DOCSLIB.ORG

Identification and Characterization of Oxalate Oxidoreductase, A

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Identification and Characterization of Oxalate Oxidoreductase, A University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Biochemistry -- Faculty Publications Biochemistry, Department of 2010 Identification and Characterization of Oxalate Oxidoreductase, a Novel Thiamine Pyrophosphate-dependent 2-Oxoacid Oxidoreductase That Enables Anaerobic Growth on Oxalate Elizabeth Pierce University of Michigan, Ann Arbor Donald F. Becker University of Nebraska-Lincoln, [email protected] Stephen W. Ragsdale University of Michigan, Ann Arbor, [email protected] Follow this and additional works at: https://digitalcommons.unl.edu/biochemfacpub Part of the Biochemistry Commons, Biotechnology Commons, and the Other Biochemistry, Biophysics, and Structural Biology Commons Pierce, Elizabeth; Becker, Donald F.; and Ragsdale, Stephen W., "Identification and Characterization of Oxalate Oxidoreductase, a Novel Thiamine Pyrophosphate-dependent 2-Oxoacid Oxidoreductase That Enables Anaerobic Growth on Oxalate" (2010). Biochemistry -- Faculty Publications. 179. https://digitalcommons.unl.edu/biochemfacpub/179 This Article is brought to you for free and open access by the Biochemistry, Department of at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Biochemistry -- Faculty Publications by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. THE JOURNAL OF BIOLOGICAL CHEMISTRY VOL. 285, NO. 52, pp. 40515–40524, December 24, 2010 © 2010 by The American Society for Biochemistry and Molecular Biology, Inc. Printed in the U.S.A. Identification and Characterization of Oxalate Oxidoreductase, a Novel Thiamine Pyrophosphate-dependent 2-Oxoacid Oxidoreductase That Enables Anaerobic Growth on Oxalate*□S Received for publication, June 17, 2010, and in revised form, October 15, 2010 Published, JBC Papers in Press, October 18, 2010, DOI 10.1074/jbc.M110.155739 Elizabeth Pierce‡, Donald F. Becker§, and Stephen W. Ragsdale‡1 From the ‡Department of Biological Chemistry, University of Michigan, Ann Arbor, Michigan 48109-0606 and the §Department of Biochemistry, University of Nebraska, Lincoln, Nebraska 68588-0664 Moorella thermoacetica is an anaerobic acetogen, a class of can use other electron acceptors (e.g. nitrate, nitrite, thiosul- bacteria that is found in the soil, the animal gastrointestinal fate, and dimethyl sulfoxide). Under most conditions, nitrate tract, and the rumen. This organism engages the Wood-Ljung- reduction occurs preferentially to CO2 reduction, and nitrate dahl pathway of anaerobic CO2 fixation for heterotrophic or has been shown to repress autotrophic growth (1, 2). How- autotrophic growth. This paper describes a novel enzyme, oxa- ever, oxalate is unique in its properties as an electron donor late oxidoreductase (OOR), that enables M. thermoacetica to by M. thermoacetica for acetogenic growth. When both ni- grow on oxalate, which is produced in soil and is a common trate and CO2 are provided to cells growing on oxalate, CO2 is component of kidney stones. Exposure to oxalate leads to the reduced to acetate during exponential growth phase, and ni- induction of three proteins that are subunits of OOR, which trate is only used as the electron acceptor during stationary oxidizes oxalate coupled to the production of two electrons phase (3). Oxalate is the only substrate with which M. ther- and CO or bicarbonate. Like other members of the 2-oxoacid: 2 moacetica has been shown to reduce CO2 instead of nitrate ferredoxin oxidoreductase family, OOR contains thiamine py- when both are present. rophosphate and three [Fe S ] clusters. However, unlike previ- 2Ϫ 4 4 Oxalate (C2O4 ) is the most oxidized two-carbon com- ously characterized members of this family, OOR does not use pound. It is made in high concentrations by some plants coenzyme A as a substrate. Oxalate is oxidized with a kcat of and fungi and can reach high micromolar concentrations ؊1 ␮ 0.09 s and a Km of 58 M at pH 8. OOR also oxidizes a few in soil (4). Oxalate is toxic to mammals but is metabolized other 2-oxoacids (which do not induce OOR) also without any by many bacteria and plants by various pathways. In Ox- requirement for CoA. The enzyme transfers its reducing alobacter formigenes, oxalate is first activated to oxalyl- equivalents to a broad range of electron acceptors, including CoA and then decarboxylated, giving formyl-CoA and ferredoxin and the nickel-dependent carbon monoxide dehy- CO2. Formyl-CoA transferase then exchanges the formyl drogenase. In conjunction with the well characterized Wood- group for an oxalyl-group on CoA, thus producing formate Ljungdahl pathway, OOR should be sufficient for oxalate me- and regenerating oxalyl-CoA. Energy for growth on oxalate tabolism by M. thermoacetica, and it constitutes a novel in O. formigenes results from a formate-oxalate antiporter, pathway for oxalate metabolism. which generates an electrochemical transmembrane gradi- ent for ATP synthesis (5, 6), so most formate produced is excreted rather than oxidized (7). Other organisms, such as Moorella thermoacetica is a strictly anaerobic Gram-posi- Cupriavidus oxalaticus, also use oxalyl-CoA decarboxylase tive acetogenic bacterium. Acetogens are commonly found in to metabolize oxalate but use formate dehydrogenase to the soil, animal gastrointestinal tract, and the rumen and generate NADH with the electrons derived from oxalate (8, grow heterotrophically or autotrophically on many different 9). Oxalyl-CoA decarboxylase is a TPP-dependent enzyme electron donors. Electrons from these substrates are used to with distant homology to yeast pyruvate decarboxylases reduce CO2 to acetate by the Wood-Ljungdahl pathway. Dur- (10). The M. thermoacetica genome has sequences with low ing growth by this pathway, acetate and cell mass are the only homology to oxalyl-CoA decarboxylase but no homolog of growth products, and electron-rich growth substrates like formyl-CoA transferase. In fungi and in some bacteria, in- glucose are converted stoichiometrically to acetate; therefore, cluding Bacillus subtilis, oxalate can also be metabolized by M. thermoacetica is called a homoacetogen. M. thermoacetica oxalate decarboxylase, a manganese-containing cupin fam- ily protein, to generate formate and CO2 (11). This reac- 2ϩ * This work was supported, in whole or in part, by National Institutes of tion requires O2. Another Mn -cupin called germin that Health (NIH) Grant GM39451 (to S. W. R.) and NIH, NCRR, Grant P20 RR- is found in plants catalyzes the oxidative decarboxylation 017675 (to D. F. B.) (for the ultracentrifugation studies). This work was of oxalate in the reaction C O2Ϫ ϩ 2Hϩ ϩ O 3 2CO ϩ also supported by National Science Foundation Grant DBI-0619764. 2 4 2 2 □ S The on-line version of this article (available at http://www.jbc.org) con- H2O2 (12). No enzyme that catalyzes anaerobic oxalate oxi- tains supplemental Figs. S1–S5 and Table S1. dation has been reported previously. 1 To whom correspondence should be addressed: Dept. of Biological Chem- During growth on oxalate, M. thermoacetica consumes 4 istry, University of Michigan, University of Michigan Medical School, 5301 MSRB III, 1150 W. Medical Center Dr., Ann Arbor, MI 48109-0606. Tel.: 734- mol of oxalate to produce 1 mol of acetate and 6 mol of CO2 615-4621; Fax: 734-763-4581; E-mail: [email protected]. (Reaction 1) (13). DECEMBER 24, 2010•VOLUME 285•NUMBER 52 JOURNAL OF BIOLOGICAL CHEMISTRY 40515 Oxalate Oxidoreductase Ϫ 2 ϩ 3 Ϫ ϩ Ϫ ϩ Ϫ ͑⌬ ϭ 4C2O4 5H2O CH3COO 6 HCO3 OH G sonication was used to break the cells and, after precipitation of proteins in methanol, the protein pellet was washed twice Ϫ ͒ 41.4 kJ/mol oxalate with ice-cold acetone (80% in water) and once with ice-cold REACTION 1 ethanol (70% in water). After washing, the protein pellets were suspended in 8 M urea, 2 M thiourea, 2% (w/v) CHAPS, Two proteins (33 and 42 kDa) were identified as being in- 2% (w/v) Triton X-100, and 50 mM dithiothreitol (DTT) to ϳ1 duced when M. thermoacetica was exposed to oxalate (14). ␮g/␮l protein. Samples (150 ␮l) were supplemented with Bio- Similarly, Daniel et al. (14) found that oxalate-grown cells Lyte ampholytes (Bio-Rad) and loaded on 7-cm Bio-Rad iso- metabolize oxalate much more quickly than cells that had electric focusing gel strips (gradient from pH 5 to 8). The gels been grown on glucose, which is consistent with an oxalate were subjected to a 12-h rehydration at 50 V, followed by fo- induction mechanism (15). They also showed that cell ex- cusing at 250 V for 15 min and then at 4000 V for 35,000 V-h. tracts from oxalate-grown cells could catalyze oxalate-depen- After isoelectric focusing, the isoelectric focusing gel strips dent benzyl viologen reduction, that this activity was only were soaked in 6 M urea, 2% (w/v) SDS, 0.375 M Tris-HCl, pH slightly stimulated by coenzyme A, and that the electron ac- 8.8, 20% (w/v) glycerol, and 20 mg/ml DTT for 15 min, fol- ceptor specificity of oxalate oxidation was different than that lowed by incubation for 15 min in the same buffer but with 25 of formate oxidation. They concluded that M. thermoacetica mg/ml iodoacetamide instead of DTT. Strips were rinsed in catabolizes oxalate by a CoA-independent mechanism that running buffer before loading them at the top of 12.5% acryl- does not use formate as an intermediate. amide gels for SDS-PAGE. After SDS-PAGE, proteins were This paper describes the characterization of the oxalate- stained with Coomassie Blue. Spots were cut from the gels, 2 induced enzyme, oxalate oxidoreductase (OOR) and demon- and proteins were identified by mass spectrometry at the Uni- strates that it, unlike all previously characterized members of versity of Michigan Protein Structure Facility. A blank spot of the thiamine pyrophosphate (TPP)-dependent 2-oxoacid: each gel was also taken and processed. The samples were sub- ferredoxin oxidoreductase family, does not require coenzyme jected to in-gel trypsin digestion. As a control, BSA was run A. Coupling OOR to the Wood-Ljungdahl pathway allows on a separate gel and subjected to the same digestion and anaerobic bacteria to generate energy by converting oxalate to mass spectrometry procedure.
Load more

Recommended publications
  • Information to Users
    INFORMATION TO USERS This reproduction was made from a copy of a manuscript sent to us for publication and microfilming. While the most advanced technology has been used to pho­ tograph and reproduce this manuscript, the quality of the reproduction is heavily dependent upon the quédlty of the material submitted. Pages in any manuscript may have indistinct print. In all cases the best available copy has been filmed. The following explanation of techniques is provided to help clarify notations which may appear on this reproduction. 1. Manuscripts may not always be complete. When it is not possible to obtain missing pages, a note appears to indicate this. 2. When copyrighted materials are removed from the manuscript, a note ap­ pears to indicate this. 3. Oversize materials (maps, drawings, and charts) are photographed by sec­ tioning the original, beginning at the upper left hemd comer and continu­ ing from left to right in equal sections with small overlaps. Each oversize page is also filmed as one exposure and is available, for an additional charge, as a standard 35mm slide or in black and white paper format. * 4. Most photographs reproduce acceptably on positive microfilm or micro­ fiche but lack clarity on xerographic copies made from the microfilm. For an additional charge, all photographs are available in black and white stcmdard 35mm slide format.* *For more information about black and white slides or enlarged paper reproductions, please contact the Dissertations Customer Services Department. IVBcrofilnis lateniai^oiial 8612390 Lee, Jong-Kwon STRESS CORROSION CRACKING AND PITTING OF SENSITIZED TYPE 304 STAINLESS STEEL IN CHLORIDE SOLUTIONS CONTAINING SULFUR SPECIES AT TEMPERATURES FROM 50 TO 200 DEGREES C The Ohio State University Ph.D.
    [Show full text]
  • Brearley, Francis Q. Thomas, Andrew D-Land
    Land-use Change Impacts on Soil Processes Tropical and Savannah Ecosystems Land-use Change Impacts on Soil Processes Tropical and Savannah Ecosystems Edited by Francis Q. Brearley Manchester Metropolitan University and Andrew D. Thomas Aberystwyth University CABI is a trading name of CAB International CABI CABI Nosworthy Way 745 Atlantic Avenue Wallingford 8th Floor Oxfordshire OX10 8DE Boston, MA 02111 UK USA Tel: +44 (0)1491 832111 Tel: +1 617 682 9015 Fax: +44 (0)1491 833508 E-mail: [email protected] E-mail: [email protected] Website: www.cabi.org © CAB International 2015. All rights reserved. No part of this publication may be reproduced in any form or by any means, electronically, mechanically, by photocopying, recording or otherwise, without the prior permission of the copyright owners. A catalogue record for this book is available from the British Library, London, UK. Library of Congress Cataloging-in-Publication Data Land-use change impacts on soil processes : tropical and savannah ecosystems / edited by Francis Q. Brearley, Manchester Metropolitan University; and Andrew D. Thomas, Aberystwyth University. pages cm Includes bibliographical references and index. ISBN 978-1-78064-210-9 (hbk : alk. paper) 1. Soils--Environmental aspects--Case studies. 2. Land use--Environmental aspects--Case studies. 3. Soil ecology--Case studies. I. Brearley, Francis Q., editor. II. Thomas, Andrew D. (Andrew David), 1970- editor. III. Title: Land use change impacts on soil processes. S596.L36 2015 577.5’7--dc23 2015021721 ISBN-13: 978 1 78064 210 9 Commissioning editors: Vicki Bonham and Nicki Dennis Editorial assistant: Emma McCann Production editors: Tracy Head and Emma Ross Typeset by SPi, Pondicherry, India.
    [Show full text]
  • Sulfate-Reducing Bacteria in Anaerobic Bioreactors Are Presented in Table 1
    Sulfate-reducing Bacteria inAnaerobi c Bioreactors Stefanie J.W.H. Oude Elferink Promotoren: dr. ir. G. Lettinga bijzonder hoogleraar ind eanaërobisch e zuiveringstechnologie en hergebruik dr. W.M. deVo s hoogleraar ind e microbiologie Co-promotor: dr. ir. AJ.M. Stams universitair docent bij deleerstoelgroe p microbiologie ^OSJO^-M'3^- Stefanie J.W.H.Oud eElferin k Sulfate-reducing Bacteria inAnaerobi c Bioreactors Proefschrift terverkrijgin g van degraa d van doctor op gezag van derecto r magnificus van deLandbouwuniversitei t Wageningen, dr. C.M. Karssen, inhe t openbaar te verdedigen opvrijda g 22me i 1998 des namiddags tehal f twee ind eAula . r.r, A tri ISBN 90 5485 8451 The research described inthi s thesiswa s financially supported by agran t ofth e Innovative Oriented Program (IOP) Committee on Environmental Biotechnology (IOP-m 90209) established by the Dutch Ministry of Economics, and a grant from Pâques BV. Environmental Technology, P.O. Box 52, 8560AB ,Balk , TheNetherlands . BIBLIOTHEEK LANDBOUWUNIVERSITEIT WAGENTNGEN 1 (J ÜOB^ . ^3"£ Stellingen 1. Inhu n lijst van mogelijke scenario's voor de anaërobe afbraak van propionaat onder sulfaatrijke condities vergeten Uberoi enBhattachary a het scenario dat ind e anaërobe waterzuiveringsreactor van depapierfabrie k teEerbee k lijkt opt etreden , namelijk de afbraak vanpropionaa t door syntrofen en sulfaatreduceerders end e afbraak van acetaat en waterstof door sulfaatreduceerders en methanogenen. Ditproefschrift, hoofdstuk 7 UberoiV, Bhattacharya SK (1995)Interactions among sulfate reducers, acetogens, and methanogens in anaerobicpropionate systems. 2. De stelling van McCartney en Oleszkiewicz dat sulfaatreduceerders inanaërob e reactoren waarschijnlijk alleen competerenme t methanogenen voor het aanwezige waterstof, omdat acetaatafbrekende sulfaatreduceerders nog nooit uit anaëroob slib waren geïsoleerd, was correct bij indiening, maar achterhaald bij publicatie.
    [Show full text]
  • Using Either Hydrogen Or Dithionite As Reductant in Uranium
    AC 2012-4906: USING EITHER HYDROGEN OR DITHIONITE AS RE- DUCTANT IN URANIUM CONTAMINATED GROUNDWATER AT POST- LEACH URANIUM MINING SITES, SOUTH TEXAS Prof. Lee Clapp, Texas A&M University, Kingsville Lee Clapp is Associate Professor in environmental engineering. Prof. Mohamed Abdelrahman, Texas A&M University, Kingsville Mohamed Abdelrahman received the B.S. and M.S. degrees in electrical engineering and engineering physics from Cairo University, Egypt in 1988 and 1992, respectively. He received an M.S. and a Ph.D. in measurement and control and nuclear engineering from Idaho State University in 1994 and 1996, re- spectively. He is currently the Associate Dean of Engineering at Texas A&M University, Kingsville. Abdelrahman’s research focus is industrial applications of sensing and control with major research fund- ing from the U.S. Department of Energy, National Science Foundation, and industry. He has also focused on collaborative and innovative educational research. Abdelrahman is passionate about outreach activities for popularizing engineering research and education. His activities in that arena included NSF funded sites for research experience for undergraduates and research experience for Teachers. He has published his research results in more than 90 papers in refereed journals and conference proceedings and 30+ technical reports. Mr. Petronilo Estandarte Pana, LBJ Middle School, PSJA ISD B.S.E.M., M.S. GeoEng’g c American Society for Engineering Education, 2012 Modeling, Simulations and Studies using Hydrogen or Dithionite as Reductants in Uranium Contaminated Groundwater at Post- Leach Uranium Mining Sites in South Texas Abstract This paper summarizes the results of a summer research project conducted by a public high school teacher.
    [Show full text]
  • Technical Report TR-00-13
    SE0100078 Technical Report TR-00-13 Thermodynamic data for copper Implications for the corrosion of copper under repository conditions I Puigdomenech Royal Institute of Technology, Stockholm C Taxen Swedish Corrosion Institute, Stockholm August 2000 Svensk Karnbranslehantering AB Swedish Nuclear Fuel and Waste Management Co Box 5864 102 40 Stockholm Tel 08-459 84 00 Fax 08-661 57 19 / PLEASE BE AWARE THAT ALL OF THE MISSING PAGES IN THIS DOCUMENT WERE ORIGINALLY BLANK Thermodynamic data for copper Implications for the corrosion of copper under repository conditions I Puigdomenech Royal Institute of Technology, Stockholm C Taxen Swedish Corrosion Institute, Stockholm August 2000 This report concerns a study which was conducted for SKB. The conclusions and viewpoints presented in the report are those of the author(s) and do not necessarily coincide with those of the client. ABSTRACT The stability of copper canisters has a central role in the safety concept for the planned nuclear spent fuel repository in Sweden. The corrosion of cop- per canisters will be influenced by the chemical and physical environment in the near-field of the repository, and thermodynamic equilibrium calculations provide the basis for understanding this system. Thermodynamic data have been selected in this work for solids and aqueous 2 2 species in the system: Cu - H2O - H+ - H2 - F~ - Cl" - S ~ - SO4 ~ - NO3~ - NC>2~ - NH41" - PO43- - CC>32~. For some reactions and compounds, for which no experimental information on temperature effects was available, entropy and heat capacity values have been estimated. The compiled data were used to calculate thermodynamic equilibria for copper systems up to 100°C.
    [Show full text]
  • Long-Term Stability of Dithionite in Alkaline Anaerobic Aqueous Solution
    ACCEPTED MANUSCRIPT 1 Long-term stability of dithionite in alkaline anaerobic aqueous solution 2 Katherine Telfeyan *, Artas A. Migdisov, Sachin Pandey, Velimir V. Vesselinov, and Paul W. 3 Reimus 4 5 Earth and Environmental Sciences Division, Los Alamos National Laboratory, Los Alamos, NM 6 87545, United States 7 8 *Corresponding author: Phone: +1 505 665 3880; e-mail: [email protected] 9 Abstract 10 Closed-system experiments were conducted to investigate the decomposition of sodium 11 dithionite in aqueous solutions under varying pH and starting concentrations to simulate the 12 deployment of dithionite as an in-situ redox barrier. Co-determination of dithionite and its 13 degradation products was conducted using UV-Vis spectrometry, iodometric titration, and ion 14 chromatography. In unbuffered solutions, dithionite reacted rapidly, whereas in near-neutral 15 solutions (pH ~7), it persisted for ~ 50 days and in alkaline solution (pH ~9.5) for >100 days. 16 These are the longest lifetimes reported to date, which we attribute to not only excluding oxygen 17 but also preventing outgassing of H 2S. Thoroughly constraining the reaction products has led to 18 the following hypothesized reaction: 2- - 2- 2- 2- + 19 4 S 2O4 + H 2O HS +SO 3 +2 SO 4 +S 4O6 + H 20 which represents relatively rapid degradation at near-neutral pH values. At the more alkaline pH, 21 and over longer time scales, the reaction is best representedMANUSCRIPT by: 2- - 2- 2- + 22 3 S 2O4 + 3 H 2O 2HS +SO 3 +3 SO 4 + 4 H 23 the following kinetic rate law was developed for the pH range studied: dC = S 10 .
    [Show full text]
  • Biochemical Studies on Sulfate-Reducing Bacteria XIII
    J. Biochem., 75, 519-529 (1974) Biochemical Studies on Sulfate-reducing Bacteria . Sulfite Reductase from Desulfovibrio vulgaris-Mechanism of Trithionate, Thiosulfate, and Sulfide Formation and Enzymatic Properties Kunihiko KOBAYASHI, Yasuhide SEKI, and Makoto ISHIMOTO Department of Chemical Microbiology, Faculty of Pharmaceutical Sciences, Hokkaido University, Sapporo Received for publication, September 10, 1973 The reaction of sulfite reductase [EC 1. 8. 99. 1] from Desulfovibrio vulgaris was investigated using a purified enzyme preparation in a system coupled with methyl viologen and hydrogenase [EC 1.12.2.1]. Trithionate, thiosulfate, and sulfide were detected even in the early phase of sulfite reduction and the amount of each compound did not decrease during the reaction or after hydrogen uptake ceased. The specific radioactivity of sulfide formed from 35S-labelled sulfite was scarcely reduced on adding cold trithionate and only slightly on adding cold thiosulfate. These results, in addition to the fact that trithionate and thiosulfate are not reduced by the enzyme, indicate that these three compounds are produced by sulfite reductase. At high concentrations of sulfite and low concentrations of methyl viologen or hydrogenase, trithionate was the dominant product. Under the opposite conditions, the formation of relatively large amounts of sulfide or thiosulfate was observed. On the basis of these findings, a mechanism was proposed for the reaction, including labile intermediates, presumably sulfoxylate and elemental sulfur, which accept electrons from reduced methyl viologen to form sulfur and sulfide or react with sulfite to produce trithionate and thiosulfate, respectively. Some enzymatic properties were examined. K,,, was 3.6•~10-3M for sulfite. The optimum pH was 5.5 to 6.0.
    [Show full text]
  • Sodium Dithionite Cas N°: 7775-14-6
    OECD SIDS SODIUM DITHIONITE FOREWORD INTRODUCTION SODIUM DITHIONITE CAS N°: 7775-14-6 OECD SIDS SODIUM DITHIONITE SIDS Initial Assessment Report For SIAM 19 Berlin, Germany, 19-22 October 2004 1. Chemical Name: Sodium dithionite 2. CAS Number: 7775-14-6 3. Sponsor Country: Germany Contact Point: BMU (Bundesministerium für Umwelt, Naturschutz und Reaktorsicherheit) Contact person: Prof. Dr. Ulrich Schlottmann Postfach 12 06 29 D- 53048 Bonn 4. Shared Partnership with: 5. Roles/Responsibilities of BASF AG = lead company the Partners: • Name of industry sponsor BASF AG, Germany /consortium Contact person: Dr. Hubert Lendle GUP/CL – Z 570 D-67056 Ludwigshafen • Process used The BUA Peer Review Process : see next page 6. Sponsorship History • How was the chemical or by ICCA-Initiative category brought into the OECD HPV Chemicals Programme? 7. Review Process Prior to last literature search (update): the SIAM: 14 February 2003 (Human Health): databases medline, toxline; search profile CAS-No. and special search terms 5 February 2004 (Ecotoxicology): databases CA, biosis; search profile CAS-No. and special search terms OECD/ICCA 8. Quality check process: As basis for the SIDS-Dossier the IUCLID was used. All data have been checked and validated by BUA. A final evaluation of the human health part has been performed by the Federal Institute for Risk Assessment (BfR) and of the ecotoxicological part by the Federal Environment Agency (UBA). 9. Date of Submission: Deadline for circulation: 23 July 2004 10. Date of last Update: 11. Comments: OECD SIDS SODIUM DITHIONITE OECD/ICCA - The BUA* Peer Review Process Qualified BUA personnel (toxicologists, ecotoxicologists) perform a quality control on the full SIDS dossier submitted by industry.
    [Show full text]
  • Activity Characteristics of Sulfate Reducing Bacteria and Formation Mechanism of Hydrogen Sulfide - 6369
    Deng et al.: Activity characteristics of sulfate reducing bacteria and formation mechanism of hydrogen sulfide - 6369 - ACTIVITY CHARACTERISTICS OF SULFATE REDUCING BACTERIA AND FORMATION MECHANISM OF HYDROGEN SULFIDE DENG, Q.1,2,3* – WU, X.2 – WANG, Y.2 – LIU, M.1,2 1State Key Laboratory Cultivation Base for Gas Geology and Gas Control, Henan Polytechnic University, 454003 Jiaozuo, P. R. China 2School of Safety Science and Engineering, Henan Polytechnic University 454003 Jiaozuo, P. R. China 3Collaborative Innovation Center of Coal Safety Production of Henan Province 454003 Jiaozuo, P. R. China *Corresponding author e-mail: [email protected]; phone: +86-391-398-6252; fax: +81-391-398-7881 (Received 31st May 2018; accepted 13th Sep 2018) Abstract. Various anaerobic environments exist in the Earth’s ecosystem, which can produce a great deal of organic matter each year. In anaerobic habitats, bacterial sulfate reduction may occur due to the action of sulfate-reducing bacteria. As a result, hydrogen sulfide (H2S) is formed. This paper focuses on sulfate- reducing bacteria and the revision of the activity characteristics of these bacteria in the reducing environment. It discusses the metabolic process of sulfate-reducing bacteria using sulphate and organo- sulfur compounds as sulfur source, the mechanism of bacterial sulfate reduction and H2S formation mechanism. There are two main ways of H2S formation in sulfate-reducing bacteria, the production of metabolic sulphate and the metabolic organo-sulfur compounds (mainly cysteine). The paper, combined with the activity characteristics of sulfate-reducing bacteria and the pathway of metabolic formation of H2S, also discusses the circulation of sulfur in the environmental system of the Earth due to the action of sulfate-reducing bacteria, concerning the redox zone division in submarine sedimentary strata and landfills, the biogas formation phase of sulfate-reducing bacteria metabolism in sedimentary formations, and the bacterial sulfate reduction action in salt lakes (seawater) systems.
    [Show full text]
  • James Okstate 0664D 13483.Pdf (6.398Mb)
    THE ELUCIDATION AND QUANTIFICATION OF THE DECOMPOSITION PRODUCTS OF SODIUM DITHIONITE AND THE DETECTION OF PEROXIDE VAPORS WITH THIN FILMS By TRAVIS HOUSTON JAMES Bachelor of Science in Chemistry Hillsdale College Hillsdale, MI 2009 Submitted to the Faculty of the Graduate College of the Oklahoma State University in partial fulfillment of the requirements for the Degree of DOCTOR OF PHILOSOPHY July, 2014 THE ELUCIDATION AND QUANTIFICATION OF THE DECOMPOSOTION PRODUCTS OF SODIUM DITHIONITE AND THE DETECTION OF PEROXIDE VAPORS WITH THIN FILMS Dissertation Approved: Dr. Nicholas F. Materer Dissertation Advisor Dr. Allen Apblett Dr. Frank Blum Dr. Richard Bunce Dr. Ziad El-Rassi Dr. Tyler Ley ii ACKNOWLEDGEMENTS I would like to thank anyone who, whether I am aware of his or her actions or not, has contributed meaningfully to my life and my efforts. iii Acknowledgements reflect the views of the author and are not endorsed by committee members or Oklahoma State University. Name: TRAVIS HOUSTON JAMES Date of Degree: JULY, 2014 Title of Study: THE ELUCIDATION AND QUANTIFICATION OF THE DECOMPOSOTION PRODUCTS OF SODIUM DITHIONITE AND THE DETECTION OF PEROXIDE VAPORS WITH THIN FILMS Major Field: CHEMISTRY Abstract: Sodium dithionite (Na2S2O4) is an oxidizable sulfur oxyanion often employed as a reducing agent in environmental and synthetic chemistry. When exposed to the atmosphere, dithionite degrades through a series of decomposition reactions to form a 2- number of compounds, with the primary two being bisulfite (HSO3 ) and thiosulfate 2- (S2O3 ). Ten samples of sodium dithionite ranging from brand new to nearly fifty years old were analyzed using ion chromatography; from this, a new quantification method for dithionite and thiosulfate was achieved and statistically validated against the current three iodometric titration method used industrially.
    [Show full text]
  • Composition for Producing Ferrous Dithionite and Process for Removing
    ~™ II 1 1 III II II I III 1 1 Ml II I II I II (19) J European Patent Office Office europeen des brevets (1 1 ) EP 0 508 676 B1 (12) EUROPEAN PATENT SPECIFICATION (45) Date of publication and mention (51) int. CI.6: C01B 17/66, C01G 49/00, of the grant of the patent: C02F 1/62 30.07.1997 Bulletin 1997/31 (21) Application number: 92302883.1 (22) Date of filing: 02.04.1992 (54) Composition for producing ferrous dithionite and process for removing dissolved heavy metals from water Zusammensetzung zur Herstellung von Eisen-Dithionit und Verfahren zur Entfernung von in Wasser geldsten Schwermetallen Composition pour preparer du dithionite ferreux et procede pour eliminer des metaux lourds dissous dans I'eau (84) Designated Contracting States: (74) Representative: Blake, John Henry Francis et al AT BE CH DE FR GB IT LI NL SE Brookes & Martin High Holborn House (30) Priority: 08.04.1991 US 682129 52/54 High Holborn London WC1V6SE(GB) (43) Date of publication of application: 14.10.1992 Bulletin 1992/42 (56) References cited: DD-A- 2 001 630 DE-A-2122 415 (73) Proprietor: ROMAR TECHNOLOGIES DE-A- 3 822 922 INCORPORATED Beverly, Massachusetts (US) • DATABASE WPI, no. 78-54 661, DERWENT PUBLICATIONS LTD., London, GB (72) Inventor: Guess, Robert G. Beverly, Massachusetts (US) CO CO CO o Note: Within nine months from the publication of the mention of the grant of the European patent, give LO any person may notice to the European Patent Office of opposition to the European patent granted.
    [Show full text]
  • Dyeing Reagents for Thin-Layer and Paper Chromatography
    Spraying: Dry the chromatogram to remove the solvent, then cool. Place it vertically Dyeing Reagents for Thin-Layer and Paper into a spraying box or into a fume cupboard and protect the surroundings by covering Chromatography with filter paper or the like. Apply the spray solution from about 30 cm until the layer is evenly wetted but not for so long that the chromatogram begins to run with liquid. In most cases the chromatogram is specially treated at this stage. For details please refer to the directions quoted for the particular reagent concerned. Unless otherwise stated, Contents subsequent treatment should be taken as meaning drying at room temperature. • Introduction Dipping: In case of quantitative evaluation dipping of the chromatogram into the staining solution is becoming ever more usual with respect to precision and • Index of compounds and compound classes and appropriate detection repeatability. In general less concentrated reagent solutions prepared with less polar reagents solvents are common for dipping purposes. Care should be taken in the choice of • Reagents in alphabetical order solvent to ensure that neither the chromatographically separated substances nor their reaction products are soluble in the solvent of the dipping reagent. Introduction Ready-to-use Spray Solutions Merck sells a number of ready-to-use spray solutions in 100 ml glass bottles which can The first collection of instructions for the preparation of staining reagents was directly be connected to the rechargeable electro-pneumatically operated TLC sprayer published by K.G. Krebs, D. Heusser, and H. Wimmer in Egon Stahl’s "Handbook of (Ord. No. 1.08540): Thin-Layer Chromatography" in the sixties and lateron in a revised form repeatedly as a brochure by E.
    [Show full text]