Taxonomic Precision of Different Hypervariable Regions of 16S Rrna Gene and Annotation Methods for Functional Bacterial Groups in Biological Wastewater Treatment
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Midas 4: a Global Catalogue of Full-Length 16S Rrna Gene
bioRxiv preprint doi: https://doi.org/10.1101/2021.07.06.451231; this version posted July 6, 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 The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity.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. MiDAS 4: A global catalogue of full-length 16S rRNA gene sequences and taxonomy for studies of bacterial communities in wastewater treatment plants Authors: Morten Simonsen Dueholm, Marta Nierychlo, Kasper Skytte Andersen, Vibeke Rudkjøbing, Simon Knutsson, the MiDAS Global Consortium, Mads Albertsen, and Per Halkjær Nielsen* Affiliation: Center for Microbial Communities, Department of Chemistry and Bioscience, Aalborg University, Aalborg, Denmark. *Correspondence to: Per Halkjær Nielsen, Center for Microbial Communities, Department of Chemistry and Bioscience, Aalborg University, Fredrik Bajers Vej 7H, 9220 Aalborg, Denmark; Phone: +45 9940 8503; Fax: Not available; E-mail: [email protected] Running title: Global microbiota of wastewater treatment plants 1 bioRxiv preprint doi: https://doi.org/10.1101/2021.07.06.451231; this version posted July 6, 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 The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity.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. Abstract Biological wastewater treatment and an increased focus on resource recovery is fundamental for environmental protection, human health, and sustainable development. Microbial communities are responsible for these processes, but our knowledge of their diversity and function is still poor, partly due to the lack of good reference databases and comprehensive global studies. -
Candidatus Amarolinea and Candidatus Microthrix Are Mainly Responsible for filamentous Bulking in Danish Municipal Wastewater Treatment Plants
This may be the author’s version of a work that was submitted/accepted for publication in the following source: Nierychlo, Marta, McIlroy, Simon J, Kucheryavskiy, Sergey, Jiang, Chen- jing, Ziegler, Anja S, Kondrotaite, Zivile, Stokholm-Bjerregaard, Mikkel, & Nielsen, Per Halkjær (2020) Candidatus Amarolinea and Candidatus Microthrix are mainly responsible for filamentous bulking in Danish municipal wastewater treatment plants. Frontiers in Microbiology, 11, Article number: 1214. This file was downloaded from: https://eprints.qut.edu.au/205774/ c The Author(s) 2020 This work is covered by copyright. Unless the document is being made available under a Creative Commons Licence, you must assume that re-use is limited to personal use and that permission from the copyright owner must be obtained for all other uses. If the docu- ment is available under a Creative Commons License (or other specified license) then refer to the Licence for details of permitted re-use. It is a condition of access that users recog- nise and abide by the legal requirements associated with these rights. If you believe that this work infringes copyright please provide details by email to [email protected] License: Creative Commons: Attribution 4.0 Notice: Please note that this document may not be the Version of Record (i.e. published version) of the work. Author manuscript versions (as Sub- mitted for peer review or as Accepted for publication after peer review) can be identified by an absence of publisher branding and/or typeset appear- ance. If there is any doubt, please refer to the published source. https://doi.org/10.3389/fmicb.2020.01214 fmicb-11-01214 June 5, 2020 Time: 19:43 # 1 ORIGINAL RESEARCH published: 09 June 2020 doi: 10.3389/fmicb.2020.01214 Candidatus Amarolinea and Candidatus Microthrix Are Mainly Responsible for Filamentous Bulking in Danish Municipal Wastewater Treatment Plants Marta Nierychlo1, Simon J. -
Chemosynthetic Symbiont with a Drastically Reduced Genome Serves As Primary Energy Storage in the Marine Flatworm Paracatenula
Chemosynthetic symbiont with a drastically reduced genome serves as primary energy storage in the marine flatworm Paracatenula Oliver Jäcklea, Brandon K. B. Seaha, Målin Tietjena, Nikolaus Leischa, Manuel Liebekea, Manuel Kleinerb,c, Jasmine S. Berga,d, and Harald R. Gruber-Vodickaa,1 aMax Planck Institute for Marine Microbiology, 28359 Bremen, Germany; bDepartment of Geoscience, University of Calgary, AB T2N 1N4, Canada; cDepartment of Plant & Microbial Biology, North Carolina State University, Raleigh, NC 27695; and dInstitut de Minéralogie, Physique des Matériaux et Cosmochimie, Université Pierre et Marie Curie, 75252 Paris Cedex 05, France Edited by Margaret J. McFall-Ngai, University of Hawaii at Manoa, Honolulu, HI, and approved March 1, 2019 (received for review November 7, 2018) Hosts of chemoautotrophic bacteria typically have much higher thrive in both free-living environmental and symbiotic states, it is biomass than their symbionts and consume symbiont cells for difficult to attribute their genomic features to either functions nutrition. In contrast to this, chemoautotrophic Candidatus Riegeria they provide to their host, or traits that are necessary for envi- symbionts in mouthless Paracatenula flatworms comprise up to ronmental survival or to both. half of the biomass of the consortium. Each species of Paracate- The smallest genomes of chemoautotrophic symbionts have nula harbors a specific Ca. Riegeria, and the endosymbionts have been observed for the gammaproteobacterial symbionts of ves- been vertically transmitted for at least 500 million years. Such icomyid clams that are directly transmitted between host genera- prolonged strict vertical transmission leads to streamlining of sym- tions (13, 14). Such strict vertical transmission leads to substantial biont genomes, and the retained physiological capacities reveal and ongoing genome reduction. -
1 Succession Within the Prokaryotic Communities
Succession within the prokaryotic communities during the VAHINE mesocosms experiment in the New Caledonia lagoon U. Pfreundt1, F. Van Wambeke2, M. Caffin2, S. Bonnet2, 3 and W. R. Hess1 5 [1]{University of Freiburg, Faculty of Biology, Schaenzlestr. 1, D-79104 Freiburg, Germany} [2]{Aix Marseille Université, CNRS/INSU, Université de Toulon, IRD, Mediterranean Institute of Oceanography (MIO) UM110, 13288, Marseille, France} [3] {Institut de Recherche pour le Développement, AMU/CNRS/INSU, Université de Toulon, 10 Mediterranean Institute of Oceanography (MIO) UM 110, 13288, Marseille-Nouméa, France- New Caledonia} 15 Correspondence to: W. R. Hess ([email protected]) Submission to Biogeosciences as a research article for the special issue “Biogeochemical and biological response to a diazotroph bloom in a low-nutrient, low-chlorophyll ecosystem: results from the VAHINE mesocosms experiment”. 20 1 Abstract N2 fixation fuels ~50 % of new primary production in the oligotrophic South Pacific Ocean. 25 The VAHINE experiment has been designed to track the fate of diazotroph derived nitrogen (DDN) and carbon within a coastal lagoon ecosystem in a comprehensive way. For this, large- volume (~50 m3) mesocosms were deployed in the New Caledonia lagoon and were intentionally fertilized with dissolved inorganic phosphorus (DIP) to stimulate N2 fixation. This study examined the temporal dynamics of the prokaryotic community together with the 30 evolution of biogeochemical parameters for 23 consecutive days in one of these mesocosms (M1) and in the Nouméa lagoon using MiSeq 16S rRNA gene sequencing and flow cytometry. Combining these methods allowed for inference of absolute cell numbers from 16S data. We observed clear successions within M1, some of which were not mirrored in the lagoon. -
Succession Within the Prokaryotic Communities During the VAHINE Mesocosms
Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Biogeosciences Discuss., 12, 20179–20222, 2015 www.biogeosciences-discuss.net/12/20179/2015/ doi:10.5194/bgd-12-20179-2015 BGD © Author(s) 2015. CC Attribution 3.0 License. 12, 20179–20222, 2015 This discussion paper is/has been under review for the journal Biogeosciences (BG). Succession within Please refer to the corresponding final paper in BG if available. the prokaryotic communities during Succession within the prokaryotic the VAHINE communities during the VAHINE mesocosms U. Pfreundt et al. mesocosms experiment in the New Caledonia lagoon Title Page Abstract Introduction U. Pfreundt1, F. Van Wambeke2, S. Bonnet2,3, and W. R. Hess1 Conclusions References 1University of Freiburg, Faculty of Biology, Schaenzlestr. 1, 79104 Freiburg, Germany Tables Figures 2Aix Marseille Université, CNRS/INSU, Université de Toulon, IRD, Mediterranean Institute of Oceanography (MIO) UM110, 13288, Marseille, France 3Institut de Recherche pour le Développement, AMU/CNRS/INSU, Université de Toulon, J I Mediterranean Institute of Oceanography (MIO) UM110, 13288, Marseille-Noumea, France-New Caledonia J I Back Close Received: 4 December 2015 – Accepted: 6 December 2015 – Published: 18 December 2015 Correspondence to: W. R. Hess ([email protected]) Full Screen / Esc Published by Copernicus Publications on behalf of the European Geosciences Union. Printer-friendly Version Interactive Discussion 20179 Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Abstract BGD N2 fixation fuels ∼ 50 % of new primary production in the oligotrophic South Pacific Ocean. The VAHINE experiment has been designed to track the fate of diazotroph 12, 20179–20222, 2015 derived nitrogen (DDN) and carbon within a coastal lagoon ecosystem in a compre- 3 5 hensive way. -
Developing a Fundamental Understanding of the Microbiological Treatment of Winery Wastewater
Developing a fundamental understanding of the microbiological treatment of winery wastewater FINAL REPORT to AUSTRALIAN GRAPE AND WINE AUTHORITY Project Number: UA 1301 Principal Investigator: Paul R Grbin Research Organisation: The University of Adelaide Date: 16 December 2016 Developing a fundamental understanding of the microbiological treatment of winery wastewater Kathryn L Eales and Paul R Grbin 16 December 2016 University of Adelaide School of Agriculture, Food and Wine PMB #1, Glen Osmond South Australia 5064 Copyright statement: This work is copyright. Apart from any use permitted under the Copyright Act 1968, no part may be reproduced by any process without written permission from the University of Adelaide. Disclaimer: This publication may be of assistance to you but the authors and their employers do not guarantee that the publication is without flaw of any kind or is wholly appropriate for your particular purposes and therefore disclaim all liability for any error, loss or other consequence which may arise from you relying on any information in this publication. Table of Contents Contents Abbreviations: ......................................................................................................................................... 4 1. Abstract ........................................................................................................................................... 5 2. Executive summary ........................................................................................................................ -
Appendix 1. Validly Published Names, Conserved and Rejected Names, And
Appendix 1. Validly published names, conserved and rejected names, and taxonomic opinions cited in the International Journal of Systematic and Evolutionary Microbiology since publication of Volume 2 of the Second Edition of the Systematics* JEAN P. EUZÉBY New phyla Alteromonadales Bowman and McMeekin 2005, 2235VP – Valid publication: Validation List no. 106 – Effective publication: Names above the rank of class are not covered by the Rules of Bowman and McMeekin (2005) the Bacteriological Code (1990 Revision), and the names of phyla are not to be regarded as having been validly published. These Anaerolineales Yamada et al. 2006, 1338VP names are listed for completeness. Bdellovibrionales Garrity et al. 2006, 1VP – Valid publication: Lentisphaerae Cho et al. 2004 – Valid publication: Validation List Validation List no. 107 – Effective publication: Garrity et al. no. 98 – Effective publication: J.C. Cho et al. (2004) (2005xxxvi) Proteobacteria Garrity et al. 2005 – Valid publication: Validation Burkholderiales Garrity et al. 2006, 1VP – Valid publication: Vali- List no. 106 – Effective publication: Garrity et al. (2005i) dation List no. 107 – Effective publication: Garrity et al. (2005xxiii) New classes Caldilineales Yamada et al. 2006, 1339VP VP Alphaproteobacteria Garrity et al. 2006, 1 – Valid publication: Campylobacterales Garrity et al. 2006, 1VP – Valid publication: Validation List no. 107 – Effective publication: Garrity et al. Validation List no. 107 – Effective publication: Garrity et al. (2005xv) (2005xxxixi) VP Anaerolineae Yamada et al. 2006, 1336 Cardiobacteriales Garrity et al. 2005, 2235VP – Valid publica- Betaproteobacteria Garrity et al. 2006, 1VP – Valid publication: tion: Validation List no. 106 – Effective publication: Garrity Validation List no. 107 – Effective publication: Garrity et al. -
(ST). the Table
1 SUPPLEMENTAL MATERIALS Growth Media Modern Condition Seawater Freshwater Light T°C Atmosphere AMCONA medium BG11 medium – Synechococcus – – Synechocystis – [C] in PAL [C] in the [C] in the Gas Nutrients Modern Nutrients (ppm) Medium Medium Ocean NaNO3 CO2 ~407.8 Na2SO4 25.0mM 29mM Nitrogen 50 Standard (17.65mM) μmol (ST) NaNO NaNO 20°C O ~209’460 Nitrogen 3 3 MgSO 0.304mM photon 2 (549µM) (13.7µM) 4 /m2s FeCl3 6.56µM 2nM Ammonium 0.6g/L ZnSO 254nM 0.5nM ferric stock N ~780’790 4 2 citrate (10ml NaMoO 105nM 105nM 4 green stock/1L) 2 Table S 1 Description of the experimental condition defined as Standard Condition (ST). The table 3 shows the concentrations of fundamental elements, such as C, N, S, and Fe used for the AMCONA 4 seawater medium (Fanesi et al., 2014) and BG11 freshwater medium (Stanier et al., 1971) flushing air 5 with using air pump (KEDSUM-310 8W pump; Xiolan, China) Growth Media Possible Proterozoic T° Condition Modified Seawater Modified Freshwater Light Atmosphere AMCONA medium BG11 medium C – Synechococcus – – Synechocystis – [C] in [C] in PPr Nutrients PPr Nutrients Medium Gas ppm Medium NH Cl Na SO 3mM Nitrogen 4 3 2 4 (0.0035mM) CO 2 10’000ppm (20%) NH Cl Possible (~ 2’450% Nitrogen 4 3 MgSO 0.035mM 50 with 20ml/ (100µM) 4 Proterozoic PAL) μmol 20° min (PPr) photon C O2 20’000ppm /m2s (in Air) (~ 10% FeCl 200nM with 5ml/ 3 PAL) Ammonium 0.6g/L stock min ferric 10ml N ZnSO 0.0nM 2 4 citrate green stock/1L (100%) Base gas with NaMoO4 10.5nM 200ml/min 6 Table S 2 Description of the experimental condition defined as Possible Proterozoic Condition (PPr). -
Abstractbook
ABSTRACTBOOK Photo credit: Wiener Wildnis 20th Symposium on Health-Related Water Microbiology (HRWM) Vienna, Austria (15-20 September 2019) www.hrwm.eu ORAL PRESENTATIONS SESSION 1 – METAGENOME, MICROBIOME AND COMMUNITY ANALYSIS 01 Quantitative Viral Metagenomic Method Combining Long and Short Read Sequencing Kathryn Langenfeld, Melissa Duhaime, Krista Wigginton University of Michigan Metagenomics are allowing unprecedented insight into microbial communities. Next generation sequencing (NGS) has led to many discoveries about viruses, but three notable challenges exist in applying NGS to study the viromes of complex matrices. Despite being the most highly abundant members of most communities, viral nucleic acids are a small portion of the total nucleic acids. Efficient viral enrichment methods are needed. Viral isolation and enrichment methods are not equally efficient. Optimized methods are needed to quantitatively compare viral representation across samples. Viral genomes are mosaic with a high mutation rate and, therefore, difficult to assemble with short reads produced with Illumina sequencing technologies. Supplemental sequencing technologies need to be explored. To address these challenges, our research advances NGS methods with a quantitative sequencing approach on the isolated virus fraction from wastewater with a combination of long and short read sequencing. Wastewater viruses are concentrated with tangential and dead-end ultrafiltration 575-fold in influent and 1,150-fold in effluent. The viruses are purified with chloroform to lyse cells and DNase to degrade extra-viral DNA. The concentration and purification protocol recovered approximately half of the viral DNA while removing 4-logs of 16S rRNA. For quantitative comparisons, 86 dsDNA and 5 ssDNA internal standards were spiked into samples at 1% of the total DNA concentration prior to simultaneously sequencing ssDNA and dsDNA on Illumina NovaSeq. -
The Endolithic and Planktonic Subsurface Microbiome Within Zones of Active Low-Temperature Serpentinization in the Samail Ophiolite of Oman
THE ENDOLITHIC AND PLANKTONIC SUBSURFACE MICROBIOME WITHIN ZONES OF ACTIVE LOW-TEMPERATURE SERPENTINIZATION IN THE SAMAIL OPHIOLITE OF OMAN by Emily Antoinette Kraus A thesis submitted to the Faculty and Board of Trustees of the Colorado School of Mines in partial fulfillment of the requirements for the degree of Doctor of Philosophy (Civil and Environmental Engineering). Golden, Colorado Date: ____________________ Signed: _____________________ Emily Antoinette Kraus Signed: _____________________ Dr. John R. Spear Thesis Advisor Golden, Colorado Date: ____________________ Signed: _____________________ Dr. Junko Munakata Marr Professor and Department Head Department of Civil and Environmental Engineering ii ABSTRACT The rock-hosted microbial ecosystems within serpentinizing subsurface environments are a prime target for future NASA missions searching for extant life in the solar system and constitute a unique habitat within Earth’s subsurface that is relatively uncharacterized. The water-rock interaction called serpentinization generates highly reduced and hyperalkaline fluids replete with hydrogen (H2) and reduced carbon compounds such as methane, which are potent electron donors and carbon sources used in microbial metabolism. This dissertation investigates the microbiome within a low-temperature terrestrial serpentinizing subsurface in the Samail ophiolite, Sultanate of Oman, from biomass collected from peridotite- and gabbro-hosted aquifer waters and drilled serpentinite rock cores. The metabolic pathways and key organisms of the Samail ophiolite’s microbial methane cycle and sulfur cycle are elucidated through multiple molecular methods with DNA and RNA sequencing and geochemical data. Results from this effort demonstrate a single active methanogen and methanotrophic populations in waters with hyperalkaline pH, representing an extension of the pH tolerance range of methanogens and suggesting biological involvement in the generation of unusual isotopic signatures of methane in the Samail ophiolite. -
Metagenomic Characterization of Candidatatus Defluviicoccus
METAGENOMIC CHARACTERIZATION OF CANDIDATATUS DEFLUVIICOCCUS TETRAFORMIS TFO71, A TETRAD-FORMING ORGANISM, PREDOMINANT IN AN ANAEROBIC-AEROBIC MEMBRANE BIOREACTOR WITH DETERIORATED BIOLOGICAL PHOSPHORUS REMOVAL BY MASARU KONISHI NOBU THESIS Submitted in partial fulfillment of the requirements for the degree of Master of Science in Environmental Engineering in Civil Engineering in the Graduate College of the University of Illinois at Urbana-Champaign 2013 Urbana, Illinois Adviser: Professor Wen-Tso Liu, Director of Research ABSTRACT In an acetate-fed anaerobic-aerobic membrane bioreactor with deteriorated enhanced biological phosphorus removal (EBPR), Defluviicoccus-related tetrad-forming organisms (DTFO) were observed to predominate in the microbial community. Using metagenomics, a partial genome of the predominant DTFO, “Candidatus Defluviicoccus tetraformis TFO71,” was successfully constructed and characterized. Examining the genome confirmed the presence of genes related to the synthesis and degradation of glycogen and polyhydroxyalkanoate (PHA), which function as energy and carbon storage compounds. Both TFO71 and Candidatus Accumulibacter phosphatis (CAP) UW-1, a representative polyphosphate-accumulating organism (PAO), have PHA metabolism-related genes with high homology, but TFO71 has unique genes for PHA synthesis, gene regulation, and granule management. We further discovered genes encoding DTFO polyphosphate (polyP) synthesis, suggesting that TFO71 may synthesize polyP under untested conditions. However, TFO71 may not activate these genes under EBPR conditions because the retrieved genome does not contain inorganic phosphate transporters that are characteristic of PAOs (CAP UW-1, Microlunatus phosphovorus NM-1, and Tetrasphaera species). As a first step in characterizing EBPR-associated DTFO metabolism, this study identifies important differences between TFO and PAO that may contribute to EBPR community competition and deterioration. -
Phylogenetic Diversity and Ecophysiology Of
Phylogenetic Diversity and Ecophysiology of Alphaproteobacterial Glycogen Accumulating Organisms in Enhanced Biological Phosphorus Removal Activated Sludge Systems Submitted by Simon Jon McIlroy Bachelor of Applied Science (Honours) La Trobe University A thesis submitted in total fulfilment of the requirements for the degree of Doctor of Philosophy School of Molecular Sciences Faculty of Science Technology and Engineering La Trobe University, Bendigo, Victoria, 3552 Australia December 2010 Table of contents Abbreviations xiv Summary xvii Statement of authorship xix List of publications xx Acknowledgements xxiv 1.0 Introduction 1 1.1 The requirement for nutrient removal in the treatment of wastewater ......................... 1 1.2 The application of activated sludge to the treatment of wastewater............................. 2 1.2.1 Enhanced biological phosphorus removal ............................................................. 2 1.2.2 Nitrogen removal ................................................................................................... 6 1.3 The need for microbiological studies on P removal ..................................................... 7 1.4 Biochemical models of EBPR and PAO metabolism................................................... 7 1.4.1 Anaerobic metabolism of the PAO........................................................................ 8 1.4.1.1 The uptake of volatile fatty acids (VFAs)....................................................... 8 1.4.1.2 The source of anaerobic reducing equivalents...............................................