The Methanol Dehydrogenase Gene, Mxaf, As a Functional and Phylogenetic Marker for Proteobacterial Methanotrophs in Natural Environments
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The Diversity of Cultivable Hydrocarbon-Degrading
THE DIVERSITY OF CULTIVABLE HYDROCARBON-DEGRADING BACTERIA ISOLATED FROM CRUDE OIL CONTAMINATED SOIL AND SLUDGE FROM ARZEW REFINERY IN ALGERIA Sonia Sekkour, Abdelkader Bekki, Zoulikha Bouchiba, Timothy Vogel, Elisabeth Navarro, Ing Sonia To cite this version: Sonia Sekkour, Abdelkader Bekki, Zoulikha Bouchiba, Timothy Vogel, Elisabeth Navarro, et al.. THE DIVERSITY OF CULTIVABLE HYDROCARBON-DEGRADING BACTERIA ISOLATED FROM CRUDE OIL CONTAMINATED SOIL AND SLUDGE FROM ARZEW REFINERY IN ALGERIA. Journal of Microbiology, Biotechnology and Food Sciences, Faculty of Biotechnology and Food Sci- ences, Slovak University of Agriculture in Nitra, 2019, 9 (1), pp.70-77. 10.15414/jmbfs.2019.9.1.70-77. ird-02497490 HAL Id: ird-02497490 https://hal.ird.fr/ird-02497490 Submitted on 3 Mar 2020 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. THE DIVERSITY OF CULTIVABLE HYDROCARBON-DEGRADING BACTERIA ISOLATED FROM CRUDE OIL CONTAMINATED SOIL AND SLUDGE FROM ARZEW REFINERY IN ALGERIA Sonia SEKKOUR1*, Abdelkader BEKKI1, Zoulikha BOUCHIBA1, Timothy M. Vogel2, Elisabeth NAVARRO2 Address(es): Ing. Sonia SEKKOUR PhD., 1Université Ahmed Benbella, Faculté des sciences de la nature et de la vie, Département de Biotechnologie, Laboratoire de biotechnologie des rhizobiums et amélioration des plantes, 31000 Oran, Algérie. -
(12) United States Patent (10) Patent No.: US 9,181,541 B2 Bogosian (45) Date of Patent: Nov
US009181541 B2 (12) United States Patent (10) Patent No.: US 9,181,541 B2 Bogosian (45) Date of Patent: Nov. 10, 2015 (54) MICROBIAL FERMENTATION METHODS FOREIGN PATENT DOCUMENTS AND COMPOSITIONS EP O140723 A1 5, 1985 EP 2390345 A1 11 2011 (71) Applicant: New leaf Symbiotics, Inc., St. Louis, KR 100755.509 B1 9, 2007 MO (US) KR 2007O 106867 A 11, 2007 KR 20070106868 A 11, 2007 (72) Inventor: Gregg Bogosian, Clarkson Valley, MO KR 2007011 1915 A 11, 2007 (US) KR 2008OO97568 A 11, 2008 KR 10.0953179 B1 4/2010 KR 10-1195899 10, 2012 (73) Assignee: New leaf Symbiotics, Inc., St. Louis, KR 10-1195899 B1 10, 2012 MO (US) WO O3O46226 A1 6, 2003 WO 2012O12671 A2 1, 2012 (*) Notice: Subject to any disclaimer, the term of this WO 2013141815 A1 9, 2013 patent is extended or adjusted under 35 WO 201318161.0 A1 12/2013 U.S.C. 154(b) by 0 days. OTHER PUBLICATIONS (21) Appl. No.: 13/907,161 Bardi et al., J Agric Food Chem, 1996, vol. 44, p. 463-467.* Verhoef et al., Carbohydrate Research, 2003, vol. 338, p. 1851 (22) Filed: May 31, 2013 1859.* Ntsaluba et al., African Journal of Microbiology Research, 2011, vol. (65) Prior Publication Data 5, No. 26, p. 453-4540.* US 2013/03244O7 A1 Dec. 5, 2013 Mackinnon et al., Clays and Clay Minerals, 1993, vol. 41, No. 5. p. 613-623. Jiang et al., “Methanotrophs: Multifunctional Bacteria with Promis ing Applications in Environmental Bioengineering'. Biochemical Related U.S. Application Data Engineering Journal, May 15, 2010, pp. -
Identification of Active Methylotroph Populations in an Acidic Forest Soil
Microbiology (2002), 148, 2331–2342 Printed in Great Britain Identification of active methylotroph populations in an acidic forest soil by stable- isotope probing Stefan Radajewski,1 Gordon Webster,2† David S. Reay,3‡ Samantha A. Morris,1 Philip Ineson,4 David B. Nedwell,3 James I. Prosser2 and J. Colin Murrell1 Author for correspondence: J. Colin Murrell. Tel: j44 24 7652 2553. Fax: j44 24 7652 3568. e-mail: cmurrell!bio.warwick.ac.uk 1 Department of Biological Stable-isotope probing (SIP) is a culture-independent technique that enables Sciences, University of the isolation of DNA from micro-organisms that are actively involved in a Warwick, Coventry CV4 7AL, UK specific metabolic process. In this study, SIP was used to characterize the active methylotroph populations in forest soil (pH 35) microcosms that were exposed 2 Department of Molecular 13 13 13 13 and Cell Biology, to CH3OH or CH4. Distinct C-labelled DNA ( C-DNA) fractions were resolved University of Aberdeen, from total community DNA by CsCl density-gradient centrifugation. Analysis of Institute of Medical 16S rDNA sequences amplified from the 13C-DNA revealed that bacteria related Sciences, Foresterhill, Aberdeen AB25 2ZD, UK to the genera Methylocella, Methylocapsa, Methylocystis and Rhodoblastus had assimilated the 13C-labelled substrates, which suggested that moderately 3 Department of Biological Sciences, University of acidophilic methylotroph populations were active in the microcosms. Essex, Wivenhoe Park, Enrichments targeted towards the active proteobacterial CH3OH utilizers were Colchester, Essex CO4 3SQ, successful, although none of these bacteria were isolated into pure culture. A UK parallel analysis of genes encoding the key enzymes methanol dehydrogenase 4 Department of Biology, and particulate methane monooxygenase reflected the 16S rDNA analysis, but University of York, PO Box 373, YO10 5YW, UK unexpectedly revealed sequences related to the ammonia monooxygenase of ammonia-oxidizing bacteria (AOB) from the β-subclass of the Proteobacteria. -
Table S1. Bacterial Otus from 16S Rrna
Table S1. Bacterial OTUs from 16S rRNA sequencing analysis including only taxa which were identified to genus level (those OTUs identified as Ambiguous taxa, uncultured bacteria or without genus-level identifications were omitted). OTUs with only a single representative across all samples were also omitted. Taxa are listed from most to least abundant. Pitcher Plant Sample Class Order Family Genus CB1p1 CB1p2 CB1p3 CB1p4 CB5p234 Sp3p2 Sp3p4 Sp3p5 Sp5p23 Sp9p234 sum Gammaproteobacteria Legionellales Coxiellaceae Rickettsiella 1 2 0 1 2 3 60194 497 1038 2 61740 Alphaproteobacteria Rhodospirillales Rhodospirillaceae Azospirillum 686 527 10513 485 11 3 2 7 16494 8201 36929 Sphingobacteriia Sphingobacteriales Sphingobacteriaceae Pedobacter 455 302 873 103 16 19242 279 55 760 1077 23162 Betaproteobacteria Burkholderiales Oxalobacteraceae Duganella 9060 5734 2660 40 1357 280 117 29 129 35 19441 Gammaproteobacteria Pseudomonadales Pseudomonadaceae Pseudomonas 3336 1991 3475 1309 2819 233 1335 1666 3046 218 19428 Betaproteobacteria Burkholderiales Burkholderiaceae Paraburkholderia 0 1 0 1 16051 98 41 140 23 17 16372 Sphingobacteriia Sphingobacteriales Sphingobacteriaceae Mucilaginibacter 77 39 3123 20 2006 324 982 5764 408 21 12764 Gammaproteobacteria Pseudomonadales Moraxellaceae Alkanindiges 9 10 14 7 9632 6 79 518 1183 65 11523 Betaproteobacteria Neisseriales Neisseriaceae Aquitalea 0 0 0 0 1 1577 5715 1471 2141 177 11082 Flavobacteriia Flavobacteriales Flavobacteriaceae Flavobacterium 324 219 8432 533 24 123 7 15 111 324 10112 Alphaproteobacteria -
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. -
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. -
HYGIENE SCIENCES 45Th ISSUE
Committed to the advancement of Clinical & Industrial Disinfection & Microbiology VOLUME - VIII ISSUE - V DEC 2015 - JAN 2016 Editorial We would like to thank all our readers for their precious inputs & encouragement in making Contents this Journal a successful effort. Here’s another issue of JHS coming your Contents way……………….. Mini Review Section - Control of microbial growth means the reduction in numbers and activity of the total microbial flora, is effected in two basic ways i.e., either by killing n Editorial 1 microorganisms or by inhibiting the growth of microorganisms. Controlling of microorganisms is done to prevent transmission of disease and infection, to prevent contamination by the growth of undesirable microorganisms and to prevent deterioration and nMini review 2 spoilage of materials by microorganisms. Control of microorganisms usually involves the use of physical agents and chemical agents. Current Trends Section - Disinfection is utmost important factor in the prevention of nCurrent Trends 5 nosocomial infections. It has been known that failure in disinfection increases the morbidity, mortality, and treatment costs, whereas unnecessary disinfection procedures increase hospital expenses and select resistant microorganisms. In order to avoid such risks, the first step in the hospital setting should be the selection of right disinfectants that have proven nIn Profile 7 activity against broad spectrum of microorganisms. Super-oxidized water has been used in various industrial areas in our country in recent years. There are many international researches being performed to determine the efficacy of super-oxidized water. However, this study is one of the very few studies that will lead further studies investigating the activity of nRelaxed Mood 8 super-oxidized water on microorganisms causing nosocomial infections. -
(12) Patent Application Publication (10) Pub. No.: US 2005/0289672 A1 Jefferson (43) Pub
US 2005O289672A1 (19) United States (12) Patent Application Publication (10) Pub. No.: US 2005/0289672 A1 Jefferson (43) Pub. Date: Dec. 29, 2005 (54) BIOLOGICAL GENE TRANSFER SYSTEM Publication Classification FOR EUKARYOTC CELLS (75) Inventor: Richard A. Jefferson, Canberra (AU) (51) Int. Cl. ............................. A01H 1700; C12N 15/82 (52) U.S. Cl. .............................................................. 800,294 Correspondence Address: CAROL NOTTENBURG 81432ND AVE 5 SEATTLE, WA 98144 (US) (57) ABSTRACT (73) Assignee: CAMBIA Appl. No.: 10/954,147 This invention relates generally to technologies for the (21) transfer of nucleic acids molecules to eukaryotic cells. In Filed: Sep. 28, 2004 particular non-pathogenic Species of bacteria that interact (22) with plant cells are used to transfer nucleic acid Sequences. Related U.S. Application Data The bacteria for transforming plants usually contain binary vectors, Such as a plasmid with a Vir region of a Tiplasmid (60) Provisional application No. 60/583,426, filed on Jun. and a plasmid with a T region containing a DNA sequence 28, 2004. of interest. pEHA105 244981 bp M3REW M13Fw f1 origin accA W pEHA105::pWBE58 (Km, Ap) moaa. Patent Application Publication Dec. 29, 2005 Sheet 1 of 24 US 2005/0289672 A1 FIGURE 1A CLASS ALPHAPROTEOBACTERIA ORDER Rhizobiales family Rhizobiaceae bgenus Rhizobium (includes former Agrobacterium) bgenus Chelatobacter bgenus Sinorhizobium Dunclassified Rhizobiaceae family Bartonellaceae bgenus Bartonella Dunclassified Bartonellaceae family Brucellaceae -
Stable-Isotope Probing Implicates Methylophaga Spp and Novel Gammaproteobacteria in Marine Methanol and Methylamine Metabolism
The ISME Journal (2007) 1, 480–491 & 2007 International Society for Microbial Ecology All rights reserved 1751-7362/07 $30.00 www.nature.com/ismej ORIGINAL ARTICLE Stable-isotope probing implicates Methylophaga spp and novel Gammaproteobacteria in marine methanol and methylamine metabolism Josh D Neufeld1, Hendrik Scha¨fer, Michael J Cox2, Rich Boden, Ian R McDonald3 and J Colin Murrell Department of Biological Sciences, University of Warwick, Coventry, UK The metabolism of one-carbon (C1) compounds in the marine environment affects global warming, seawater ecology and atmospheric chemistry. Despite their global significance, marine micro- organisms that consume C1 compounds in situ remain poorly characterized. Stable-isotope probing (SIP) is an ideal tool for linking the function and phylogeny of methylotrophic organisms by the metabolism and incorporation of stable-isotope-labelled substrates into nucleic acids. By combining DNA-SIP and time-series sampling, we characterized the organisms involved in the assimilation of methanol and methylamine in coastal sea water (Plymouth, UK). Labelled nucleic acids were analysed by denaturing gradient gel electrophoresis (DGGE) and clone libraries of 16S rRNA genes. In addition, we characterized the functional gene complement of labelled nucleic acids with an improved primer set targeting methanol dehydrogenase (mxaF) and newly designed primers for methylamine dehydrogenase (mauA). Predominant DGGE phylotypes, 16S rRNA, methanol and methylamine dehydrogenase gene sequences, and cultured isolates all implicated Methylophaga spp, moderately halophilic marine methylotrophs, in the consumption of both methanol and methylamine. Additionally, an mxaF sequence obtained from DNA extracted from sea water clustered with those detected in 13C-DNA, suggesting a predominance of Methylophaga spp among marine methylotrophs. -
Widespread Soil Bacterium That Oxidizes Atmospheric Methane
Widespread soil bacterium that oxidizes atmospheric methane Alexander T. Tveita,1, Anne Grethe Hestnesa,1, Serina L. Robinsona, Arno Schintlmeisterb, Svetlana N. Dedyshc, Nico Jehmlichd, Martin von Bergend,e, Craig Herboldb, Michael Wagnerb, Andreas Richterf, and Mette M. Svenninga,2 aDepartment of Arctic and Marine Biology, Faculty of Biosciences, Fisheries and Economics, UiT The Arctic University of Norway, 9037 Tromsoe, Norway; bCenter of Microbiology and Environmental Systems Science, Division of Microbial Ecology, University of Vienna, 1090 Vienna, Austria; cWinogradsky Institute of Microbiology, Research Center of Biotechnology of Russian Academy of Sciences, 117312 Moscow, Russia; dDepartment of Molecular Systems Biology, Helmholtz Centre for Environmental Research-UFZ, 04318 Leipzig, Germany; eFaculty of Life Sciences, Institute of Biochemistry, University of Leipzig, 04109 Leipzig, Germany; and fCenter of Microbiology and Environmental Systems Science, Division of Terrestrial Ecosystem Research, University of Vienna, 1090 Vienna, Austria Edited by Mary E. Lidstrom, University of Washington, Seattle, WA, and approved March 7, 2019 (received for review October 22, 2018) The global atmospheric level of methane (CH4), the second most as-yet-uncultured clades within the Alpha- and Gammaproteobacteria important greenhouse gas, is currently increasing by ∼10 million (16–18) which were designated as upland soil clusters α and γ tons per year. Microbial oxidation in unsaturated soils is the only (USCα and USCγ, respectively). Interest in soil atmMOB has known biological process that removes CH4 from the atmosphere, increased significantly since then because they are responsible but so far, bacteria that can grow on atmospheric CH4 have eluded for the only known biological removal of atmospheric CH4 all cultivation efforts.