The Hazards of Secondary Poisoning from Zinc Phosphide to Selected Vertebrate Species
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Environmental Properties of Chemicals Volume 2
1 t ENVIRONMENTAL 1 PROTECTION Esa Nikunen . Riitta Leinonen Birgit Kemiläinen • Arto Kultamaa Environmental properties of chemicals Volume 2 1 O O O O O O O O OO O OOOOOO Ol OIOOO FINNISH ENVIRONMENT INSTITUTE • EDITA Esa Nikunen e Riitta Leinonen Birgit Kemiläinen • Arto Kultamaa Environmental properties of chemicals Volume 2 HELSINKI 1000 OlO 00000001 00000000000000000 Th/s is a second revfsed version of Environmental Properties of Chemica/s, published by VAPK-Pub/ishing and Ministry of Environment, Environmental Protection Department as Research Report 91, 1990. The pubiication is also available as a CD ROM version: EnviChem 2.0, a PC database runniny under Windows operating systems. ISBN 951-7-2967-2 (publisher) ISBN 952-7 1-0670-0 (co-publisher) ISSN 1238-8602 Layout: Pikseri Julkaisupalvelut Cover illustration: Jussi Hirvi Edita Ltd. Helsinki 2000 Environmental properties of chemicals Volume 2 _____ _____________________________________________________ Contents . VOLUME ONE 1 Contents of the report 2 Environmental properties of chemicals 3 Abbreviations and explanations 7 3.1 Ways of exposure 7 3.2 Exposed species 7 3.3 Fffects________________________________ 7 3.4 Length of exposure 7 3.5 Odour thresholds 8 3.6 Toxicity endpoints 9 3.7 Other abbreviations 9 4 Listofexposedspecies 10 4.1 Mammais 10 4.2 Plants 13 4.3 Birds 14 4.4 Insects 17 4.5 Fishes 1$ 4.6 Mollusca 22 4.7 Crustaceans 23 4.8 Algae 24 4.9 Others 25 5 References 27 Index 1 List of chemicals in alphabetical order - 169 Index II List of chemicals in CAS-number order -
Federal Law and Vertebrate Pest Control
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Proceedings of the 1st Vertebrate Pest Vertebrate Pest Conference Proceedings Conference (1962) collection February 1962 FEDERAL LAW AND VERTEBRATE PEST CONTROL Justus C. Ward Director, Pesticides Regulation Division, Agricultural Research Service, U.S. Department of Agriculture Follow this and additional works at: https://digitalcommons.unl.edu/vpcone Part of the Environmental Health and Protection Commons Ward, Justus C., "FEDERAL LAW AND VERTEBRATE PEST CONTROL" (1962). Proceedings of the 1st Vertebrate Pest Conference (1962). 25. https://digitalcommons.unl.edu/vpcone/25 This Article is brought to you for free and open access by the Vertebrate Pest Conference Proceedings collection at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Proceedings of the 1st Vertebrate Pest Conference (1962) by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. FEDERAL LAW AND VERTEBRATE PEST CONTROL By: Justus C. Ward, Director, Pesticides Regulation Division, Agricultural Research Service, U.S. Department of Agriculture Presented at the Vertebrate Pest Control Conference, Sacramento, California, February 6 and 7, 1 962 Shortly after the passage of the Federal Insecticide Act of 1910> mammal control specialists in the Bureau of Biological Survey began to consider a similar law to cover the chemicals with which they were concerned. Work on the project went slowly a nd spasmodically, but reached the point of having a Federal Rodenticide Act available for study and possible revision in 1928. At this time, the mammal control chemicals in use were limited to strychnine -- alkaloid and sulphate -arsenic, barium carbonate, th allium sulphate, phosphorus, s odium and calcium cyanide, carbon disulphide, and red squill. -
Efficacy of 3 In-Burrow Treatments to Control Black-Tailed Prairie Dogs
EFFICACY OF 3 JN-BURROW TREATMENTS TO CONTROL BLACK-TAJLED PRAIRIE DOGS CHARLES D. LEE, Department of Animal Science, Kansas State University Research and Extension, Manhattan, KS, USA JEFF LEFLORE , East Cheyenne County Pest Control, Cheyenne Wells , CO, USA Abstract: Management of prairie dog ( Cynomys ludovicianus) movement by colony expansion or dispersal may involve the use of toxicants to reduce local populations. Hazards associated with the use of toxicants cause concern for non-target species. Applying the bait in-burrow should reduce the primary exposure of the toxicants to non-target wildlife. Some literature suggests prairie dogs will not consume bait when applied in the burrow. In this trial we compared efficacy of Rozol ® (chlorophacinone), Kaput-D Prairie Dog Bait ® (diphacinone), 2% zinc phosphide oats applied in-burrow and 2% zinc phosphide oats applied on the surface. Results are reported as change in prairie dog activity. Key words: chlorophacinone , control, Cynomys ludovicianus, diphacinone, in-burrow, management , prairie dog, toxicant , zinc phosphide Proceedings of the I 2'h Wildlife Damage Management Conference (D.L. Nolte , W.M. Arjo, D.H. Stalman, Eds). 2007 INTRODUCTION This type of controversy has lead to scrutiny Control of black-tailed prame dogs of all types of control , especially the use of (Cynomys ludovicianus) is controversial on toxicants . Although there are numerous the Great Plains. Prairie dogs have been control techniques for prairie dogs, many controlled on rangeland for many years landowner s are dissatisfied with their largely with the use of toxicants applied consistency of efficacy and ease of use . above ground (Witmer and Fagerstone Most of the literature on black-tailed 2003). -
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. -
Economic Implications of Using Zinc Phosphide to Replace Endrin in Apple Orchards
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Wildlife Damage Management, Internet Center Eastern Pine and Meadow Vole Symposia for March 1977 Economic Implications of Using Zinc Phosphide To Replace Endrin in Apple Orchards Walter L. Ferguson Economic Research Service Follow this and additional works at: https://digitalcommons.unl.edu/voles Part of the Environmental Health and Protection Commons Ferguson, Walter L., "Economic Implications of Using Zinc Phosphide To Replace Endrin in Apple Orchards" (1977). Eastern Pine and Meadow Vole Symposia. 116. https://digitalcommons.unl.edu/voles/116 This Article is brought to you for free and open access by the Wildlife Damage Management, Internet Center for at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Eastern Pine and Meadow Vole Symposia by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. 33 Economic Implications of Using Zinc Phosphide To Replace Endrin in Apple Orchards 11 Walter L. Ferguson II Consideration is being given to suspend or restrict the use of endrin for controlling mice in orchards. If endrin were not available for this use, State extension and experiment station personnel in 6 Eastern States and 2 Western States estimated that apple production losses would increase from mice injury on 33,400 endrin-treated bearing acres, (12,500 acres in the Eastern States and 20,900 acres in the Western States). The 6 Eastern States include Georgia, Maryland, North Carolina, South Carolina, Virginia and West Virginia: the 2 Western States are Idaho and Washington. Estimates of production changes without endrin were made assuming zinc phosphide is the only feasible Federally registered chemical alternative to endrin. -
Step-By-Step Guide to Better Laboratory Management Practices
Step-by-Step Guide to Better Laboratory Management Practices Prepared by The Washington State Department of Ecology Hazardous Waste and Toxics Reduction Program Publication No. 97- 431 Revised January 2003 Printed on recycled paper For additional copies of this document, contact: Department of Ecology Publications Distribution Center PO Box 47600 Olympia, WA 98504-7600 (360) 407-7472 or 1 (800) 633-7585 or contact your regional office: Department of Ecology’s Regional Offices (425) 649-7000 (509) 575-2490 (509) 329-3400 (360) 407-6300 The Department of Ecology is an equal opportunity agency and does not discriminate on the basis of race, creed, color, disability, age, religion, national origin, sex, marital status, disabled veteran’s status, Vietnam Era veteran’s status or sexual orientation. If you have special accommodation needs, or require this document in an alternate format, contact the Hazardous Waste and Toxics Reduction Program at (360)407-6700 (voice) or 711 or (800) 833-6388 (TTY). Table of Contents Introduction ....................................................................................................................................iii Section 1 Laboratory Hazardous Waste Management ...........................................................1 Designating Dangerous Waste................................................................................................1 Counting Wastes .......................................................................................................................8 Treatment by Generator...........................................................................................................12 -
RRAC Guidelines on Anticoagulant Rodenticide Resistance Management Editor: Rodenticide Resistance Action Committee (RRAC) of Croplife International Aim
RRAC guidelines on Anticoagulant Rodenticide Resistance Management Editor: Rodenticide Resistance Action Committee (RRAC) of CropLife International Aim This document provides guidance to advisors, national authorities, professionals, practitioners and others on the nature of anticoagulant resistance in rodents, the identification of anticoagulant resistance, strategies for rodenticide application that will avoid the development of resistance and the management of resistance where it occurs. The Rodenticide Resistance Action Committee (RRAC) is a working group within the framework of CropLife International. Participating companies include: Bayer CropScience, BASF, LiphaTech S. A., PelGar, Rentokil Initial, Syngenta and Zapi. Senior technical specialists, with specific expertise in rodenticides, represent their companies on this committee. The RRAC is grateful to the following co-authors: Stefan Endepols, Alan Buckle, Charlie Eason, Hans-Joachim Pelz, Adrian Meyer, Philippe Berny, Kristof Baert and Colin Prescott. Photos provided by Stefan Endepols. Contents 1. Introduction ............................................................................................................................................................................................................. 2 2. Classification and history of rodenticide compounds ..............................................................................................3 3. Mode of action of anticoagulant rodenticides, resistance mechanisms, and resistance mutations ......................................................................................................6 -
Toxicological Profile for Barium and Barium Compounds
TOXICOLOGICAL PROFILE FOR BARIUM AND BARIUM COMPOUNDS U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry August 2007 BARIUM AND BARIUM COMPOUNDS ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. BARIUM AND BARIUM COMPOUNDS iii UPDATE STATEMENT A Toxicological Profile for Barium and Barium Compounds, Draft for Public Comment was released in September 2005. This edition supersedes any previously released draft or final profile. Toxicological profiles are revised and republished as necessary. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology and Environmental Medicine/Applied Toxicology Branch 1600 Clifton Road NE Mailstop F-32 Atlanta, Georgia 30333 BARIUM AND BARIUM COMPOUNDS iv This page is intentionally blank. v FOREWORD This toxicological profile is prepared in accordance with guidelines developed by the Agency for Toxic Substances and Disease Registry (ATSDR) and the Environmental Protection Agency (EPA). The original guidelines were published in the Federal Register on April 17, 1987. Each profile will be revised and republished as necessary. The ATSDR toxicological profile succinctly characterizes the toxicologic and adverse health effects information for the hazardous substance described therein. Each peer-reviewed profile identifies and reviews the key literature that describes a hazardous substance's toxicologic properties. Other pertinent literature is also presented, but is described in less detail than the key studies. The profile is not intended to be an exhaustive document; however, more comprehensive sources of specialty information are referenced. -
Secondary Poisoning of Foxes and Buzzards
Pergamon Chemosphere, Vol. 35, No. 8, pp. 1817-1829, 1997 © 1997 Elsevier Science Ltd All rights reserved. Printed in Great Britain PII: S0045-6535(97)00242-7 0045-6535197 $17.00+0.00 FIELD EVIDENCE OF SECONDARY POISONING OF FOXES (Vulpes vulpes) AND BUZZARDS (Buteo buteo) BY BROMADIOLONE, A 4-YEAR SURVEY Philippe J. Berny*, Thierry Buronfosse*, Florence Buronfosse**, Franqois Lamarque °and Guy Lorgue* * D6pt.SBFA - Laboratoire de Toxicologie - ENVL - BP-83 - 69280 Marcy l'Etoile (France) ** CNITV - ENVL - BP-83 - 69280 Marcy l'Etoile (France) ° ONC - Domaine de St Benotst - 78160 Auffargis (France) (Received in USA 17 February 1997; accepted 21 March 1997) Abstract This paper presents the result of a 4 year survey in France (1991-1994) based on the activity of a wildlife disease surveillance network (SAGIR). The purpose of this study was to evaluate the detrimental effects of anticoagulant (Ac) rodenticides in non-target wild animals. Ac poisoning accounted for a very limited number of the identified causes of death (1-3%) in most species. Predators (mainly foxes and buzzards) were potentially exposed to anticoagulant compounds (especially bromadiolone) via contaminated prey in some instances. The liver concentrations of bromadiolone residues were elevated and species-specific diagnostic values were determined. These values were quite similar to those reported in the litterature when secondary anticoagulant poisoning was experimentally assessed. ©1997 Elsevier Science Ltd Introduction This study reports anticoagulant (Ac) poisoning in wildlife. The Toxicology Laboratory of the Veterinary school in Lyon is involved in a unique nation-wide network for wildlife diseases surveillance (see material and methods). Ac poisoning is seldom described or investigated in wild animals, despite extensive use of rodenticides in the fields. -
Chemistry 1000 Lecture 13: the Alkaline Earth Metals
Chemistry 1000 Lecture 13: The alkaline earth metals Marc R. Roussel September 25, 2018 Marc R. Roussel Alkaline earth metals September 25, 2018 1 / 23 Mg{Ra Group 2: The alkaline earth metals Group 2, except maybe Be Soft metals Form M2+ cations Very negative reduction potentials: 2+ − M(aq) + 2e ! M(s) Element Be Mg Ca Sr Ba Ra E◦=V −1:847 −2:356 −2:84 −2:89 −2:92 −2:92 Relatively small 1st and 2nd ionization energies: Element Be Mg Ca Sr Ba Ra −1 I1=kJ mol 899:5 737:7 589:8 549:5 502:9 509:3 −1 I2=kJ mol 1757:1 1450:7 1145:4 1064:2 965:2 979:0 Marc R. Roussel Alkaline earth metals September 25, 2018 2 / 23 Mg{Ra Comparison to alkali metals Physical Properties: Property Na Mg Mohs hardness 0.5 2.5 Density=g cm−3 0.968 1.738 Melting point=◦C 97.72 650 Boiling point=◦C 883 1090 Chemical properties are often similar to those of the alkali metals, but less reactive: Example: Reaction with water: M(s) + 2H2O ! M(OH)2 + H2(g) =) Often has to be done in hot water or with steam Marc R. Roussel Alkaline earth metals September 25, 2018 3 / 23 Mg{Ra Why \alkaline earth" metals? The name \alkaline earth" was originally applied to the oxides of these metals. Earth is a term applied by early chemists to nonmetallic substances which are insoluble in water and remain stable when heated. The alkaline earth metal oxides have these properties. -
Rodenticidal Effects of Zinc Phosphide and Strychnine of Nontarget Species
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Great Plains Wildlife Damage Control Workshop Wildlife Damage Management, Internet Center Proceedings for April 1987 Rodenticidal Effects of Zinc Phosphide and Strychnine of Nontarget Species Daniel W. Uresk Rocky Mountain Forest and Range Experiment Station, Rapid City, South Dakota Rudy M. King Rocky Mountain Forest and Range Experiment Station, Rapid City, South Dakota Anthony D. Apa South Dakota School of Mines and Technology Michele S. Deisch South Dakota School of Mines and Technology Raymond L. Linder South Dakota Cooperative Fish and Wildlife Research Unit, South Dakota State University - Brookings Follow this and additional works at: https://digitalcommons.unl.edu/gpwdcwp Part of the Environmental Health and Protection Commons Uresk, Daniel W.; King, Rudy M.; Apa, Anthony D.; Deisch, Michele S.; and Linder, Raymond L., "Rodenticidal Effects of Zinc Phosphide and Strychnine of Nontarget Species" (1987). Great Plains Wildlife Damage Control Workshop Proceedings. 102. https://digitalcommons.unl.edu/gpwdcwp/102 This Article is brought to you for free and open access by the Wildlife Damage Management, Internet Center for at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Great Plains Wildlife Damage Control Workshop Proceedings by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Rodenticidal Effects of Zinc Phosphide and Strychnine on Nontarget Species1 Daniel W. Uresk, Rudy M. King, Anthony D. Apa, Michele S. Deisch, and Raymond L. Linder Abstract.—When three rodenticide treatments—zinc phosphide (prebaited) and strychnine (both with and without prebait)—were evaluated, zinc phosphide was the most effec- tive in reducing active burrows of prairie dogs; but, it also resulted in a reduction in deer mouse densities. -
(Mrls) for Phosphane and Phosphide Salts According to Article 12 of Regulation (EC) No 396/2005
REASONED OPINION APPROVED: 25 November 2015 PUBLISHED: 04 December 2015 doi:10.2903/j.efsa.2015.4325 Review of the existing maximum residue levels (MRLs) for phosphane and phosphide salts according to Article 12 of Regulation (EC) No 396/2005 European Food Safety Authority (EFSA) Abstract According to Article 12 of Regulation (EC) No 396/2005, the European Food Safety Authority (EFSA) has reviewed the maximum residue levels (MRLs) currently established at European level for phosphane; this residue may result from the use of phosphane itself or from the use of certain phosphide salts. In order to assess the occurrence of phosphane residues in plants, processed commodities, rotational crops and livestock, EFSA considered the conclusions derived in the framework of Directive 91/414/EEC, the MRLs established by the Codex Alimentarius Commission as well as the European authorisations reported by Member States (incl. the supporting residues data). Based on the assessment of the available data, MRL proposals were derived and a consumer risk assessment was carried out. Although no apparent risk to consumers was identified, some information required by the regulatory framework was missing. Hence, the consumer risk assessment is considered indicative only and some MRL proposals derived by EFSA still require further consideration by risk managers. © European Food Safety Authority, 2015 Keywords: phosphane, phosphide, MRL review, Regulation (EC) No 396/2005, consumer risk assessment, fumigant Requestor: European Commission Question number: EFSA-Q-2009-00095; EFSA-Q-2009-00151; EFSA-Q-2009-00157; EFSA-Q-2009-00173; EFSA-Q-2012-00944 Correspondence: [email protected] www.efsa.europa.eu/efsajournal EFSA Journal 2015;13(12):4325 Review of the existing MRLs for phosphane and phosphide salts Acknowledgement: EFSA wishes to thank the rapporteur Member State Germany for the preparatory work on this scientific output.