oxidizing and Fe(III)-reducing microorganisms, storing and releasing electrons; thus, it functions as a biogeobattery. However, the ability of MNPs to act as biogeobatteries over consecutive redox cycles and the consequences for mineral integrity and identity remain unknown. Here, we show MNPs working as biogeobatteries in two consecutive redox cycles over 41 days. MNPs were first oxidized by the autotrophic nitrate-reducing Fe(II)-oxidizing culture KS and subsequently reduced by the Fe(III)-reducing Geobacter sulfurreducens. In addition to reduced magnetite, we identified the Fe(II) mineral vivianite after reductions, suggesting partial reductive dissolution of MNPs and re-crystallization of Fe2+ with phosphate from the growth medium. Measurements of the Fe(II)/Fe(III) ratio revealed microbial oxidation and reduction for both the first redox cycle (oxidation: 0.29±0.014, reduction: 0.75±0.023) and the second redox cycle (oxidation: 0.30±0.015, reduction: 1.64±0.10). Relative changes in magnetic susceptibility (∆κ in %) revealed greater changes for the second oxidation (–8.7±1.99%) than the first (–3.9±0.19%) but more minor changes for the second reduction (+14.29±0.39%) compared to the first (+25.42±1.31%). Our results suggest that MNPs served as biogeobatteries but became less stable over time, which has significant consequences for associated contaminants, nutrients and bioavailability for Fe-metabolizing microorganisms.

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Article
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
© The Author(s), 2024. Published by Cambridge University Press on behalf of The Mineralogical Society of Great Britain and Ireland
Figure 0

Figure 1. (a) Changes in the Fe(II)/Fe(III) ratio determined by ferrozine assay over time and (b) relative changes of magnetic susceptibility (∆κ in %), with respect to the starting value of each oxidation or reduction cycle, of MNPs incubated with either culture KS (yellow background) or G. sulfurreducens (green background). Symbols and error bars represent the mean and standard deviation of at least five replicates for Fe ratio and six replicates for ∆κ. Controls were performed in triplicate. Black circles show biological replicates and white circles show controls.

Figure 1

Figure 2. 57Fe Mössbauer spectra of MNPs collected at 140 K at (a) the start and (b) the end of the first oxidation, (c) after the first reduction, (d) after the second oxidation, and (e) after the second reduction. Characteristic sextets of tetrahedral (light blue) and octahedral (grey) magnetite could be observed. We additionally detected a Fe(III) phase (light green) due to inoculation with culture KS and a Fe(II) phase (red), which was confirmed to be (partially) vivianite.

Figure 2

Figure 3. μXRD patterns of MNPs collected before the experiment (initial phases) and at the end of each oxidation/reduction for the biotic experiments (Bio) and the abiotic controls (Ctrl). References of vivianite and magnetite are shown at the bottom.

Figure 3

Figure 4. Fourier-transformed infrared (FTIR) spectra of anoxically dried magnetite samples. (a-b) Biological replicates collected after the second oxidation, (c-e) biological replicates collected after the second reduction, (f) control collected after the second oxidation, (g) control collected after the second reduction.

Figure 4

Figure 5. SEM images of samples collected at the end of the second reduction. (a) High magnification of MNPs, (b) overview of MNPs and newly formed vivianite, (c) remains of biomass/cells (presumably G. sulfurreducens) (cells were not fixed with glutaraldehyde), (d) close contact of MNPs and formed vivianite and cells, (e-f) characteristic twinning of vivianite crystals and close contact with MNPs. White arrows point to cells and blue arrows to MNPs-vivianite associations.

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