Comparison of Physiology and Genome-Wide Expression in Two Nitrosomonas Spp

Total Page:16

File Type:pdf, Size:1020Kb

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. ii Acknowledgements: I would like to thank Dr. Lisa Stein for her full support and supervision throughout my graduate career. I’m very grateful for all the feedback during my Masters and throughout the writing of this thesis. I would also like to thank Albert Rosana in aiding with the laboratory work of this thesis. I would like to thank Kerim Kits as well for his continuous and constructive comments and support throughout my graduate career. Lastly, I would like to thank everyone in Dr. Stein’s lab and within the Department of Biological Sciences for their support. Furthermore, I would like to thank each and every professor at the Department of Biological Sciences that have helped throughout my career. I would also like to thank the University of Alberta for accepting me and providing me with the funds, through Teaching Assistantship, needed to complete my postgraduate degree. iii Table of Contents CHAPTER 1 INTRODUCTION ............................................................................................................... 1 1.1 THE EVOLUTION OF THE GLOBAL NITROGEN CYCLE ................................................................................... 1 1.2 THE HISTORY OF NITROGEN CYCLE EVOLUTION DURING THE ANOXIC ERA ............................................. 3 1.3 THE LINK BETWEEN METHANE AND AMMONIA OXIDATION ...................................................................... 6 1.4 TAXONOMY OF AMMONIA OXIDIZING BACTERIA ......................................................................................... 8 1.5 COMPLETE GENOME SEQUENCES OF AOB AND THEIR PROPERTIES ...................................................... 12 1.6 NITROSOMONAS EUROPAEA/NITROSOMONAS MOBILIS LINEAGE ............................................................ 14 1.7 GENERAL ISOLATION, ENRICHMENT, AND MAINTENANCE PROCEDURES ............................................ 18 1.8 ECOLOGY AND APPLICATION ........................................................................................................................ 21 1.9 THE BEGINNING OF NITRIFICATION FOCUSED RESEARCH........................................................................ 24 1.10 NITROSOMONAS EUROPAEA AND ITS GENOME ANALYSIS ....................................................................... 25 1.11 PRINCIPAL NITRIFICATION/DENITRIFICATION ENZYMES IN N. EUROPAEA ....................................... 27 1.12 NITROSOMONAS EUTROPHA AND ITS GENOME ANALYSIS ...................................................................... 32 1.13 MY THESIS PROJECT .................................................................................................................................... 37 CHAPTER 2 MATERIALS AND METHODS ...................................................................................... 39 2.1 CULTURE CARE AND PHYSIOLOGICAL MEASUREMENTS: .......................................................................... 39 2.2 RNA EXTRACTION: ........................................................................................................................................ 40 2.3 RRNA REMOVAL AND RNA PURIFICATION: .............................................................................................. 42 2.4 RNA ANALYSIS: .............................................................................................................................................. 43 CHAPTER 3 RESULTS .......................................................................................................................... 45 3.1 COMPARISON OF PHYSIOLOGY ..................................................................................................................... 45 3.2 GENE EXPRESSION IN N. EUROPAEA ............................................................................................................ 50 3.2.1 Metabolism ................................................................................................................................................... 50 3.2.2 Enzymes ......................................................................................................................................................... 53 3.2.3 Cellular processes ...................................................................................................................................... 55 3.2.4 Membrane proteins .................................................................................................................................. 56 3.2.5 Remaining categories .............................................................................................................................. 57 3.3 GENE EXPRESSION IN N. EUTROPHA ........................................................................................................... 58 3.3.1 Metabolism ................................................................................................................................................... 59 3.3.2 Enzymes ......................................................................................................................................................... 65 3.3.3 Cellular processes ...................................................................................................................................... 69 3.3.4 Environmental Information Processing ......................................................................................... 70 3.3.5 Bacterial Motility ...................................................................................................................................... 71 3.3.6 Remaining categories .............................................................................................................................. 72 3.4 GENE EXPRESSION COMPARISON BETWEEN N. EUROPAEA AND N. EUTROPHA ................................... 73 3.4.1 Metabolism ................................................................................................................................................... 75 3.4.2 Enzymes ......................................................................................................................................................... 77 3.4.3 Cellular processes ...................................................................................................................................... 77 3.4.4 Environmental information processing .......................................................................................... 78 3.4.5 Bacterial motility ...................................................................................................................................... 79 3.4.6 Membrane proteins, Iron-binding proteins and Human diseases ...................................... 80 CHAPTER 4 DISCUSSION .................................................................................................................... 83 4.1 SIMILARITIES AND DIFFERENCES IN GROWTH .......................................................................................... 83 4.2 SIMILARITIES AND DIFFERENCES IN NITRITE PRODUCTION AND O2 CONSUMPTION .......................... 86 4.3 SIMILARITIES AND DIFFERENCES IN N2O PRODUCTION .......................................................................... 90 4.4 GENOME-WIDE EXPRESSION ........................................................................................................................ 92 iv 4.5 BACTERIAL MOTILITY ................................................................................................................................... 95 4.6 EXPRESSION OF PRINCIPAL GENES .............................................................................................................
Recommended publications
  • WO 2018/009838 Al 11 January 2018 (11.01.2018) W !P O PCT
    (12) INTERNATIONAL APPLICATION PUBLISHED UNDER THE PATENT COOPERATION TREATY (PCT) (19) World Intellectual Property Organization International Bureau (10) International Publication Number (43) International Publication Date WO 2018/009838 Al 11 January 2018 (11.01.2018) W !P O PCT (51) International Patent Classification: Declarations under Rule 4.17: C12N 5/075 (2010.01) — as to applicant's entitlement to apply for and be granted a (21) International Application Number: patent (Rule 4.1 7(H)) PCT/US2017/041 155 — as to the applicant's entitlement to claim the priority of the earlier application (Rule 4.17(Hi)) (22) International Filing Date: 07 July 2017 (07.07.2017) Published: — with international search report (Art. 21(3)) (25) Filing Language: English — before the expiration of the time limit for amending the (26) Publication Langi English claims and to be republished in the event of receipt of amendments (Rule 48.2(h)) (30) Priority Data: — with sequence listing part of description (Rule 5.2(a)) 62/359,416 07 July 2016 (07.07.2016) US (71) Applicant: RUBIUS THERAPEUTICS, INC. [US/US]; 620 Memorial Dr #100W, Cambridge, MA 02139 (US). (72) Inventors; and (71) Applicants: HARANDI, Omid [US/US]; 39 Rowena Road, Newton, MA 02459 (US). KHANWALKAR, Ur- jeet [IN/US]; 2 11 Elm Street, Apt. 3, Cambridge, MA 02139 (US). HARIHARAN, Sneha [IN/US]; 18 Hamilton Road, Apt. 407, Arlington, MA 02472 (US). (72) Inventors: KAHVEJIAN, Avak; 2 Beverly Road, Arling ton, MA 02474 (US). MATA-FINK, Jordi; 8 Windsor Rd #1, Somerville, MA 02144 (US).DEANS, Robert, J.; 1609 Ramsgate Court, Riverside, CA 92506 (US).
    [Show full text]
  • 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.
    [Show full text]
  • Rhodococcus Jostii Strain 8
    Functional characterisation of alkane-degrading monooxygenases in Rhodococcus jostii strain 8 Jindarat Ekprasert A thesis submitted to the School of Environmental Sciences in fulfilment of the requirements for the degree of Doctor of Philosophy September 2014 University of East Anglia Norwich, UK i Contents List of figures viii List of tables xiii Declaration xv Acknowledgements xvi Abbreviations xvii Abstract xxi Chapter 1 introduction 1 1.1. Significance of alkanes in the environment 2 1.1.1. Chemistry of alkanes 2 1.2. The Rhodococcus genus 3 1.2.1. Common characteristics of Rhodococcus spp. 3 1.2.2. Rhodococcus spp. are capable of degrading gaseous alkanes 4 1.2.3. Potential applications of Rhodococcus in biotechnology 5 1.3. Bacterial enzymes responsible for alkane degradation 6 1.3.1. Integral membrane, non-heme iron alkane hydroxylases (AlkB) 6 1.3.2. Soluble di-iron monooxygenases (SDIMO) 8 1.3.2.1. SDIMO classification 10 1.3.2.2. Molecular genetics of SDIMOs 13 1.3.2.3. Mutagenesis of soluble methane monooxygenase 13 1.3.3. Cytochrome P450 alkane hydroxylases 14 3.3.1. Class I P450 14 3.3.2. Class II P450 (CYP52) 15 3.3.3. Class II P450 (CYP2E, CYP4B) 15 1.3.4. Membrane bound copper-containing (and possibly iron-containing) monooxygenases 15 1.4. Alkane metabolisms in Rhodococcus spp. 16 1.4.1. Aerobic metabolism of C2-C4 gaseous alkanes in bacteria 16 1.4.1.1. Ethane (C2H6) metabolism 16 1.4.1.2. Propane (C3H8) metabolism 17 ii 1.4.1.3.
    [Show full text]
  • 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 ..............................................................................................
    [Show full text]
  • KEGG Orthology-Based Annotation of the Predicted
    Dunlap et al. BMC Genomics 2013, 14:509 http://www.biomedcentral.com/1471-2164/14/509 DATABASE Open Access KEGG orthology-based annotation of the predicted proteome of Acropora digitifera: ZoophyteBase - an open access and searchable database of a coral genome Walter C Dunlap1,2, Antonio Starcevic4, Damir Baranasic4, Janko Diminic4, Jurica Zucko4, Ranko Gacesa4, Madeleine JH van Oppen1, Daslav Hranueli4, John Cullum5 and Paul F Long2,3* Abstract Background: Contemporary coral reef research has firmly established that a genomic approach is urgently needed to better understand the effects of anthropogenic environmental stress and global climate change on coral holobiont interactions. Here we present KEGG orthology-based annotation of the complete genome sequence of the scleractinian coral Acropora digitifera and provide the first comprehensive view of the genome of a reef-building coral by applying advanced bioinformatics. Description: Sequences from the KEGG database of protein function were used to construct hidden Markov models. These models were used to search the predicted proteome of A. digitifera to establish complete genomic annotation. The annotated dataset is published in ZoophyteBase, an open access format with different options for searching the data. A particularly useful feature is the ability to use a Google-like search engine that links query words to protein attributes. We present features of the annotation that underpin the molecular structure of key processes of coral physiology that include (1) regulatory proteins of
    [Show full text]
  • 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.
    [Show full text]
  • Modelling of the Melissa Artificial Ecosystem
    ESTEC/CONTRACT 8125/88/NL/‘FG PRF 141315 Modelling of the MELiSSA artificial ecosystem Toward a structured model of the nitrifying compartment - Description of the respiratory chain of nitrifying organisms - Development of assumptions for the reverse electron flow in the respiratory electron transport chain - Stoichiometric description of the nitrification - Determination of KL~ for oxygen transfer limitation TECHNICAL NOTE 23.2 L. Poughon Laboratoire de Genie Chimique Biologique 63177 AUBIERE Cedex, FRANCE April 1995 Technical note 23.2 Toward a structured model of the nitrifying compartment T.N. 23.2: Modelling of the MELiSSA artificial ecosystem TOWARD A STRUCl-URJZD MODEL OF THE NITRIFYING COMPARTMENT L. Poughon. Laboratoire de Genie Chimique Biologique 63177 AUBIERE Cedex. France. INTRODUCTION In the MELiSSA loop the nitrifying compartment has the same function than the nitrifying process in the terrestrial ecosystem (figure 1) which is to provide an edible N-source for plants or micro-organisms (as Spirulines in the case of the MELiSSA loop). The ammoniflcation processes from organic waste (as for example the human waste faeces and urea) are performed in the MELiSSA loop by the 2 first compartments (liquefying and anoxygenic phototrophs compartments). It must be noted that there are some structural differences between the MELiSSA N-loop and the terrestrial ecosystem: l- the MELiSSA loop represent a very simplified part of the N loop encountered on earth; 2- the denitrification process (N mineral -> N2) or the N2 removing (N2 -> N mineral) are not considered 3- the sole N - source is N03- for Spirulina, it is NlQ+ for phototrophs and it is organic N for the crew.
    [Show full text]
  • Relating Metatranscriptomic Profiles to the Micropollutant
    1 Relating Metatranscriptomic Profiles to the 2 Micropollutant Biotransformation Potential of 3 Complex Microbial Communities 4 5 Supporting Information 6 7 Stefan Achermann,1,2 Cresten B. Mansfeldt,1 Marcel Müller,1,3 David R. Johnson,1 Kathrin 8 Fenner*,1,2,4 9 1Eawag, Swiss Federal Institute of Aquatic Science and Technology, 8600 Dübendorf, 10 Switzerland. 2Institute of Biogeochemistry and Pollutant Dynamics, ETH Zürich, 8092 11 Zürich, Switzerland. 3Institute of Atmospheric and Climate Science, ETH Zürich, 8092 12 Zürich, Switzerland. 4Department of Chemistry, University of Zürich, 8057 Zürich, 13 Switzerland. 14 *Corresponding author (email: [email protected] ) 15 S.A and C.B.M contributed equally to this work. 16 17 18 19 20 21 This supporting information (SI) is organized in 4 sections (S1-S4) with a total of 10 pages and 22 comprises 7 figures (Figure S1-S7) and 4 tables (Table S1-S4). 23 24 25 S1 26 S1 Data normalization 27 28 29 30 Figure S1. Relative fractions of gene transcripts originating from eukaryotes and bacteria. 31 32 33 Table S1. Relative standard deviation (RSD) for commonly used reference genes across all 34 samples (n=12). EC number mean fraction bacteria (%) RSD (%) RSD bacteria (%) RSD eukaryotes (%) 2.7.7.6 (RNAP) 80 16 6 nda 5.99.1.2 (DNA topoisomerase) 90 11 9 nda 5.99.1.3 (DNA gyrase) 92 16 10 nda 1.2.1.12 (GAPDH) 37 39 6 32 35 and indicates not determined. 36 37 38 39 S2 40 S2 Nitrile hydration 41 42 43 44 Figure S2: Pearson correlation coefficients r for rate constants of bromoxynil and acetamiprid with 45 gene transcripts of ECs describing nucleophilic reactions of water with nitriles.
    [Show full text]
  • 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).
    [Show full text]
  • 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).
    [Show full text]
  • 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
    [Show full text]
  • A Mass Balance Field Study of the Phytoremediation of Trichloroethylene with Transgenic Poplars Genetically Modified with Cytochrome P450 2E1
    A Mass Balance Field Study of the Phytoremediation of Trichloroethylene with Transgenic Poplars Genetically Modified with Cytochrome P450 2E1 Emily K. Legault A thesis submitted in partial fulfillment of the requirements for the degree of Master of Science in Civil Engineering University of Washington 2013 Committee: Stuart Strand Dave Stahl Sharon Doty Program Authorized to Offer Degree: Civil and Environmental Engineering ©Copyright 2013 Emily K. Legault Table of Contents 1 Abstract .................................................................................................................................... 1 2 Introduction ............................................................................................................................. 2 3 Materials and Methods ............................................................................................................ 6 3.1 Field Site Description ....................................................................................................... 6 3.2 Water Management and Chemical Dosing....................................................................... 7 3.3 Water Sampling and Analysis .......................................................................................... 7 3.4 Soil Sampling and Analysis ............................................................................................. 9 3.5 Soil and Stem Volatilization .......................................................................................... 10 3.6 Evapotranspiration ........................................................................................................
    [Show full text]