Evaluation of Duopath Legionella Kit for the Rapid Identification Of
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The Role of Earthworm Gut-Associated Microorganisms in the Fate of Prions in Soil
THE ROLE OF EARTHWORM GUT-ASSOCIATED MICROORGANISMS IN THE FATE OF PRIONS IN SOIL Von der Fakultät für Lebenswissenschaften der Technischen Universität Carolo-Wilhelmina zu Braunschweig zur Erlangung des Grades eines Doktors der Naturwissenschaften (Dr. rer. nat.) genehmigte D i s s e r t a t i o n von Taras Jur’evič Nechitaylo aus Krasnodar, Russland 2 Acknowledgement I would like to thank Prof. Dr. Kenneth N. Timmis for his guidance in the work and help. I thank Peter N. Golyshin for patience and strong support on this way. Many thanks to my other colleagues, which also taught me and made the life in the lab and studies easy: Manuel Ferrer, Alex Neef, Angelika Arnscheidt, Olga Golyshina, Tanja Chernikova, Christoph Gertler, Agnes Waliczek, Britta Scheithauer, Julia Sabirova, Oleg Kotsurbenko, and other wonderful labmates. I am also grateful to Michail Yakimov and Vitor Martins dos Santos for useful discussions and suggestions. I am very obliged to my family: my parents and my brother, my parents on low and of course to my wife, which made all of their best to support me. 3 Summary.....................................................………………………………………………... 5 1. Introduction...........................................................................................................……... 7 Prion diseases: early hypotheses...………...………………..........…......…......……….. 7 The basics of the prion concept………………………………………………….……... 8 Putative prion dissemination pathways………………………………………….……... 10 Earthworms: a putative factor of the dissemination of TSE infectivity in soil?.………. 11 Objectives of the study…………………………………………………………………. 16 2. Materials and Methods.............................…......................................................……….. 17 2.1 Sampling and general experimental design..................................................………. 17 2.2 Fluorescence in situ Hybridization (FISH)………..……………………….………. 18 2.2.1 FISH with soil, intestine, and casts samples…………………………….……... 18 Isolation of cells from environmental samples…………………………….………. -
NCTC) Bacterial Strain Equivalents to American Type Culture Collection (ATCC) Bacterial Strains
This list shows National Collection of Type Cultures (NCTC) bacterial strain equivalents to American Type Culture Collection (ATCC) bacterial strains. NCTC Number CurrentName ATCC Number NCTC 7212 Acetobacter pasteurianus ATCC 23761 NCTC 10138 Acholeplasma axanthum ATCC 25176 NCTC 10171 Acholeplasma equifetale ATCC 29724 NCTC 10128 Acholeplasma granularum ATCC 19168 NCTC 10172 Acholeplasma hippikon ATCC 29725 NCTC 10116 Acholeplasma laidlawii ATCC 23206 NCTC 10134 Acholeplasma modicum ATCC 29102 NCTC 10188 Acholeplasma morum ATCC 33211 NCTC 10150 Acholeplasma oculi ATCC 27350 NCTC 10198 Acholeplasma parvum ATCC 29892 NCTC 8582 Achromobacter denitrificans ATCC 15173 NCTC 10309 Achromobacter metalcaligenes ATCC 17910 NCTC 10807 Achromobacter xylosoxidans subsp. xylosoxidans ATCC 27061 NCTC 10808 Achromobacter xylosoxidans subsp. xylosoxidans ATCC 17062 NCTC 10809 Achromobacter xylosoxidans subsp. xylosoxidans ATCC 27063 NCTC 12156 Acinetobacter baumannii ATCC 19606 NCTC 10303 Acinetobacter baumannii ATCC 17904 NCTC 7844 Acinetobacter calcoaceticus ATCC 15308 NCTC 12983 Acinetobacter calcoaceticus ATCC 23055 NCTC 8102 acinetobacter dna group 13 ATCC 17903 NCTC 10304 Acinetobacter genospecies 13 ATCC 17905 NCTC 10306 Acinetobacter haemolyticus ATCC 17907 NCTC 10305 Acinetobacter haemolyticus subsp haemolyticus ATCC 17906 NCTC 10308 Acinetobacter johnsonii ATCC 17909 NCTC 10307 Acinetobacter junii ATCC 17908 NCTC 5866 Acinetobacter lwoffii ATCC 15309 NCTC 12870 Actinobacillus delphinicola ATCC 700179 NCTC 8529 Actinobacillus equuli ATCC 19392 -
The Risk to Human Health from Free-Living Amoebae Interaction with Legionella in Drinking and Recycled Water Systems
THE RISK TO HUMAN HEALTH FROM FREE-LIVING AMOEBAE INTERACTION WITH LEGIONELLA IN DRINKING AND RECYCLED WATER SYSTEMS Dissertation submitted by JACQUELINE MARIE THOMAS BACHELOR OF SCIENCE (HONOURS) AND BACHELOR OF ARTS, UNSW In partial fulfillment of the requirements for the award of DOCTOR OF PHILOSOPHY in ENVIRONMENTAL ENGINEERING SCHOOL OF CIVIL AND ENVIRONMENTAL ENGINEERING FACULTY OF ENGINEERING MAY 2012 SUPERVISORS Professor Nicholas Ashbolt Office of Research and Development United States Environmental Protection Agency Cincinnati, Ohio USA and School of Civil and Environmental Engineering Faculty of Engineering The University of New South Wales Sydney, Australia Professor Richard Stuetz School of Civil and Environmental Engineering Faculty of Engineering The University of New South Wales Sydney, Australia Doctor Torsten Thomas School of Biotechnology and Biomolecular Sciences Faculty of Science The University of New South Wales Sydney, Australia ORIGINALITY STATEMENT '1 hereby declare that this submission is my own work and to the best of my knowledge it contains no materials previously published or written by another person, or substantial proportions of material which have been accepted for the award of any other degree or diploma at UNSW or any other educational institution, except where due acknowledgement is made in the thesis. Any contribution made to the research by others, with whom 1 have worked at UNSW or elsewhere, is explicitly acknowledged in the thesis. I also declare that the intellectual content of this thesis is the product of my own work, except to the extent that assistance from others in the project's design and conception or in style, presentation and linguistic expression is acknowledged.' Signed ~ ............................ -
WO 2016/188962 Al 1 December 2016 (01.12.2016) P O P C T
(12) INTERNATIONAL APPLICATION PUBLISHED UNDER THE PATENT COOPERATION TREATY (PCT) (19) World Intellectual Property Organization International Bureau (10) International Publication Number (43) International Publication Date WO 2016/188962 Al 1 December 2016 (01.12.2016) P O P C T (51) International Patent Classification: (74) Agents: GOODFELLOW, Hugh Robin et al; Carpmaels C12Q 1/68 (2006.01) & Ransford LLP, One Southampton Row, London WC1B 5HA (GB). (21) International Application Number: PCT/EP2016/061599 (81) Designated States (unless otherwise indicated, for every kind of national protection available): AE, AG, AL, AM, (22) Date: International Filing AO, AT, AU, AZ, BA, BB, BG, BH, BN, BR, BW, BY, 23 May 20 16 (23.05.2016) BZ, CA, CH, CL, CN, CO, CR, CU, CZ, DE, DK, DM, (25) Filing Language: English DO, DZ, EC, EE, EG, ES, FI, GB, GD, GE, GH, GM, GT, HN, HR, HU, ID, IL, IN, IR, IS, JP, KE, KG, KN, KP, KR, (26) Publication Language: English KZ, LA, LC, LK, LR, LS, LU, LY, MA, MD, ME, MG, (30) Priority Data: MK, MN, MW, MX, MY, MZ, NA, NG, NI, NO, NZ, OM, 1508860.2 22 May 2015 (22.05.2015) GB PA, PE, PG, PH, PL, PT, QA, RO, RS, RU, RW, SA, SC, SD, SE, SG, SK, SL, SM, ST, SV, SY, TH, TJ, TM, TN, (71) Applicant: NATIONAL UNIVERSITY OF IRELAND, TR, TT, TZ, UA, UG, US, UZ, VC, VN, ZA, ZM, ZW. GALWAY [IE/IE]; University Road, Galway (IE). (84) Designated States (unless otherwise indicated, for every (72) Inventors: REDDINGTON, Kate Mary; Deerpack East, kind of regional protection available): ARIPO (BW, GH, Newport Road, Westport, Co. -
Aquascreen® Legionella Species Qpcr Detection Kit
AquaScreen® Legionella species qPCR Detection Kit INSTRUCTIONS FOR USE FOR USE IN RESEARCH AND QUALITY CONTROL Symbols Lot No. Cat. No. Expiry date Storage temperature Number of reactions Manufacturer INDICATION The AquaScreen® Legionella species qPCR Detection kit is specifically designed for the quantitative detection of several Legionella species in water samples prepared with the AquaScreen® FastExt- ract kit. Its design complies with the requirements of AFNOR T90-471 and ISO/TS 12869:2012. Legionella are ubiquitous bacteria in surface water and moist soil, where they parasitize protozoa. The optimal growth temperature lies between +15 and +45 °C, whereas these gram-negative bacteria are dormant below 20 °C and do not survive above 60 °C. Importantly, Legionella are well-known as opportunistic intracellular human pathogens causing Legionnaires’ disease and Pontiac fever. The transmission occurs through inhalation of contami- nated aerosols generated by an infected source (e.g. human-made water systems like shower- heads, sink faucets, heaters, cooling towers, and many more). In order to efficiently prevent Legionella outbreaks, water safety control measures need syste- matic application but also reliable validation by fast Legionella testing. TEST PRINCIPLE The AquaScreen® Legionella species Kit uses qPCR for quantitative detection of legionella in wa- ter samples. In contrast to more time-consuming culture-based methods, AquaScreen® assays need less than six hours including sample preparation and qPCR to reliably detect Legionella. Moreover, the AquaScreen® qPCR assay has proven excellent performance in terms of specificity and sensitivity: other bacterial genera remain undetected whereas linear quantification is obtai- ned up to 1 x 106 particles per sample, therefore requiring no material dilution. -
Detection of Legionella Pneumophila in Water and Biofilm Samples by Culture and Molecular Methods from Man-Made Systems in São Paulo - Brazil
Brazilian Journal of Microbiology (2007) 38:743-751 ISSN 1517-8382 DETECTION OF LEGIONELLA PNEUMOPHILA IN WATER AND BIOFILM SAMPLES BY CULTURE AND MOLECULAR METHODS FROM MAN-MADE SYSTEMS IN SÃO PAULO - BRAZIL Fábio R. S. Carvalho; Annette S. Foronda; Vivian H. Pellizari* Laboratório de Microbiologia Ambiental, Departamento de Microbiologia, Instituto de Ciências Biomédicas, Universidade de São Paulo, São Paulo, SP, Brasil. Submitted: January 09, 2007; Returned to authors for corrections: March 30, 2007; Approved: September 20, 2007. ABSTRACT Legionella pneumophila is a pathogenic bacteria associated to aquatic habitat of natural and artificial environments. Clinical cases of legionellosis have been reported in Brazil but there is a lack of information about the incidence and concentration of this bacterium in environmental sources. Thus, the present study was designed to evaluate the occurrence of legionellae in São Paulo city, Brazil, using different methods of detection and identification. Sixty-seven water and biofilm samples from natural reservoirs and man-made systems were collected and analyzed for the presence of Legionella spp by culturing onto a selective medium, coculture in axenic free-living amoebae and direct fluorescent antibody (DFA) assay. Results showed that freshwater of reservoirs did not contain legionellae, Legionella pneumophila was isolated from man-made systems, with predominance of Legionella pneumophila serogroup 1 strains. Although there was no statistical difference among the proposed detection methods, the plate culture method yielded a higher number of L. pneumophila positive samples, followed by amoebic coculture procedure and direct fluorescent antibody assay. Results of PCR and sequencing reactions revealed that application of macrophage infectivity potentiator gene as a molecular marker was an important tool for the identification of environmental isolates of L. -
Legionella and Non-Tuberculous Mycobacteria Using MALDI TOF MS (Matrix Assisted Laser Desorption Ionisation Time of Flight Mass Spectrometry)
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by OTHES DIPLOMARBEIT Titel der Diplomarbeit Establishment of a reference database for Acanthamoeba, Legionella and non-tuberculous mycobacteria using MALDI TOF MS (Matrix Assisted Laser Desorption Ionisation Time of Flight Mass Spectrometry) Verfasserin Dzenita HASANACEVIC angestrebter akademischer Grad Magistra der Naturwissenschaften (Mag.rer.nat.) Wien, 2012 Studienkennzahl lt. A 442 Studienblatt: Studienrichtung lt. Studienblatt: Anthropologie Betreuerin: Ass. Prof. Univ. Doz. Mag. Dr. Julia Walochnik Contents 1 ABBREVIATIONS ..................................................................................................... 5 2 INTRODUCTION ....................................................................................................... 6 2.1 Acanthamoeba .................................................................................................... 6 2.1.1 Classification ................................................................................................ 6 2.1.1.1 Phylogeny of Acanthamoeba ................................................................. 6 2.1.1.2 Methods of classification ....................................................................... 8 2.1.2 Ecology and geographical distribution ........................................................ 11 2.1.2.1 Life cycle ............................................................................................. 11 2.1.2.2 Trophozoites ...................................................................................... -
Methods Development for Unregulated Contaminants in Drinking Water
Method Development for Unregulated Contaminants in Drinking Water: Public Meeting and Webinar Held June 6, 2018 USEPA, Office of Ground Water and Drinking Water Office of Water (MLK 140) EPA 815-A-18-001 June 2018 Methods Development for Unregulated Contaminants in Drinking Water Methods Development for Unregulated Contaminants in Drinking Water Public Meeting and Webinar June 6, 2018 9:00 a.m. ‐ 3:00 p.m. ET U.S. EPA Office of Water and Office of Research and Development Welcome & SDWA Regulatory Process Brenda Parris, U.S. EPA Office of Ground Water and Drinking Water Technical Support Center Page 1 of 103 Methods Development for Unregulated Contaminants in Drinking Water Participating by Webinar • Listen‐only mode Figure 1 • Click on “+” next to “Questions” in the control panel (Figure 1) to submit questions/comments Figure 2 • Type a question in the box; click send (Figure 2) • Submit questions as soon as possible • Questions will be answered at the end of the presentations June 2018 U.S. Environmental Protection Agency Slide 3 of 206 Agenda 8:30‐9:00 Stakeholder Sign‐In Welcome & SDWA Regulatory Process Overview of Method Development EPA Method 542 EPA Methods 524.2/524.3/524.4 and 525.3 EPA Method 556.1 ~10:15‐10:30 Break EPA Method 540 & 543 EPA Methods 537 & 538 Method in Development: PFAS Method in Development 558: Ethyl carbamate (Urethane) and N‐Methyl‐2‐pyrrolidone Method in Development: Nonylphenols ~11:45‐12:45 Lunch Method in Development: Legionella Method in Development: Mycobacterium ~1:45‐2:00 Break 2:00‐3:00 Open Forum and Discussion Closing Remarks Page 2 of 103 Methods Development for Unregulated Contaminants in Drinking Water Overview • Regulatory background for UCMR • Safe Drinking Water Act (SDWA) authority • Relationships to: • Contaminant Candidate List (CCL) • Unregulated Contaminant Monitoring Rule (UCMR) • Regulatory Determination • Six‐Year Review June 2018 U.S. -
Appendix 1. New and Emended Taxa Described Since Publication of Volume One, Second Edition of the Systematics
188 THE REVISED ROAD MAP TO THE MANUAL Appendix 1. New and emended taxa described since publication of Volume One, Second Edition of the Systematics Acrocarpospora corrugata (Williams and Sharples 1976) Tamura et Basonyms and synonyms1 al. 2000a, 1170VP Bacillus thermodenitrificans (ex Klaushofer and Hollaus 1970) Man- Actinocorallia aurantiaca (Lavrova and Preobrazhenskaya 1975) achini et al. 2000, 1336VP Zhang et al. 2001, 381VP Blastomonas ursincola (Yurkov et al. 1997) Hiraishi et al. 2000a, VP 1117VP Actinocorallia glomerata (Itoh et al. 1996) Zhang et al. 2001, 381 Actinocorallia libanotica (Meyer 1981) Zhang et al. 2001, 381VP Cellulophaga uliginosa (ZoBell and Upham 1944) Bowman 2000, VP 1867VP Actinocorallia longicatena (Itoh et al. 1996) Zhang et al. 2001, 381 Dehalospirillum Scholz-Muramatsu et al. 2002, 1915VP (Effective Actinomadura viridilutea (Agre and Guzeva 1975) Zhang et al. VP publication: Scholz-Muramatsu et al., 1995) 2001, 381 Dehalospirillum multivorans Scholz-Muramatsu et al. 2002, 1915VP Agreia pratensis (Behrendt et al. 2002) Schumann et al. 2003, VP (Effective publication: Scholz-Muramatsu et al., 1995) 2043 Desulfotomaculum auripigmentum Newman et al. 2000, 1415VP (Ef- Alcanivorax jadensis (Bruns and Berthe-Corti 1999) Ferna´ndez- VP fective publication: Newman et al., 1997) Martı´nez et al. 2003, 337 Enterococcus porcinusVP Teixeira et al. 2001 pro synon. Enterococcus Alistipes putredinis (Weinberg et al. 1937) Rautio et al. 2003b, VP villorum Vancanneyt et al. 2001b, 1742VP De Graef et al., 2003 1701 (Effective publication: Rautio et al., 2003a) Hongia koreensis Lee et al. 2000d, 197VP Anaerococcus hydrogenalis (Ezaki et al. 1990) Ezaki et al. 2001, VP Mycobacterium bovis subsp. caprae (Aranaz et al. -
Legionella Prevalence and Risk of Legionellosis in Japanese Households
Epidemiol. Infect. (2017), 145, 1398–1408. © Cambridge University Press 2017 doi:10.1017/S0950268817000036 Legionella prevalence and risk of legionellosis in Japanese households T. KUROKI1*, Y. WATANABE1†,H.TERANISHI2,S.IZUMIYAMA3, 4 4 J. AMEMURA-MAEKAWA AND F. KURA 1 Department of Microbiology, Kanagawa Prefectural Institute of Public Health, Chigasaki, Kanagawa, Japan 2 Department of Regional Hygiene Inspection, Kanagawa Prefectural Institute of Public Health, Chigasaki, Kanagawa, Japan 3 Department of Parasitology, National Institute of Infectious Diseases, Shinjuku-ku, Tokyo, Japan 4 Department of Bacteriology I, National Institute of Infectious Diseases, Shinjuku-ku, Tokyo, Japan Received 6 September 2016; Final revision 28 December 2016; Accepted 28 December 2016; first published online 7 February 2017 SUMMARY This study determined the occurrence of legionellae in private houses for which there were no available data on aquatic environments other than the water supply system. From June 2013 to November 2014, we collected 138 water and 90 swab samples from aquatic environments in 19 houses. Legionella DNA was detected via a loop-mediated isothermal amplification assay in 66 (47·8%) water and 17 (18·9%) swab samples. High Legionella DNA detection rates were observed in water samples from washing machines and aquariums. Legionella spp. was isolated from 9 (6·5%) water and 3 (3·3%) swab samples. Legionella pneumophila SG 1 was detected from the outlet water of a bathtub spout and a bath sponge. Use of amoebic co-culture effectively increased legionellae and Legionella DNA detection rates from all sample types. A logistic regression analysis revealed that the heterotrophic plate count was significantly related to Legionella contamination. -
Legionella and Stagnation in Water Services – Awareness of Problems, Especially in a Post Covid World Presenter- Niall Phillips
South Cumbria Occupational Health & Safety Group Preventing Legionella and stagnation in water services – awareness of problems, especially in a post Covid world Presenter- Niall Phillips • Chemistry at Manchester Polytechnic • Technical Manager at Hydraclean Ltd • Worked for ABK Technical services, which then became Rentokill W&V as Laboratory Manager, looking at biocidal efficacy among other things. • Hydraclean for 29 Years. • Experienced Legionella control across Chemical, Nuclear, Manufacturing, Housing, Education, Government and Property Portfolios etc. etc. WHAT IS LEGIONELLOSIS (1.) Legionellosis Covers:- (5.) The first identified outbreak of • Legionnaires Disease (Legionella Legionnaires Disease was amongst Pneumophila (or L. Longbeachae in people who attended the Pennsylvania composts)) State convention of the American • Pontiac Fever Legion in 1976 - An “apparently” new bacterium was isolated from living • Lochgoilhead Fever (L.micdadei) specimens. (234 ill: 34 dead) (2.) It Is A Bacterium - Not A Virus (6.) Legionella is ubiquitous i.e... it is widely found in natural (3.) Legionella Pneumophila has various and man made systems. forms known as serogroups. Serogroup 1 is known to be the most virulent form. (7.) Over 58 species have been identified of which over 20 associated with disease in humans (4.) Legionella Pneumophila is known to be the species most commonly responsible for infection in humans. Species of Legionella • Legionella adelaidensis • Legionella longbeachae • Legionella anisa • Legionella lytica • Legionella -
9260 DETECTION of PATHOGENIC BACTERIA* 9260 A. Introduction
9260 DETECTION OF PATHOGENIC BACTERIA* 9260 A. Introduction 1. General Discussion cludes 11 microbes for methods development and potential fu- ture regulation.8,9 One purpose of drinking water and wastewater treatment is to Water contamination and disease transmission may result reduce the numbers of viable organisms to acceptable levels, and from conditions generated at overloaded and/or malfunctioning to remove or inactivate all pathogens capable of causing human sanitary waste disposal and potable water treatment systems. In disease. Despite the remarkable success of water treatment and addition, common outdoor recreational activities, such as swim- sanitation programs in improving public health, sporadic cases ming (including pools and hot tubs), wind surfing, and water- and point-source outbreaks of waterborne diseases continue to skiing, all place humans at risk of waterborne diseases from occur. Water and wastewater may contain a wide variety of ingestion or direct contact with contaminated water.10 Outbreaks bacteria that cause intestinal or extra-intestinal infections. Wa- of gastroenteritis, pharyngoconjunctivitis, folliculitis, otitis, and terborne pathogens enter human hosts through intact or compro- pneumonia are associated with these recreational activities. mised skin, inhalation, ingestion, aspiration, and direct contact Overcrowded parks and recreational areas contribute to the con- with the mucous membranes of the eye, ear, nose, mouth, and tamination of surface and groundwater. genitals. This section provides an introduction to bacterial agents Laboratory diagnosis of infectious disease depends on detec- responsible for diseases transmitted by drinking and recreational tion or isolation of the etiologic agent or demonstration of waters in the United States. antibody response in the patient.