Nitrosococcus Watsonii Sp. Nov., a New Species of Marine Obligate
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CUED Phd and Mphil Thesis Classes
High-throughput Experimental and Computational Studies of Bacterial Evolution Lars Barquist Queens' College University of Cambridge A thesis submitted for the degree of Doctor of Philosophy 23 August 2013 Arrakis teaches the attitude of the knife { chopping off what's incomplete and saying: \Now it's complete because it's ended here." Collected Sayings of Muad'dib Declaration High-throughput Experimental and Computational Studies of Bacterial Evolution The work presented in this dissertation was carried out at the Wellcome Trust Sanger Institute between October 2009 and August 2013. This dissertation is the result of my own work and includes nothing which is the outcome of work done in collaboration except where specifically indicated in the text. This dissertation does not exceed the limit of 60,000 words as specified by the Faculty of Biology Degree Committee. This dissertation has been typeset in 12pt Computer Modern font using LATEX according to the specifications set by the Board of Graduate Studies and the Faculty of Biology Degree Committee. No part of this dissertation or anything substantially similar has been or is being submitted for any other qualification at any other university. Acknowledgements I have been tremendously fortunate to spend the past four years on the Wellcome Trust Genome Campus at the Sanger Institute and the European Bioinformatics Institute. I would like to thank foremost my main collaborators on the studies described in this thesis: Paul Gardner and Gemma Langridge. Their contributions and support have been invaluable. I would also like to thank my supervisor, Alex Bateman, for giving me the freedom to pursue a wide range of projects during my time in his group and for advice. -
General Introduction
Physiological Characteristics and Genomic Properties of Nitrosomonas mobilis Isolated from Nitrifying Granule of Wastewater Treatment Bioreactor December 2016 Soe Myat Thandar ソー ミャット サンダー Physiological Characteristics and Genomic Properties of Nitrosomonas mobilis Isolated from Nitrifying Granule of Wastewater Treatment Bioreactor December 2016 Waseda University Graduate School of Advanced Science and Engineering Department of Life Science and Medical Bioscience Research on Environmental Biotechnology Soe Myat Thandar ソー ミャット サンダー Contents Abbreviations ................................................................................................................... i Chapter 1-General introduction .................................................................................... 1 1.1. Nitrification and wastewater treatment system .......................................................... 3 1.2. Important of Nitrosomonas mobilis ........................................................................... 8 1.3. Objectives and outlines of this study ....................................................................... 12 1.4. Reference.................................................................................................................. 12 Chapter 2- Physiological characteristics of Nitrosomonas mobilis Ms1 ................... 17 2.1. Introduction .............................................................................................................. 19 2.2. Material and methods .............................................................................................. -
APP201895 APP201895__Appli
APPLICATION FORM DETERMINATION Determine if an organism is a new organism under the Hazardous Substances and New Organisms Act 1996 Send by post to: Environmental Protection Authority, Private Bag 63002, Wellington 6140 OR email to: [email protected] Application number APP201895 Applicant Neil Pritchard Key contact NPN Ltd www.epa.govt.nz 2 Application to determine if an organism is a new organism Important This application form is used to determine if an organism is a new organism. If you need help to complete this form, please look at our website (www.epa.govt.nz) or email us at [email protected]. This application form will be made publicly available so any confidential information must be collated in a separate labelled appendix. The fee for this application can be found on our website at www.epa.govt.nz. This form was approved on 1 May 2012. May 2012 EPA0159 3 Application to determine if an organism is a new organism 1. Information about the new organism What is the name of the new organism? Briefly describe the biology of the organism. Is it a genetically modified organism? Pseudomonas monteilii Kingdom: Bacteria Phylum: Proteobacteria Class: Gamma Proteobacteria Order: Pseudomonadales Family: Pseudomonadaceae Genus: Pseudomonas Species: Pseudomonas monteilii Elomari et al., 1997 Binomial name: Pseudomonas monteilii Elomari et al., 1997. Pseudomonas monteilii is a Gram-negative, rod- shaped, motile bacterium isolated from human bronchial aspirate (Elomari et al 1997). They are incapable of liquefing gelatin. They grow at 10°C but not at 41°C, produce fluorescent pigments, catalase, and cytochrome oxidase, and possesse the arginine dihydrolase system. -
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 -
Comparison of Physiology and Genome-Wide Expression in Two Nitrosomonas Spp
Comparison of physiology and genome-wide expression in two Nitrosomonas spp. under batch cultivation By Mohammad Ghashghavi A thesis submitted in partial fulfillment of the requirements for the degree of Master of Science In Microbiology and Biotechnology Department of Biological Sciences University of Alberta © Mohammad Ghashghavi, 2014 Abstract: Ammonia oxidizing bacteria (AOB) play a central role in the nitrogen cycle by oxidizing ammonia to nitrite. Nitrosomonas europaea ATCC 19718 has been the single most studied AOB that has contributed to our understanding of chemolithotrophic ammonia oxidation. As a closely related species, Nitrosomonas eutropha C91 has also been extensively studied. Both of these bacteria are involved in wastewater treatment systems and play a crucial part in major losses of ammonium-based fertilizers globally. Although comparative genome analysis studies have been done before, change in genome-wide expression between closely related organisms are scarce. In this study, we compared these two organisms through physiology and transcriptomic experiments during exponential and early stationary growth phase. We found that under batch cultivation, N. europaea produces more N2O while N. eutropha consumes more nitrite. From transcriptomic analysis, we also found that there are selections of motility genes that are highly expressed in N. eutropha during early stationary growth phase and such observation was completely absent in N. europaea. Lastly, principle homologous genes that have been well studied had different patterns of expression in these strains. This study not only gives us a better understanding regarding physiology and genome-wide expression of these two AOB, it also opens a wide array of opportunities to further our knowledge in understanding other closely related species with regards to their evolution, physiology and niche preference. -
Lydia H. Zeglin MBL Microbial Diversity Final Project Report 29 July 2008 How Does Salinity Affect Aerobic Ammonia Oxidizer Abundance and Diversity?
Lydia H. Zeglin MBL Microbial Diversity Final Project Report 29 July 2008 How does salinity affect aerobic ammonia oxidizer abundance and diversity? Introduction Microorganisms are capable of making a living in diverse ways. For instance, chemolithoautotrophic microbes utilize inorganic electron donors and acceptors to supply cellular energy. Perhaps the most environmentally ubiquitous chemolithoautotrophic metabolic pathway is ammonia oxidation to nitrite, coupled with nitrite oxidation to nitrate, together + - - commonly referred to as nitrification (NH4 ⇒ NO2 ⇒ NO3 ). Ammonia oxidation to nitrite and nitrite oxidation to nitrate are separate steps performed by separate groups of organisms. + = + Ammonia oxidation (NH4 + 1.5 O2 ⇒ NO2 + H2O + 2H ) has been studied as an aerobic bacterial-mediated pathway for many years. Two monophyletic bacterial groups were thought to dominate this pathway: Nitrosomonas spp. (Betaproteobacteria: Nitrosomonadales: Nitrosomonadaceae) and Nitrosococcus spp. (Gammaproteobacteria: Chromatiales: Chromatiaceae). Recent insights have complicated this framework, as archaeal (Crenarchaeota, e.g. “Nitrosopumilis maritimus”, (Konneke et al., 2005)) microorganisms may perform a significant proportion of aerobic nitrification. A number of recent studies show a high abundance, diversity and activity of ammonia-oxidizing Crenarchaea in soils, marine waters and sediments (e.g. Francis et al. 2005, Leininger et al. 2006). There may also be a differential distribution of ammonia-oxidizing bacteria (AOB) and ammonia-oxidizing -
Drivers of Bacterial Β-Diversity Depend on Spatial Scale
Drivers of bacterial β-diversity depend on spatial scale Jennifer B. H. Martinya,1, Jonathan A. Eisenb, Kevin Pennc, Steven D. Allisona,d, and M. Claire Horner-Devinee aDepartment of Ecology and Evolutionary Biology, and dDepartment of Earth System Science, University of California, Irvine, CA 92697; bDepartment of Evolution and Ecology, University of California Davis Genome Center, Davis, CA 95616; cCenter for Marine Biotechnology and Biomedicine, The Scripps Institution of Oceanography, University of California at San Diego, La Jolla, CA 92093; and eSchool of Aquatic and Fishery Sciences, University of Washington, Seattle, WA 98195 Edited by Edward F. DeLong, Massachusetts Institute of Technology, Cambridge, MA, and approved March 31, 2011 (received for review November 1, 2010) The factors driving β-diversity (variation in community composi- spatial scale (12). Fifty-years ago, Preston (13) noted that the tion) yield insights into the maintenance of biodiversity on the turnover rate (rate of change) of bird species composition across planet. Here we tested whether the mechanisms that underlie space within a continent is lower than that across continents. He bacterial β-diversity vary over centimeters to continental spatial attributed the high turnover rate across continents to evolu- scales by comparing the composition of ammonia-oxidizing bacte- tionary diversification (i.e., speciation) between faunas as a result ria communities in salt marsh sediments. As observed in studies of dispersal limitation and the lower turnover rates of bird spe- β of macroorganisms, the drivers of salt marsh bacterial -diversity cies within continents as a result of environmental variation. depend on spatial scale. In contrast to macroorganism studies, Here we investigate whether the mechanisms underlying β- fi however, we found no evidence of evolutionary diversi cation diversity in bacteria also vary by spatial scale. -
Ammonia Oxidizers in a Grazing Land with a History of Poultry
AMMONIA OXIDIZERS IN A GRAZING LAND WITH A HISTORY OF POULTRY LITTER APPLICATION by ABHA MUNDEPI (Under the Direction of Mussie Y. Habteselassie) ABSTRACT Poultry litter (PL) is widely applied on grazing lands in Georgia, but it is not clear how it affects the function and community structure of ammonia-oxidizing bacteria (AOB) and archaea (AOA). In 2009, soil samples were collected from plots that received PL for 15 years at 8 Mg ha-1 annually and those plots were resampled in 2013 after 2 years of PL stoppage, with the objective of examining the long-term impacts of PL and its legacy effects on AOB and AOA. In 2009, the abundance of AOB and AOA were significantly higher in PL treated soils (6.98 and 7.06 log copies g soil-1 for AOB and AOA, respectively) than controls plots that received equivalent amount of nitrogen (N) in the form of urea ammonium nitrate (6.39 and 6.53 log copies g soil-1 for AOB and AOA, respectively). In 2013, AOB abundance decreased significantly in response to the discontinuation of PL application. We used dicyandiamide to separate the roles of AOB and AOA in nitrification in PL and CL (no N added) soils. At early stage of incubation, AOA dominated nitrification in both PL and unamended CL, accounting for ≥70% of nitrification potential (NP). With time, AOB contribution to NP grew in PL, accounting for ≥50% at high ammonium level. We designed a laboratory study to examine how AOB and AOA respond to elevated levels of Zinc (Zn) and Copper (Cu). -
Nitrosomonas Stercoris Sp. Nov., a Chemoautotrophic Ammonia-Oxidizing Bacterium Tolerant of High Ammonium Isolated from Composted Cattle Manure
Microbes Environ. Vol. 30, No. 3, 221-227, 2015 https://www.jstage.jst.go.jp/browse/jsme2 doi:10.1264/jsme2.ME15072 Nitrosomonas stercoris sp. nov., a Chemoautotrophic Ammonia-Oxidizing Bacterium Tolerant of High Ammonium Isolated from Composted Cattle Manure TATSUNORI NAKAGAWA1* and REIJI TAKAHASHI1 1College of Bioresource Sciences, Nihon University, 1866 Kameino, Fujisawa, Kanagawa 252–0880, Japan (Received February 4, 2014—Accepted May 18, 2015—Published online July 4, 2015) Among ammonia-oxidizing bacteria, Nitrosomonas eutropha-like microbes are distributed in strongly eutrophic environments such as wastewater treatment plants and animal manure. In the present study, we isolated an ammonia-oxidizing bacterium tolerant of high ammonium levels, designated strain KYUHI-ST, from composted cattle manure. Unlike the other known Nitrosomonas species, this isolate grew at 1,000 mM ammonium. Phylogenetic analyses based on 16S rRNA and amoA genes indicated that the isolate belonged to the genus Nitrosomonas and formed a unique cluster with the uncultured ammonia oxidizers found in wastewater systems and animal manure composts, suggesting that these ammonia oxidizers contributed to removing higher concentrations of ammonia in strongly eutrophic environments. Based on the physiological and phylogenetic data presented here, we propose and call for the validation of the provisional taxonomic assignment Nitrosomonas stercoris, with strain KYUHI-S as the type strain (type strain KYUHI-ST = NBRC 110753T = ATCC BAA-2718T). Key words: high ammonium-tolerant, cattle manure, ammonia-oxidizing bacteria, compost, Nitrosomonas stercoris Chemoautotrophic ammonia-oxidizing bacteria (AOB) that phylogenetically related to Nitrosomonas europaea and oxidize ammonium to nitrite are found not only in natural Nitrosomonas eutropha are involved in the conversion of ecosystems such as soils, sediment, freshwater, and marine ammonia to nitrite within manure composts (18, 22, 36–38). -
Stop AA Length Cluster ID Order Family Genus RBS
Replicon Start Stop AA Lengthlpha-Score Cluster IDHasNR HasPro Order Family Genus RBS NC_008573 190900 191019 39 100 7 FALSE TRUE Alteromonadales Shewanellaceae Shewanella FALSE NC_009438 285981 286100 39 100 7 FALSE TRUE Alteromonadales Shewanellaceae Shewanella FALSE NC_009778 42140404214159 39 100 7 FALSE TRUE Enterobacteriales Enterobacteriaceae Cronobacter FALSE NC_009649 79985 79866 39 100 7 FALSE TRUE Enterobacteriales Enterobacteriaceae Klebsiella FALSE NC_009838 134371 134490 39 100 7 FALSE TRUE Enterobacteriales Enterobacteriaceae Escherichia FALSE NC_010468 37346433734524 39 100 7 FALSE TRUE Enterobacteriales Enterobacteriaceae Escherichia FALSE NC_006856 1475 1579 34 100 67 FALSE FALSE Enterobacteriales Enterobacteriaceae Salmonella FALSE NC_010410 3640820 3640924 34 100 67 FALSE FALSE Pseudomonadales Moraxellaceae Acinetobacter FALSE NC_010488 122800 122696 34 100 67 FALSE FALSE Enterobacteriales Enterobacteriaceae Escherichia FALSE NC_008344 679346 679233 37 100 60 FALSE FALSE Nitrosomonadales Nitrosomonadaceae Nitrosomonas FALSE NC_004741 2605885 2605772 37 100 60 FALSE FALSE Enterobacteriales Enterobacteriaceae Shigella FALSE NC_008344 2385914 2386027 37 100 60 FALSE FALSE Nitrosomonadales Nitrosomonadaceae Nitrosomonas FALSE NC_009085 792681 792794 37 100 60 FALSE FALSE Pseudomonadales Moraxellaceae Acinetobacter FALSE NC_008344 683849 683736 37 100 57 FALSE FALSE Nitrosomonadales Nitrosomonadaceae Nitrosomonas FALSE NC_004741 2610384 2610271 37 100 57 FALSE FALSE Enterobacteriales Enterobacteriaceae Shigella FALSE NC_008344 -
Complete Nitrification by Nitrospira Bacteria Holger Daims1, Elena V
ARTICLE doi:10.1038/nature16461 Complete nitrification by Nitrospira bacteria Holger Daims1, Elena V. Lebedeva2, Petra Pjevac1, Ping Han1, Craig Herbold1, Mads Albertsen3, Nico Jehmlich4, Marton Palatinszky1, Julia Vierheilig1, Alexandr Bulaev2, Rasmus H. Kirkegaard3, Martin von Bergen4,5, Thomas Rattei6, Bernd Bendinger7, Per H. Nielsen3 & Michael Wagner1 Nitrification, the oxidation of ammonia via nitrite to nitrate, has always been considered to be a two-step process catalysed by chemolithoautotrophic microorganisms oxidizing either ammonia or nitrite. No known nitrifier carries out both steps, although complete nitrification should be energetically advantageous. This functional separation has puzzled microbiologists for a century. Here we report on the discovery and cultivation of a completely nitrifying bacterium from the genus Nitrospira, a globally distributed group of nitrite oxidizers. The genome of this chemolithoautotrophic organism encodes the pathways both for ammonia and nitrite oxidation, which are concomitantly expressed during growth by ammonia oxidation to nitrate. Genes affiliated with the phylogenetically distinct ammonia monooxygenase and hydroxylamine dehydrogenase genes of Nitrospira are present in many environments and were retrieved on Nitrospira- contigs in new metagenomes from engineered systems. These findings fundamentally change our picture of nitrification and point to completely nitrifying Nitrospira as key components of nitrogen-cycling microbial communities. Nitrification is catalysed by ammonia-oxidizing -
Microbial Nitrogen Metabolism in Chloraminated Drinking Water
bioRxiv preprint doi: https://doi.org/10.1101/655316; this version posted June 13, 2019. 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. 1 Microbial Nitrogen Metabolism in Chloraminated Drinking Water 2 Reservoirs 3 4 Sarah C Potgietera, Zihan Daic, Stefanus N Ventera, Makhosazana Sigudud and Ameet J 5 Pintob* 6 7 a Rand Water Chair in Water Microbiology, Department of Microbiology and Plant 8 Pathology, University of Pretoria, South Africa 9 b Department of Civil and Environmental Engineering, Northeastern University, Boston, USA 10 c College of Science and Engineering, School of Engineering, University of Glasgow, UK 11 d Scientific Services, Rand Water, Vereeniging, South Africa 12 13 *corresponding author: Dr Ameet J Pinto 14 Email address: [email protected] 15 16 17 18 19 20 21 22 23 24 25 bioRxiv preprint doi: https://doi.org/10.1101/655316; this version posted June 13, 2019. 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. 26 Abstract 27 Nitrification is a common concern in chloraminated drinking water distribution systems. The 28 addition of ammonia promotes the growth of nitrifying organisms, causing the depletion of 29 chloramine residuals and resulting in operational problems for many drinking water utilities. 30 Therefore, a comprehensive understanding of the microbially mediated processes behind 31 nitrogen metabolism together with chemical water quality data, may allow water utilities to 32 better address the undesirable effects caused by nitrification.