Spectroscopic and computational investigations of organometallic complexation of group 12 transition metals by methanobactins from Methylocystis sp. SB2

https://doi.org/10.1016/j.jinorgbio.2021.111496Get rights and content

Highlights

  • Methylocystis sp. strain SB2 methanobactin forms complexes with Group 12 transition metals.

  • Absorbance and fluorescence spectra change with methanobactin-metal stoichiometry and time.

  • Hg L3-edge extended x-ray absorption fine structure suggests linear Hg—S coordination.

  • Computational results suggest Hg2+-methanobactin coordination differs from Zn2+ and Cd2+

  • Fluorescence enhancement observed suggests complexation-hindered isomerization mechanism.

Abstract

Methanotrophic bacteria catalyze the aerobic oxidation of methane to methanol using Cu-containing enzymes, thereby exerting a modulating influence on the global methane cycle. To facilitate the acquisition of Cu ions, some methanotrophic bacteria secrete small modified peptides known as “methanobactins,” which strongly bind Cu and function as an extracellular Cu recruitment relay, analogous to siderophores and Fe. In addition to Cu, methanobactins form complexes with other late transition metals, including the Group 12 transition metals Zn, Cd, and Hg, although the interplay among solution-phase configurations, metal interactions, and the spectroscopic signatures of methanobactin-metal complexes remains ambiguous. In this study, the complexation of Zn, Cd, and Hg by methanobactin from Methylocystis sp. strain SB2 was studied using a combination of absorbance, fluorescence, extended x-ray absorption fine structure (EXAFS) spectroscopy, and time-dependent density functional theory (TD-DFT) calculations. We report changes in sample absorbance and fluorescence spectral dynamics, which occur on a wide range of experimental timescales and characterize a clear stoichiometric complexation dependence. Mercury L3-edge EXAFS and TD-DFT calculations suggest a linear model for Hgsingle bondS coordination, and TD-DFT suggests a tetrahedral model for Zn2+ and Cd2+. We observed an enhancement in the fluorescence of methanobactin upon interaction with transition metals and propose a mechanism of complexation-hindered isomerization drawing inspiration from the wild-type Green Fluorescent Protein active site. Collectively, our results represent the first combined computational and experimental spectroscopy study of methanobactins and shed new light on molecular interactions and dynamics that characterize complexes of methanobactins with Group 12 transition metals.

Graphical abstract

The complexation of Group 12 transition metals by methanobactin peptides from Methylocystis sp. strain SB2 is studied using absorbance spectroscopy, fluorescence emission spectroscopy, and electronic structure calculations. Trends in transition metal complexation are reported and a molecular mechanism for a notable fluorescence enhancement with transition metal complexation is proposed.

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Introduction

Anthropogenic emissions of greenhouse gases are a central factor in one of the most pivotal environmental issues of the twenty-first century, global climate change. One such greenhouse gas is methane, which is released to the atmosphere by anthropogenic and natural sources. Natural biotic methane production (methanogenesis) occurs primarily through the anaerobic metabolism of carbon dioxide and organic matter by archaea (methanogens). Methane emissions from methanogens are naturally modulated by methane-oxidizing bacteria (methanotrophs), which can metabolize methane as the sole source of carbon and energy [1,2]. The first step in the oxidation of methane to methanol by aerobic methanotrophs involves the enzyme methane monooxygenase (MMO). Two forms of MMO have been characterized: soluble MMO (sMMO), which contains an Fe-based active site and is found in the cytoplasm, and particulate MMO (pMMO), which is membrane-associated and contains Cu [[3], [4], [5], [6], [7]]. Copper is a relatively sparse transition metal, with a natural abundance of 60 ppm in the earth's crust and 0.25 ppb in the ocean [8]. sMMO is typically expressed under Cu-limiting conditions and pMMO at higher Cu concentrations [[9], [10], [11]], and methanotrophic bacteria excrete Cu-binding metallophores (chalkophores) to facilitate Cu acquisition [[12], [13], [14], [15], [16], [17]]. These post-translationally modified peptides (~850–1300 Da) are known as methanobactins and function in a manner analogous to siderophores in the extracellular acquisition of Fe [18,19]. Methanobactins are excreted by methanotrophic bacteria under conditions of Cu deprivation [11]. Although extracellular Cu acquisition is believed to be their primary function, several studies suggest methanobactins may also serve other functions in environmental systems. For example, methanobactins are hypothesized to have a secondary function as signaling molecules within methanotrophic communities [20] and they have been shown to reduce toxicity associated with mercuric mercury (Hg2+) in pure culture studies with methanotrophs [21]. Furthermore, recent studies demonstrated that methanobactins facilitate the degradation of highly toxic methylmercury (MeHg) [22], and they also increase the bioavailability of inorganic Hg for methylation by some anaerobic bacteria [23]. Thus, methanobactins may affect net MeHg production in environments where methanotrophs are prevalent.

In addition to their biogeochemical significance, methanobactins are ideal for experimental analysis using optical spectroscopic methods. Unlike most proteins and peptides, methanobactins contain biochemically unusual oxazolone-, imidazolone-, and pyrazine-based chromophores that absorb strongly across the entire UV spectrum and into the visible. The chromophores are directly involved in the complexation of transition metals, so the absorbance and fluorescence spectra of methanobactins are sensitive to the coordination state of the peptide (Fig. 1). Early spectroscopic and isothermal calorimetry experiments demonstrated that methanobactins may form coordination complexes with many early- and mid-transition metals [21,24] and ultimately influence transition metal bioavailability. Similar investigations of methanobactins from Methylosinus trichosporium OB3b (mb-OB3b) and Methylocystis sp. strain SB2 (mb-SB2) have revealed characteristic concentration-dependent changes in spectral characteristics upon binding of Hg2+ [21,24] and suggested that both chromophores are involved in the complexation. Furthermore, although methanobactins have a high affinity for binding Cu ions, Hg2+ was found to displace Cu2+ bound to mb-SB2 [21,24]. However, the specific coordination geometries induced by the complexation of methanobactins with metals are not well understood. Electronic structure calculations in combination with thorough spectroscopic characterization can provide insights into binding geometries and unique molecular properties associated with the binding of different metal ions. The absorbance and fluorescence spectra of methanobactin peptides have not been studied theoretically and the specific correlations between changes in spectroscopic and molecular features have yet to be established. Here, we conducted time-dependent density functional theory (TD-DFT) calculations to describe the geometry and electronic structure of mb-SB2 chromophores, which give rise to characteristic UV–visible absorbance spectra. Furthermore, we collected fluorescence spectra and relate observed emissions to coordination geometries of mb-SB2 complexed with Zn2+, Cd2+, and Hg2+. Finally, the structure of mb-SB2 complexed with Hg2+at variable molar ratios was probed with Extended X-ray Absorption Fine Structure (EXAFS) spectroscopy and compared with geometries predicted by TD-DFT calculations. Our data offer molecular-scale insights into the interactions of trace metals with the functional groups present in methanobactins. Understanding these interactions will aid in developing improved speciation models that adequately describe the effect of methanobactins on the biogeochemical cycling of Group 12 transition metals.

Section snippets

Methanobactin SB2 isolation and solutions preparation

Methanobactin was isolated from mb-SB2 following an established protocol [25]. Briefly, the bacteria were cultured in nitrate mineral salts [26] amended with 0.2 μM CuSO4 [15,27]., Cells were separated from the culture medium using a Millipore tangential flow filtration system (Pall Corp., Port Washington, NY, USA) containing a 100,000 Da molecular mass cutoff filter cassette. The filtrate was loaded onto a Diaion HP-20 column (Supelco, Bellefonte, PA, USA) and washed with 2 to 3 bed volumes of

Absorbance spectra

The absorbance spectra of mb-SB2 titrated with Zn2+, Cd2+, and Hg2+ in a 10 mM phosphate buffer are shown in Fig. 2. The UV absorbance spectrum of metal-free mb-SB2 shows four primary features at 384, 338, 300, and 250 nm—these peaks are designated as Peaks 1–4 in Fig. 2, and the remainder of this manuscript. Peak 1 is attributed to the 4-imidazolone-enethiol moiety, though this has been disputed, [40] and Peak 2 is attributed to the 4-oxazolone-enethiol moiety. We are unaware of any

Concentration-dependent spectral changes in mb-SB2

Our results show metal-specific changes in both absorption and fluorescence spectra. A clear transition in spectral changes occurred at concentrations of 5 μM transition metal (0.5 equivalents) in the absorbance and fluorescence data (Fig. 2, Fig. 4). Similar concentration-dependent spectral trends were previously observed in mixtures of methanobactin from mb-OB3b with Zn2+ and Cd2+, and the formation of dimeric peptide complexes that persist in the presence of excess transition metal was

Conclusions

The spectroscopic data presented here suggest a multiphasic complexation process for Group 12 elements by mb-SB2. When the peptide is present in excess, the absorption data suggests the formation of dimeric complexes, which give way to monomers as an equivalent ratio of peptide and transition metal is reached. A similar concentration-dependence was evident in the fluorescence data, at least initially, and we propose a mechanism for a strong transition-metal induced fluorescence enhancement. A

Authors contribution statement

PE, AJ, BG and EMP conceptualized the study and analyzed the absorbance and fluorescence data.

JR, RS, PE, AJ, EH, and EMP conceptualized, analyzed, and interpreted the X-ray absorption spectroscopy data.

JDS and AAD isolated the methanobactin SB2 samples. • All authors helped to interpret data, write, and edit the final manuscript.

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgments

This research was sponsored by the Office of Biological and Environmental Research (BER) within the Office of Science of the US Department of Energy (DOE), as part of the Subsurface Biogeochemical Research program Science Focus Area project at the Oak Ridge National Laboratory, which is managed by UT-Battelle, LLC under Contract No. DE-AC05-00OR22725 with DOE. This research was also supported by the BER within the Office of Science of the DOE under DE-SC00018059 and DE-SC0020174. The DOE will

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      Studies have also shown that methanobactin, a large chalkophore peptide produced by the methanotroph Methylosinus trichosporium OB3b, forms a tetrahedral coordination with the metal ion via 2 S and 2 N atoms (Baral et al., 2014; Semrau et al., 2018) and can substantially enhance Hg(II) methylation by PCA cells (Yin et al., 2020). However, a similar methanobactin produced by Methylocystis sp. strain SB2 forms a linear Hg(II)-S coordination with 2 S atoms (Eckert et al., 2021) and strongly inhibits Hg(II) methylation (Yin et al., 2020). It is thus concluded that Hg(II) coordination with OB3b-methanobactin likely facilitated the exchange and transfer of Hg(II) to certain cell surface binding sites, which may accept Hg(II) and direct it to the HgcAB proteins for methylation (Yin et al., 2020).

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