Nitrogen Cycle of the Open Ocean: from Genes to Ecosystems
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Nitrogen Fixation by Trichodesmium Spp.: an Important Source of New Nitrogen to the Tropical and Subtropical North Atlantic Ocean Douglas G
GLOBAL BIOGEOCHEMICAL CYCLES, VOL. 19, GB2024, doi:10.1029/2004GB002331, 2005 Nitrogen fixation by Trichodesmium spp.: An important source of new nitrogen to the tropical and subtropical North Atlantic Ocean Douglas G. Capone,1 James A. Burns,1,2 Joseph P. Montoya,3 Ajit Subramaniam,4 Claire Mahaffey,1,5 Troy Gunderson,1 Anthony F. Michaels,1 and Edward J. Carpenter6 Received 6 July 2004; revised 19 January 2005; accepted 9 March 2005; published 8 June 2005. [1] The broad distribution and often high densities of the cyanobacterium Trichodesmium spp. in oligotrophic waters imply a substantial role for this one taxon in the oceanic N cycle of the marine tropics and subtropics. New results from 154 stations on six research cruises in the North Atlantic Ocean show depth-integrated N2 fixation by Trichodesmium spp. at many stations that equalled or exceeded the estimated vertical flux À of NO3 into the euphotic zone by diapycnal mixing. Areal rates are consistent with those derived from several indirect geochemical analyses. Direct measurements of N2 fixation rates by Trichodesmium are also congruent with upper water column N budgets derived from parallel determinations of stable isotope distributions, clearly showing that N2 fixation by Trichodesmium is a major source of new nitrogen in the tropical North Atlantic. We project a conservative estimate of the annual input of new N into the tropical 12 North Atlantic of at least 1.6 Â 10 mol N by Trichodesmium N2 fixation alone. This input can account for a substantial fraction of the N2 fixation in the North Atlantic inferred by several of the geochemical approaches. -
Host-Secreted Antimicrobial Peptide Enforces Symbiotic Selectivity in Medicago Truncatula
Host-secreted antimicrobial peptide enforces symbiotic selectivity in Medicago truncatula Qi Wanga, Shengming Yanga, Jinge Liua, Kata Terecskeib, Edit Ábrahámb, Anikó Gombárc, Ágota Domonkosc, Attila Szucs} b, Péter Körmöczib, Ting Wangb, Lili Fodorc, Linyong Maod,e, Zhangjun Feid,e, Éva Kondorosib,1, Péter Kalóc, Attila Keresztb, and Hongyan Zhua,1 aDepartment of Plant and Soil Sciences, University of Kentucky, Lexington, KY 40546; bInstitute of Biochemistry, Biological Research Center, Szeged 6726, Hungary; cNational Agricultural Research and Innovation Centre, Agricultural Biotechnology Institute, Gödöllo} 2100, Hungary; dBoyce Thompson Institute for Plant Research, Cornell University, Ithaca, NY 14853; and eU.S. Department of Agriculture–Agricultural Research Service Robert W. Holley Center for Agriculture and Health, Cornell University, Ithaca, NY 14853 Contributed by Éva Kondorosi, February 14, 2017 (sent for review January 17, 2017; reviewed by Rebecca Dickstein and Julia Frugoli) Legumes engage in root nodule symbioses with nitrogen-fixing effectors or microbe-associated molecular patterns (MAMPs) soil bacteria known as rhizobia. In nodule cells, bacteria are enclosed such as surface polysaccharides to facilitate their invasion of the in membrane-bound vesicles called symbiosomes and differentiate host (7, 8). Therefore, effector- or MAMP-triggered plant im- into bacteroids that are capable of converting atmospheric nitrogen munity mediated by intracellular nucleotide binding/leucine-rich into ammonia. Bacteroid differentiation -
Detection and Study of Blooms of Trichodesmium Erythraeum and Noctiluca Miliaris in NE Arabian Sea S
Detection and study of blooms of Trichodesmium erythraeum and Noctiluca miliaris in NE Arabian Sea S. G. Prabhu Matondkar 1*, R.M. Dwivedi 2, J. I. Goes 3, H.do.R. Gomes 3, S.G. Parab 1and S.M.Pednekar 1 1National Institute of Oceanography, Dona-Paula 403 004, Goa, INDIA 2Space Application Centre, Ahmedabad, Gujarat, INDIA 3Bigelow Laboratory for Ocean Sciences, West Boothbay Harbor, Maine, 04575, USA Abstract The Arabian Sea is subject to semi-annual wind reversals associated with the monsoon cycle that result in two periods of elevated phytoplankton productivity, one during the northeast (NE) monsoon (November-February) and the other during the southwest (SW) monsoon (June- September). Although the seasonality of phytoplankton biomass in these offshore waters is well known, the abundance and composition of phytoplankton associated with this distinct seasonal cycle is poorly understood. Monthly samples were collected from the NE Arabian Sea (offshore) from November to May. Phytoplankton were studied microscopically up to the species level. Phytoplankton counts are supported by Chl a estimations and chemotaxonomic studies using HPLC. Surface phytoplankton cell counts varied from 0.1912 (Mar) to 15.83 cell x104L-1 (Nov). In Nov Trichodesmium thiebautii was the dominant species. It was replaced by diatom and dinoflagellates in the following month. Increased cell counts during Jan were predominantly due to dinoflagellates Gymnodinium breve , Gonyaulax schilleri and Amphidinium carteare . Large blooms of Noctiluca miliaris were observed in Feb a direct consequence of the large populations of G. schilleri upon which N. miliaris is known to graze. In Mar and April, N. miliaris was replaced by blooms of Trichodesmium erythraeum . -
Periodic and Coordinated Gene Expression Between a Diazotroph and Its Diatom Host
The ISME Journal (2019) 13:118–131 https://doi.org/10.1038/s41396-018-0262-2 ARTICLE Periodic and coordinated gene expression between a diazotroph and its diatom host 1 1,2 1 3 4 Matthew J. Harke ● Kyle R. Frischkorn ● Sheean T. Haley ● Frank O. Aylward ● Jonathan P. Zehr ● Sonya T. Dyhrman1,2 Received: 11 April 2018 / Revised: 28 June 2018 / Accepted: 28 July 2018 / Published online: 16 August 2018 © International Society for Microbial Ecology 2018 Abstract In the surface ocean, light fuels photosynthetic carbon fixation of phytoplankton, playing a critical role in ecosystem processes including carbon export to the deep sea. In oligotrophic oceans, diatom–diazotroph associations (DDAs) play a keystone role in ecosystem function because diazotrophs can provide otherwise scarce biologically available nitrogen to the diatom host, fueling growth and subsequent carbon sequestration. Despite their importance, relatively little is known about the nature of these associations in situ. Here we used metatranscriptomic sequencing of surface samples from the North Pacific Subtropical Gyre (NPSG) to reconstruct patterns of gene expression for the diazotrophic symbiont Richelia and we – 1234567890();,: 1234567890();,: examined how these patterns were integrated with those of the diatom host over day night transitions. Richelia exhibited significant diel signals for genes related to photosynthesis, N2 fixation, and resource acquisition, among other processes. N2 fixation genes were significantly co-expressed with host nitrogen uptake and metabolism, as well as potential genes involved in carbon transport, which may underpin the exchange of nitrogen and carbon within this association. Patterns of expression suggested cell division was integrated between the host and symbiont across the diel cycle. -
Municipal Wastewater Denitrification Evaluation City of Windom, Minnesota
Municipal Wastewater Denitrification Evaluation City of Windom, Minnesota July 29, 2016 – Revised November 4, 2016 Bolton & Menk, Inc. Project No. T22.109023 Prepared by: Submitted by: Bolton & Menk, Inc. 12224 Nicollet Blvd Burnsvillle, MN 55337 P: 952-890-0509 F: 952-890-8065 wq-wwtp5-91 MUNICIPAL WASTEWATER DENITRIFICATION EVALUATION CITY OF WINDOM, MINNESOTA JULY 2016 BMI Project No. T22.109023 I hereby certify that this plan, specification or report was prepared by me or under my direct supervision, and that I am a duly Licensed Professional Engineer under the laws of the State of Minnesota. Signature: Typed or Printed Name: Lana Tullis, P.E. Date: July 29, 2016 Lic. No. 41450 I hereby certify that this plan, specification or report was prepared by me or under my direct supervision, and that I am a duly Licensed Professional Engineer under the laws of the State of Minnesota. Signature: Typed or Printed Name: Herman Dharmarajah, Ph.D., P.E. Date: July 29, 2016 Lic. No. 18256 I hereby certify that this plan, specification or report was prepared by me or under my direct supervision, and that I am a duly Licensed Professional Engineer under the laws of the State of Minnesota. BOLTON & MENK, INC. CONSULTING ENGINEERS AND LAND SURVEYORS This page intentionally left blank. TABLE OF CONTENTS SECTION 1 INTRODUCTION ............................................................................................... 1-1 A. Project Background ........................................................................................ 1-1 B. Nitrate Standards -
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 Metabolism in Phytoplankton - Y
MARINE ECOLOGY – Nitrogen Metabolism in Phytoplankton - Y. Collos, J. A. Berges NITROGEN METABOLISM IN PHYTOPLANKTON Y. Collos Laboratoire d'Hydrobiologie CNRS, Université Montpellier II, France J. A. Berges School of Biology and Biochemistry, Queen's University of Belfast, UK Keywords: uptake, reduction, excretion, proteases, chlorophyllases, cell death. Contents 1. Introduction 2. Availability and use of different forms of nitrogen 2.1 Nitrate 2.2. Nitrite 2.3. Ammonium 2.4. Molecular N2 2.5. Dissolved organic N (DON) 2.6. Particulate nitrogen (PN) 3. Assimilation pathways 4. Accumulation and storage 4.1. Inorganic compounds 4.2. Organic compounds 5. Nutrient classification and preferences 6. Plasticity in cell composition 7. Overflow mechanisms: excretion and release processes 8. Recycling of N within the cell 9. Degradation pathways 9.1. Requirements for and roles of degradation 9.2. How is degradation accomplished? 9.3. Variation in degradation 9.4. Pathogenesis and Cell Death 10. From uptake to growth: time-lag phenomena 11. Relationships with carbon metabolism 12. Future directions AcknowledgementsUNESCO – EOLSS Glossary Bibliography SAMPLE CHAPTERS Biographical Sketches Summary Phytoplankton use a large variety of nitrogen compounds and are extremely well adapted to fluctuating environmental conditions by a high capacity to change their chemical composition.Degradation and turnover of nitrogen within phytoplankton is essential for many processes including normal cell maintenance, acclimations to changes in light, salinity, and nutrients, and cell defence against pathogens. The ©Encyclopedia of Life Support Systems (EOLSS) MARINE ECOLOGY – Nitrogen Metabolism in Phytoplankton - Y. Collos, J. A. Berges pathways by which N degradation is accomplished are very poorly understood, but based on work in higher plant species, protein degradation is likely to be of central importance. -
Mixotrophic Protists Among Marine Ciliates and Dinoflagellates: Distribution, Physiology and Ecology
FACULTY OF SCIENCE UNIVERSITY OF COPENHAGEN PhD thesis Woraporn Tarangkoon Mixotrophic Protists among Marine Ciliates and Dinoflagellates: Distribution, Physiology and Ecology Academic advisor: Associate Professor Per Juel Hansen Submitted: 29/04/10 Contents List of publications 3 Preface 4 Summary 6 Sammenfating (Danish summary) 8 สรุป (Thai summary) 10 The sections and objectives of the thesis 12 Introduction 14 1) Mixotrophy among marine planktonic protists 14 1.1) The role of light, food concentration and nutrients for 17 the growth of marine mixotrophic planktonic protists 1.2) Importance of marine mixotrophic protists in the 20 planktonic food web 2) Marine symbiont-bearing dinoflagellates 24 2.1) Occurrence of symbionts in the order Dinophysiales 24 2.2) The spatial distribution of symbiont-bearing dinoflagellates in 27 marine waters 2.3) The role of symbionts and phagotrophy in dinoflagellates with symbionts 28 3) Symbiosis and mixotrophy in the marine ciliate genus Mesodinium 30 3.1) Occurrence of symbiosis in Mesodinium spp. 30 3.2) The distribution of marine Mesodinium spp. 30 3.3) The role of symbionts and phagotrophy in marine Mesodinium rubrum 33 and Mesodinium pulex Conclusion and future perspectives 36 References 38 Paper I Paper II Paper III Appendix-Paper IV Appendix-I Lists of publications The thesis consists of the following papers, referred to in the synthesis by their roman numerals. Co-author statements are attached to the thesis (Appendix-I). Paper I Tarangkoon W, Hansen G Hansen PJ (2010) Spatial distribution of symbiont-bearing dinoflagellates in the Indian Ocean in relation to oceanographic regimes. Aquat Microb Ecol 58:197-213. -
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. -
Human Alteration of the Global Nitrogen Cycle: Causes And
Published by the Ecological Society of America Number 1, Spring 1997 Causes andConsequences Human Alterationofthe Issues in EcologyGlobal NitrogenCycle: Photo by Nadine Cavender Issues in Ecology Number 1 Spring 1997 Human Alteration of the Global Nitrogen Cycle: Causes and Consequences SUMMARY Human activities are greatly increasing the amount of nitrogen cycling between the living world and the soil, water, and atmosphere. In fact, humans have already doubled the rate of nitrogen entering the land-based nitrogen cycle, and that rate is continuing to climb. This human-driven global change is having serious impacts on ecosystems around the world because nitrogen is essential to living organisms and its availability plays a crucial role in the organization and functioning of the worlds ecosystems. In many ecosystems on land and sea, the supply of nitrogen is a key factor controlling the nature and diversity of plant life, the population dynamics of both grazing animals and their predators, and vital ecologi- cal processes such as plant productivity and the cycling of carbon and soil minerals. This is true not only in wild or unmanaged systems but in most croplands and forestry plantations as well. Excessive nitrogen additions can pollute ecosystems and alter both their ecological functioning and the living communities they support. Most of the human activities responsible for the increase in global nitrogen are local in scale, from the production and use of nitrogen fertilizers to the burning of fossil fuels in automobiles, power generation plants, and industries. However, human activities have not only increased the supply but enhanced the global movement of various forms of nitrogen through air and water. -
Global Distribution Patterns of Marine Nitrogen-Fixers by Imaging and Molecular Methods Running Title: Diazotrophs in Tara Oceans
bioRxiv preprint doi: https://doi.org/10.1101/2020.10.17.343731; this version posted April 1, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY 4.0 International license. Global distribution patterns of marine nitrogen-fixers by imaging and molecular methods Running title: Diazotrophs in Tara Oceans Juan José Pierella Karlusich1,2, Eric Pelletier2,3,, Fabien Lombard2,5,8 , Madeline Carsique1, Etienne Dvorak1, Sébastien Colin4,6,10, Marc Picheral2,5, Francisco M. Cornejo-Castillo4, Silvia G. Acinas7, Rainer Pepperkok2,6, Eric Karsenti1,2,6, Colomban de Vargas2,4, Patrick Wincker2,3, Chris Bowler1,2*, Rachel A Foster 9* 1 Institut de Biologie de l'ENS (IBENS), Département de biologie, École normale supérieure, CNRS, INSERM, Université PSL, 75005 Paris, France 2 CNRS Research Federation for the study of Global Ocean Systems Ecology and Evolution, FR2022/Tara Oceans GOSEE, 3 rue Michel-Ange, 75016 Paris, France 3 Génomique Métabolique, Genoscope, Institut François Jacob, CEA, CNRS, Univ Evry, Université Paris-Saclay, 91057 Evry, France 4 Sorbonne Université, CNRS, Station Biologique de Roscoff, UMR 7144, ECOMAP, 29680 Roscoff, France 5 Sorbonne Universités, CNRS, Laboratoire d'Océanographie de Villefranche (LOV), 06230 Villefranche-sur-Mer, France 6 European Molecular Biology Laboratory, Heidelberg, Germany 7 Department of Marine Biology and Oceanography, Institut de Ciènces del -
Within-Arctic Horizontal Gene Transfer As a Driver of Convergent Evolution in Distantly Related 1 Microalgae 2 Richard G. Do
bioRxiv preprint doi: https://doi.org/10.1101/2021.07.31.454568; this version posted August 2, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 1 Within-Arctic horizontal gene transfer as a driver of convergent evolution in distantly related 2 microalgae 3 Richard G. Dorrell*+1,2, Alan Kuo3*, Zoltan Füssy4, Elisabeth Richardson5,6, Asaf Salamov3, Nikola 4 Zarevski,1,2,7 Nastasia J. Freyria8, Federico M. Ibarbalz1,2,9, Jerry Jenkins3,10, Juan Jose Pierella 5 Karlusich1,2, Andrei Stecca Steindorff3, Robyn E. Edgar8, Lori Handley10, Kathleen Lail3, Anna Lipzen3, 6 Vincent Lombard11, John McFarlane5, Charlotte Nef1,2, Anna M.G. Novák Vanclová1,2, Yi Peng3, Chris 7 Plott10, Marianne Potvin8, Fabio Rocha Jimenez Vieira1,2, Kerrie Barry3, Joel B. Dacks5, Colomban de 8 Vargas2,12, Bernard Henrissat11,13, Eric Pelletier2,14, Jeremy Schmutz3,10, Patrick Wincker2,14, Chris 9 Bowler1,2, Igor V. Grigoriev3,15, and Connie Lovejoy+8 10 11 1 Institut de Biologie de l'ENS (IBENS), Département de Biologie, École Normale Supérieure, CNRS, 12 INSERM, Université PSL, 75005 Paris, France 13 2CNRS Research Federation for the study of Global Ocean Systems Ecology and Evolution, 14 FR2022/Tara Oceans GOSEE, 3 rue Michel-Ange, 75016 Paris, France 15 3 US Department of Energy Joint Genome Institute, Lawrence Berkeley National Laboratory, 1 16 Cyclotron Road, Berkeley,