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Methanotrophic Bacteria: Use in Bioremediation

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TLDR
The methanotrophic bacteria that oxidize methane as an energy source and carbon source through the enzyme methane monooxygenase (MMO) can cometabolize or transform nongrowth substrates by either growing or resting cells as discussed by the authors.
Abstract
The methanotrophs are aerobic bacteria that oxidize methane as an energy source and carbon source through the enzyme methane monooxygenase (MMO). This MMO can cometabolize or transform nongrowth substrates by either growing or resting cells. Cometabolism is a result of nonspecific MMO activity towards organic compounds that do not serve as carbon or energy sources. While many cometabolizing bacterial species have been identified, the best studied are the methanotrophs. The reason for this is that methanotrophs are ubiquitous and can cometabolize many aliphatic compounds, alkanes, and aromatic compounds. Methanotrophs have been intensely studied for use in degrading chlorinated solvents, most notably trichloroethylene, to environmentally acceptable concentrations in soils, sediment, and groundwater. Stimulation of methanotrophic bacteria is accomplished through the addition of methane and other gaseous nutrients resulting in an increase in contaminant biodegradation and biotransformation. The composition of gaseous nutrients used with methane is dependent on the characteristics of the site geochemistry and microbiology. This biostimulation may be applied in situ within the contaminated aquifer or soil. If necessary, the contaminated soil or groundwater can be moved and treated ex situ based on the site-specific needs.

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Involvement of Linear Plasmids in Aerobic Biodegradation of Vinyl Chloride

TL;DR: Metabolism of VC and ethene by strains AJ and TD is initiated by an alkene monooxygenase, and this process occurs at many but not all sites where groundwater is contaminated with chloroethenes.
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Bioaugmentation of chlorothalonil-contaminated soil with hydrolytically or reductively dehalogenating strain and its effect on soil microbial community.

TL;DR: In insights into the effects of halogenated fungicide application and bioaugmentation on indigenous soil microbiomes, little influence on soil microbial community was observed for each inoculation treatment, showing that TPN treatment is the main force for the shift in indigenous consortia.
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Copper Biogeochemistry: A Cornerstone in Aerobic Methanotrophic Bacterial Ecology and Activity?

TL;DR: This discussion is focused on methanotrohphic bacterial population dynamics observed during growth on various copper species, to extrapolate their impact on geomicrobiological processes.

The interactions between xenobiotics and soil microbial communities

Smriti Rayu
TL;DR: In this article, the authors investigated the impact of industrial xenobiotics on soil microbial communities and their functional capabilities, with particular focus on widely used pesticides (chlorpyrifos and imidacloprid) and industrial solvents (trichloroethene).
Journal ArticleDOI

Native hydrocarbonoclastic bacteria and hydrocarbon mineralization processes

TL;DR: In this paper, the authors have isolated fourteen hydrocarbonoclastic bacterial strains from the crude oil contaminated soil of Assam, India, which were designated as RC1-RC14 that includes Alcaligenes, Bacillus, Enterobacter, and Pseudomonas species; which were able to metabolize crude oil to different extents.
References
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Journal ArticleDOI

Trichloroethylene biodegradation by a methane-oxidizing bacterium.

TL;DR: It is proposed that TCE biodegradation by methanotrophs occurs by formation of TCE epoxide, which breaks down spontaneously in water to form dichloroacetic and glyoxylic acids and one-carbon products.
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Product toxicity and cometabolic competitive inhibition modeling of chloroform and trichloroethylene transformation by methanotrophic resting cells.

TL;DR: Significantly diminished formate oxidation by cells exposed to either CR or TCE without acetylene compared with that with acetylene suggests that the solvents themselves were not toxic under the experimental conditions but their transformation products were, suggesting a greater toxicity from CF transformation.
Journal ArticleDOI

Microbial degradation of trichloroethylene in the rhizosphere: potential application to biological remediation of waste sites

TL;DR: Biomass determinations, disappearance of TCE from the headspace of spiked soil slurries, and mineralization of [14C]TCE to 14CO2 all showed that microbial activity is greater in rhizosphere soils and that TCE degradation occurs faster in therhizosphere than in the edaphosphere, suggesting vegetation may be an important variable in the biological restoration of surface and near-surface soils.
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Trending Questions (2)
Is natural gas toxic for aerobic methanotrophic bacteria ?

The paper does not directly mention whether natural gas is toxic for aerobic methanotrophic bacteria.

Is there any contest between methanotrophic and methanogenic bacteria?

The provided paper does not mention any contest between methanotrophic and methanogenic bacteria.