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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. -
Supplementary Information for Microbial Electrochemical Systems Outperform Fixed-Bed Biofilters for Cleaning-Up Urban Wastewater
Electronic Supplementary Material (ESI) for Environmental Science: Water Research & Technology. This journal is © The Royal Society of Chemistry 2016 Supplementary information for Microbial Electrochemical Systems outperform fixed-bed biofilters for cleaning-up urban wastewater AUTHORS: Arantxa Aguirre-Sierraa, Tristano Bacchetti De Gregorisb, Antonio Berná, Juan José Salasc, Carlos Aragónc, Abraham Esteve-Núñezab* Fig.1S Total nitrogen (A), ammonia (B) and nitrate (C) influent and effluent average values of the coke and the gravel biofilters. Error bars represent 95% confidence interval. Fig. 2S Influent and effluent COD (A) and BOD5 (B) average values of the hybrid biofilter and the hybrid polarized biofilter. Error bars represent 95% confidence interval. Fig. 3S Redox potential measured in the coke and the gravel biofilters Fig. 4S Rarefaction curves calculated for each sample based on the OTU computations. Fig. 5S Correspondence analysis biplot of classes’ distribution from pyrosequencing analysis. Fig. 6S. Relative abundance of classes of the category ‘other’ at class level. Table 1S Influent pre-treated wastewater and effluents characteristics. Averages ± SD HRT (d) 4.0 3.4 1.7 0.8 0.5 Influent COD (mg L-1) 246 ± 114 330 ± 107 457 ± 92 318 ± 143 393 ± 101 -1 BOD5 (mg L ) 136 ± 86 235 ± 36 268 ± 81 176 ± 127 213 ± 112 TN (mg L-1) 45.0 ± 17.4 60.6 ± 7.5 57.7 ± 3.9 43.7 ± 16.5 54.8 ± 10.1 -1 NH4-N (mg L ) 32.7 ± 18.7 51.6 ± 6.5 49.0 ± 2.3 36.6 ± 15.9 47.0 ± 8.8 -1 NO3-N (mg L ) 2.3 ± 3.6 1.0 ± 1.6 0.8 ± 0.6 1.5 ± 2.0 0.9 ± 0.6 TP (mg -
Resilience of Microbial Communities After Hydrogen Peroxide Treatment of a Eutrophic Lake to Suppress Harmful Cyanobacterial Blooms
microorganisms Article Resilience of Microbial Communities after Hydrogen Peroxide Treatment of a Eutrophic Lake to Suppress Harmful Cyanobacterial Blooms Tim Piel 1,†, Giovanni Sandrini 1,†,‡, Gerard Muyzer 1 , Corina P. D. Brussaard 1,2 , Pieter C. Slot 1, Maria J. van Herk 1, Jef Huisman 1 and Petra M. Visser 1,* 1 Department of Freshwater and Marine Ecology, Institute for Biodiversity and Ecosystem Dynamics, University of Amsterdam, 1090 GE Amsterdam, The Netherlands; [email protected] (T.P.); [email protected] (G.S.); [email protected] (G.M.); [email protected] (C.P.D.B.); [email protected] (P.C.S.); [email protected] (M.J.v.H.); [email protected] (J.H.) 2 Department of Marine Microbiology and Biogeochemistry, NIOZ Royal Netherland Institute for Sea Research, 1790 AB Den Burg, The Netherlands * Correspondence: [email protected]; Tel.: +31-20-5257073 † These authors have contributed equally to this work. ‡ Current address: Department of Technology & Sources, Evides Water Company, 3006 AL Rotterdam, The Netherlands. Abstract: Applying low concentrations of hydrogen peroxide (H2O2) to lakes is an emerging method to mitigate harmful cyanobacterial blooms. While cyanobacteria are very sensitive to H2O2, little Citation: Piel, T.; Sandrini, G.; is known about the impacts of these H2O2 treatments on other members of the microbial com- Muyzer, G.; Brussaard, C.P.D.; Slot, munity. In this study, we investigated changes in microbial community composition during two P.C.; van Herk, M.J.; Huisman, J.; −1 lake treatments with low H2O2 concentrations (target: 2.5 mg L ) and in two series of controlled Visser, P.M. -
Physiology of Dimethylsulfoniopropionate Metabolism
PHYSIOLOGY OF DIMETHYLSULFONIOPROPIONATE METABOLISM IN A MODEL MARINE ROSEOBACTER, Silicibacter pomeroyi by JAMES R. HENRIKSEN (Under the direction of William B. Whitman) ABSTRACT Dimethylsulfoniopropionate (DMSP) is a ubiquitous marine compound whose degradation is important in carbon and sulfur cycles and influences global climate due to its degradation product dimethyl sulfide (DMS). Silicibacter pomeroyi, a member of the a marine Roseobacter clade, is a model system for the study of DMSP degradation. S. pomeroyi can cleave DMSP to DMS and carry out demethylation to methanethiol (MeSH), as well as degrade both these compounds. Dif- ferential display proteomics was used to find proteins whose abundance increased when chemostat cultures of S. pomeroyi were grown with DMSP as the sole carbon source. Bioinformatic analysis of these genes and their gene clusters suggested roles in DMSP metabolism. A genetic system was developed for S. pomeroyi that enabled gene knockout to confirm the function of these genes. INDEX WORDS: Silicibacter pomeroyi, Ruegeria pomeroyi, dimethylsulfoniopropionate, DMSP, roseobacter, dimethyl sulfide, DMS, methanethiol, MeSH, marine, environmental isolate, proteomics, genetic system, physiology, metabolism PHYSIOLOGY OF DIMETHYLSULFONIOPROPIONATE METABOLISM IN A MODEL MARINE ROSEOBACTER, Silicibacter pomeroyi by JAMES R. HENRIKSEN B.S. (Microbiology), University of Oklahoma, 2000 B.S. (Biochemistry), University of Oklahoma, 2000 A Dissertation Submitted to the Graduate Faculty of The University of Georgia in Partial Fulfillment of the Requirements for the Degree DOCTOR OF PHILOSOPHY ATHENS, GEORGIA 2008 cc 2008 James R. Henriksen Some Rights Reserved Creative Commons License Version 3.0 Attribution-Noncommercial-Share Alike PHYSIOLOGY OF DIMETHYLSULFONIOPROPIONATE METABOLISM IN A MODEL MARINE ROSEOBACTER, Silicibacter pomeroyi by JAMES R. -
Section 4. Guidance Document on Horizontal Gene Transfer Between Bacteria
306 - PART 2. DOCUMENTS ON MICRO-ORGANISMS Section 4. Guidance document on horizontal gene transfer between bacteria 1. Introduction Horizontal gene transfer (HGT) 1 refers to the stable transfer of genetic material from one organism to another without reproduction. The significance of horizontal gene transfer was first recognised when evidence was found for ‘infectious heredity’ of multiple antibiotic resistance to pathogens (Watanabe, 1963). The assumed importance of HGT has changed several times (Doolittle et al., 2003) but there is general agreement now that HGT is a major, if not the dominant, force in bacterial evolution. Massive gene exchanges in completely sequenced genomes were discovered by deviant composition, anomalous phylogenetic distribution, great similarity of genes from distantly related species, and incongruent phylogenetic trees (Ochman et al., 2000; Koonin et al., 2001; Jain et al., 2002; Doolittle et al., 2003; Kurland et al., 2003; Philippe and Douady, 2003). There is also much evidence now for HGT by mobile genetic elements (MGEs) being an ongoing process that plays a primary role in the ecological adaptation of prokaryotes. Well documented is the example of the dissemination of antibiotic resistance genes by HGT that allowed bacterial populations to rapidly adapt to a strong selective pressure by agronomically and medically used antibiotics (Tschäpe, 1994; Witte, 1998; Mazel and Davies, 1999). MGEs shape bacterial genomes, promote intra-species variability and distribute genes between distantly related bacterial genera. Horizontal gene transfer (HGT) between bacteria is driven by three major processes: transformation (the uptake of free DNA), transduction (gene transfer mediated by bacteriophages) and conjugation (gene transfer by means of plasmids or conjugative and integrated elements). -
Draft Genome Sequence of Thalassobius Mediterraneus CECT 5383T, a Poly-Beta-Hydroxybutyrate Producer
Genomics Data 7 (2016) 237–239 Contents lists available at ScienceDirect Genomics Data journal homepage: www.elsevier.com/locate/gdata Data in Brief Draft genome sequence of Thalassobius mediterraneus CECT 5383T, a poly-beta-hydroxybutyrate producer Lidia Rodrigo-Torres, María J. Pujalte, David R. Arahal ⁎ Departamento de Microbiología y Ecología and Colección Española de Cultivos Tipo (CECT), Universidad de Valencia, Valencia, Spain article info abstract Article history: Thalassobius mediterraneus is the type species of the genus Thalassobius and a member of the Roseobacter clade, an Received 23 December 2015 abundant representative of marine bacteria. T. mediterraneus XSM19T (=CECT 5383T) was isolated from the Received in revised form 8 January 2016 Western Mediterranean coast near Valencia (Spain) in 1989. We present here the draft genome sequence and Accepted 14 January 2016 annotation of this strain (ENA/DDBJ/NCBI accession number CYSF00000000), which is comprised of Available online 15 January 2016 3,431,658 bp distributed in 19 contigs and encodes 10 rRNA genes, 51 tRNA genes and 3276 protein coding fi Keywords: genes. Relevant ndings are commented, including the complete set of genes required for poly-beta- Rhodobacteraceae hydroxybutyrate (PHB) synthesis and genes related to degradation of aromatic compounds. Roseobacter clade © 2016 The Authors. Published by Elsevier Inc. This is an open access article under the CC BY-NC-ND license PHB (http://creativecommons.org/licenses/by-nc-nd/4.0/). Aromatic compounds 1. Direct link to deposited data has not been yet validated, and even more recently T. abysii has been Specifications also proposed [6]. Organism/cell line/tissue Thalassobius mediterraneus Strain CECT 5383T Sequencer or array type Illumina MiSeq 2. -
Horizontal Operon Transfer, Plasmids, and the Evolution of Photosynthesis in Rhodobacteraceae
The ISME Journal (2018) 12:1994–2010 https://doi.org/10.1038/s41396-018-0150-9 ARTICLE Horizontal operon transfer, plasmids, and the evolution of photosynthesis in Rhodobacteraceae 1 2 3 4 1 Henner Brinkmann ● Markus Göker ● Michal Koblížek ● Irene Wagner-Döbler ● Jörn Petersen Received: 30 January 2018 / Revised: 23 April 2018 / Accepted: 26 April 2018 / Published online: 24 May 2018 © The Author(s) 2018. This article is published with open access Abstract The capacity for anoxygenic photosynthesis is scattered throughout the phylogeny of the Proteobacteria. Their photosynthesis genes are typically located in a so-called photosynthesis gene cluster (PGC). It is unclear (i) whether phototrophy is an ancestral trait that was frequently lost or (ii) whether it was acquired later by horizontal gene transfer. We investigated the evolution of phototrophy in 105 genome-sequenced Rhodobacteraceae and provide the first unequivocal evidence for the horizontal transfer of the PGC. The 33 concatenated core genes of the PGC formed a robust phylogenetic tree and the comparison with single-gene trees demonstrated the dominance of joint evolution. The PGC tree is, however, largely incongruent with the species tree and at least seven transfers of the PGC are required to reconcile both phylogenies. 1234567890();,: 1234567890();,: The origin of a derived branch containing the PGC of the model organism Rhodobacter capsulatus correlates with a diagnostic gene replacement of pufC by pufX. The PGC is located on plasmids in six of the analyzed genomes and its DnaA- like replication module was discovered at a conserved central position of the PGC. A scenario of plasmid-borne horizontal transfer of the PGC and its reintegration into the chromosome could explain the current distribution of phototrophy in Rhodobacteraceae. -
Insights Into Mutualism Mechanism and Versatile Metabolism Of
www.nature.com/scientificreports OPEN Insights into mutualism mechanism and versatile metabolism of Ketogulonicigenium vulgare Hbe602 Received: 20 January 2016 Accepted: 29 February 2016 based on comparative genomics Published: 16 March 2016 and metabolomics studies Nan Jia1,2, Ming-Zhu Ding1,2, Jin Du1,2, Cai-Hui Pan1,2, Geng Tian3, Ji-Dong Lang3, Jian-Huo Fang3, Feng Gao1,2,4 & Ying-Jin Yuan1,2 Ketogulonicigenium vulgare has been widely used in vitamin C two steps fermentation and requires companion strain for optimal growth. However, the understanding of K. vulgare as well as its companion strain is still preliminary. Here, the complete genome of K. vulgare Hbe602 was deciphered to provide insight into the symbiosis mechanism and the versatile metabolism. K. vulgare contains the LuxR family proteins, chemokine proteins, flagellar structure proteins, peptides and transporters for symbiosis consortium. Besides, the growth state and metabolite variation of K. vulgare were observed when five carbohydrates (D-sorbitol, L-sorbose, D-glucose, D-fructose and D-mannitol) were used as carbon source. The growth increased by 40.72% and 62.97% respectively when K. vulgare was cultured on D-mannitol/D-sorbitol than on L-sorbose. The insufficient metabolism of carbohydrates, amino acids and vitamins is the main reason for the slow growth of K. vulgare. The combined analysis of genomics and metabolomics indicated that TCA cycle, amino acid and nucleotide metabolism were significantly up-regulated when K. vulgare was cultured on the D-mannitol/D-sorbitol, which facilitated the better growth. The present study would be helpful to further understand its metabolic structure and guide the engineering transformation. -
Strain-Level Diversity Drives Alternative Community Types in Millimeter Scale
bioRxiv preprint doi: https://doi.org/10.1101/280271; this version posted March 11, 2018. 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. Strain-level diversity drives alternative community types in millime- ter scale granular biofilms Gabriel E. Leventhal,1 Carles Boix,1 Urs Kuechler,2 Tim N. Enke,1,2 Elzbieta Sliwerska,2 Christof Holliger,3 Otto X. Cordero1,2,y 1 Dept. of Civil and Environmental Engineering, Massachusetts Institute of Technology (MIT), Cambridge, MA, U.S.A.; 2 Dept. of Environmental System Sciences, ETH Zurich, Zurich, Switzerland; 3 Laboratory for Environmental Biotechnology, École Polytechnique Fédéral de Lausanne (EPFL), Lausanne, Switzer- land [email protected] Keywords: Microbial communities; Strain diversity; Alternative states, Activated granular sludge; Accumulibac- ter; EBPR; Co-evolution; Microbial communities are often highly diverse in their composition, both at the level of coarse-grained taxa such as genera as well as at the level of strains within species. This variability can be driven by both extrinsic factors like temperature, pH, etc., as well as by intrinsic ones, such as demographic fluctuations or ecologi- cal interactions. The relative contributions of these factors and the taxonomic level at which they influence community structure remain poorly understood, in part because of the difficulty of identifying true com- munity replicates assembled under the same environmental parameters. Here, we address this problem using an activated granular sludge reactor in which millimeter scale biofilm granules represent true com- munity replicates whose differences in composition are expected to be driven primarily by biotic factors. -
Research Collection
Research Collection Doctoral Thesis Development and application of molecular tools to investigate microbial alkaline phosphatase genes in soil Author(s): Ragot, Sabine A. Publication Date: 2016 Permanent Link: https://doi.org/10.3929/ethz-a-010630685 Rights / License: In Copyright - Non-Commercial Use Permitted This page was generated automatically upon download from the ETH Zurich Research Collection. For more information please consult the Terms of use. ETH Library DISS. ETH NO.23284 DEVELOPMENT AND APPLICATION OF MOLECULAR TOOLS TO INVESTIGATE MICROBIAL ALKALINE PHOSPHATASE GENES IN SOIL A thesis submitted to attain the degree of DOCTOR OF SCIENCES of ETH ZURICH (Dr. sc. ETH Zurich) presented by SABINE ANNE RAGOT Master of Science UZH in Biology born on 25.02.1987 citizen of Fribourg, FR accepted on the recommendation of Prof. Dr. Emmanuel Frossard, examiner PD Dr. Else Katrin Bünemann-König, co-examiner Prof. Dr. Michael Kertesz, co-examiner Dr. Claude Plassard, co-examiner 2016 Sabine Anne Ragot: Development and application of molecular tools to investigate microbial alkaline phosphatase genes in soil, c 2016 ⃝ ABSTRACT Phosphatase enzymes play an important role in soil phosphorus cycling by hydrolyzing organic phosphorus to orthophosphate, which can be taken up by plants and microorgan- isms. PhoD and PhoX alkaline phosphatases and AcpA acid phosphatase are produced by microorganisms in response to phosphorus limitation in the environment. In this thesis, the current knowledge of the prevalence of phoD and phoX in the environment and of their taxonomic distribution was assessed, and new molecular tools were developed to target the phoD and phoX alkaline phosphatase genes in soil microorganisms. -
Phage As Agents of Lateral Gene Transfer Carlos Canchaya, Ghislain Fournous, Sandra Chibani-Chennoufi, Marie-Lise Dillmann and Harald Bru¨ Ssowã
417 Phage as agents of lateral gene transfer Carlos Canchaya, Ghislain Fournous, Sandra Chibani-Chennoufi, Marie-Lise Dillmann and Harald Bru¨ ssowà When establishing lysogeny, temperate phages integrate their Lateral gene transfer genome as a prophage into the bacterial chromosome. With about 100 sequenced genomes of bacteria in the Prophages thus constitute in many bacteria a substantial part public database and many more to come, genomics has of laterally acquired DNA. Some prophages contribute changed our understanding of microbiology. In fact, the lysogenic conversion genes that are of selective advantage to genomes of bacteria are remarkably fluid. A substantial the bacterial host. Occasionally, phages are also involved part of the bacterial DNA is not transferred from the in the lateral transfer of other mobile DNA elements or parental cell to its descendent (‘vertical’ transfer), but is bacterial DNA. Recent advances in the field of genomics acquired horizontally by transformation, conjugation or have revealed a major impact by phages on bacterial transduction (‘lateral’ transfer) [1]. The replacement of chromosome evolution. a tree-like by a web-like representation of the phyloge- netic relationship between bacteria is a visual expression Addresses of this change in perception of microbial evolution. An Nestle´ Research Centre, CH-1000 Lausanne 26, Vers-chez-les-Blanc, important element of mobile DNA is bacteriophages. Switzerland à Infection of a bacterial cell with a temperate phage e-mail: [email protected] (Figure 1a,b) can have two outcomes: multiplication of the phage with concomitant lysis of the bacterial host Current Opinion in Microbiology 2003, 6:417–424 (Figure 1c) or lysogenization, (i.e. -
Compile.Xlsx
Silva OTU GS1A % PS1B % Taxonomy_Silva_132 otu0001 0 0 2 0.05 Bacteria;Acidobacteria;Acidobacteria_un;Acidobacteria_un;Acidobacteria_un;Acidobacteria_un; otu0002 0 0 1 0.02 Bacteria;Acidobacteria;Acidobacteriia;Solibacterales;Solibacteraceae_(Subgroup_3);PAUC26f; otu0003 49 0.82 5 0.12 Bacteria;Acidobacteria;Aminicenantia;Aminicenantales;Aminicenantales_fa;Aminicenantales_ge; otu0004 1 0.02 7 0.17 Bacteria;Acidobacteria;AT-s3-28;AT-s3-28_or;AT-s3-28_fa;AT-s3-28_ge; otu0005 1 0.02 0 0 Bacteria;Acidobacteria;Blastocatellia_(Subgroup_4);Blastocatellales;Blastocatellaceae;Blastocatella; otu0006 0 0 2 0.05 Bacteria;Acidobacteria;Holophagae;Subgroup_7;Subgroup_7_fa;Subgroup_7_ge; otu0007 1 0.02 0 0 Bacteria;Acidobacteria;ODP1230B23.02;ODP1230B23.02_or;ODP1230B23.02_fa;ODP1230B23.02_ge; otu0008 1 0.02 15 0.36 Bacteria;Acidobacteria;Subgroup_17;Subgroup_17_or;Subgroup_17_fa;Subgroup_17_ge; otu0009 9 0.15 41 0.99 Bacteria;Acidobacteria;Subgroup_21;Subgroup_21_or;Subgroup_21_fa;Subgroup_21_ge; otu0010 5 0.08 50 1.21 Bacteria;Acidobacteria;Subgroup_22;Subgroup_22_or;Subgroup_22_fa;Subgroup_22_ge; otu0011 2 0.03 11 0.27 Bacteria;Acidobacteria;Subgroup_26;Subgroup_26_or;Subgroup_26_fa;Subgroup_26_ge; otu0012 0 0 1 0.02 Bacteria;Acidobacteria;Subgroup_5;Subgroup_5_or;Subgroup_5_fa;Subgroup_5_ge; otu0013 1 0.02 13 0.32 Bacteria;Acidobacteria;Subgroup_6;Subgroup_6_or;Subgroup_6_fa;Subgroup_6_ge; otu0014 0 0 1 0.02 Bacteria;Acidobacteria;Subgroup_6;Subgroup_6_un;Subgroup_6_un;Subgroup_6_un; otu0015 8 0.13 30 0.73 Bacteria;Acidobacteria;Subgroup_9;Subgroup_9_or;Subgroup_9_fa;Subgroup_9_ge;