Emerging Patterns of Marine Nitrogen Fixation
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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 -
Methanotrophs Are Core Members of the Diazotroph Community in Decaying T Norway Spruce Logs
Soil Biology and Biochemistry 120 (2018) 230–232 Contents lists available at ScienceDirect Soil Biology and Biochemistry journal homepage: www.elsevier.com/locate/soilbio Short Communication Methanotrophs are core members of the diazotroph community in decaying T Norway spruce logs ∗ Raisa Mäkipääa, , Sanna M. Leppänena, Sonia Sanz Munoza, Aino Smolandera, Marja Tiirolab, Tero Tuomivirtaa, Hannu Fritzea a Natural Resources Institute Finland, Finland b University of Jyväskylä, Finland ARTICLE INFO ABSTRACT Keywords: Dead wood is initially a nitrogen (N) poor substrate, where the N content increases with decay, partly due to fi Asymbiotic nitrogen xation biological N2 fixation, but the drivers of the N accumulation are poorly known. We quantified the rate of N2 Coarse woody debris fixation in decaying Norway spruce logs of different decay stages and studied the potential regulators of the N2- − − Dead wood fixation activity. The average rate for acetylene reduction in the decaying wood was 7.5 nmol ethylene g 1d 1, nifH − − − which corresponds to 52.9 μgN kg 1d 1. The number of nifH copies (g 1 dry matter) was higher at the later Picea abies decay stages, but no correlation between the copy number and the in vitro N2 fixation rate was found. All recovered nifH sequences were assigned to the order Rhizobiales, and therein mostly (60%) to methane oxidizing genera. We confirm that nitrogen fixing methanotrophs are present in all the wood decay phases and suggest that their interaction between methane producing organisms in decaying wood should be further studied. In boreal forests with nitrogen (N) supply deficiency, asymbiotic N2 (Karst)) logs (using four replicates per sample log) followed the fixation occurs in the dead wood (Brunner and Kimmins, 2003; Hicks methods described in Rinne et al. -
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. -
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 -
Nitrogen Fixation Among Marine Bacterioplankton
Nitrogen Fixation Among Marine Bacterioplankton Kjärstin H. Boström Department of Biology & Environmental Science University of Kalmar Sweden 2006 AKADEMISK AVHANDLING som för avläggande av Filosofie Doktorsexamen vid Naturvetenskapliga Fakulteten vid högskolan i Kalmar kommer att offentligt försvaras fredagen den 20 januari 2006 Doctoral thesis 2006 University of Kalmar Faculty of Natural Sciences Dissertation series No. 26 Kjärstin H. Boström Department of Biology and Environmental Science University of Kalmar, SE 391 82 Kalmar, Sweden Supervisor: Dr. Lasse Riemann, Assistant Professor Department of Biology and Environmental Science University of Kalmar, SE 391 82 Kalmar, Sweden Opponent: Dr. Grieg Steward, Assistant Professor Department of Oceanography University of Hawaii, Honolulu, HI 96822, USA 2006 Kjärstin H. Boström ISBN: 91-89584-52-X, ISSN: 1650-2779, pp. 1-26 Printed by: Högskolans tryckeri, Kalmar 2 To Frida & Emma 3 TABLE OF CONTENTS TABLE OF CONTENTS.............................................................................................................4 ABSTRACT...................................................................................................................................5 SVENSK SAMMANFATTNING...............................................................................................6 LIST OF PUBLICATIONS.........................................................................................................8 INTRODUCTION ........................................................................................................................9 -
Diversity of Free-Living Nitrogen Fixing Bacteria in the Badlands of South Dakota Bibha Dahal South Dakota State University
South Dakota State University Open PRAIRIE: Open Public Research Access Institutional Repository and Information Exchange Theses and Dissertations 2016 Diversity of Free-living Nitrogen Fixing Bacteria in the Badlands of South Dakota Bibha Dahal South Dakota State University Follow this and additional works at: http://openprairie.sdstate.edu/etd Part of the Bacteriology Commons, and the Environmental Microbiology and Microbial Ecology Commons Recommended Citation Dahal, Bibha, "Diversity of Free-living Nitrogen Fixing Bacteria in the Badlands of South Dakota" (2016). Theses and Dissertations. 688. http://openprairie.sdstate.edu/etd/688 This Thesis - Open Access is brought to you for free and open access by Open PRAIRIE: Open Public Research Access Institutional Repository and Information Exchange. It has been accepted for inclusion in Theses and Dissertations by an authorized administrator of Open PRAIRIE: Open Public Research Access Institutional Repository and Information Exchange. For more information, please contact [email protected]. DIVERSITY OF FREE-LIVING NITROGEN FIXING BACTERIA IN THE BADLANDS OF SOUTH DAKOTA BY BIBHA DAHAL A thesis submitted in partial fulfillment of the requirements for the Master of Science Major in Biological Sciences Specialization in Microbiology South Dakota State University 2016 iii ACKNOWLEDGEMENTS “Always aim for the moon, even if you miss, you’ll land among the stars”.- W. Clement Stone I would like to express my profuse gratitude and heartfelt appreciation to my advisor Dr. Volker Brӧzel for providing me a rewarding place to foster my career as a scientist. I am thankful for his implicit encouragement, guidance, and support throughout my research. This research would not be successful without his guidance and inspiration. -
Fine Scale Sampling Unveils Diazotroph Patchiness in the South
bioRxiv preprint doi: https://doi.org/10.1101/2020.10.02.323808; this version posted October 2, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission. 1 Fine scale sampling unveils diazotroph patchiness in the South Pacific Ocean 2 3 Running title: Fine scale diazotroph distribution 4 5 1,*Mar Benavides, 1Louis Conradt, 1Sophie Bonnet, 2Ilana Berman-Frank, 1Stéphanie 6 Barrillon, 1Anne Petrenko, 1Andrea M. Doglioli 7 8 1Aix Marseille Univ, Université de Toulon, CNRS, IRD, MIO UM 110, 13288, Marseille, 9 France 10 2Leon H. Charney School of Marine Sciences, University of Haifa, Mt. Carmel, Haifa 11 3498838, Israel 12 13 *Corresponding author: Mar Benavides [email protected] 14 15 Abstract 16 17 Diazotrophs are important contributors to reactive nitrogen availability in the ocean. 18 Oceanographic cruise data accumulated along decades has revealed a heterogeneous 19 distribution of diazotroph species at regional to global scales. However, the role of dynamic 20 fine scale structures in distributing diazotrophs is not well understood. This is due to typical 21 insufficient spatiotemporal resolution sampling and the lack of detailed physical studies in 22 parallel. Here We show the distribution of five groups of diazotrophs in the South Pacific at 23 an unprecedented resolution of 7-16 km. We find a patchy distribution of diazotrophs, With 24 each group being differently affected by parameters describing fine scale structures. The 25 observed variability could not have been revealed with a loWer resolution sampling, 26 highlighting the need to consider fine scale physics to resolve the distribution of diazotrophs 27 in the ocean. -
Insect-Mediated Nitrogen Dynamics in Decomposing Wood
Ecological Entomology (2015), 40 (Suppl. 1), 97–112 DOI: 10.1111/een.12176 INSECTS AND ECOSYSTEM SERVICES SPECIAL ISSUE Insect-mediated nitrogen dynamics in decomposing wood MICHAEL D. ULYSHEN USDA Forest Service, Athens, Georgia, U.S.A. Abstract. 1. Wood decomposition is characterised by complex and poorly understood nitrogen (N) dynamics with unclear implications for forest nutrient cycling and productivity. Wood-dwelling microbes have developed unique strategies for coping with the N limitations imposed by their substrate, including the translocation of N into wood by cord-forming fungi and the fixation of atmospheric nitrogen2 (N ) by bacteria and Archaea. 2. By accelerating the release of nutrients immobilised in fungal tissues and promoting N2 fixation by free-living and endosymbiotic prokaryotes, saproxylic insects have the potential to influence N dynamics in forests. 3. Prokaryotes capable of fixing N2 appear to be commonplace among wood-feeding insects, with published records from three orders (Blattodea, Coleoptera and Hymenoptera), 13 families, 33 genera and at least 60 species. These organisms appear to play a significant role in the N economies of their hosts and represent a widespread solution to surviving on a diet of wood. 4. While agricultural research has demonstrated the role that termites and other insects can play in enhancing crop yields, the importance of saproxylic insects to forest productivity remains unexplored. Key words. Arthropods, diazotroph, ecosystem services, Isoptera, mineralisation, saproxylic, symbiosis. Introduction the N-rich tissues of particular insect and fungal species. For example, Baker (1969) reported that Anobium punctatum (De Nitrogen (N) is the limiting nutrient in many systems (Vitousek Geer) developing in dry wood acquired 2.5 times the amount & Howarth, 1991; LeBauer & Treseder, 2008) and this is espe- of N provided by the wood itself. -
Nitrogenase; Nitrogen Fixation Vs Haber-Bosch Process
Nitrogenase; Nitrogen Fixation vs Haber-Bosch Process Anna Balinski, Jacob Watson Texas A&M University, College Station, TX 77843 Abstract Comparison of Processes Haber-Bosch Process Overview:The Nitrogen Cycle is a chemical cycle which recycles nitrogen into usable forms, such as ammonium, nitrates, and nitrites. Nitrogen and nitrogen compounds are important Haber-Bosch Reaction because they make up our atmosphere as well as our earthly environments. Nitrogen can be recycled into ammonium naturally via nitrogen fixing bacteria, or synthetically using the + - Discovered by Fritz Haber, process scaled up by Haber-Bosch process. Nitrogen fixation in bacteria follows the reaction N2 + 8 H + 8 e 2 • Carl Bosch NH3 + H2 and is powered by the hydrolysis of 16 ATP equivalents. The Haber-Bosch process Response to Germany’s need for ammonia for follows the reaction scheme of N2 + 3 H2 2 NH3 and is powered by using high pressures, • temperatures, and catalysts. Using the Haber-Bosch process an optimum yield of 97% explosive during WWI ammonium can be obtained. These reactions both use diatomic nitrogen as well as Nitrogen Fixation Reaction • Prolonged WWI when Germany was able to hydrogen, but differ in their final products as bacterial nitrogen fixation releases hydrogen produce fertilizer and explosives gas as a byproduct. Bacteria in the soil use nitrogen to create energy to grow and reproduce Fritz Haber Carl Bosch as well as to introduce nitrogen for use by other species. The Haber-Bosch process produces ammonium which can be used for a range of activities such as the production of fertilizers, or even explosives. -
Phylogeny of Nitrogenase Structural and Assembly Components Reveals New Insights Into the Origin and Distribution of Nitrogen Fixation Across Bacteria and Archaea
microorganisms Article Phylogeny of Nitrogenase Structural and Assembly Components Reveals New Insights into the Origin and Distribution of Nitrogen Fixation across Bacteria and Archaea Amrit Koirala 1 and Volker S. Brözel 1,2,* 1 Department of Biology and Microbiology, South Dakota State University, Brookings, SD 57006, USA; [email protected] 2 Department of Biochemistry, Genetics and Microbiology, University of Pretoria, Pretoria 0004, South Africa * Correspondence: [email protected]; Tel.: +1-605-688-6144 Abstract: The phylogeny of nitrogenase has only been analyzed using the structural proteins NifHDK. As nifHDKENB has been established as the minimum number of genes necessary for in silico predic- tion of diazotrophy, we present an updated phylogeny of diazotrophs using both structural (NifHDK) and cofactor assembly proteins (NifENB). Annotated Nif sequences were obtained from InterPro from 963 culture-derived genomes. Nif sequences were aligned individually and concatenated to form one NifHDKENB sequence. Phylogenies obtained using PhyML, FastTree, RapidNJ, and ASTRAL from individuals and concatenated protein sequences were compared and analyzed. All six genes were found across the Actinobacteria, Aquificae, Bacteroidetes, Chlorobi, Chloroflexi, Cyanobacteria, Deferribacteres, Firmicutes, Fusobacteria, Nitrospira, Proteobacteria, PVC group, and Spirochaetes, as well as the Euryarchaeota. The phylogenies of individual Nif proteins were very similar to the overall NifHDKENB phylogeny, indicating the assembly proteins have evolved together. Our higher resolution database upheld the three cluster phylogeny, but revealed undocu- Citation: Koirala, A.; Brözel, V.S. mented horizontal gene transfers across phyla. Only 48% of the 325 genera containing all six nif genes Phylogeny of Nitrogenase Structural and Assembly Components Reveals are currently supported by biochemical evidence of diazotrophy. -
Overview and Case Studies on Biological Nitrogen Fixation: Perspectives and Limitations
Case Study B2: Overview and Case studies on Biological Nitrogen Fixation: Perspectives and Limitations Adriana Montañez1 Problem statement: Biological Nitrogen Fixation and Sustainable Agriculture Nitrogen is an essential plant nutrient. It is the nutrient that is most commonly deficient in soils, contributing to reduced agricultural yields throughout the world. Nitrogen can be supplied to crops by biological nitrogen fixation (BNF), a process which is becoming more important for not only reducing energy costs, but also in seeking more sustainable agricultural production. Nitrogen fixing micro-organisms could therefore be an important component of sustainable agricultural systems. There are several significant reasons to seek alternatives to fertilisers that provide chemically fixed nitrogen: Ø Environmental Nitrogen fertilisers affect the balance of the global nitrogen cycle, and may pollute groundwater, increase the risk of chemical spills, and increase atmospheric nitrous oxide (N2O), a potent “greenhouse” gas. Ø Energy The primary energy source for the manufacture of nitrogen fertiliser is natural gas together with petroleum and coal. On the contrary, the energy requirements of BNF are met by renewable sources such as plant-synthesised carbohydrates rather than from non- renewable fossil fuels. Ø Sustainability Long- term sustainability of agricultural systems must rely on the use and effective management of internal resources. The process of BNF offers an economically attractive and ecologically sound means of reducing external nitrogen input and improving the quality and quantity of internal resources. Ø Nutrition It is estimated that about 20% of food protein worldwide is derived from legumes. There are more than 13,000 described species of legumes and for only 3,000 species examined more than 90% were found to form root nodules. -
Interactions Among Soil Biology, Nutrition, and Performance of Actinorhizal Plant Species in the H.J
'I 'l I Applied Soil Ecology ELSEVIER Applied Soil Ecology 19 (2002) 13-26 www.elsevier com/Iocate/apsoll Interactions among soil biology, nutrition, and performance of actinorhizal plant species in the H.J. Andrews Experimental Forest of Oregon N.S. Rojas a, D.A. Perry b, C.Y. Li c'*, L.M. Ganio d a 118 Trail East St, Hendersonvtlle, TN37075, USA b Box 8, Papa 'au, HI 96755, USA c USDA Forest Service, PacificNorthwest Research Station, Forestry. Sciences Laboratory, 3200 SW Jefferson Way, Corvallis, 0R97331, USA d Department of Forest Science, Oregon State Umversit3 Corvalhs, OR 97331, USA Received 2 July 2001 ; accepted 7 August 2091 Abstract The study examined the effect ofFrankia, macronutrients, micronutrients, mycorrhizal fungi, and plant-growth-promoting fluorescent Pseudomonas sp. on total biomass, nodule weight, and nitrogen fixation of red aider (Alnus rubra) and snowbrush (Ceanothus velutinus) under greenhouse conditions. The soil samples were collected from a 10-year-old clearcut on the H.J. Andrews Experimental Forest, Oregon. Within the clearcut, four sampling points were selected along a slope gradient. Red alder and snowbrush plants were greenhouse-grown in a mix of sod-vermiculite-perlite (2:1:1) for 6 and 12 months, respectively. Plants were inoculated with Frankia and a fluorescent Pseudomonas sp. Some of the red alder were also inoculated with ectomycorrhlzal Alpova diplophloeus, and some snowbrush with endomycorrhizal Glomus intraradix. There was no interaction between treatment and slope location for either species. There were significant treatment effects for red alder, but not for snowbmsh. Red alder seedlings given Frankia and macronutrients produced more biomass and had greater nitrogen fixation than seedlings grown without addtttons; adding A.