Susceptibility of Ammonia-Oxidizing Bacteria to Nitrification Inhibitors
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Nitrobacter As an Indicator of Toxicity in Wastewater
State Water Survey Division WATER QUALITY SECTION AT Illinois Department of PEORIA, ILLINOIS Energy and Natural Resources SWS Contract Report 326 NITROBACTER AS AN INDICATOR OF TOXICITY IN WASTEWATER by Wuncheng Wang and Paula Reed Prepared for and funded by the Illinois Department of Energy and Natural Resources September 1983 CONTENTS PAGE Abstract 1 Introduction 1 Scope of study 3 Acknowledgments 3 Literature review 3 Microbial nitrification 3 Influence of toxicants on nitrification 5 Materials and methods 10 Culture 10 Methods 11 Results 12 Preliminary tests 13 Metal toxicity 13 Organic compounds toxicity 16 Time effect 22 Discussion 22 References 27 NITROBACTER AS AN INDICATOR OF TOXICITY IN WASTEWATER by Wuncheng Wang and Paula Reed ABSTRACT This report presents the results of a study of the use of Nitrobacter as an indicator of toxicity. Nitrobacter are strictly aerobic, autotrophic, and slow growing bacteria. Because they convert nitrite to nitrate, the effects that toxins have on them can be detected easily by monitoring changes in their nitrite consumption rate. The bacterial cultures were obtained from two sources — the Peoria and Princeton (Illinois) wastewater treatment plants — and tests were con• ducted to determine the effects on the cultures of inorganic ions and organic compounds. The inorganic ions included cadmium, copper, lead, and nickel. The organic compounds were phenol, chlorophenol (three derivatives), dichlo- rophenol (two derivatives), and trichlorophenol. The bioassay procedure is relatively simple and the results are repro• ducible . The effects of these chemical compounds on Nitrobacter were not dramatic. For example, of the compounds tested, 2,4,6-trichlorophenol was the most toxic to Nitrobacter. -
Cometabolic Biodegradation of Halogenated Aliphatic Hydrocarbons by Ammonia-Oxidizing Microorganisms Naturally Associated with Wetland Plant Roots
Wright State University CORE Scholar Browse all Theses and Dissertations Theses and Dissertations 2015 Cometabolic Biodegradation of Halogenated Aliphatic Hydrocarbons by Ammonia-oxidizing Microorganisms Naturally Associated with Wetland Plant Roots Ke Qin Wright State University Follow this and additional works at: https://corescholar.libraries.wright.edu/etd_all Part of the Environmental Sciences Commons Repository Citation Qin, Ke, "Cometabolic Biodegradation of Halogenated Aliphatic Hydrocarbons by Ammonia-oxidizing Microorganisms Naturally Associated with Wetland Plant Roots" (2015). Browse all Theses and Dissertations. 1430. https://corescholar.libraries.wright.edu/etd_all/1430 This Dissertation is brought to you for free and open access by the Theses and Dissertations at CORE Scholar. It has been accepted for inclusion in Browse all Theses and Dissertations by an authorized administrator of CORE Scholar. For more information, please contact [email protected]. COMETABOLIC BIODEGRADATION OF HALOGENATED ALIPHATIC HYDROCARBONS BY AMMONIA-OXIDIZING MICROORGANISMS NATURALLY ASSOCIATED WITH WETLAND PLANT ROOTS A dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy By KE QIN MRes., University of York, 2008 2014 Wright State University i COPYRIGHT BY KE QIN 2014 ii WRIGHT STATE UNIVERSITY GRADUATE SCHOOL JANUARY 12, 2015 I HEREBY RECOMMEND THAT THE DISSERTATION PREPARED UNDER MY SUPERVISION BY Ke Qin ENTITLED Cometabolic Biodegradation of Halogenated Aliphatic Hydrocarbons by Ammonia-Oxidizing Microorganisms Naturally Associated with Wetland Plant Roots BE ACCEPTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF Doctor of Philosophy. ________________________________ Abinash Agrawal, Ph.D. Dissertation Director ________________________________ Donald Cipollini, Ph.D. Director, ES Ph.D. Program ________________________________ Committee on Robert E.W. -
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 .............................................................................................. -
Human Alteration of the Global Nitrogen Cycle
What is Nitrogen? Human Alteration of the Nitrogen is the most abundant element in Global Nitrogen Cycle the Earth’s atmosphere. Nitrogen makes up 78% of the troposphere. Nitrogen cannot be absorbed directly by the plants and animals until it is converted into compounds they can use. This process is called the Nitrogen Cycle. Heather McGraw, Mandy Williams, Suzanne Heinzel, and Cristen Whorl, Give SIUE Permission to Put Our Presentation on E-reserve at Lovejoy Library. The Nitrogen Cycle How does the nitrogen cycle work? Step 1- Nitrogen Fixation- Special bacteria convert the nitrogen gas (N2 ) to ammonia (NH3) which the plants can use. Step 2- Nitrification- Nitrification is the process which converts the ammonia into nitrite ions which the plants can take in as nutrients. Step 3- Ammonification- After all of the living organisms have used the nitrogen, decomposer bacteria convert the nitrogen-rich waste compounds into simpler ones. Step 4- Denitrification- Denitrification is the final step in which other bacteria convert the simple nitrogen compounds back into nitrogen gas (N2 ), which is then released back into the atmosphere to begin the cycle again. How does human intervention affect the nitrogen cycle? Nitric Oxide (NO) is released into the atmosphere when any type of fuel is burned. This includes byproducts of internal combustion engines. Production and Use of Nitrous Oxide (N2O) is released into the atmosphere through Nitrogen Fertilizers bacteria in livestock waste and commercial fertilizers applied to the soil. Removing nitrogen from the Earth’s crust and soil when we mine nitrogen-rich mineral deposits. Discharge of municipal sewage adds nitrogen compounds to aquatic ecosystems which disrupts the ecosystem and kills fish. -
Nitrogen Removal Training Program
Nitrogen Removal Training Program Module 1 Nitrogen in the Aquatic Environment • Forms of Nitrogen and Nitrogen Transformations • Nitrogen in Surface Waters • Water Quality Impacts of Nitrogen Discharges • Nitrogen in Wastewater Module 1 Transparency 1 Nitrogen Removal Training Program Module 1 Forms of Nitrogen and Nitrogen Transformations Module 1 Transparency 2 Forms of Nitrogen in the Environment Unoxidized Forms Oxidized Forms of Nitrogen of Nitrogen Nitrite (NO -) • Nitrogen Gas (N2) • 2 + Nitrate (NO -) • Ammonia (NH4 , NH3) • 3 • Organic Nitrogen (urea, • Nitrous Oxide (N2O) amino acids, peptides, proteins, etc...) • Nitric Oxide (NO) • Nitrogen Dioxide (NO2) Module 1 Transparency 3 Nitrogen Fixation • Biological Fixation - Use of atmospheric nitrogen by certain photosynthetic blue-green algae and bacteria for growth. Nitrogen Gas Organic Nitrogen (N2) • Lightning Fixation - Conversion of atmospheric nitrogen to nitrate by lightning. lightning Nitrogen Gas + Ozone Nitrate - (N2) (O3)(NO3 ) • Industrial Fixation - Conversion of nitrogen gas to ammonia and nitrate-nitrogen (used in the manufacture of fertilizers and explosives). Module 1 Transparency 4 Biological Nitrogen Fixation Nitrogen Gas (N2) Bacteria Blue-green Algae Organic N Organic N Certain blue-green algae and bacteria use atmospheric nitrogen to produce organic nitrogen compounds. Module 1 Transparency 5 Atmospheric Fixation Lightning converts Nitrogen Gas and Ozone to Nitrate. Nitrogen Gas Nitrate Module 1 Transparency 6 Industrial Fixation N2 Nitrogen gas is converted to ammonia and nitrate in the production of fertilizer and explosives. NH3 - NO3 Module 1 Transparency 7 Ammonification and Assimilation Ammonification - Conversion of organic nitrogen to ammonia-nitrogen resulting from the biological decomposition of dead plant and animal tissue and animal fecal matter. -
Nutrient Control Design Manual: State of Technology Review Report,” Were
United States Office of Research and EPA/600/R‐09/012 Environmental Protection Development January 2009 Agency Washington, DC 20460 Nutrient Control Design Manual State of Technology Review Report EPA/600/R‐09/012 January 2009 Nutrient Control Design Manual State of Technology Review Report by The Cadmus Group, Inc 57 Water Street Watertown, MA 02472 Scientific, Technical, Research, Engineering, and Modeling Support (STREAMS) Task Order 68 Contract No. EP‐C‐05‐058 George T. Moore, Task Order Manager United States Environmental Protection Agency Office of Research and Development / National Risk Management Research Laboratory 26 West Martin Luther King Drive, Mail Code 445 Cincinnati, Ohio, 45268 Notice This document was prepared by The Cadmus Group, Inc. (Cadmus) under EPA Contract No. EP‐C‐ 05‐058, Task Order 68. The Cadmus Team was lead by Patricia Hertzler and Laura Dufresne with Senior Advisors Clifford Randall, Emeritus Professor of Civil and Environmental Engineering at Virginia Tech and Director of the Occoquan Watershed Monitoring Program; James Barnard, Global Practice and Technology Leader at Black & Veatch; David Stensel, Professor of Civil and Environmental Engineering at the University of Washington; and Jeanette Brown, Executive Director of the Stamford Water Pollution Control Authority and Adjunct Professor of Environmental Engineering at Manhattan College. Disclaimer The views expressed in this document are those of the individual authors and do not necessarily, reflect the views and policies of the U.S. Environmental Protection Agency (EPA). Mention of trade names or commercial products does not constitute endorsement or recommendation for use. This document has been reviewed in accordance with EPA’s peer and administrative review policies and approved for publication. -
Effects of Phosphorus on Nitrification Process in a Fertile Soil Amended
agriculture Article Effects of Phosphorus on Nitrification Process in a Fertile Soil Amended with Urea Jianfeng Ning 1,2,*, Yuji Arai 2 , Jian Shen 1, Ronghui Wang 1 and Shaoying Ai 1,* 1 Institute of Agricultural Resources and Environment, Guangdong Academy of Agricultural Sciences, Key Laboratory of Plant Nutrition and Fertilizer in South Region, Ministry of Agriculture and Rural Affairs, Guangdong Key Laboratory of Nutrient Cycling and Farmland Conservation, Guangzhou 510640, China; [email protected] (J.S.); [email protected] (R.W.) 2 Department of Natural Resources and Environmental Sciences, University of Illinois at Urbana-Champaign, Urbana, IL 61801, USA; [email protected] * Correspondence: [email protected] (J.N.); [email protected] (S.A.) Abstract: While the effects of carbon on soil nitrogen (N) cycle have been extensively studied, it is not clearly understood how co-existing macronutrients, such as phosphorus (P), affect the N cycle in agroecosystems. In this study, P amendment effects on nitrification in a fertile agricultural soil were investigated under a typical N-P amendment rate. In a laboratory incubation study, soils were amended with urea, monopotassium phosphate and a mixture of urea and monopotassium phosphate at the same rate. In soils that received no amendments (control), P only, urea only, and urea plus P amendment, nitrification occurred within the first five days, with an average net nitrification rate of 5.30, 5.77, 16.66 and 9.00 mg N kg−1d−1, respectively. Interestingly, nitrification in urea-treated soils was retarded by P addition where a N:P ratio seemed to be a key factor impeding nitrification. -
High Functional Diversity Among Nitrospira Populations That Dominate Rotating Biological Contactor Microbial Communities in a Municipal Wastewater Treatment Plant
The ISME Journal (2020) 14:1857–1872 https://doi.org/10.1038/s41396-020-0650-2 ARTICLE High functional diversity among Nitrospira populations that dominate rotating biological contactor microbial communities in a municipal wastewater treatment plant 1 1 1 1 1 2 Emilie Spasov ● Jackson M. Tsuji ● Laura A. Hug ● Andrew C. Doxey ● Laura A. Sauder ● Wayne J. Parker ● Josh D. Neufeld 1 Received: 18 October 2019 / Revised: 3 March 2020 / Accepted: 30 March 2020 / Published online: 24 April 2020 © The Author(s) 2020. This article is published with open access Abstract Nitrification, the oxidation of ammonia to nitrate via nitrite, is an important process in municipal wastewater treatment plants (WWTPs). Members of the Nitrospira genus that contribute to complete ammonia oxidation (comammox) have only recently been discovered and their relevance to engineered water treatment systems is poorly understood. This study investigated distributions of Nitrospira, ammonia-oxidizing archaea (AOA), and ammonia-oxidizing bacteria (AOB) in biofilm samples collected from tertiary rotating biological contactors (RBCs) of a municipal WWTP in Guelph, Ontario, 1234567890();,: 1234567890();,: Canada. Using quantitative PCR (qPCR), 16S rRNA gene sequencing, and metagenomics, our results demonstrate that Nitrospira species strongly dominate RBC biofilm samples and that comammox Nitrospira outnumber all other nitrifiers. Genome bins recovered from assembled metagenomes reveal multiple populations of comammox Nitrospira with distinct spatial and temporal distributions, including several taxa that are distinct from previously characterized Nitrospira members. Diverse functional profiles imply a high level of niche heterogeneity among comammox Nitrospira, in contrast to the sole detected AOA representative that was previously cultivated and characterized from the same RBC biofilm. -
Indications for Enzymatic Denitriication to N2O at Low Ph in an Ammonia
The ISME Journal (2019) 13:2633–2638 https://doi.org/10.1038/s41396-019-0460-6 BRIEF COMMUNICATION Indications for enzymatic denitrification to N2O at low pH in an ammonia-oxidizing archaeon 1,2 1 3 4 1 4 Man-Young Jung ● Joo-Han Gwak ● Lena Rohe ● Anette Giesemann ● Jong-Geol Kim ● Reinhard Well ● 5 2,6 2,6,7 1 Eugene L. Madsen ● Craig W. Herbold ● Michael Wagner ● Sung-Keun Rhee Received: 19 February 2019 / Revised: 5 May 2019 / Accepted: 27 May 2019 / Published online: 21 June 2019 © The Author(s) 2019. This article is published with open access Abstract Nitrous oxide (N2O) is a key climate change gas and nitrifying microbes living in terrestrial ecosystems contribute significantly to its formation. Many soils are acidic and global change will cause acidification of aquatic and terrestrial ecosystems, but the effect of decreasing pH on N2O formation by nitrifiers is poorly understood. Here, we used isotope-ratio mass spectrometry to investigate the effect of acidification on production of N2O by pure cultures of two ammonia-oxidizing archaea (AOA; Nitrosocosmicus oleophilus and Nitrosotenuis chungbukensis) and an ammonia-oxidizing bacterium (AOB; Nitrosomonas 15 europaea). For all three strains acidification led to increased emission of N2O. However, changes of N site preference (SP) 1234567890();,: 1234567890();,: values within the N2O molecule (as indicators of pathways for N2O formation), caused by decreasing pH, were highly different between the tested AOA and AOB. While acidification decreased the SP value in the AOB strain, SP values increased to a maximum value of 29‰ in N. oleophilus. In addition, 15N-nitrite tracer experiments showed that acidification boosted nitrite transformation into N2O in all strains, but the incorporation rate was different for each ammonia oxidizer. -
270. E. B.: Two Kinds of Lithotrophs Missing in Nature, Zeitschrift Für Allgemeine Mikrobiologie 17 (1977), 491-493
270. E. B.: Two Kinds of Lithotrophs Missing in Nature, Zeitschrift für Allgemeine Mikrobiologie 17 (1977), 491-493. Zeitschrift für Allg. Mikrobiologie 1977 491-493 (Institut für Physikalische Chemie, Universität Wien) Two kinds of lithotrophs missing in nature E. BRODA (Eingegangen am 14. 9.1976) Two groups of lithotrophic bacteria, the existence of which may be expected on evolutionary and thermodynamical grounds, have not yet been detected: (A) photosynthetic, anaerobic, am- monia bacteria, analogous to coloured sulphur bacteria, and (B) chemosynthetic bacteria that oxidize ammonia to nitrogen with O2 or nitrate as oxidant. The versatility of the prokaryotes in their energy metabolism has long astonished microbiologists. The bacteria have developed processes, i.e., enzymes, for the utili- zation of a wide range indeed of exergonic reactions. Attention is now drawn to further processes in energy metabolism which on the basis of considerations on the evolution of the bioenergetic processes (BRODA I975a) may be expected to have existed, or to exist, but which have not yet been found. Two kinds of "lithotrophic" bacteria with such mechanisms will now be predicted. Lithotrophs are bacteria that use in- organic reductants in their energy metabolism (FROl\fAGEOT and SENEZ 1960); all autotrophs must be lithotrophs, though the reverse need not be true. The two bac- teria here predicted would generate dinitrogen (N2). The nitrifying bacteria make adenosine triphosphate, ATP, through oxidative phos- phorylation coupled to the aerobic oxidation of ammonia, a highly exergonic process. Thus, in nitrification Nitrosomonas produces nitrite, and Nitrobacter makes nitrate. The redox reactions are: NHt + 1.5 O2 = H 20 + NO;- + 2 H+; = - 65 kcal (1) NO;- + 0.5 O2 = NO;-; = - 18 kcal (2) The negativity of the free enthalpy change, is the precondition for the produc- tion of ATP and, consequently, for the endergonic reduction of CO 2 to biomass. -
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. -
The Impact of Nitrite on Aerobic Growth of Paracoccus Denitrificans PD1222
Katherine Hartop | January 2014 The Impact of Nitrite on Aerobic Growth of Paracoccus denitrificans PD1222 Submitted for approval by Katherine Rachel Hartop BSc (Hons) For the qualification of Doctor of Philosophy University of East Anglia School of Biological Sciences January 2014 This copy of the thesis has been supplied on conditions that anyone who consults it is understood to recognise that its copyright rests with the author and that use of any information derived there from must be in accordance with current UK Copyright Law. In addition, any quotation or extract must include full attribution. i Katherine Hartop | January 2014 Acknowledgments Utmost thanks go to my supervisors Professor David Richardson, Dr Andy Gates and Dr Tom Clarke for their continual support and boundless knowledge. I am also delighted to have been supported by the funding of the University of East Anglia for the length of my doctorial research. Thank you to the Richardson laboratory as well as those I have encountered and had the honour of collaborating with from the School of Biological Sciences. Thank you to Georgios Giannopoulos for your contribution to my research and support during the writing of this thesis. Thanks to my friends for their patience, care and editorial input. Deepest thanks to Dr Rosa María Martínez-Espinosa and Dr Gary Rowley for examining me and my research. This work is dedicated to my parents, Keith and Gill, and my family. ii Katherine Hartop | January 2014 Abstract The effect of nitrite stress induced in Paracoccus denitrificans PD1222 was examined using additions of sodium nitrite to an aerobic bacterial culture.