Heterologous Biosynthesis of Methanobactin from Methylocystis sp. Strain SB2 in Methylosinus trichosporium OB3b.

Aerobic methanotrophs, or methane-consuming microbes, are strongly dependent on copper for their activity. To satisfy this requirement, some methanotrophs produce a copper-binding compound, or chalkophore, called methanobactin (MB). In addition to playing a critical role in methanotrophy, MB has also been shown to have great promise in treating copper-related human diseases, perhaps most significantly Wilson's disease. In this congenital disorder, copper builds up in the liver, leading to irreversible damage and, in severe cases, complete organ failure. Remarkably, MB has been shown to reverse such damage in animal models, and there is a great deal of interest in upscaling MB production for expanded clinical trials. Such efforts, however, are currently hampered as (1) the natural rate of MB production rate by methanotrophs is low, (2) the use of methane as a substrate for MB production is problematic as it is explosive in air, (3) there is limited understanding of the entire pathway of MB biosynthesis, and (4) the most attractive form of MB is produced by Methylocystis sp. strain SB2, a methanotroph that is genetically intractable. Herein, we report heterologous biosynthesis of MB from Methylocystis sp. strain SB2 in an alternative methanotroph, Methylosinus trichosporium OB3b, not only on methane but also on methanol. As a result, the strategy described herein not only facilitates enhanced MB production but also provides opportunities to construct various mutants to delineate the entire pathway of MB biosynthesis, as well as the creation of modified forms of MB that may have enhanced therapeutic value.

Purification and biochemical characterization of methanobactin biosynthetic enzymes.

Methanobactin (Mbn) is a ribosomally synthesized and post-translationally modified peptide (RiPP) natural product that binds Cu(I) with high affinity. The copper-chelating thioamide/oxazolone groups in Mbn are installed on the precursor peptide MbnA by the core enzyme complex, MbnBC, which includes the multinuclear non-heme iron-dependent oxidase (MNIO) MbnB and its RiPP recognition element-containing partner protein MbnC. For the extensively characterized Mbn biosynthetic gene cluster (BGC) from the methanotroph Methylosinus trichosporium OB3b, the tailoring aminotransferase MbnN further modifies MbnA after leader sequence cleavage by an unknown mechanism. Here we detail methods to express and purify M. trichosporium OB3b MbnBC and MbnN along with protocols for assessing MbnA modification by MbnBC and MbnN aminotransferase activity. In addition, we describe crystallization and structure determination of MbnBC. These procedures can be adapted for other MNIOs and partner proteins encoded in Mbn and Mbn-like BGCs. Furthermore, these methods provide a first step toward in vitro biosynthesis of Mbns and related natural products as potential therapeutics.

Methylosinus trichosporium OB3b bioaugmentation unleashes polyhydroxybutyrate-accumulating potential in waste-activated sludge.

BACKGROUND: Wastewater treatment plants contribute approximately 6% of anthropogenic methane emissions. Methanotrophs, capable of converting methane into polyhydroxybutyrate (PHB), offer a promising solution for utilizing methane as a carbon source, using activated sludge as a seed culture for PHB production. However, maintaining and enriching PHB-accumulating methanotrophic communities poses challenges. RESULTS: This study investigated the potential of Methylosinus trichosporium OB3b to bioaugment PHB-accumulating methanotrophic consortium within activated sludge to enhance PHB production. Waste-activated sludges with varying ratios of M. trichosporium OB3b (1:0, 1:1, 1:4, and 0:1) were cultivated. The results revealed substantial growth and methane consumption in waste-activated sludge with M. trichosporium OB3b-amended cultures, particularly in a 1:1 ratio. Enhanced PHB accumulation, reaching 37.1% in the same ratio culture, indicates the dominance of Type II methanotrophs. Quantification of methanotrophs by digital polymerase chain reaction showed gradual increases in Type II methanotrophs, correlating with increased PHB production. However, while initial bioaugmentation of M. trichosporium OB3b was observed, its presence decreased in subsequent cycles, indicating the dominance of other Type II methanotrophs. Microbial community analysis highlighted the successful enrichment of Type II methanotrophs-dominated cultures due to the addition of M. trichosporium OB3b, outcompeting Type I methanotrophs. Methylocystis and Methylophilus spp. were the most abundant in M. trichosporium OB3b-amended cultures. CONCLUSIONS: Bioaugmentation strategies, leveraging M. trichosporium OB3b could significantly enhance PHB production and foster the enrichment of PHB-accumulating methanotrophs in activated sludge. These findings contribute to integrating PHB production in wastewater treatment plants, providing a sustainable solution for resource recovery.

Solid phase speciation controls copper mobilisation from marine sediments by methanobactin.

Although marine environments represent huge reservoirs of the potent greenhouse gas methane, they currently contribute little to global net methane emissions. Most of the methane is oxidized by methanotrophs, minimizing escape to the atmosphere. Aerobic methanotrophs oxidize methane mostly via the copper (Cu)-bearing enzyme particulate methane monooxygenase (pMMO). Therefore, aerobic methane oxidation depends on sufficient Cu acquisition by methanotrophs. Because they require both oxygen and methane, aerobic methanotrophs reside at oxic-anoxic interfaces, often close to sulphidic zones where Cu bioavailability can be limited by poorly soluble Cu sulphide mineral phases. Under Cu-limiting conditions, certain aerobic methanotrophs exude Cu-binding ligands termed chalkophores, such as methanobactin (mb) exuded by Methylosinus trichosporium OB3b. Our main objective was to establish whether chalkophores can mobilise Cu from Cu sulphide-bearing marine sediments to enhance Cu bioavailability. Through a series of kinetic batch experiments, we investigated Cu mobilisation by mb from a set of well-characterized sulphidic marine sediments differing in sediment properties, including Cu content and phase distribution. Characterization of solid-phase Cu speciation included X-ray absorption spectroscopy and a targeted sequential extraction. Furthermore, in batch experiments, we investigated to what extent adsorption of metal-free mb and Cu-mb complexes to marine sediments constrains Cu mobilisation. Our results are the first to show that both solid phase Cu speciation and chalkophore adsorption can constrain methanotrophic Cu acquisition from marine sediments. Only for certain sediments did mb addition enhance dissolved Cu concentrations. Cu mobilisation by mb was not correlated to the total Cu content of the sediment, but was controlled by solid-phase Cu speciation. Cu was only mobilised from sediments containing a mono-Cu-sulphide (CuSx) phase. We also show that mb adsorption to sediments limits Cu acquisition by mb to less compact (surface) sediments. Therefore, in sulphidic sediments, mb-mediated Cu acquisition is presumably constrained to surface-sediment interfaces containing mono-Cu-sulphide phases.

Advances in degradation of chlorinated hydrocarbons by obligate and facultative methanotrophs / 生物工程学报

Bioremediation is one of the most effective ways to treat and dispose of chlorinated hydrocarbons, and methanotrophs are potentially useful to do so. Recent studies found that facultative methanotrophs can use compounds containing C-C bond as sources of carbon and energy, thus overcoming the limitation that obligate methanotrophsone uses only C1 compounds for this process. This is a unique metabolic approach that is becoming increasingly attractive in the field of contaminant biodegradation. Here, we summarized the bioremediation of chlorinated hydrocarbons by obligate and facultative methanotrophs. This process involves the degradation of various chlorinated hydrocarbons by diverse strains, including pure cultures and mixed cultures. We also compare the activity expression and catalytic properties of different types of methane monooxygenases in various substrates. We furthermore summarize the kinetic characteristics of the degradation of chlorinated hydrocarbons using the model strain Methylosinus trichosporium OB3b, and outline the degradation and potential of chlorinated hydrocarbons by facultative methanotrophs. Lastly, we discuss current problems and future research directions for degradation of chlorinated hydrocarbons by methanotrophs.

Analysis of methane biodegradation by Methylosinus trichosporium OB3b / Análise da biodegradação de metano por Methylosinus trichosporium OB3b

The microbial oxidation of methane in the atmosphere is performed by methanotrophic bacteria that use methane as a unique source of carbon and energy. The objective of this work consisted of the investigation of the best conditions of methane biodegradation by methanotrophic bacteria Methylosinus trichosporium OB3b that oxidize it to carbon dioxide, and the use of these microorganisms in monitoring methods for methane. The results showed that M. trichosporium OB3b was capable to degrade methane in a more effective way with an initial microorganism concentration of 0.0700 g.L-1, temperature of 30ºC, pH 6.5 and using 1.79 mmol of methane. In these same conditions, there was no bacterial growth when 2.69 mmol of methane was used. The specific rate of microorganism growth, the conversion factor, the efficiency and the volumetric productivity, for the optimized conditions of biodegradation were, respectively, 0.0324 h-1, 0.6830 gcells/gCH4, 73.73% and 2.7732.10-3 gcells/L.h. The final product of methane microbiological degradation, carbon dioxide, was quantified through the use of a commercial electrode, and, through this, the grade of methane conversion in carbon dioxide was calculated.

A oxidação microbiológica de metano na atmosfera é realizada por bactérias metanotróficas, que o utilizam como fonte única de carbono e energia. O objetivo deste trabalho consistiu na investigação das melhores condições de biodegradação do metano por bactérias metanotróficas Methylosinus trichosporium OB3b, que o oxidam a dióxido de carbono, para o emprego destes microrganismos em métodos de monitoração para metano. Os resultados obtidos mostraram que M.trichosporium OB3b foi capaz de degradar o metano de forma mais eficaz partindo-se de uma concentração inicial de microrganismos de 0.0700 g.L-1, a uma temperatura de 30ºC, pH igual a 6.5 e empregando-se 1.79 mmol de metano. Nestas mesmas condições, não houve crescimento bacteriano quando foram empregados 2.69 mmol de metano. A taxa específica de crescimento do microrganismo, o fator de conversão, a eficiência e a produtividade volumétrica para as condições otimizadas de biodegradação foram, respectivamente, 0.0324 h-1, 0.6830 gcélulas/gCH4, 73.73% e 2.7732.10-3 gcélulas/L.h. O produto final da degradação microbiológica do metano, o dióxido de carbono, foi quantificado através do emprego de um eletrodo comercial, e, através desta medida, foi calculado o percentual de conversão de metano em dióxido de carbono.

Methane monooxygenases hydroxylase from a type II methanotroph: purification and physical-chemical properties / 生物工程学报

Methanotrophs can catalyze hydroxylate of methane and some hydrocarbon. Which play an important role in mitigating global warming and have also potential significance for industrial applications or bioremediation. A high activity of hydroxylase, a crucial component in sMMO, from Methylosinus trichosporium IMV 3011 has been purified to homologues by using chromatographic techniques. The molecular weight of the hydroxylase determined by gel filtration is 201.3 kD, and SDS-PAGE showed that hydroxylase consists of three subunits(alpha beta gamma) with molecular weights of 58kD, 36kD and 23kD respectively, drawing a comparison both methods indicated that the hydroxylase is a homodimer with an (alpha beta gamma)2 configuration. Purified hydroxylase has a pI at 5.2 judged by thin layer isoelectric focusing. The purified hydroxylase contains 3.02 mol of iron per mol of protein. The stability pH for the hydroxylase in solution is 5.8-8.0 and the stability temperature is below 35 degrees C. The cells form show a long, bent, and rod-shaped with even surface observed by scanning electron microscopy.