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“Baits and Baiting Strategies for Multi-Species Pest Control and Feral
Baits and baiting strategies for multi-species pest control and feral cats SCIENCE FOR CONSERVATION: 40 D.R. Morgan, J. Innes, C. Ryan, L. Meikle Published by Department of Conservation P.O. Box 10-420 Wellington, New Zealand 1 Science for Conservation presents the results of investigations contracted to science providers outside the Department of Conservation. Reports are subject to peer review within the Department and, in some instances, to a review from outside both the Department and the science providers. November 1996, Department of Conservation ISSN 1173-2946 ISBN 0-478-01855-X This publication originated from work done under Department of Conservation contract 1748 carried out by D.R. Morgan, J. Innes and C. Ryan, Manaaki Whenua – Landcare Research, P.O. Box 69, Lincoln; and contract 617, carried out by D.R. Morgan and L. Meikle, Manaaki Whenua – Landcare Research, P.O. box 31-011, Christchurch. It was approved for publication by the Director, Science and Research Division, Department of Conservation, Wellington. Cataloguing-in-Publication data Baits and baiting strategies for multi-species pest control and feral cats / D.R. Morgan ... {et al.} Wellington, N.Z. : Dept. of Conservation, 1996. 1 v. ; 30 cm. (Science for conservation, 1173-2946 ; 40.) Includes bibliographical references. ISBN 047801855X 1. Pests- -Control- -New Zealand. I. Morgan, D.R. (David Rowland), 1950- II. Series: Science for conservation (Wellington, N.Z.) ; 40. 632.9510993 20 zbn96-124202 2 CONTENTS PART 1: DEVELOPMENT OF MULTI-SPECIES BAITING (D.R. Morgan, J. Innes, C. Ryan) Abstract 5 1. Introduction 5 2. Background 6 3. Objectives 6 4. -
Photoreactivity of Coumaryl Compounds Toward Dna
PHOTOREACTIVITY OF COUMARYL COMPOUNDS TOWARD DNA PYRIMIDINE BASES by DYNA KERNS McINTURFF, B.S. A THESIS IN CHEMISTRY Submitted to the Graduate Faculty of Texas Tech University in Partial Fulfillment of the Requirements for the Degree of MASTER OF SCIENCE Approved Accepted December, 1975 Hf<D I : u: It ACKNOWLEDGMENTS I am indebted to Professor Pill-Soon Song for his direction of this thesis and to the other members of my committee. Professors John A. Anderson and Ira C. Felkner, for their helpful criticism. I am also appreciative of early encouragement by Dr. W. J. Kerns and technical assistance by Dr. W. W. Mantulin. ii CONTENTS ACKNOWLEDGMENTS ii LIST OF TABLES iv LIST OF ILLUSTRATIONS v I. INTRODUCTION 1 Purpose and Scope of the Thesis 1 Review of the Literature 2 II. MATERIALS AND METHODS 15 Materials 15 Methods 16 III. RESULTS AND DISCUSSION 18 Results 18 Discussion 24 IV. CONCLUSIONS 30 REFERENCES 31 APPENDIX 34 11 LIST OF TABLES Table Page 1. Relative rates of the photoreaction between photosensitizers and 2 to 4 x 10~^M pyrimidine bases 20 2. Relative rates of the photoreaction between photosensitizers and 2 to 4 x 10 M pyrimidine bases 21 3. Effect of oxygen quenching on the photoreactions between photosensitizers and 2 to 4 x 10~^M pyrimidine bases 22 4. Relative rates of the photoreactions of the 5-methoxypsoralen, 5-hydroxypsoralen and 8-hydroxypsoralen systems studied. All pyrimidine bases are 2 to 4 x 10" M 23 IV LIST OF ILLUSTRATIONS 1. Structural formulas of coumarin, 8-methoxypsoralen, and benzodipyrones 8 2. -
Low Molecular Weight Heparin Versus Acenocoumarol in the Secondary Prophylaxis of Deep Vein Thrombosis
Thromb Haemost 1999; 81: 26–31 © 1999 Schattauer Verlag, Stuttgart Low Molecular Weight Heparin versus Acenocoumarol in the Secondary Prophylaxis of Deep Vein Thrombosis S. Lopaciuk, H. Bielska-Falda1, W. Noszczyk1, M. Bielawiec 2, W. Witkiewicz 3, S. Filipecki 4, J. Michalak 5, L. Ciesielski 6, Z. Mackiewicz 7, E. Czestochowska 8, K. Zawilska 9, A. Cencora 10, among others* From the Institute of Hematology and Blood Transfusion, Warsaw, 1st 1Department of Surgery, Medical School, Warsaw, 2Department of Hematology, Medical School, Bialystok, 3Department of Vascular Surgery, District General Hospital, Wroclaw, 4Department of Internal Medicine, Institute of Tuberculosis and Lung Diseases, Warsaw, 5Department of Vascular Surgery, Medical School, Lublin, 1st 6Department of Surgery, Medical School, Lodz, 7Department of Vascular Surgery, Medical School, Bydgoszcz, 3rd 8Department of Internal Medicine, Medical School, Gdansk, 9Department of Hematology, Medical School, Poznan, and 10Department of Vascular Surgery, District General Hospital, Krakow, Poland Summary oral anticoagulant for at least 3 months (secondary prophylaxis). Al- though long-term anticoagulation with coumarin drugs, the most popu- The aim of this study was to determine the efficacy and safety of lar of which are warfarin and acenocoumarol, has been repeatedly dem- subcutaneous weight-adjusted dose low molecular weight heparin onstrated effective in the prevention of recurrent venous thromboembo- (LMWH) compared with oral anticoagulant (OA) in the prevention of lism, it suffers from a number of limitations. This treatment requires recurrent venous thromboembolism. In a prospective multicenter trial, strict laboratory control and consequent adjustments of the drug dosage 202 patients with symptomatic proximal deep vein thrombosis (DVT) and carries a substantial risk of bleeding complications (1). -
The Persistence and Secondary Poisoning Risks of Sodium Monofluoroacetate (1080), Brodifacoum, and Cholecalciferol in Possums
THE PERSISTENCE AND SECONDARY POISONING RISKS OF SODIUM MONOFLUOROACETATE (1080), BRODIFACOUM, AND CHOLECALCIFEROL IN POSSUMS C. T. EASON, G. R. WRIGHT, and L. MEIKLE, Manaaki Whenua - Landcare Research, P.O. Box 69, Lincoln, New Zealand. P. ELDER, Steroid and Immunobiochemistry Unit, Christchurch Health Laboratories, Christchurch Hospital, P.O. Box 151, Christchurch, New Zealand. ABSTRACT: To determine the risk of secondary poisoning for animals preying on sub-lethally poisoned brushtail possums, captive possums were treated with near-lethal doses of sodium monofluoroacetate (1080) or brodifacoum, and toxicant concentrations in blood and tissue were monitored over time. Sodium monofluoroacetate was rapidly eliminated from the blood (within three days). Brodifacoum was retained in the liver and, to a lesser extent, the muscle of possums for eight months after dosing. To determine the potential risk for animals scavenging on the carcasses of possums poisoned with cholecalciferol, cats were fed poisoned carcasses for six days. No changes in behavior, appetite, or body weight were observed. Serum calcium concentrations increased slightly, but remained within the normal range for cats. KEY WORDS: vertebrate pest control, secondary poisoning, sodium monofluoroacetate, brodifacown, cholecalciferol Proc. 17th Yertebr. Pest Conf. (R.M. Timm & A.C. Crabb, Eds.) Published at Univ. of Calif., Davis. 1996. INTRODUCTION 1995), and toxic amounts of brodifacoum may be retained Sodium monofluoroacetate (1080) has been used for in a carcass. vertebrate pest control in New Zealand since 1954. It is The existence of an effective antidote to brodifacoum currently used most frequently in aerially sown baits and in the form of vitamin Kl means that dogs that have eaten in baits in bait stations for the control of the Australian carcasses containing brodifacoum residues can usually be brushtail possum (Trichosurus vulpecula) (Livingstone saved. -
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. -
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. -
STUDY PROTOCOL Study Information Title Apixaban Drug
Apixaban B0661076NON-INTERVENTIONAL STUDY PROTOCOL Final, 15-Feb-2016 NON-INTERVENTIONAL (NI) STUDY PROTOCOL Study information Title Apixaban drug utilization study in Stroke prevention in atrial fibrillation (SPAF) Protocol number B0661076 AEMPS Code PFI-API-2016-01 Protocol version identifier 4.0 Date of last version of protocol 15-Feb-2016 Active substance Apixaban B01AF02 Medicinal product Eliquis® Research question and objectives Evaluate the apixaban utilization according to the approved SPAF indication and recommendations by EMA. The study objectives are: Objective 1: To characterise patients using apixaban according to demographics, comorbidity, risk of thromboembolic events (CHADS2 and CHA2DS2-Vasc scores), risk of bleeding events (HAS-BLED score), comedications and compare it with the profile of patients treated with VKA, dabigatran and rivaroxaban. Objective 2: Describe the level of appropriate usage according to the posology recommended in the apixaban SmPC. Objective 3: Describe the potential interactions with other drugs prescribed concomitantly according with the SmPC recommendations. Objective 4: Estimate the level of apixaban adherence by the medication possession ratio (MPR) and discontinuation rates and compare it with VKA, dabigatran and CT24-GSOP-RF03 NI Study Protocol Template; Version 3.0, Effective Date 10-Oct-2014 Pfizer Confidential Page 1 of 28 Apixaban B0661076NON-INTERVENTIONAL STUDY PROTOCOL Final, 15-Feb-2016 rivaroxaban cohort. Objective 5: To analyze INR (International Normalized Ratio) values during the last 12 months and to obtain TTR (Time in Therapeutic Range) values in patients previously treated with VKA and, during the whole study period for those in the cohort treated with VKA Author Ángeles Quijada Manuitt, IDIAP Jordi Gol Rosa Morros Pedrós, IDIAP Jordi Gol Jordi Cortés, IDIAP Jordi Gol José Chaves Puertas, Pfizer SLU Sponsor Pfizer S.L.U Avda. -
First Evidence of Anticoagulant Rodenticides in Fish in German
Environmental Science and Pollution Research https://doi.org/10.1007/s11356-018-1385-8 ADVANCEMENTS IN CHEMICAL METHODS FOR ENVIRONMENTAL RESEARCH First evidence of anticoagulant rodenticides in fish and suspended particulate matter: spatial and temporal distribution in German freshwater aquatic systems Matthias Kotthoff1 & Heinz Rüdel2 & Heinrich Jürling1 & Kevin Severin1 & Stephan Hennecke1 & Anton Friesen3 & Jan Koschorreck3 Received: 27 September 2017 /Accepted: 24 January 2018 # The Author(s) 2018. This article is an open access publication Abstract Anticoagulant rodenticides (ARs) have been used for decades for rodent control worldwide. Research on the exposure of the environment and accumulation of these active substances in biota has been focused on terrestrial food webs, but few data are available on the impact of ARs on aquatic systems and water organisms. To fill this gap, we analyzed liver samples of bream (Abramis brama) and co-located suspended particulate matter (SPM) from the German Environmental Specimen Bank (ESB). An appropriate method was developed for the determination of eight different ARs, including first- and second-generation ARs, in fish liver and SPM. Applying this method to bream liver samples from 17 and 18 sampling locations of the years 2011 and 2015, respectively, five ARs were found at levels above limits of quantifications (LOQs, 0.2 to 2 μgkg−1). For 2015, brodifacoum was detected in 88% of the samples with a maximum concentration of 12.5 μgkg−1. Moreover, difenacoum, bromadiolone, difethialone, and flocoumafen were detected in some samples above LOQ. In contrast, no first generation AR was detected in the ESB samples. In SPM, only bromadiolone could be detected in 56% of the samples at levels up to 9.24 μgkg−1.A temporal trend analysis of bream liver from two sampling locations over a period of up to 23 years revealed a significant trend for brodifacoum at one of the sampling locations. -
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. -
Part IV: Basic Considerations of the Psoralens
CORE Metadata, citation and similar papers at core.ac.uk Provided by Elsevier - Publisher Connector THE CHEMISTRY OF THE PSORALENS* W. L. FOWLKS, Ph.D. The psoralens belong to a group of compoundsfled since biological activity of the psoralens and which have been considered as derivatives ofangelicins has been demonstrated. They appear coumarin, the furocoumarins. There are twelveto have specific biochemical properties which different ways a furan ring can be condensed withmay contribute to the survival of certain plant the coumarin molecule and each of the resultingspecies. Specifically these compounds belong to compounds could be the parent for a family ofthat group of substances which can inhibit certain derivatives. Examples of most of these possibleplant growth without otherwise harming the furocoumarins have been synthesized; but natureplant (2, 3, 5). is more conservative so that all of the naturally It is interesting that it was this property which occurring furocoumarins so far described turnled to the isolation of the only new naturally out to be derivativesof psoralen I or angelicinoccuring furocoumarin discovered in the United II (1). States. Bennett and Bonner (2) isolated tharn- nosmin from leaves of the Desert Rue (Tham- n.osma montana) because a crude extract of this 0 0 plant was the best growth inhibitor found among /O\/8/O\/ the extracts of a number of desert plants sur- i' Ii veyed for this property, although all the extracts showed seedling growth inhibition. One could I II speculate as to the role such growth inhibition plays in the economy of those desert plants These natural derivatives of psoralen and angeli-when survival may depend upon a successful cm have one or more of the following substituentsfight for the little available water. -
Authorisation of Anticoagulant Rodenticides in Germany FAQ on Environmental Risks, Risk Mitigation Measures and Best Practice
background // december 2019 Authorisation of Anticoagulant Rodenticides in Germany FAQ on Environmental Risks, Risk Mitigation Measures and Best Practice For our environment Imprint Publisher: Image sources: German Environment Agency Front page: Fotolia/tomatito26 Section IV 1.2 Biocides Page 3: UBA/Agnes Kalle & Susanne Hein Section IV 1.4 Health Pests and their Control Page 7: Alex Yeung PO Box 14 06 Page 8: Taton Moïse/Unsplash 06813 Dessau-Roßlau Page 10: autark – Photocase Tel.: +49 340-2103-0 Page 11: UBA/Figure 1 [email protected] Page 12: Fotolia/silvioheidler/Figure A Internet: www.umweltbundesamt.de/en Page 12: Fotolia/Jolanta Mayerberg/Figure B Page 12: Fotolia/Erni/Figure C /umweltbundesamt.de Page 12: Fotolia/Hans and Crista Ede/Figure D /umweltbundesamt Page 12: Fotolia/Sergey Ryzhkov/Figure E /umweltbundesamt Page 12: Fotolia/phototrip.cz/Figure F /umweltbundesamt Page 14: Fotolia/Loveleen/Silhouette of a rat Page 17: Photocase/marsj/Mouse in building Authors: Page 17: UBA/Erik Schmolz/Bait station Juliane Fischer, Anton Friesen, Anke Geduhn, Susanne Page 17: Fotolia/SB/Rat burrow in open area Hein, Stefanie Jacob, Barbara Jahn, Agnes Kalle, Anja Page 18: Mella/Photocase Kehrer, Ingrid Nöh, Eleonora Petersohn, Caroline Page 20: Fotolia/fotocejen/Barn owl Riedhammer, Ricarda Rissel, Annika Schlötelburg, Erik Page 21: Fotolia/Stefan/Kestrel Schmolz, Beatrice Schwarz-Schulz, Christiane Stahr, Ute Page 21: Fotolia/Romuald/Stoat Trauer-Kizilelma, Kristina Wege, Stefanie Wieck Page 22: Fotolia/Valeriy Kirsanov/Red fox Page -
Sound Management of Pesticides and Diagnosis and Treatment Of
* Revision of the“IPCS - Multilevel Course on the Safe Use of Pesticides and on the Diagnosis and Treatment of Presticide Poisoning, 1994” © World Health Organization 2006 All rights reserved. The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the World Health Organization concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. Dotted lines on maps represent approximate border lines for which there may not yet be full agreement. The mention of specific companies or of certain manufacturers’ products does not imply that they are endorsed or recommended by the World Health Organization in preference to others of a similar nature that are not mentioned. Errors and omissions excepted, the names of proprietary products are distinguished by initial capital letters. All reasonable precautions have been taken by the World Health Organization to verify the information contained in this publication. However, the published material is being distributed without warranty of any kind, either expressed or implied. The responsibility for the interpretation and use of the material lies with the reader. In no event shall the World Health Organization be liable for damages arising from its use. CONTENTS Preface Acknowledgement Part I. Overview 1. Introduction 1.1 Background 1.2 Objectives 2. Overview of the resource tool 2.1 Moduledescription 2.2 Training levels 2.3 Visual aids 2.4 Informationsources 3. Using the resource tool 3.1 Introduction 3.2 Training trainers 3.2.1 Organizational aspects 3.2.2 Coordinator’s preparation 3.2.3 Selection of participants 3.2.4 Before training trainers 3.2.5 Specimen module 3.3 Trainers 3.3.1 Trainer preparation 3.3.2 Selection of participants 3.3.3 Organizational aspects 3.3.4 Before a course 4.