Les Mutations Spontanées Du Gène Vkorc1 Chez L’Homme Et Le Rat : Réalité De La Résistance Ahmed Hodroge

Total Page:16

File Type:pdf, Size:1020Kb

Les Mutations Spontanées Du Gène Vkorc1 Chez L’Homme Et Le Rat : Réalité De La Résistance Ahmed Hodroge Les mutations spontanées du gène Vkorc1 chez l’homme et le rat : réalité de la résistance Ahmed Hodroge To cite this version: Ahmed Hodroge. Les mutations spontanées du gène Vkorc1 chez l’homme et le rat : réalité de la résis- tance. Sciences agricoles. Université Claude Bernard - Lyon I, 2011. Français. NNT : 2011LYO10281. tel-00866731 HAL Id: tel-00866731 https://tel.archives-ouvertes.fr/tel-00866731 Submitted on 27 Sep 2013 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. N° d’ordre 281-2011 Année 2011 THESE DE L‘UNIVERSITE DE LYON Délivrée par L’UNIVERSITE CLAUDE BERNARD LYON 1 ECOLE DOCTORALE EDISS Pour l’obtention du DIPLOME DE DOCTORAT (arrêté du 7 août 2006) Soutenue publiquement le 13 décembre 2011 par Ahmed HODROGE TITRE : Les mutations spontanées du gène Vkorc1 chez l’homme et le rat. Réalité de la résistance. Directeur de thèse : Pr Etienne BENOIT & Dr Virginie LATTARD JURY : Mme Virginie LATTARD Chargée de Recherche CR1 CNRS- Nancy 1 Mme Sophie RAHUEL-CLERMONT Chargée de Recherche CR 1, CNRS-Nancy 1 Mme Helene GREIGE-GERGES Professeur, Faculté des Sciences-2- Liban M Etienne BENOIT Professeur, Campus Vétérinaire UCBL1 M François MION Professeur, faculté de Médecine UCBL1 M Yves MICHELIN Professeur, Campus agronomique-Clermont M François PENIN Ingénieur de Recherche CNRS UCBL1 1 Je tiens tout d’abord à remercier les membres de ce jury à Madame le Professeur Helene GREIGE-GERGES, qui m’a fait le plaisir et l’honneur d’être rapporteur de cette thèse et à qui j’exprime ma profonde gratitude. à Madame Sophie RAHUEL-CLERMONT, qui m’a fait l’honneur de s’intéresser à mon travail et qui a accepté d’être rapporteur de cette thèse. à Monsieur le professeur Yves MICHELIN, Directeur adjoint de l'UMR Métafort, qui m’a fait l’honneur et le plaisir d’accepter d’être rapporteur de ce travail. à Monsieur le professeur François MION, pour sa précieuse participation au jury et son soutien. Je le remercie très respectueusement. à Monsieur François PENIN, qui a accepté de participer au jugement de mon travail. à Monsieur le professeur Etienne BENOIT, et Madame Virginie LATTARD, pour leur encadrement, leur enseignement, leur confiance, leurs grandes qualités scientifiques et leur humour. Ce sont eux qui m’ont donné le goût de la recherche. Je leur dis Merci. Ce travail a été réalisé au sein de « USC 1233 Mycotoxines et toxicologie Comparée des xénobiotiques, à VetAgro Sup, campus vétérinaire de Lyon » Ce travail a bénéficié du soutien financier du Ministère de l’agriculture et de la pêche, de l’Institut Nationale de la Recherche Agronomique et de VetAgro Sup A mes parents Je tiens ensuite à remercier : Etienne BENOIT, qui m’a accueilli et encadré au sein de son laboratoire me permettant de réaliser ce travail, merci d’être toujours présent Virginie LATTARD, pour sont encadrement, sa confiance, qui m’a appris beaucoup, sans elle c’était loin d’être fini. Un petit coucou à Antoine et Chloé et à la famille BENOIT. Merci évidemment à toutes les personnes de l’école vétérinaire qui ont contribué de près ou de loin à la réalisation de cette thèse, que ce soit d’un point de vue technique ou par un simple soutien. A mes amis (par ordre alphabétique) : Abdé (bro), Adrien, Aurélia, Aymeric, Benjamin (Abdel bechir), Camille, Chloé, Gary, Jérôme (Maître), Olivier. Les amis du service de Biochimie, du service d’informatique et le laboratoire de Tox, d’Alim, du R.U, aux doctorants, pour nos discussions sérieuses et surtout moins sérieuses. A mes compatriotes libanais avec qui j’ai partagé quatre ans sur Lyon et particulièrement à Zeinab, Hussein, Mohamad…. A mon cousin et sa famille. Je souhaite enfin remercier tous mes proches (Hassan, Ali, Mona, Zahra, Abass, Aziza), en particulier toutes les personnes que j’aime et qui m’aiment. Table des matières 1 INTRODUCTION GENERALE.......................................................................................... 12 2 PARTIE BIBLIOGRAPHIQUE .......................................................................................... 14 2.1 La coagulation .................................................................................................................... 14 2.1.1 Hémostase primaire ....................................................................................................................... 14 2.1.2 La coagulation plasmatique ........................................................................................................... 16 2.1.3 La Fibrinolyse ou hémostase tertiaire............................................................................................ 19 2.2 Cycle de la vitamine K et coagulation .............................................................................. 21 2.2.1 Les vitamines K ............................................................................................................................. 21 2.2.2 Cycle de la vitamine K .................................................................................................................. 31 2.3 Les anticoagulants antivitaminique K .............................................................................. 46 2.3.1 Historique des antivitamines K ..................................................................................................... 46 2.3.2 Structure et propriétés physico-chimiques des AVKs ................................................................... 47 2.3.3 Mécanismes d’action des AVKs ................................................................................................... 50 2.3.4 Métabolisme des AVKs ................................................................................................................ 51 2.3.5 Utilisation pratique des AVKs en médecine humaine ................................................................... 54 2.4 La résistance aux anticoagulants ...................................................................................... 61 2.4.1 Définition de la résistance ............................................................................................................. 61 2.4.2 Historique de la résistance aux AVKs chez les rongeurs .............................................................. 61 2.4.3 Mécanisme de la résistance aux AVKs ......................................................................................... 64 2.4.4 Réalité de la résistance chez l’homme ........................................................................................... 71 3 OBJECTIFS DE MON TRAVAIL ...................................................................................... 79 4 STRATEGIE ..................................................................................................................... 82 5 MATERIELS ET METHODES .......................................................................................... 83 5.1 Matériels ............................................................................................................................. 83 5.1.1 Réactifs de biologie cellulaire ....................................................................................................... 83 5.1.2 Réactifs biochimiques ................................................................................................................... 83 5.1.3 Réactifs de biologie moléculaire ................................................................................................... 83 5.2 Méthodes expérimentales .................................................................................................. 84 5.2.1 Etude pharmacogénétique ............................................................................................................. 84 5.2.2 Etude biochimique......................................................................................................................... 87 6 RESULTATS .................................................................................................................... 94 6.1 Validation du modèle d’expression hétérologue de l’enzyme VKORC1 ...................... 94 3 6.1.1 Objectifs ........................................................................................................................................ 94 6.1.2 Méthodes ....................................................................................................................................... 95 6.1.3 Principaux résultats ....................................................................................................................... 95 6.2 Etude de l’implication des mutations de rVKORC1 dans la résistance aux AVKs ..... 97 6.2.1 Objectifs ........................................................................................................................................ 97 6.2.2 Méthodes ....................................................................................................................................... 97 6.2.3 Principaux résultats ......................................................................................................................
Recommended publications
  • Occurrence, Elimination, and Risk of Anticoagulant Rodenticides in Wastewater and Sludge
    Occurrence, elimination, and risk of anticoagulant rodenticides in wastewater and sludge Silvia Lacorte, Cristian Gómez- Canela Department of Environmental Chemistry, IDAEA-CSIC, Jordi Girona 18-26, 08034 Barcelona Rats and super-rats Neverending story 1967 Coumachlor 1 tn rodenticides /city per campaign “It will be the LAST ONE” Rodenticides Biocides: use regulated according to EU. Used mainly as bait formulations. First generation: multiple feedings, less persistent in tissues, commensal and outdoor use. Second generation: single feeding (more toxic), more persistent in tissue, commensal use only. Toxic: vitamin K antagonists that cause mortality by blocking an animal’s ability to produce several key blood clotting factors. High oral, dermal and inhalation toxicity. Origin and fate of rodenticides Study site: Catalonia (7.5 M inhabitants) 1693 km of sewage corridor 13 fluvial tanks (70.000 m3) 130,000,000 € / 8 YEARS 32,000 km2 378,742 kg/y AI 2,077,000 € Objectives 1. To develop an analytical method to determine most widely used rodenticides in wastewater and sludge. 2. To monitor the presence of rodenticides within 9 WWTP receiving urban and agricultural waters. 3. To evaluate the risk of rodenticides using Daphnia magna as aquatic toxicological model. 4. To study the accumulation of rodenticides in sludge. Compounds studied Coumachlor* Pindone C19H15ClO4 C14H14O3 Dicoumarol Warfarin C19H12O6 C19H16O4 Coumatetralyl Ferulenol FGARs C19H16O3 C24H30O3 Acenocoumarol Chlorophacinone • Solubility C19H15NO6 C23H15ClO3 0.001-128 mg/L • pKa 3.4-6.6 Flocoumafen Bromadiolone C H F O C H BrO 33 25 3 40 30 23 4 • Log P 1.92-8.5 Brodifacoum Fluindione C H BrO 31 23 3 C15H9FO2 SGARs Difenacoum Fenindione C31H24O3 C15H10O2 1.
    [Show full text]
  • Wastewater-Borne Exposure of Limnic Fish to Anticoagulant Rodenticides
    Water Research 167 (2019) 115090 Contents lists available at ScienceDirect Water Research journal homepage: www.elsevier.com/locate/watres Wastewater-borne exposure of limnic fish to anticoagulant rodenticides * Julia Regnery a, , Pia Parrhysius a, Robert S. Schulz a, Christel Mohlenkamp€ a, Georgia Buchmeier b, Georg Reifferscheid a, Marvin Brinke a a Department of Biochemistry, Ecotoxicology, Federal Institute of Hydrology, Am Mainzer Tor 1, 56068 Koblenz, Germany b Unit Aquatic Ecotoxicology, Microbial Ecology, Bavarian Environment Agency, Demollstr. 31, 82407 Wielenbach, Germany article info abstract Article history: The recent emergence of second-generation anticoagulant rodenticides (AR) in the aquatic environment Received 18 June 2019 emphasizes the relevance and impact of aquatic exposure pathways during rodent control. Pest control Received in revised form in municipal sewer systems of urban and suburban areas is thought to be an important emission 12 September 2019 pathway for AR to reach wastewater and municipal wastewater treatment plants (WWTP), respectively. Accepted 13 September 2019 To circumstantiate that AR will enter streams via effluent discharges and bioaccumulate in aquatic or- Available online 14 September 2019 ganisms despite very low predicted environmental emissions, we conducted a retrospective biological monitoring of fish tissue samples from different WWTP fish monitoring ponds exclusively fed by Keywords: fl Bioaccumulation municipal ef uents in Bavaria, Germany. At the same time, information about rodent control in asso- Biocides ciated sewer systems was collected by telephone survey to assess relationships between sewer baiting Monitoring and rodenticide residues in fish. In addition, mussel and fish tissue samples from several Bavarian surface PBT-Substances waters with different effluent impact were analyzed to evaluate the prevalence of anticoagulants in Sewer baiting indigenous aquatic organisms.
    [Show full text]
  • Pharmacokinetics of Anticoagulant Rodenticides in Target and Non-Target Organisms Katherine Horak U.S
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln USDA National Wildlife Research Center - Staff U.S. Department of Agriculture: Animal and Plant Publications Health Inspection Service 2018 Pharmacokinetics of Anticoagulant Rodenticides in Target and Non-target Organisms Katherine Horak U.S. Department of Agriculture, [email protected] Penny M. Fisher Landcare Research Brian M. Hopkins Landcare Research Follow this and additional works at: https://digitalcommons.unl.edu/icwdm_usdanwrc Part of the Life Sciences Commons Horak, Katherine; Fisher, Penny M.; and Hopkins, Brian M., "Pharmacokinetics of Anticoagulant Rodenticides in Target and Non- target Organisms" (2018). USDA National Wildlife Research Center - Staff Publications. 2091. https://digitalcommons.unl.edu/icwdm_usdanwrc/2091 This Article is brought to you for free and open access by the U.S. Department of Agriculture: Animal and Plant Health Inspection Service at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in USDA National Wildlife Research Center - Staff ubP lications by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Chapter 4 Pharmacokinetics of Anticoagulant Rodenticides in Target and Non-target Organisms Katherine E. Horak, Penny M. Fisher, and Brian Hopkins 1 Introduction The concentration of a compound at the site of action is a determinant of its toxicity. This principle is affected by a variety of factors including the chemical properties of the compound (pKa, lipophilicity, molecular size), receptor binding affinity, route of exposure, and physiological properties of the organism. Many compounds have to undergo chemical changes, biotransformation, into more toxic or less toxic forms. Because of all of these variables, predicting toxic effects and performing risk assess- ments of compounds based solely on dose are less accurate than those that include data on absorption, distribution, metabolism (biotransformation), and excretion of the compound.
    [Show full text]
  • Some Rodenticidal Properties of Coumatetralyl
    J.Hyg.,Camb. (1969), 67, 311 311 Printed in Great Britain Some rodenticidal properties of coumatetralyl BY J. H. GREAVES AND PRISCILLA AYRES Infestation Control Laboratory, Ministry of Agriculture, Fisheries and Food, Tolworth, Surrey {Received 26 September 1968) INTRODUCTION Coumatetralyl (3-(a-tetralyl)-4-hydroxycoumarin), an anti-coagulant rodenti- cide developed by Farbenfabriken Bayer A.G., has been used extensively against rats in Germany (Schultze, 1965). Comparatively little information is available, however, concerning its rodenticidal properties. The present laboratory study was therefore undertaken to investigate the toxicity of the anti-coagulant to warfarin- resistant and warfarin-susceptible rats (Rattus norvegicus Berk.) and to compare its palatability with that of warfarin (3-(<x-acetonylbenzyl)-4-hydroxycoumarin). METHODS Wild rats, presumed not to be resistant to warfarin (NR rats) were caught in a Midlands refuse destructor and on a Surrey farm. Warfarin-resistant (WR) rats were trapped on farms in three different areas of Britain: Nottinghamshire (WR Notts), Gloucestershire (WR Glos) and the Salop-Montgomeryshire area (WR Welsh). Field investigations had shown that the rats on the Nottinghamshire and Gloucestershire farms could not be controlled with warfarin. All ten WR Glos rats used in tests with coumatetralyl had first been given, and had survived, un- restricted feeding for 6 days on 0-005 % warfarin in the laboratory and similarly all but six of the 23 WR Notts rats had first been given periods of from 3 to 6 days on warfarin. The 53 WR Welsh animals had survived either 6 days feeding on 0-005 % warfarin or a single subcutaneous injection of 200 mg./kg.
    [Show full text]
  • Heavy Rainfall Provokes Anticoagulant Rodenticides' Release from Baited
    Journal Pre-proof Heavy rainfall provokes anticoagulant rodenticides’ release from baited sewer systems and outdoor surfaces into receiving streams Julia Regnery1,*, Robert S. Schulz1, Pia Parrhysius1, Julia Bachtin1, Marvin Brinke1, Sabine Schäfer1, Georg Reifferscheid1, Anton Friesen2 1 Department of Biochemistry, Ecotoxicology, Federal Institute of Hydrology, 56068 Koblenz, Germany 2 Section IV 1.2 Biocides, German Environment Agency, 06813 Dessau-Rosslau, Germany *Corresponding author. Email: [email protected] (J. Regnery); phone: +49 261 1306 5987 Journal Pre-proof A manuscript prepared for possible publication in: Science of the Total Environment May 2020 1 Journal Pre-proof Abstract Prevalent findings of anticoagulant rodenticide (AR) residues in liver tissue of freshwater fish recently emphasized the existence of aquatic exposure pathways. Thus, a comprehensive wastewater treatment plant and surface water monitoring campaign was conducted at two urban catchments in Germany in 2018 and 2019 to investigate potential emission sources of ARs into the aquatic environment. Over several months, the occurrence and fate of all eight ARs authorized in the European Union as well as two pharmaceutical anticoagulants was monitored in a variety of aqueous, solid, and biological environmental matrices during and after widespread sewer baiting with AR-containing bait. As a result, sewer baiting in combined sewer systems, besides outdoor rodent control at the surface, was identified as a substantial contributor of these biocidal active ingredients in the aquatic environment. In conjunction with heavy or prolonged precipitation during bait application in combined sewer systems, a direct link between sewer baiting and AR residues in wastewater treatment plant influent, effluent, and the liver of freshwater fish was established.
    [Show full text]
  • Study Protocol
    Protocol 3-001 Confidential 28APRIL2017 Version 4.1 Asahi Kasei Pharma America Corporation Synopsis Title of Study: A Randomized, Double-Blind, Placebo-Controlled, Phase 3 Study to Assess the Safety and Efficacy of ART-123 in Subjects with Severe Sepsis and Coagulopathy Name of Sponsor/Company: Asahi Kasei Pharma America Corporation Name of Investigational Product: ART-123 Name of Active Ingredient: thrombomodulin alpha Objectives Primary: x To evaluate whether ART-123, when administered to subjects with bacterial infection complicated by at least one organ dysfunction and coagulopathy, can reduce mortality. x To evaluate the safety of ART-123 in this population. Secondary: x Assessment of the efficacy of ART-123 in resolution of organ dysfunction in this population. x Assessment of anti-drug antibody development in subjects with coagulopathy due to bacterial infection treated with ART-123. Study Center(s): Phase of Development: Global study, up to 350 study centers Phase 3 Study Period: Estimated time of first subject enrollment: 3Q 2012 Estimated time of last subject enrollment: 3Q 2018 Number of Subjects (planned): Approximately 800 randomized subjects. Page 2 of 116 Protocol 3-001 Confidential 28APRIL2017 Version 4.1 Asahi Kasei Pharma America Corporation Diagnosis and Main Criteria for Inclusion of Study Subjects: This study targets critically ill subjects with severe sepsis requiring the level of care that is normally associated with treatment in an intensive care unit (ICU) setting. The inclusion criteria for organ dysfunction and coagulopathy must be met within a 24 hour period. 1. Subjects must be receiving treatment in an ICU or in an acute care setting (e.g., Emergency Room, Recovery Room).
    [Show full text]
  • CHAPTER 1 General Introduction
    CHAPTER 1 General Introduction Chapter 1 1.1 General Introduction Drugs are defined as chemical substances that are used to prevent or cure diseases in humans and animals. Drugs can also act as poisons if taken in excess. For example paracetamol overdose causes coma and death. Apart from the curative effect of drugs, most of them have several unwanted biological effects known as side effects. Aspirin which is commonly used as an analgesic to relieve minor aches and pains, as an antipyretic to reduce fever and as an anti-inflammatory medication, may also cause gastric irritation and bleeding. Also many drugs, such as antibiotics, when over used develop resistance to the patients, microorganisms and virus which are intended to control by drug. Resistance occurs when a drug is no longer effective in controlling a medical condition.1 Thus, new drugs are constantly required to surmount drug resistance, for the improvement in the treatment of existing diseases, the treatment of newly identified disease, minimise the adverse side effects of existing drugs etc. Drugs are classified in number of different ways depending upon their mode of action such as antithrombotic drugs, analgesic, antianxiety, diuretics, antidepressant and antibiotics etc.2 Antithrombotic drugs are one of the most important classes of drugs which can be shortly defined as ―drugs that reduce the formation of blood clots‖. The blood coagulation, also known as haemostasis is a physiological process in which body prevents blood loss by forming stable clot at the site of injury. Clot formation is a coordinated interplay of two fundamental processes, aggregation of platelets and formation of fibrin.
    [Show full text]
  • Chemical Compatibility Storage Group
    CHEMICAL SEGREGATION Chemicals are to be segregated into 11 different categories depending on the compatibility of that chemical with other chemicals The Storage Groups are as follows: Group A – Compatible Organic Acids Group B – Compatible Pyrophoric & Water Reactive Materials Group C – Compatible Inorganic Bases Group D – Compatible Organic Acids Group E – Compatible Oxidizers including Peroxides Group F– Compatible Inorganic Acids not including Oxidizers or Combustible Group G – Not Intrinsically Reactive or Flammable or Combustible Group J* – Poison Compressed Gases Group K* – Compatible Explosive or other highly Unstable Material Group L – Non-Reactive Flammable and Combustible, including solvents Group X* – Incompatible with ALL other storage groups The following is a list of chemicals and their compatibility storage codes. This is not a complete list of chemicals, but is provided to give examples of each storage group: Storage Group A 94‐75‐7 2,4‐D (2,4‐Dichlorophenoxyacetic acid) 94‐82‐6 2,4‐DB 609-99-4 3,5-Dinitrosalicylic acid 64‐19‐7 Acetic acid (Flammable liquid @ 102°F avoid alcohols, Amines, ox agents see SDS) 631-61-8 Acetic acid, Ammonium salt (Ammonium acetate) 108-24-7 Acetic anhydride (Flammable liquid @102°F avoid alcohols see SDS) 79‐10‐7 Acrylic acid Peroxide Former 65‐85‐0 Benzoic acid 98‐07‐7 Benzotrichloride 98‐88‐4 Benzoyl chloride 107-92-6 Butyric Acid 115‐28‐6 Chlorendic acid 79‐11‐8 Chloroacetic acid 627‐11‐2 Chloroethyl chloroformate 77‐92‐9 Citric acid 5949-29-1 Citric acid monohydrate 57-00-1 Creatine 20624-25-3
    [Show full text]
  • Anticoagulant Residues in Rats and Secondary Non-Target Risk
    Anticoagulant residues in rats and secondary non-target risk DOC SCIENCE INTERNAL SERIES 188 P. Fisher, C. O’Connor, G. Wright and C.T. Eason Published by Department of Conservation PO Box 10-420 Wellington, New Zealand DOC Science Internal Series is a published record of scientific research carried out, or advice given, by Department of Conservation staff or external contractors funded by DOC. It comprises reports and short communications that are peer-reviewed. Individual contributions to the series are first released on the departmental website in pdf form. Hardcopy is printed, bound, and distributed at regular intervals. Titles are also listed in the DOC Science Publishing catalogue on the website, refer http://www.doc.govt.nz under Publications, then Science and Research. © Copyright September 2004, New Zealand Department of Conservation ISSN 1175–6519 ISBN 0–478–22607–1 In the interest of forest conservation, DOC Science Publishing supports paperless electronic publishing. When printing, recycled paper is used wherever possible. This report was prepared for publication by DOC Science Publishing, Science & Research Unit; editing by Katrina Rainey and Helen O’Leary and layout by Geoff Gregory. Publication was approved by the Manager, Science & Research Unit, Science Technology and Information Services, Department of Conservation, Wellington. CONTENTS Abstract 5 1. Introduction 6 1.1 Objectives 6 1.2 Assessing secondary non-target risk 6 2. Methods 8 2.1 Animal husbandry 8 2.2 Feeding trials and analysis of bait samples 8 2.3 Rats offered a lethal amount of bait over 4 days (Trial 1) 10 2.4 One day’s feeding ad libitum on bait (Trial 2) 11 2.5 Ad libitum feeding on a choice of bait and non-toxic pellets until death (Trial 3) 11 2.6 Analysis of tissue samples 12 2.7 Calculation and comparison of potential secondary poisoning risk 12 3.
    [Show full text]
  • Head Injury Partial Update
    Head Injury partial update Literature search strategies Appendix A: Literature search strategies Contents Introduction Search methodology Section A.1 Population search strategies A.1.1 Head injury A.1.2 General trauma A.1.3 Spinal injury Section A.2 Study filter terms A.2.1 Excluded studies designs and publication types A.2.2 Observational studies A.2.3 Patient views A.2.4 Qualitative studies A.2.5 Predictive rules A.2.6 Triage A.2.7 Economic studies A.2.8 Quality of life Section A.3 Searches for specific questions with intervention A.3.1 Direct transport to hospital A.3.2 Imaging A.3.3 Anticoagulants A.3.4 Biomarkers A.3.5 Cervical spine A.3.6 Patient information Section A.4 Economic searches A.4.1 Economic reviews A.4.2 Quality of Life in anticoagulation patients and cervical spine patients Section A.5 References Search strategies used for the Head Injury guideline are outlined below and were run in accordance with the methodology in the NICE Guidelines Manual 2009.{National Institute for Health and Clinical Excellence, 2009 NICE2009 /id} All searches were run up to 31 May 2013 unless otherwise stated. Any studies added to the databases after this date were not included unless specifically stated in the text. Where possible searches were limited to retrieve material published in English. Searches to update questions covered in the previous NICE guidance on Head injury (reference) were limited to retrieve material published since the date of the original searches for that guideline. The date limitations for each search are indicated with the searches below.
    [Show full text]
  • Acute Toxicity of Diphacinone in Northern Bobwhite Effects On
    Ecotoxicology and Environmental Safety 73 (2010) 1159–1164 Contents lists available at ScienceDirect Ecotoxicology and Environmental Safety journal homepage: www.elsevier.com/locate/ecoenv Acute toxicity of diphacinone in Northern bobwhite: Effects on survival and blood clotting Barnett A. Rattner a,n, Katherine E. Horak b, Sarah E. Warner a, John J. Johnston b a Patuxent Wildlife Research Center, U.S. Geological Survey, Department of the Interior, 10300 Baltimore Avenue, BARC East-308, Beltsville, MD 20705, USA b National Wildlife Research Center, Animal and Plant Health Inspection Service, U.S. Department of Agriculture, Ft. Collins, CO 80521, USA article info abstract Article history: The anticoagulant rodenticide diphacinone was slightly toxic (acute oral LD50 2014 mg/kg) to Northern Received 24 March 2010 bobwhite (Colinus virginianus) in a 14-day acute toxicity trial. Precise and sensitive assays of blood Received in revised form clotting (prothrombin time, Russell’s Viper venom time, and thrombin clotting time) were adapted for 28 May 2010 use in quail, and this combination of assays is recommended to measure the effects of anticoagulant Accepted 30 May 2010 rodenticides. A single oral sublethal dose of diphacinone (434 mg/kg body weight) prolonged clotting Available online 30 June 2010 time at 48 h post-dose compared to controls. At 783 mg/kg (approximate LD02), clotting time was Keywords: prolonged at both 24 and 48 h post-dose. Prolongation of in vitro clotting time reflects impaired Anticoagulant coagulation complex activity, and was detected before overt signs of toxicity were apparent at the Birds greatest dosages (2868 and 3666 mg/kg) in the acute toxicity trial.
    [Show full text]
  • Diphacinone with Cholecalciferol for Controlling Possums and Ship Rats
    NEW ZEALAND JOURNAL OF ZOOLOGY https://doi.org/10.1080/03014223.2019.1657473 RESEARCH ARTICLE Diphacinone with cholecalciferol for controlling possums and ship rats Charles Easona,b, Lee Shapirob,c, Candida Easonc, Duncan MacMorranc and James Ross b aCawthron Institute, Nelson, New Zealand; bCentre for Wildlife Management and Conservation, Lincoln University, Lincoln, Canterbury, New Zealand; cConnovation Ltd., Manukau, New Zealand ABSTRACT ARTICLE HISTORY Potent second-generation anticoagulant rodenticides such as Received 17 May 2019 brodifacoum have been used as more effective alternatives to Accepted 14 August 2019 first-generation anticoagulants, such as warfarin. A combination of HANDLING EDITOR diphacinone at 0.005% and cholecalciferol at 0.06% produces a Chris Jones slow-acting bait that is effective at killing possums (Trichosurus vulpecula) and rodents. Cage trials with groups of possums and KEYWORDS ship rats (Rattus rattus) achieved a mortality of 87% and 86% for Cholecalciferol; combination; possums and ship rats, respectively. Two field trials, each 200 diphacinone; Rattus rattus; hectares in size, targeting possums, ship rats and mice achieved toxicology; Trichosurus an average reduction in the abundance of 94% for possums, 94% vulpecula; vertebrate for ship rats and 80% for mice. The combination of diphacinone pesticide and cholecalciferol appears effective and has a favourable risk profile compared with second-generation anticoagulant rodenticides, such as brodifacoum. Approval of this new bait by the New Zealand Environmental Protection Agency was granted in 2018 and final registration obtained from the Ministry of Primary Industries in 2019. Introduction Prior to 1950 all vertebrate pesticides used worldwide were non-anticoagulants, most of them acute or quick acting, but after the introduction of warfarin and the other anticoagu- lants, the importance of these non-anticoagulants was somewhat reduced, at least for rodent control (Eason et al.
    [Show full text]