Ultrastructure of intracytoplasmic membranes of Methanomonas margaritae cells grown under different conditions

Copper-responsive gene expression in the methanotroph Methylosinus trichosporium OB3b

Methanotrophic bacteria convert methane to methanol using methane monooxygenase (MMO) enzymes. In many strains, either an iron-containing soluble (sMMO) or a copper-containing particulate (pMMO) enzyme can be produced depending on copper availability; the mechanism of this copper switch has not been elucidated. A key player in methanotroph copper homeostasis is methanobactin (Mbn), a ribosomally produced, post-translationally modified natural product with a high affinity for copper. The Mbn precursor peptide is encoded within an operon that contains a range of putative transporters, regulators, and biosynthetic proteins, but the involvement of these genes in Mbn-related processes remains unclear. Extensive time-dependent qRT-PCR studies of Methylosinus trichosporium OB3b and the constitutive sMMO-producing mutant M. trichosporium OB3b PP358 show that the Mbn operon is indeed copper-regulated, providing experimental support for its bioinformatics-based identification. Moreover, the Mbn operon is co-regulated with the sMMO operon and reciprocally regulated with the pMMO operon. Within the Mbn and sMMO operons, a subset of regulatory genes exhibits a distinct and shared pattern of expression, consistent with their proposed functions as internal regulators. In addition, genome sequencing of the M. trichosporium OB3b PP358 mutant provides new evidence for the involvement of genes adjacent to the pMMO operon in methanotroph copper homeostasis.

Methanobactin and the Link between Copper and Bacterial Methane Oxidation

Methanobactins (mbs) are low-molecular-mass (<1,200 Da) copper-binding peptides, or chalkophores, produced by many methane-oxidizing bacteria (methanotrophs). These molecules exhibit similarities to certain iron-binding siderophores but are expressed and secreted in response to copper limitation. Structurally, mbs are characterized by a pair of heterocyclic rings with associated thioamide groups that form the copper coordination site. One of the rings is always an oxazolone and the second ring an oxazolone, an imidazolone, or a pyrazinedione moiety. The mb molecule originates from a peptide precursor that undergoes a series of posttranslational modifications, including (i) ring formation, (ii) cleavage of a leader peptide sequence, and (iii) in some cases, addition of a sulfate group. Functionally, mbs represent the extracellular component of a copper acquisition system. Consistent with this role in copper acquisition, mbs have a high affinity for copper ions. Following binding, mbs rapidly reduce Cu(2+) to Cu(1+). In addition to binding copper, mbs will bind most transition metals and near-transition metals and protect the host methanotroph as well as other bacteria from toxic metals. Several other physiological functions have been assigned to mbs, based primarily on their redox and metal-binding properties. In this review, we examine the current state of knowledge of this novel type of metal-binding peptide. We also explore its potential applications, how mbs may alter the bioavailability of multiple metals, and the many roles mbs may play in the physiology of methanotrophs.

Bioconversion of natural gas to liquid fuel: opportunities and challenges

Natural gas is a mixture of low molecular weight hydrocarbon gases that can be generated from either fossil or anthropogenic resources. Although natural gas is used as a transportation fuel, constraints in storage, relatively low energy content (MJ/L), and delivery have limited widespread adoption. Advanced utilization of natural gas has been explored for biofuel production by microorganisms. In recent years, the aerobic bioconversion of natural gas (or primarily the methane content of natural gas) into liquid fuels (Bio-GTL) by biocatalysts (methanotrophs) has gained increasing attention as a promising alternative for drop-in biofuel production. Methanotrophic bacteria are capable of converting methane into microbial lipids, which can in turn be converted into renewable diesel via a hydrotreating process. In this paper, biodiversity, catalytic properties and key enzymes and pathways of these microbes are summarized. Bioprocess technologies are discussed based upon existing literature, including cultivation conditions, fermentation modes, bioreactor design, and lipid extraction and upgrading. This review also outlines the potential of Bio-GTL using methane as an alternative carbon source as well as the major challenges and future research needs of microbial lipid accumulation derived from methane, key performance index, and techno-economic analysis. An analysis of raw material costs suggests that methane-derived diesel fuel has the potential to be competitive with petroleum-derived diesel.

Soluble Methane Monooxygenase Production and Trichloroethylene Degradation by a Type I Methanotroph, Methylomonas methanica 68-1

A methanotroph (strain 68-1), originally isolated from a trichloroethylene (TCE)-contaminated aquifer, was identified as the type I methanotroph Methylomonas methanica on the basis of intracytoplasmic membrane ultrastructure, phospholipid fatty acid profile, and 16S rRNA signature probe hybridization. Strain 68-1 was found to oxidize naphthalene and TCE via a soluble methane monooxygenase (sMMO) and thus becomes the first type I methanotroph known to be able to produce this enzyme. The specific whole-cell sMMO activity of 68-1, as measured by the naphthalene oxidation assay and by TCE biodegradation, was comparatively higher than sMMO activity levels in Methylosinus trichosporium OB3b grown in the same copper-free conditions. The maximal naphthalene oxidation rates of Methylomonas methanica 68-1 and Methylosinus trichosporium OB3b were 551 +/- 27 and 321 +/- 16 nmol h mg of protein , respectively. The maximal TCE degradation rates of Methylomonas methanica 68-1 and Methylosinus trichosporium OB3b were 2,325 +/- 260 and 995 +/- 160 nmol h mg of protein, respectively. The substrate affinity of 68-1 sMMO to naphthalene (K(m), 70 +/- 4 muM) and TCE (K(m), 225 +/- 13 muM), however, was comparatively lower than that of the sMMO of OB3b, which had affinities of 40 +/- 3 and 126 +/- 8 muM, respectively. Genomic DNA slot and Southern blot analyses with an sMMO gene probe from Methylosinus trichosporium OB3b showed that the sMMO genes of 68-1 have little genetic homology to those of OB3b. This result may indicate the evolutionary diversification of the sMMOs.

Methanotrophs and copper

Methanotrophs, cells that consume methane (CH(4)) as their sole source of carbon and energy, play key roles in the global carbon cycle, including controlling anthropogenic and natural emissions of CH(4), the second-most important greenhouse gas after carbon dioxide. These cells have also been widely used for bioremediation of chlorinated solvents, and help sustain diverse microbial communities as well as higher organisms through the conversion of CH(4) to complex organic compounds (e.g. in deep ocean and subterranean environments with substantial CH(4) fluxes). It has been well-known for over 30 years that copper (Cu) plays a key role in the physiology and activity of methanotrophs, but it is only recently that we have begun to understand how these cells collect Cu, the role Cu plays in CH(4) oxidation by the particulate CH(4) monooxygenase, the effect of Cu on the proteome, and how Cu affects the ability of methanotrophs to oxidize different substrates. Here we summarize the current state of knowledge of the phylogeny, environmental distribution, and potential applications of methanotrophs for regional and global issues, as well as the role of Cu in regulating gene expression and proteome in these cells, its effects on enzymatic and whole-cell activity, and the novel Cu uptake system used by methanotrophs.

Methanotrophic bacteria

Methane-utilizing bacteria (methanotrophs) are a diverse group of gram-negative bacteria that are related to other members of the Proteobacteria. These bacteria are classified into three groups based on the pathways used for assimilation of formaldehyde, the major source of cell carbon, and other physiological and morphological features. The type I and type X methanotrophs are found within the gamma subdivision of the Proteobacteria and employ the ribulose monophosphate pathway for formaldehyde assimilation, whereas type II methanotrophs, which employ the serine pathway for formaldehyde assimilation, form a coherent cluster within the beta subdivision of the Proteobacteria. Methanotrophic bacteria are ubiquitous. The growth of type II bacteria appears to be favored in environments that contain relatively high levels of methane, low levels of dissolved oxygen, and limiting concentrations of combined nitrogen and/or copper. Type I methanotrophs appear to be dominant in environments in which methane is limiting and combined nitrogen and copper levels are relatively high. These bacteria serve as biofilters for the oxidation of methane produced in anaerobic environments, and when oxygen is present in soils, atmospheric methane is oxidized. Their activities in nature are greatly influenced by agricultural practices and other human activities. Recent evidence indicates that naturally occurring, uncultured methanotrophs represent new genera. Methanotrophs that are capable of oxidizing methane at atmospheric levels exhibit methane oxidation kinetics different from those of methanotrophs available in pure cultures. A limited number of methanotrophs have the genetic capacity to synthesize a soluble methane monooxygenase which catalyzes the rapid oxidation of environmental pollutants including trichloroethylene.

Localization of methanol dehydrogenase in two strains of methylotrophic bacteria detected by immunogold labeling

Antibodies to methanol dehydrogenase purified from Methylobacterium sp. strain AM1 and Methylomonas sp. strain A4 were raised. The antibody preparations were used in indirect immunogold labeling studies. With this approach, methanol dehydrogenase was found to be preferentially localized to the periplasmic region of the methylotroph Methylobacterium sp. strain AM1 and to the intracytoplasmic membrane of the methanotroph Methylomonas sp. strain A4. Antibody cross-reactivity to other methylotrophic bacteria was detected.

Effect of Copper on Methylomonas albus BG8

Addition of copper to the medium for Methylomonas albus BG8 increased cell yield and methane monooxygenase activity. Intracytoplasmic membrane was formed only in cells grown with copper supplementation. Additionally, the abundances of two major membrane proteins were affected by copper in the growth medium. These findings indicate that effects of copper on the physiology of methanotrophic bacteria are not limited to those on types II and X.

Characteristics of a nitrogen-fixing methanotroph, Methylocystis T-1

A methane-oxidizing bacterium capable of nitrogen fixation was isolated from soil taken from an area which leaked methane gas. Strain T-1 was a catalase and oxidase-positive, gram-negative straight rod-shaped strictly aerobic bacterium which formed lipid cysts and type II intracytoplasmic membranes. The organism was a microaerophilic nitrogen-fixing methanotroph. Strain T-1 is considered to be classified into Methylocystis. The organism evolved hydrogen gas when grown in the nitrogen-free medium of atmospheric oxygen concentrations of 1.5% or more. Below this level, however, hydrogen gas was not evolved. In addition to methanol, formaldehyde and formate, ethanol, acetate and hydrogen gas served as oxidizable substrates for the acetylene reduction test. H2-stimulated nitrogenase activity was limited in a very narrow range of oxygen concentration and not detected at 2% O2. With acetate as the substrate, however, about an 80% of the maximum acetylene reduction activity was detected at 2% O2. These results suggest that strain T-1 is capable of recycling the hydrogen gas evolved during nitrogen fixation under low partial pressures of O2.

Copper ions as inhibitors of protein C of soluble methane monooxygenase of Methylococcus capsulatus (Bath)

Copper(I), copper(II) and silver ions have been shown to be potent inhibitors of purified soluble methane monooxygenase (MMO) of Methylococcus capsulatus (Bath). A weaker inhibition has been observed with zinc and cadmium ions. Proteins A and B of soluble MMO are unaffected by copper but protein C is rapidly and irreversibly inhibited. The site of copper inhibition has been shown to be primarily at the iron-sulphur centre of protein C with a secondary effect at the FAD centre when the copper(II):protein C ratio is high. Copper appears to bring about the inhibition of soluble MMO by interacting with protein C to disrupt the protein structure causing, firstly, the loss of the iron-sulphur centre, preventing the transfer of electrons from protein C to protein A, and secondly, the loss of FAD preventing the protein from accepting electrons from NADH. Inhibition and spectral data are provided to support this thesis. The inactivation of protein C is associated with the tight binding of four Cu atoms to each protein C molecule. These data extend our knowledge of how copper, which is known to have a key role in the cellular location of MMO, interacts with and rapidly and irreversibly inactivates the soluble form of this enzyme.

Methane-oxidizing microorganisms

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