Defending Nature Against Rodenticides
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Threats to Sources of Drinking Water and Aquatic Ecosystem Health in Canada Threats to Sources of Drinking Water and Aquatic Ecosystem Health in Canada
THREATS TO SOURCES OF DRINKING WATER AND AQUATIC ECOSYSTEM HEALTH IN CANADA THREATS TO SOURCES OF DRINKING WATER AND AQUATIC ECOSYSTEM HEALTH IN CANADA NWRI Scientific Assessment Report Series No. 1 NATIONAL WATER RESEARCH INSTITUTE ENVIRONMENT CANADA © Minister of Public Works and Government Services Canada 2001 To obtain additional copies: Science Liaison Branch National Water Research Institute Environment Canada 867 Lakeshore Road, P.O. Box 5050 Burlington, ON L7R 4A6 Or download a copy in pdf format from the NWRI web site: http://www.cciw.ca/nwri/ National Library of Canada Cataloguing in Publication data Main entry under title: Threats to sources of drinking water and aquatic ecosystem health in Canada (NWRI Scientific Assessment Report Series, ISSN 1499-5905; no. 1) Issued also in French under title: Menaces pour les sources d’eau potable et les écosystèmes aquatiques au Canada. ISBN 0-662-31315-1 Cat. No. En40-237/1-2001E 1. Drinking water – – Contamination – – Canada – – Congresses. 2. Water – – Pollution – – Canada – – Congresses. 3. Water quality – – Canada – – Congresses. I. National Water Research Institute (Canada) II. Series. TD226.T47 2001 363.6’1’0971 C2001-980362-1 This report may be cited as follows: Environment Canada. 2001. Threats to Sources of Drinking Water and Aquatic Ecosystem Health in Canada. National Water Research Institute, Burlington, Ontario. NWRI Scientific Assessment Report Series No. 1. 72 p. ii Table of Contents Foreword . v Executive Summary . .. vii 1. Waterborne Pathogens . 1 2. Algal Toxins and Taste and Odour . 5 3. Pesticides . 9 4. Persistent Organic Pollutants and Mercury . 13 5. Endocrine Disrupting Substances . 17 6. Nutrients—Nitrogen and Phosphorus . -
Rattus Norvegicus Polymorphic For. Warfarin Resistance
Heredity (1979), 43(2), 239-246 RELATIVE FITNESS OF GENOTYPES IN A POPULATION OF RATTUS NORVEGICUS POLYMORPHIC FOR. WARFARIN RESISTANCE G. G. PARTRIDGE Department of Genetics, University of Liverpool, Liverpool L69 38X* Received11 .iii.79 SUMMARY Resistance to warfarin and an increased vitamin K requirement appear to be pleiotropic effects of the same allele (Rw 2).Ina natural population containing resistant individuals where the use of warfarin is discouraged the change in the frequency of resistance should reflect the relative fitnesses of the three possible genotypes. A large polymorphic population of rats was extensively poisoned with warfarin and the level of resistance monitored regularly for a period of 18 months after withdrawal of the poison. During this period the proportion of resistant animals in live-capture samples decreased significantly from approxi-. mately 80 per cent to 33 per cent. This decline is consistent with a hypothesis of reduced fitness of both RwZRw2andRw'Rw2 genotypes relative to Rw'Rw' under natural conditions. The relative fitnesses of these genotypes were calculated using an optimisation method based on least squares analysis. These estimates were: Rw2Rw2 (0.46), Rw'Rw2 (077) and Rw1Rw' (100). Homozygous resistant individuals were found in some of the samples, confirm- log that the Rw2 allele does not act as a recessive lethal, although it must be extremely disadvantageous. Some heterogeneity was observed in the proportion of resistant animals in samples taken from different areas of the farm building complex. This could reflect stochastic processes influencing the Rw2 allele frequency in small peripheral populations. 1. INTRODUCTION THE anticoagulant rodenticide warfarin was introduced into Britain in 1953 (Greaves, 1971). -
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. -
Biopesticides – Expectations for Control
Biopesticides – Expectations for Control Jeanette Gaultier, Crops Knowledge Centre, Manitoba Agriculture, Food and Rural Initiatives, Carman, MB R0G 0J0 Email: [email protected] A biopesticide is a naturally occurring organism or substance that can be used to control pests. The term ‘biopesticide’ can be applied to microorganisms, biochemicals and plant extracts that are used as pest control products. Although not the case in Canada, some countries also consider plants with ‘incorporated protectants’ (i.e. transgenic crops) as biopesticides. Interest in biopesticides is increasing because such products are often recognized as ‘reduced’ or ‘low’ risk alternatives to conventional pesticides. In Canada, a pesticide is considered to be of reduced risk if human health and/or environmental risks are decreased relative to other pesticides registered for the same use. General characteristics of reduced risk pesticides include (PMRA, 2002): • Low toxicity; • Limited effects on non-target organisms; • Good environmental profile; • Low pest resistance potential; • Decreased application rates or applications; and • Compatible with integrated pest management principles. A product doesn’t have to be a biopesticide to be considered reduced risk. Conversely, biopesticides are often, but not always, classified as reduced risk. Biopesticides currently account for only a small percentage (~1%) of the global pesticide market (Copping and Menn, 2000; Warrior, 2000; Rodgers, 1993). These products have generally found commercial success in niche markets such as horticulture, greenhouse, nursery and ornamental, and organic production. Uptake and use of biopesticides in conventional field crop agriculture remains low. Why is this the case? What should agricultural producers expect from biopesticides? Regulatory Expectations All pesticides, including biopesticides, available for use in Canada are regulated by Health Canada’s Pest Management Regulatory Agency (PMRA). -
A California Without Rodenticides: Challenges for Commensal Rodent Management in the Future
Human–Wildlife Interactions 13(2):212–225, Fall 2019 • digitalcommons.usu.edu/hwi A California without rodenticides: challenges for commensal rodent management in the future Niamh Quinn, University of California Agriculture and Natural Resources, South Coast Research and Extension Center, Irvine, CA 92618, USA [email protected] Sylvia Kenmuir, BASF, 26 Davis Drive, Research Triangle Park, NC 27709, USA Laura Krueger, Orange County Mosquito and Vector Control District, Garden Grove, CA 92843, USA Abstract: Rodenticides are an essential tool in the integrated pest management of infestations of commensal rodents (Rattus norvegicus, R. rattus, and Mus musculus). With the introduction of Assembly Bill 1788, the California Ecosystems Protection Act of 2019, California is potentially facing a future with new restrictions on the use of anticoagulant rodenticides to manage commensal rodents in urban areas. Assembly Bill 1788 has been proposed specifically to protect predators from anticoagulant rodenticide poisoning and seeks to restrict the application of second-generation anticoagulant rodenticides (SGARs) for use in many urban and non-urban areas of California, USA. Exclusion and cultural practices, such as landscape management and sanitation (i.e., cleaning of property including but not limited to trash containment and removal, and drain sanitation), remain important and successful tools for managing rodent populations. However, increased exposure of wildlife to anticoagulant rodenticides has been detected California. Several animal species have been documented as having succumbed to rodenticide toxicosis. When rodents are killed by SGARs and consumed by predators, SGAR residues have been detected in the livers of predatory species. However, the effects of chronic, sublethal exposure to predators are not well understood. -
Master List of Actions on the Reduction And/Or Elimination of Releases of Pops
UNITED NATIONS ENVIRONMENT PROGRAMME Chemicals MMAASSTTEERR LLIISSTT OOFF AACCTTIIOONNSS On the Reduction and/or Elimination of the Releases of Persistent Organic Pollutants Fourth Edition Prepared by UNEP Chemicals June 2002 INTER-ORGANIZATION PROGRAMME FOR THE SOUND MANAGEMENT OF CHEMICALS IOMC A cooperative agreement among UNEP, ILO, FAO, WHO, UNIDO, UNITAR and OECD This publication is produced within the framework of the Inter-Organization Programme for the Sound Management of Chemicals (IOMC) The Inter-Organization Programme for the Sound Management of Chemicals (IOMC), was established in 1995 by UNEP, ILO, FAO, WHO, UNIDO and OECD (Participating Organizations), following recommendations made by the 1992 UN Conference on Environment and Development to strengthen cooperation and increase coordination in the field of chemical safety. In January 1998, UNITAR formally joined the IOMC as a Participating Organization. The purpose of the IOMC is to promote coordination of the policies and activities pursued by the Participating Organizations, jointly or separately, to achieve the sound management of chemicals in relation to human health and the environment. The photograph on the cover page was taken by Steve C. Delaney. Copies of this report are available from: UNEP Chemicals 11-13, chemin des Anémones CH-1219 Châtelaine, GE Switzerland Phone: +41 22 917 1234 Fax: +41 22 797 3460 E-mail: [email protected] Web: http://www.chem.unep.ch/pops UNEP CHEMICALS UNEP Chemicals is part of UNEP’s Technology, Industry and Economics Division UNITED NATIONS ENVIRONMENT PROGRAMME Chemicals MMAASSTTEERR LLIISSTT OOFF AACCTTIIOONNSS On the Reduction and/or Elimination of the Releases of Persistent Organic Pollutants Fourth Edition Issued by UNEP Chemicals Geneva, Switzerland June 2002 Table of contents Page Executive summary i Introduction xvii Organization and xviii structure of the tables Chapter 1 Information on global activities aiming at the reduction 1 and/or elimination of releases of POPs received from Inter-Governmental Organizations. -
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 -
Appendix B. Brodifacoum Papers That Were Accepted for ECOTOX
Appendix B. Brodifacoum Papers that Were Accepted for ECOTOX Acceptable for ECOTOX and OPP 1. Abou El-Khear, R. K. (2005). Evaluation and Records of Rome Anticoagulant Rodenticides Against Wild Rats Under the Reclaimed Lands Conditions. Alexandria Sci. Exch. 26: 142-147. EcoReference No.: 153588 Chemical of Concern: BDF,CPC,DFM,PPCP,WFN; Habitat: T; Effect Codes: POP; Code: LITE EVAL CODED (BDF,CPC), NO SURVEY (PPCP,WFN). 2. Ahmad, M. S. and Munir, S. (1990). Comparative Evaluation of Three Anticoagulants Brodifacoum, Bromadialone and Flucoumafen Against Indian Gerbil, Tatera indica. Pak.J.Zool. 22: 421-426. EcoReference No.: 75417 Chemical of Concern: BDF,BDL; Habitat: T; Effect Codes: MOR,BEH; Rejection Code: LITE EVAL CODED(BDF,BDL). 3. Ahmad, N. and Parshad, V. R. (1991). Evaluation of Rodenticidal Baits in Fields of Sugarcane (Saccharum officinarum). Indian J.Agric.Sci. 61: 281-284. EcoReference No.: 75653 Chemical of Concern: ZnP,BDF,BDL; Habitat: T; Effect Codes: POP; Rejection Code: LITE EVAL CODED(ZnP,BDF,BDL). 4. Ahmad, N., SHEIKHER, C., and Guraya, S. S. (1989). Rodenticidal Baitings in Wheat Fields of the Garhwal Himalayas. Trop.Pest Manag. 35: 282-285. EcoReference No.: 75606 Chemical of Concern: ZnP,BDF,BDL; Habitat: T; Effect Codes: POP; Rejection Code: LITE EVAL CODED(ZnP,BDF,BDL). 5. Alterio, N., Brown, K., and Moller, H. (1997). Secondary Poisoning of Mustelids in a New Zealand Nothofagus Forest. J.Zool.(London) 243: 863-869. EcoReference No.: 75652 Chemical of Concern: BDF; Habitat: T; Effect Codes: POP,MOR; Rejection Code: LITE EVAL CODED(BDF). 6. Alterio, N. and Moller, H. -
Persistent Organic Pollutants
PERSISTENT ORGANIC POLLUTANTS An Assessment Report on: DDT-Aldrin-Dieldrin-Endrin-Chlordane Heptachlor-Hexachlorobenzene Mirex-Toxaphene Polychlorinated Biphenyls Dioxins and Furans Prepared by: L. Ritter, K.R. Solomon, J. Forget Canadian Network of Toxicology Centres 620 Gordon Street Guelph ON Canada and M. Stemeroff and C.O'Leary Deloitte and Touche Consulting Group 98 Macdonell St., Guelph ON Canada For: The International Programme on Chemical Safety (IPCS) within the framework of the Inter-Organization Programme for the Sound Management of Chemicals (IOMC) This report is produced for the International Programme on Chemical Safety (IPCS). The work is carried out within the framework of the Inter-Organization Programme for the Sound Management of Chemicals (IOMC). The report does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. The International Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experimental laboratory, and risk-assessment methods that could produce internationally comparable results, and the development of human resources in the field of chemical safety. Other activities carried out by the IPCS include the development of know-how for coping with chemical accidents, strengthening capabilities for prevention of an response to chemical accidents and their follow-up, coordination of laboratory testing and epidemiological studies, and promotion of research on the mechanisms of the biological action of chemicals. -
Additional Mitigation Measures for Rodenticides
Questions and Answers – Additional Mitigation Measures for Rodenticides About the Evaluation of Rodenticides 1. What are rodenticides? Rodenticides are pest control products registered for controlling mice, rats and other rodents that pose threats to public health, critical habitats, native plants and animals, crops, and food supplies. 2. Why did Health Canada re-evaluate rodenticides? As required under the Pest Control Product Act, Health Canada’s Pest Management Regulatory Agency (PMRA) conducts re-evaluations of older pesticides to ensure they meet modern health and safety standards. As scientific knowledge evolves and new information becomes available, the PMRA requires that registered pesticides be re-evaluated according to modern risk assessment approaches. The PMRA re-evaluated six rodenticides (brodifacoum, bromadiolone, chlorophacinone, diphacinone, warfarin and zinc phosphide) and published Re-evaluation Decision Documents (RRD2006-11 and RVD2007-01) in 2006 and 2007, respectively. The public was consulted prior to finalizing these decision documents (PACR2004-27 and PACR2006-08). 3. Why are additional mitigation measures required following re-evaluation? In 2010, the PMRA required additional protective measures for several rodenticides containing the following active ingredients: brodifacoum, bromadiolone, bromethalin, chlorophacinone, diphacinone, difethialone, warfarin and zinc phosphide, as part of an overall risk-reduction strategy for rodenticides in Canada. The name of the active ingredient contained in a rodenticide product is listed on the product label under “guarantee”. Rodenticides are highly acutely toxic compounds, and can be used in residential and agricultural settings. Additional protective measures are warranted in order to prevent exposure of children, pets and non-target wildlife to these chemicals. Manufacturers have until December 31, 2012 to have new labelling in place. -
Pesticides: Making the Right Choice For
House of Commons Committees - ENVI (36-2) - Pesticides: Making the Right Choice for... Page 1 of 1 Secilon hforne Francais:^ JaSte off Contend > hM Publications Options Gorrtrerttee Report Back_tp_raports and responses * PESTICIDES MAKING THE RIGHT CHOICE FOR THE PROTECTION OF HEALTH AND THE ENVIRONMENT Report of the Standing Committee on Environment and Sustainable Development May 2000 Jk, > No<: http://www2.paFl. gc.ca/'HouscPiiblrcationa/Publication.aspx?DocId=1033697&Laiiguage=E.„ 7/6/2009 House of Commons Committees - ENVI (36-2) - Pesticides: Making the Right Choice for... Page 1 of 4 Section Home I'fvWfi i >tlert Publications Options Committee Report Back to reports and responses Table of Contents List of Members Mandate CHAIR'S PREFACE TO THE REPORT EXECUTIVE SUMMARY: KEY DIRECTIONS FOR CHANGE Introduction PART A: BACKGROUND Chapter 1 - THE FEDERAL REGULATORY SYSTEM AND THE ROLE OF THE PEST MANAGEMENT REGULATORY AGENCY Chapter 3 - THE NEED FOR NEW LEGISLATION An Outdated Statute Guiding Principles for the New Legislation PART B: PESTICIDES AND THEIR HARMFUL EFFECTS Chapter 3 - HISTORY OF PESTICIDE USE The Main Classes of Chemical Pesticides Sectors of Pesticide Use General Characteristics of Pesticides Appendix 3,1: Pesticides and Golf Courses Appendix 3.2: Description of Major Groups of Chemical Pesticides Chapter 4 - PESTICIDES IN THE ENVIRONMENT Transportation and Dispersion of Pesticides in Soil, Air and Water Long-Range Transportation of Pesticides: Persistent Organic Pollutants (POPs) Increasing Levels of Pesticides in the -
The Use of Sodium Cyanide in Wildlife Damage Management
Human Health and Ecological Risk Assessment for the Use of Wildlife Damage Management Methods by USDA-APHIS-Wildlife Services Chapter VII THE USE OF SODIUM CYANIDE IN WILDLIFE DAMAGE MANAGEMENT May 2017 Peer Reviewed Final October 2019 THE USE OF SODIUM CYANIDE IN WILDLIFE DAMAGE MANAGEMENT EXECUTIVE SUMMARY USDA-APHIS Wildlife Services (WS) uses sodium cyanide (NaCN) to manage coyotes, red foxes, gray foxes, arctic foxes, and wild dogs that prey upon livestock, poultry, and federally designated threatened and endangered species or animals that are vectors of disease. This human health and ecological risk assessment is an evaluation of the risks to human health, nontarget animals, and the environment from NaCN use by WS. WS uses the M-44, the name for the ejector device that delivers a single dose NaCN from a capsule, to target canids. The M-44 is spring-activated and is actuated when an animal pulls up on the capsule holder; a plunger propelled by the spring breaks through a capsule with dry NaCN to deliver the contents into the mouth of an animal. The WS applicator baits the M-44 capsule holder sides to attract target canids. Sodium cyanide reacts rapidly with moisture in the mouth or mucus membranes of the nose and eyes to form hydrogen cyanide (HCN), a toxicant. One NaCN capsule contains enough cyanide to be lethal to animals through oral contact, inhalation contact, and moist dermal pathway contact. WS annually averaged the known take of 13,959 target canids and 362 nontarget species with NaCN between FY11 and FY15, recording 1,548,000 Method Nights with M-44s in 17 States.