Genome-Scale Metabolic Reconstruction and Metabolic Versatility of an Obligate Methanotroph Methylococcus Capsulatus Str. Bath
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Hydrogen Isotope Fractionation in Lipids of the Methane-Oxidizing Bacterium Methylococcus Capsulatus
Geochimica et Cosmochimica Acta, Vol. 66, No. 22, pp. 3955–3969, 2002 Copyright © 2002 Elsevier Science Ltd Pergamon Printed in the USA. All rights reserved 0016-7037/02 $22.00 ϩ .00 PII S0016-7037(02)00981-X Hydrogen isotope fractionation in lipids of the methane-oxidizing bacterium Methylococcus capsulatus 1, 2 3 1 ALEX L. SESSIONS, *LINDA L. JAHNKE, ARNDT SCHIMMELMANN, and JOHN M. HAYES 1Department of Geology and Geophysics, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA 2Exobiology Branch, NASA-Ames Research Center, Moffett Field, CA 94035, USA 3Biogeochemical Laboratories, Department of Geological Sciences, Indiana University, Bloomington, IN 47405, USA (Received December 10, 2001; accepted in revised form June 7, 2002) Abstract—Hydrogen isotopic compositions of individual lipids from Methylococcus capsulatus, an aerobic, methane-oxidizing bacterium, were analyzed by hydrogen isotope-ratio-monitoring gas chromatography–mass spectrometry (GC-MS). The purposes of the study were to measure isotopic fractionation factors between methane, water, and lipids and to examine the biochemical processes that determine the hydrogen isotopic composition of lipids. M. capsulatus was grown in six replicate cultures in which the ␦D values of methane and water were varied independently. Measurement of concomitant changes in ␦D values of lipids allowed estimation of the proportion of hydrogen derived from each source and the isotopic fractionation associated with the utilization of each source. All lipids examined, including fatty acids, sterols, and hopanols, derived 31.4 Ϯ 1.7% of their hydrogen from methane. This was apparently true whether the cultures were harvested during exponential or stationary phase. Examination of the relevant biochemical pathways indicates that no hydrogen is transferred directly (with C-H bonds intact) from methane to lipids. -
Reduced Net Methane Emissions Due to Microbial Methane Oxidation in a Warmer Arctic
LETTERS https://doi.org/10.1038/s41558-020-0734-z Reduced net methane emissions due to microbial methane oxidation in a warmer Arctic Youmi Oh 1, Qianlai Zhuang 1,2,3 ✉ , Licheng Liu1, Lisa R. Welp 1,2, Maggie C. Y. Lau4,9, Tullis C. Onstott4, David Medvigy 5, Lori Bruhwiler6, Edward J. Dlugokencky6, Gustaf Hugelius 7, Ludovica D’Imperio8 and Bo Elberling 8 Methane emissions from organic-rich soils in the Arctic have bacteria (methanotrophs) and the remainder is mostly emitted into been extensively studied due to their potential to increase the atmosphere (Fig. 1a). The methanotrophs in these wet organic the atmospheric methane burden as permafrost thaws1–3. soils may be low-affinity methanotrophs (LAMs) that require However, this methane source might have been overestimated >600 ppm of methane (by moles) for their growth and mainte- without considering high-affinity methanotrophs (HAMs; nance23. But in dry mineral soils, the dominant methanotrophs are methane-oxidizing bacteria) recently identified in Arctic min- high-affinity methanotrophs (HAMs), which can survive and grow 4–7 eral soils . Herein we find that integrating the dynamics of at a level of atmospheric methane abundance ([CH4]atm) of about HAMs and methanogens into a biogeochemistry model8–10 1.8 ppm (Fig. 1b)24. that includes permafrost soil organic carbon dynamics3 leads Quantification of the previously underestimated HAM-driven −1 to the upland methane sink doubling (~5.5 Tg CH4 yr ) north of methane sink is needed to improve our understanding of Arctic 50 °N in simulations from 2000–2016. The increase is equiva- methane budgets. -
Supplementary Information for Microbial Electrochemical Systems Outperform Fixed-Bed Biofilters for Cleaning-Up Urban Wastewater
Electronic Supplementary Material (ESI) for Environmental Science: Water Research & Technology. This journal is © The Royal Society of Chemistry 2016 Supplementary information for Microbial Electrochemical Systems outperform fixed-bed biofilters for cleaning-up urban wastewater AUTHORS: Arantxa Aguirre-Sierraa, Tristano Bacchetti De Gregorisb, Antonio Berná, Juan José Salasc, Carlos Aragónc, Abraham Esteve-Núñezab* Fig.1S Total nitrogen (A), ammonia (B) and nitrate (C) influent and effluent average values of the coke and the gravel biofilters. Error bars represent 95% confidence interval. Fig. 2S Influent and effluent COD (A) and BOD5 (B) average values of the hybrid biofilter and the hybrid polarized biofilter. Error bars represent 95% confidence interval. Fig. 3S Redox potential measured in the coke and the gravel biofilters Fig. 4S Rarefaction curves calculated for each sample based on the OTU computations. Fig. 5S Correspondence analysis biplot of classes’ distribution from pyrosequencing analysis. Fig. 6S. Relative abundance of classes of the category ‘other’ at class level. Table 1S Influent pre-treated wastewater and effluents characteristics. Averages ± SD HRT (d) 4.0 3.4 1.7 0.8 0.5 Influent COD (mg L-1) 246 ± 114 330 ± 107 457 ± 92 318 ± 143 393 ± 101 -1 BOD5 (mg L ) 136 ± 86 235 ± 36 268 ± 81 176 ± 127 213 ± 112 TN (mg L-1) 45.0 ± 17.4 60.6 ± 7.5 57.7 ± 3.9 43.7 ± 16.5 54.8 ± 10.1 -1 NH4-N (mg L ) 32.7 ± 18.7 51.6 ± 6.5 49.0 ± 2.3 36.6 ± 15.9 47.0 ± 8.8 -1 NO3-N (mg L ) 2.3 ± 3.6 1.0 ± 1.6 0.8 ± 0.6 1.5 ± 2.0 0.9 ± 0.6 TP (mg -
Table S4. Phylogenetic Distribution of Bacterial and Archaea Genomes in Groups A, B, C, D, and X
Table S4. Phylogenetic distribution of bacterial and archaea genomes in groups A, B, C, D, and X. Group A a: Total number of genomes in the taxon b: Number of group A genomes in the taxon c: Percentage of group A genomes in the taxon a b c cellular organisms 5007 2974 59.4 |__ Bacteria 4769 2935 61.5 | |__ Proteobacteria 1854 1570 84.7 | | |__ Gammaproteobacteria 711 631 88.7 | | | |__ Enterobacterales 112 97 86.6 | | | | |__ Enterobacteriaceae 41 32 78.0 | | | | | |__ unclassified Enterobacteriaceae 13 7 53.8 | | | | |__ Erwiniaceae 30 28 93.3 | | | | | |__ Erwinia 10 10 100.0 | | | | | |__ Buchnera 8 8 100.0 | | | | | | |__ Buchnera aphidicola 8 8 100.0 | | | | | |__ Pantoea 8 8 100.0 | | | | |__ Yersiniaceae 14 14 100.0 | | | | | |__ Serratia 8 8 100.0 | | | | |__ Morganellaceae 13 10 76.9 | | | | |__ Pectobacteriaceae 8 8 100.0 | | | |__ Alteromonadales 94 94 100.0 | | | | |__ Alteromonadaceae 34 34 100.0 | | | | | |__ Marinobacter 12 12 100.0 | | | | |__ Shewanellaceae 17 17 100.0 | | | | | |__ Shewanella 17 17 100.0 | | | | |__ Pseudoalteromonadaceae 16 16 100.0 | | | | | |__ Pseudoalteromonas 15 15 100.0 | | | | |__ Idiomarinaceae 9 9 100.0 | | | | | |__ Idiomarina 9 9 100.0 | | | | |__ Colwelliaceae 6 6 100.0 | | | |__ Pseudomonadales 81 81 100.0 | | | | |__ Moraxellaceae 41 41 100.0 | | | | | |__ Acinetobacter 25 25 100.0 | | | | | |__ Psychrobacter 8 8 100.0 | | | | | |__ Moraxella 6 6 100.0 | | | | |__ Pseudomonadaceae 40 40 100.0 | | | | | |__ Pseudomonas 38 38 100.0 | | | |__ Oceanospirillales 73 72 98.6 | | | | |__ Oceanospirillaceae -
Novel Methanotrophs of the Family Methylococcaceae from Different Geographical Regions and Habitats
Microorganisms 2015, 3, 484-499; doi:10.3390/microorganisms3030484 OPEN ACCESS microorganisms ISSN 2076-2607 www.mdpi.com/journal/microorganisms Article Novel Methanotrophs of the Family Methylococcaceae from Different Geographical Regions and Habitats Tajul Islam 1,*, Øivind Larsen 2, Vigdis Torsvik 1, Lise Øvreås 1, Hovik Panosyan 3, J. Colin Murrell 4, Nils-Kåre Birkeland 1 and Levente Bodrossy 5 1 Department of Biology, University of Bergen, Thormøhlensgate 53B, Postboks 7803, 5006 Bergen, Norway; E-Mails: [email protected] (V.T.); [email protected] (L.Ø.); [email protected] (N.-K.B.) 2 Uni Research Environment, Thormøhlensgate 49B, 5006 Bergen, Norway; E-Mail: [email protected] 3 Department of Microbiology, Plant and Microbe Biotechnology, Yerevan State University, A. Manoogian 1, 0025 Yarevan, Armenia; E-Mail: [email protected] 4 School of Environmental Sciences, University of East Anglia, Norwich Research Park, Norwich, NR4 7TJ, UK; E-Mail: [email protected] 5 Commonwealth Scientific and Industrial Research Organization (CSIRO), Marine and Atmospheric Research and Wealth from Oceans National Research Flagship, Hobart, TAS 7004, Australia; E-Mail: [email protected] * Author to whom correspondence should be addressed; E-Mail: [email protected]; Tel./Fax: +47-5558-4400. Academic Editors: Ricardo Amils and Elena González Toril Received: 10 July 2015 / Accepted: 7 August 2015 / Published: 21 August 2015 Abstract: Terrestrial methane seeps and rice paddy fields are important ecosystems in the methane cycle. Methanotrophic bacteria in these ecosystems play a key role in reducing methane emission into the atmosphere. Here, we describe three novel methanotrophs, designated BRS-K6, GFS-K6 and AK-K6, which were recovered from three different habitats in contrasting geographic regions and ecosystems: waterlogged rice-field soil and methane seep pond sediments from Bangladesh; and warm spring sediments from Armenia. -
The Ratio of Methanogens to Methanotrophs and Water-Level Dynamics Drive Methane Exchange Velocity in a Temperate Kettle-Hole Peat Bog
Biogeosciences Discuss., https://doi.org/10.5194/bg-2019-116 Manuscript under review for journal Biogeosciences Discussion started: 23 April 2019 c Author(s) 2019. CC BY 4.0 License. The ratio of methanogens to methanotrophs and water-level dynamics drive methane exchange velocity in a temperate kettle-hole peat bog Camilo Rey-Sanchez1,4, Gil Bohrer1, Julie Slater2, Yueh-Fen Li3, Roger Grau-Andrés2, Yushan Hao2, 5 Virginia I. Rich3, & G. Matt Davies2 1Department of Civil and Environmental Engineering and Geodetic Science, The Ohio State University, Columbus, Ohio, 43210, USA 2School of Environment and Natural Resources, The Ohio State University, Columbus, Ohio, 43210, USA 3Department of Microbiology, The Ohio State University, Columbus, Ohio, 43210, USA 10 4Current address, Department of Environmental Science, Management and Policy, University of California- Berkeley, California, 94720, USA Correspondence to: Camilo Rey-Sanchez ([email protected]) 15 Abstract. Peatlands are a large source of methane (CH4) to the atmosphere, yet the uncertainty around the estimates of CH4 flux from peatlands is large. To better understand the spatial heterogeneity in temperate peatland CH4 emissions and their response to physical and biological drivers, we studied CH4 dynamics throughout the growing seasons of 2017 and 2018 in Flatiron Lake Bog, a kettle-hole peat bog in Ohio. The site is composed of six different hydro-biological zones: an open water zone, four concentric vegetation zones surrounding the open water, and a restored zone connected to the main bog by a narrow 20 channel. At each of these locations, we monitored water level (WL), CH4 pore-water concentration at different peat depths, CH4 fluxes from the ground and from representative plant species using chambers, and microbial community composition with focus here on known methanogens and methanotrophs. -
Downloaded from the Fungene Database (
bioRxiv preprint doi: https://doi.org/10.1101/2020.09.21.307504; this version posted September 22, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission. Enhancement of nitrous oxide emissions in soil microbial consortia via copper competition between proteobacterial methanotrophs and denitrifiers Jin Chang,a,b Daehyun Daniel Kim,a Jeremy D. Semrau,b Juyong Lee,a Hokwan Heo,a Wenyu Gu,b* Sukhwan Yoona# aDepartment of Civil and Environmental Engineering, Korea Advanced Institute of Science and Technology, Daejeon, 34141, Korea bDepartment of Civil and Environmental Engineering, University of Michigan, Ann Arbor, MI, 48109 Running Title: Methanotrophic influence on N2O emissions #Address correspondence to Sukhwan Yoon, [email protected]. *Present address: Department of Civil & Environmental Engineering, Stanford University, Palo Alto CA, 94305 bioRxiv preprint doi: https://doi.org/10.1101/2020.09.21.307504; this version posted September 22, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission. Abstract Unique means of copper scavenging have been identified in proteobacterial methanotrophs, particularly the use of methanobactin, a novel ribosomally synthesized post-translationally modified polypeptide that binds copper with very high affinity. The possibility that copper sequestration strategies of methanotrophs may interfere with copper uptake of denitrifiers in situ and thereby enhance N2O emissions was examined using a suite of laboratory experiments performed with rice paddy microbial consortia. Addition of purified methanobactin from Methylosinus trichosporium OB3b to denitrifying rice paddy soil microbial consortia resulted in substantially increased N2O production, with more pronounced responses observed for soils with lower copper content. -
Methane Utilization in Methylomicrobium Alcaliphilum 20ZR: a Systems Approach Received: 8 September 2017 Ilya R
www.nature.com/scientificreports OPEN Methane utilization in Methylomicrobium alcaliphilum 20ZR: a systems approach Received: 8 September 2017 Ilya R. Akberdin1,2, Merlin Thompson1, Richard Hamilton1, Nalini Desai3, Danny Alexander3, Accepted: 22 January 2018 Calvin A. Henard4, Michael T. Guarnieri4 & Marina G. Kalyuzhnaya1 Published: xx xx xxxx Biological methane utilization, one of the main sinks of the greenhouse gas in nature, represents an attractive platform for production of fuels and value-added chemicals. Despite the progress made in our understanding of the individual parts of methane utilization, our knowledge of how the whole-cell metabolic network is organized and coordinated is limited. Attractive growth and methane-conversion rates, a complete and expert-annotated genome sequence, as well as large enzymatic, 13C-labeling, and transcriptomic datasets make Methylomicrobium alcaliphilum 20ZR an exceptional model system for investigating methane utilization networks. Here we present a comprehensive metabolic framework of methane and methanol utilization in M. alcaliphilum 20ZR. A set of novel metabolic reactions governing carbon distribution across central pathways in methanotrophic bacteria was predicted by in-silico simulations and confrmed by global non-targeted metabolomics and enzymatic evidences. Our data highlight the importance of substitution of ATP-linked steps with PPi-dependent reactions and support the presence of a carbon shunt from acetyl-CoA to the pentose-phosphate pathway and highly branched TCA cycle. The diverged TCA reactions promote balance between anabolic reactions and redox demands. The computational framework of C1-metabolism in methanotrophic bacteria can represent an efcient tool for metabolic engineering or ecosystem modeling. Climate change concerns linked to increasing concentrations of anthropogenic methane have spiked inter- est in biological methane utilization as a novel platform for improving ecological and human well-being1–4. -
(Antarctica) Glacial, Basal, and Accretion Ice
CHARACTERIZATION OF ORGANISMS IN VOSTOK (ANTARCTICA) GLACIAL, BASAL, AND ACCRETION ICE Colby J. Gura A Thesis Submitted to the Graduate College of Bowling Green State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE December 2019 Committee: Scott O. Rogers, Advisor Helen Michaels Paul Morris © 2019 Colby Gura All Rights Reserved iii ABSTRACT Scott O. Rogers, Advisor Chapter 1: Lake Vostok is named for the nearby Vostok Station located at 78°28’S, 106°48’E and at an elevation of 3,488 m. The lake is covered by a glacier that is approximately 4 km thick and comprised of 4 different types of ice: meteoric, basal, type 1 accretion ice, and type 2 accretion ice. Six samples were derived from the glacial, basal, and accretion ice of the 5G ice core (depths of 2,149 m; 3,501 m; 3,520 m; 3,540 m; 3,569 m; and 3,585 m) and prepared through several processes. The RNA and DNA were extracted from ultracentrifugally concentrated meltwater samples. From the extracted RNA, cDNA was synthesized so the samples could be further manipulated. Both the cDNA and the DNA were amplified through polymerase chain reaction. Ion Torrent primers were attached to the DNA and cDNA and then prepared to be sequenced. Following sequencing the sequences were analyzed using BLAST. Python and Biopython were then used to collect more data and organize the data for manual curation and analysis. Chapter 2: As a result of the glacier and its geographic location, Lake Vostok is an extreme and unique environment that is often compared to Jupiter’s ice-covered moon, Europa. -
Large Scale Biogeography and Environmental Regulation of 2 Methanotrophic Bacteria Across Boreal Inland Waters
1 Large scale biogeography and environmental regulation of 2 methanotrophic bacteria across boreal inland waters 3 running title : Methanotrophs in boreal inland waters 4 Sophie Crevecoeura,†, Clara Ruiz-Gonzálezb, Yves T. Prairiea and Paul A. del Giorgioa 5 aGroupe de Recherche Interuniversitaire en Limnologie et en Environnement Aquatique (GRIL), 6 Département des Sciences Biologiques, Université du Québec à Montréal, Montréal, Québec, Canada 7 bDepartment of Marine Biology and Oceanography, Institut de Ciències del Mar (ICM-CSIC), Barcelona, 8 Catalunya, Spain 9 Correspondence: Sophie Crevecoeur, Canada Centre for Inland Waters, Water Science and Technology - 10 Watershed Hydrology and Ecology Research Division, Environment and Climate Change Canada, 11 Burlington, Ontario, Canada, e-mail: [email protected] 12 † Current address: Canada Centre for Inland Waters, Water Science and Technology - Watershed Hydrology and Ecology Research Division, Environment and Climate Change Canada, Burlington, Ontario, Canada 1 13 Abstract 14 Aerobic methanotrophic bacteria (methanotrophs) use methane as a source of carbon and energy, thereby 15 mitigating net methane emissions from natural sources. Methanotrophs represent a widespread and 16 phylogenetically complex guild, yet the biogeography of this functional group and the factors that explain 17 the taxonomic structure of the methanotrophic assemblage are still poorly understood. Here we used high 18 throughput sequencing of the 16S rRNA gene of the bacterial community to study the methanotrophic 19 community composition and the environmental factors that influence their distribution and relative 20 abundance in a wide range of freshwater habitats, including lakes, streams and rivers across the boreal 21 landscape. Within one region, soil and soil water samples were additionally taken from the surrounding 22 watersheds in order to cover the full terrestrial-aquatic continuum. -
The Methanol Dehydrogenase Gene, Mxaf, As a Functional and Phylogenetic Marker for Proteobacterial Methanotrophs in Natural Environments
The Methanol Dehydrogenase Gene, mxaF, as a Functional and Phylogenetic Marker for Proteobacterial Methanotrophs in Natural Environments The Harvard community has made this article openly available. Please share how this access benefits you. Your story matters Citation Lau, Evan, Meredith C. Fisher, Paul A. Steudler, and Colleen Marie Cavanaugh. 2013. The methanol dehydrogenase gene, mxaF, as a functional and phylogenetic marker for proteobacterial methanotrophs in natural environments. PLoS ONE 8(2): e56993. Published Version doi:10.1371/journal.pone.0056993 Citable link http://nrs.harvard.edu/urn-3:HUL.InstRepos:11807572 Terms of Use This article was downloaded from Harvard University’s DASH repository, and is made available under the terms and conditions applicable to Open Access Policy Articles, as set forth at http:// nrs.harvard.edu/urn-3:HUL.InstRepos:dash.current.terms-of- use#OAP The Methanol Dehydrogenase Gene, mxaF,asa Functional and Phylogenetic Marker for Proteobacterial Methanotrophs in Natural Environments Evan Lau1,2*, Meredith C. Fisher2, Paul A. Steudler3, Colleen M. Cavanaugh2 1 Department of Natural Sciences and Mathematics, West Liberty University, West Liberty, West Virginia, United States of America, 2 Department of Organismic and Evolutionary Biology, Harvard University, Cambridge, Massachusetts, United States of America, 3 The Ecosystems Center, Marine Biological Laboratory, Woods Hole, Massachusetts, United States of America Abstract The mxaF gene, coding for the large (a) subunit of methanol dehydrogenase, is highly conserved among distantly related methylotrophic species in the Alpha-, Beta- and Gammaproteobacteria. It is ubiquitous in methanotrophs, in contrast to other methanotroph-specific genes such as the pmoA and mmoX genes, which are absent in some methanotrophic proteobacterial genera. -
Nitrification 31
NITROGEN IN SOILS/Nitrification 31 See also: Eutrophication; Greenhouse Gas Emis- Powlson DS (1993) Understanding the soil nitrogen cycle. sions; Isotopes in Soil and Plant Investigations; Soil Use and Management 9: 86–94. Nitrogen in Soils: Cycle; Nitrification; Plant Uptake; Powlson DS (1999) Fate of nitrogen from manufactured Symbiotic Fixation; Pollution: Groundwater fertilizers in agriculture. In: Wilson WS, Ball AS, and Hinton RH (eds) Managing Risks of Nitrates to Humans Further Reading and the Environment, pp. 42–57. Cambridge: Royal Society of Chemistry. Addiscott TM, Whitmore AP, and Powlson DS (1991) Powlson DS (1997) Integrating agricultural nutrient man- Farming, Fertilizers and the Nitrate Problem. Wallingford: agement with environmental objectives – current state CAB International. and future prospects. Proceedings No. 402. York: The Benjamin N (2000) Nitrates in the human diet – good or Fertiliser Society. bad? Annales de Zootechnologie 49: 207–216. Powlson DS, Hart PBS, Poulton PR, Johnston AE, and Catt JA et al. (1998) Strategies to decrease nitrate leaching Jenkinson DS (1986) Recovery of 15N-labelled fertilizer in the Brimstone Farm experiment, Oxfordshire, UK, applied in autumn to winter wheat at four sites in eastern 1988–1993: the effects of winter cover crops and England. Journal of Agricultural Science, Cambridge unfertilized grass leys. Plant and Soil 203: 57–69. 107: 611–620. Cheney K (1990) Effect of nitrogen fertilizer rate on soil Recous S, Fresnau C, Faurie G, and Mary B (1988) The fate nitrate nitrogen content after harvesting winter wheat. of labelled 15N urea and ammonium nitrate applied to a Journal of Agricultural Science, Cambridge 114: winter wheat crop.