Influence of organics and silica on Fe(II) oxidation rates and cell–mineral aggregate formation by the green-sulfur Fe(II)-oxidizing bacterium Chlorobium ferrooxidans KoFox – Implications for Fe(II) oxidation in ancient oceans
Graphical abstract
Introduction
Geochemical conditions of the Precambrian oceans were different from today, with dissolved silica concentrations at least 1 mM (Jones et al., 2015), and potentially approaching the saturation state of amorphous silica (up to 2.2 mM) (Siever, 1962), while dissolved Fe(II) concentrations ranged from 50 μM (Holland, 1973) to ∼1 mM (Morris, 1993). Under these siliceous and ferruginous conditions the deposition of banded iron formations (BIF) took place (see Bekker et al., 2014 for review). Several mechanisms have been put forth to explain Fe(II) oxidation in Precambrian oceans: (1) abiotic or microbiological reactions with O2 produced by cyanobacteria, (2) abiotic, UV-induced photo-oxidation, or (3) direct photosynthetic utilization of Fe(II) by phototrophic Fe(II)-oxidizers, the so called photoferrotrophs. Emerging evidence suggests that photoferrotrophs were the most probable drivers for the deposition of the precursor ferric oxyhydroxide layers that led to BIF before the Great Oxidation Event, some 2.45 billion years ago (Czaja et al., 2013, Kappler et al., 2005).
Photoferrotrophic organisms use light energy and Fe(II) as an electron donor for CO2 reduction and the production of cell biomass (Widdel et al., 1993). This type of metabolism was shown to be widespread amongst freshwater and marine phototrophic bacteria, including purple sulfur bacteria (Croal et al., 2004), purple non-sulfur bacteria (Poulain and Newman, 2009, Widdel et al., 1993, Wu et al., 2014) and green sulfur bacteria (GSB) (Crowe et al., 2008, Heising et al., 1999). To date, the bulk of our understanding on how photoferrotrophs metabolize, and under what environmental conditions, has mainly come from the study of purple non-sulfur bacteria. However, it has been shown that in modern ferruginous freshwater lakes, GSB were present in the anoxic layers of the photic zone, where they can play an important role for the biogeochemical Fe and C cycles in these environments (Crowe et al., 2008, Llirós et al., 2015). Due to their adaptation to low light conditions (Llirós et al., 2015), GSB are perfectly suited for such conditions, much better than purple-sulfur and purple non-sulfur bacteria, underpinning their importance in ferruginous environments.
Only one strain of GSB capable of phototrophic Fe(II) oxidation has been studied in detail (Heising et al., 1999). This Chlorobium ferrooxidans strain KoFox was shown to oxidize Fe(II) at very low light intensities (>50 lux) (Hegler et al., 2008). It also grows in co-culture with Geospirillum sp. strain KoFum; the latter grows by fermenting fumarate to organic acids, which in turn, enhances Fe(II) oxidation by KoFox (Heising et al., 1999). It is known from abiotic Fe(II) oxidation experiments that the presence of such organics during Fe(II) oxidation influences the structure, particle size, and crystallinity of Fe(III) minerals (Mikutta et al., 2008).
Previous studies have additionally revealed that in the Fe(II)-oxidizing co-culture KoFox/KoFum, the cell surfaces of the fermenting strain KoFum become thinly encrusted in Fe(III) minerals after Fe(II) oxidation. In contrast, cells of the Fe(II)-oxidizing KoFox remained largely free of Fe(III) particles, with the exception of sparse, flat mineral particles (Schädler et al., 2009). This suggests that in this co-culture it is probably the non-Fe(II)-oxidizing partner and not the Fe(II)-oxidizer that will leave a trace in the rock record as a mineral-encrusted microfossil. However, these previous biomineralization studies have not taken into account the complex chemistry of ancient seawater, and how the presence of organic compounds consumed and produced by KoFum influences the mineralogy of the resulting ferric oxyhydroxides, or the influence that different activities of the Fe(II)-oxidizer might have on encrustation. For instance, dissolved silica has a high affinity for iron and it can influence the association of the cells with Fe(III) minerals (Eickhoff et al., 2014, Mayer and Jarrell, 1996). As the Precambrian oceans were Si-rich, its presence might have influenced cell–mineral interactions and thereby needs to be considered when conducting such experiments.
This study, therefore, aims to answer the following questions: (i) how do dissolved silica, fumarate (as an organic model compound that is fermented by KoFum), and variable light intensities impact the activity of the Fe(II)-oxidizer and thus influence Fe(II) oxidation rates, encrustation patterns and cell–mineral interactions in the KoFox/KoFum co-culture, and (ii) which minerals are formed during Fe(II) oxidation in the presence and absence of dissolved silica and organics.
Section snippets
Source of microorganisms
Chlorobium ferrooxidans strain KoFox was described as the first GSB capable of using Fe(II) as electron donor coupled to anoxygenic photosynthesis (Heising et al., 1999). It grows in co-culture with the fermenting ε-proteobacterium Geospirillum sp. strain KoFum. The co-culture was isolated from a ditch at the University of Konstanz, Germany (Heising et al., 1999), and provided by B. Schink (University of Konstanz, Germany). It has been maintained in our lab strain collection since.
Microbial growth medium and growth conditions
For routine
Fe(II) oxidation rates at different light intensities and in presence of silica
To determine the influence of dissolved silica and different light intensities on Fe(II) oxidation rates of KoFox, the co-culture was grown under high (∼1300 lux), moderate (∼450 lux) and low (∼25 lux) light conditions, either in the absence or presence of dissolved silica. Fe(II) oxidation under high light conditions started after a delay of approximately 9–10 days in the absence (Fig. 1A) or presence (Fig. 1B) of dissolved silica, but was significantly faster when silica was present (
Impact of Si and organics on rates of Fe(II) oxidation
It was previously shown in cultures of nitrate-reducing, Fe(II)-oxidizing bacteria that higher concentrations of phosphate can decrease Fe(II) oxidation rates possibly due to formation of solid Fe(II)-phosphate phases that are more difficult to access as an iron source (Larese-Casanova et al., 2010). In our co-culture KoFox/KoFum, changes in the geochemical composition of the medium and the light intensities applied also influenced the Fe(II) oxidation rates, and thus obviously the activity of
Acknowledgments
This work was supported by the German Research Foundation (DFG) funded research training group RTG 1708 “Molecular principles of bacterial survival strategies” (to TG and AK) and by grant 165831 of the Natural Sciences and Engineering Research Council of Canada (NSERC) (to KOK). We would like to thank E. Struve for HPLC and M. Halama for μ-XRD measurements. F. Zeitvogel, P. Weigold and J. Harter are acknowledged for helpful discussions and A. Oatway for help with SEM and TEM work. We also thank
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