Sustainable Use of Rodenticides As Biocides in the EU
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Society Responds to Contamination …</Italic>: Changes in Pest
Society responds to contamination . Changes in pest control practices reduce toll on wildlife Daniel W. Anderson ... All this beauty of life is fading year by year, ...fa ding like the glow of a sunset, ...fo undering in the grossness of modern refinement. - John Muir, 1868 While biocides, or pesticides, are designed to kill agricultural pests, many of these toxicants have the unintended effect of depleting natural biodiversity. Determining the specific effect of a biocide on biodiversity is com- plicated because other factors, such as direct habitat loss, also decrease biodiversity. Both in California and nationwide, farmers The agricultural spraying of toxaphene pesticide near wildlife habitat in 1971. Tox- have been among the first bio- aphene has been replaced with more effective and safer pest-control agents. cide-users to respond to the chal- lenge of reducing unintentional contamination of the environment. As a result, today agriculture faces fter direct habitat loss and degra- Twenty years ago, it looked as if many fewer biocide-diversity con- dation, toxic environmental con- biocide use, mostly from agricultural flicts than it did even a decade taminants pose the greatest challenges and public health pest control opera- ago. Changes in use of biocides for conservation. Toxicants, whether tions, was going to be a major continu- have led to recoveries of many antibiotics or biocides, dry-cleaning ing cause of wildlife extirpations at in- previously affected populations solvents or naturally occurring ex- creasing and unprecedented rates. But of birds, which are perhaps the cesses of selenium, are any substances today the picture is brighter due to ex- most studied aspects of bio- capable of destroying living organ- tensive research on how biocides affect diversity in these situations. -
An Independent Contract Research Organisation Specialising in Agrochemical, Biocide, Bio-Pesticide and Seed Product Evaluation
Expert services delivering competitive advantage An independent Contract Research Organisation specialising in agrochemical, biocide, bio-pesticide and seed product evaluation SynTech Research UK range of services include: As part of the EU/Global organisation Program design, planning and project management Laboratory and field ecotoxicology trials Development, evaluation and enhanced target Analytical studies research trials (GEP) Preparation and delivery of biological assess- Environmental fate studies (GLP) ment dossiers and regulatory submissions Crop variety, bio-stimulant and trait evaluation Provision of data summaries and recommendations HQ and Lab services Main sites Associations Contact: Mr Jerry Calloway, UK Managing Director UK HQ +44 (0) 1359 231 732 [email protected] www.syntechresearch.com Program Design and Management Working closely with clients to plan & design the field program and protocols to their objectives and the needs of regulatory authorities Study Monitoring and Direction through experienced multi-disciplined Project Managers Efficacy and Environmental Fate trials Field and Glasshouse characterisation of product performance (GEP) and environmental fate (GLP) Cereal, OSR, potato, pulses, grass, vegetables and top fruit crop coverage (field and protected) Fungicide, herbicide, insecticide, nematicide, plant growth regulator, bio-stimulant, fertiliser & nutrient, adjuvant and safener product testing Early screening through to development and registration; routine efficacy testing and special -
US EPA, Pesticide Product Label, ELECTRO-BIOCIDE,04/21/2020
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, DC 20460 OFFICE OF CHEMICAL SAFETY AND POLLUTION PREVENTION April 21, 2020 David Swain Authorized Agent for Strategic Resource Optimization, Inc. Scientific & Regulatory Consultants, Inc. 201 W. Van Buren Street Columbia City, Indiana 46725 Subject: Label Amendment: Emerging Viral Pathogens Claim Product Name: ELECTRO-BIOCIDE EPA Registration Number: 87492-1 Application Date: March 20, 2020 Decision Number: 561528 Dear Mr. Swain: The amended label referred to above, submitted in connection with registration under the Federal Insecticide, Fungicide and Rodenticide Act, as amended, is acceptable. This approval does not affect any conditions that were previously imposed on this registration. You continue to be subject to existing conditions on your registration and any deadlines connected with them. A stamped copy of your labeling is enclosed for your records. This labeling supersedes all previously accepted labeling. You must submit one copy of the final printed labeling before you release the product for shipment with the new labeling. In accordance with 40 CFR 152.130(c), you may distribute or sell this product under the previously approved labeling for 18 months from the date of this letter. After 18 months, you may only distribute or sell this product if it bears this new revised labeling or subsequently approved labeling. “To distribute or sell” is defined under FIFRA section 2(gg) and its implementing regulation at 40 CFR 152.3. Because you have opted to add statements pertaining to emerging viral pathogens to your label as described in the August 19, 2016, Guidance to Registrants: Process For Making Claims Against Emerging Viral Pathogens Not On EPA-Registered Disinfectant Labels (“Guidance”), https://www.epa.gov/sites/production/files/2016- 09/documents/emerging_viral_pathogen_program_guidance_final_8_19_16_001_0.pdf, you are subject to the following additional terms of registration: 1. -
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 -
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. -
Bromethalin: Secondary Toxicity
TECHNICAL BULLETIN RODENTICIDES BROMETHALIN: SECONDARY TOXICITY PRODUCT SCOPE Secondary toxicity of Bromethalin, the active ingredient in Fastrac and Talpirid Mole Bait. SECONDARY TOXICITY Bromethalin exerts its primary toxicity after conversion to the toxic metabolite, desbromethalin, which prevents cells from converting food into energy, leading to swelling of nerve cells, increased cerebrospinal pressure, and lethal disruption of the nervous system. In general, secondary toxicity occurs when an animal ingests a poisoned animal and then itself is impacted by the poison. The risk of secondary poisoning is aected by many factors: the sensitivity of the secondary consumer to the active ingredient, the amount and timing of rodenticide ingestion by the primary consumer, and the length of time the rodenticide remainsINSERT in the rodent TITLE tissue. LABORATORY STUDIES AND ANALYSIS OF WILDLIFE EXPOSURES Laboratory studies that involve feeding tissue from poisoned rodents to non-target animals and information from wildlife exposures are used to help assess secondary risk; however, the amount of data available for bromethalin is limited. In a secondary toxicity study in dogs conducted by an independent laboratory, daily feeding for two weeks with tissue from rats that were killed with 0.005% bromethalin showed no evidence of toxicity. PREVENTION As of 2018, to the best of our knowledge, there have been no reported cases of secondary poisoning from bromethalin rodenticides. However, rodenticide labels contain standard warning language to alert the user to the potential for unknown secondary toxicity risks. Pest control operators can reduce the risk for secondary poisoning in non-target animals by employing least hazardous methods and adhering to the label restrictions when using rodenticides. -
Transitional Guidance on the Biocidal Products Regulation
SUPERSEDED GUIDANCE - NEWER VERSION AVAILA BLE Transitional Guidance on the Biocidal Products Regulation Transitional Guidance on Efficacy Assessment for Product Type 18, Insecticide, Acaricides & other Biocidal Products against Arthropods and Product Type 19, Repellents & Attractants September 2016 TRANSITIONAL GUIDANCE Transitional Guidance on PT18 + PT19 2 September 2016 LEGAL NOTICE This document aims to assist users in complying with their obligations under the Biocidal Products Regulation (BPR). However, users are reminded that the text of the BPR is the only authentic legal reference and that the information in this document does not constitute legal advice. Usage of the information remains under the sole responsibility of the user. The European Chemicals Agency does not accept any liability with regard to the use that may be made of the information contained in this document. Transitional Guidance on Efficacy Assessment for Product Type 18 Insecticide, Acaricides & other Biocidal Products against Arthropods and Product Type 19 Repellents & Attractants. Publ.date: September 2016 Language: EN © European Chemicals Agency, 2016 If you have questions or comments in relation to this document please send them (indicating the document reference, issue date, chapter and/or page of the document which your comment refers) using the Guidance feedback form. The feedback form can be accessed via the ECHA website or directly via the following link: https://comments.echa.europa.eu/comments_cms/FeedbackGuidance.aspx European Chemicals Agency Mailing address: P.O. Box 400, FI-00121 Helsinki, Finland Visiting address: Annankatu 18, Helsinki, Finland Transitional Guidance on PT18 + PT19 3 September 2016 PREFACE This Transitional Guidance is to be applied to applications for active substance approval and product authorisation submitted under the Biocidal Product Regulation (EU) No 528/2012 (the BPR). -
Biocide Standards Reference Guide
Biocide Standards Reference Guide Main Group I: Main Group II: Disinfectants & Preservatives General Biocidal Products Main Group III: Main Group IV: Pest Control Other Biocidal Products AccuStandard® A biocide can be defined as a chemical or micro-organism which prevents, controls and/or renders harmless organisms through chemical or biological means. Biocides are used wherever organisms may cause product contamination or a health threat to people and/or animals. Biocides can be added to other materials to protect them against biological growth or infestation. “Treated articles” are included within the biocides regulations and are subject to the same requirements as biocides. Biocides are used by workers in all types of industries to control viruses, bacteria, fungi, insects and animals. The intended use and chemical potency of biocides require that their use, storage and disposal be controlled to prevent adverse effects to the public and/or environment. To ensure the safety of biocides, government regulations are in place to assess the active substances within commercial products. One such regulation is the Biological Products Directive 98/8/EC (BPD) which has been recently revised and is now designated as EU Biocides Regulation 528/2012 (EU BPR). Under this legislation, active compounds are submitted for approval on the list of Approved Active Substances. This regulation went into effect in September 2013, and classifies biocides into 22 biocide product types, grouped into four main areas. Biological Products Directive 98/8/EC (BPD) revised 2012 Biocides Main Group I Main Group II Disinfectants and Preservatives general biocidal products Product Type Product Type 6. In-can preservatives 1. -
A Review of the Secondary Poisoning Hazard Potential
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Proceedings of the Tenth Vertebrate Pest Vertebrate Pest Conference Proceedings collection Conference (1982) 2-23-1982 A REVIEW OF THE SECONDARY POISONING HAZARD POTENTIAL TO WILDLIFE FROM THE USE OF ANTICOAGULANT RODENTICIDES Dale Kaukeinen Biological Research Center, ICI Americas Inc., Goldsboro, North Carolina 27530 Follow this and additional works at: http://digitalcommons.unl.edu/vpc10 Part of the Environmental Health and Protection Commons Kaukeinen, Dale, "A REVIEW OF THE SECONDARY POISONING HAZARD POTENTIAL TO WILDLIFE FROM THE USE OF ANTICOAGULANT RODENTICIDES" (1982). Proceedings of the Tenth Vertebrate Pest Conference (1982). Paper 27. http://digitalcommons.unl.edu/vpc10/27 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 Tenth Vertebrate Pest Conference (1982) by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. A REVIEW OF THE SECONDARY POISONING HAZARD POTENTIAL TO WILDLIFE FROM THE USE OF ANTICOAGULANT RODENTICIDES DALE KAUKEINEN, Biological Research Center, ICI Americas Inc., Goldsboro, North Carolina 27530 ABSTRACT: The utility and characteristics of the family of anticoagulant rodenticides are reviewed, including the new members difenacoum, bromadiolone and brodifacoum. General considerations are given in investigating the likelihood of nontarget poisoning with rodenticides. The literature dealing with secondary poisoning studies and concerns with the use of anticoagulant rodenticides is reviewed. The utility of laboratory toxicity data versus field-generated exposure data is compared. Considerations of secondary poisoning by anticoagulants are reviewed as regards parameters such as specific predator- prey systems, biotopes, rodenticide use patterns, and risk-benefit assessments. -
Managing Pesticide Poisoning Risk and Understanding the Signs and Symptoms Clyde L
EC2505 Revised June 2018 Managing Pesticide Poisoning Risk and Understanding the Signs and Symptoms Clyde L. Ogg, Extension Educator Jan R. Hygnstrom, Project Manager Cheryl A. Alberts, Project Coordinator Erin C. Bauer, Entomology Lecturer The potential for accidents with pesticides is real. Ac- cidental exposure or overexposure to pesticides can have seri- ous consequences. While most pesticides can be used with relatively little risk when label directions are followed, some are extremely toxic and require special precautions. The Poison Control Centers receive about 90,000 calls each year related to pesticide exposures. Pesticides are re- sponsible for about 3 percent of all accidental exposures to children 5 years and younger and about 4 percent for adults. In addition, pesticides are the cause of about 3 percent of children’s deaths reported to the Poison Control Centers. Routes of Exposure Pesticides can enter the human body three ways: 1) der- mal exposure, by absorption through the skin or eyes; 2) oral exposure, through the mouth; and 3) through inhalation or respiratory exposure, by inhaling into the lungs. Some classify exposure through the eyes as ocular exposure. Dermal exposure results in absorption immediately after Figure 1. Absorption rates of different a pesticide contacts the skin or eyes. Absorption will contin- parts of the body based on the absorption ue as long as the pesticide remains in contact with the skin or of parathion into the forearm over 24 eyes. The rate at which dermal absorption occurs is different hours. for each part of the body (Figure 1). Maiback and Feldman (1974) measured the amount of the pesticide parathion absorbed by different parts of the human body over 24 hours. -
Modelling Biocide and Herbicide Concentrations in Catchments of The
Hydrol. Earth Syst. Sci. Discuss., https://doi.org/10.5194/hess-2017-628 Manuscript under review for journal Hydrol. Earth Syst. Sci. Discussion started: 2 November 2017 c Author(s) 2017. CC BY 4.0 License. Modelling biocide and herbicide concentrations in catchments of the Rhine basin Andreas Moser1, Devon Wemyss1#, Ruth Scheidegger1, Fabrizio Fenicia1, Mark Honti2, Christian 1 Stamm 5 1Eawag – Swiss Federal Institute of Aquatic Science and Technology, Dübendorf, 8600, Switzerland 2MTA-BME Water Research Group, Hungarian Academy of Sciences, Budapest, 1111, Hungary #current address: ZHAW School of Management and Law, Winterthur, 8400, Switzerland Correspondence to: Christian Stamm ([email protected]) 10 Abstract. Impairment of water quality by organic micropollutants such as pesticides, pharmaceuticals or household chemicals is a problem in many catchments worldwide. These chemicals originate from different urban and agricultural usages and are transferred to surface waters from point or diffuse sources by a number of transport pathways. The quantification of this form of pollution in streams is challenging and especially demanding for diffuse pollution due to the high spatio-temporal concentration dynamics, which requires large sampling and analytical efforts to obtain representative 15 data on the actual water quality. Models can also be used to predict information to which degree streams are affected by these pollutants. However, spatially distributed modeling of water quality is challenging for a number of reasons. Key issues are the lack of such models that incorporate both urban and agricultural sources of organic micropollutants, the large number of parameters to be estimated 20 for many available water quality models, and the difficulty to transfer parameter estimates from calibration sites to areas where predictions are needed. -
Triameen® Y12D – High Performance, Broad Spectrum Biocide
Thannhausen, Germany, December 19, 2019 Thannhausen, Germany, | Volume 145 Volume | 12/19 vegan silk ® How can silk be vegan? Triameen Y12D – SEPAWA High Performance, congress 12 event report 2019 english Broad Spectrum Biocide home care for Disinfection and sensors High Performance, Broad Spectrum Biocide High-acyl Gellan Gum as a Functional for Disinfection and Preservation Polyacrylate Substitute in Emulsions Preservation skin care Cosmetic Peeling Formulations: Skin- & Environment-friendly Breaking New Ground in the Exploration on Skin Microbiome Biotechnological Active Ingredient, Protecting Skin Microbiota R. Borgmann-Strahsen SOFW Journal 12/19 | Volume 145 | Thannhausen, Germany, December 19, 2019 home care | safety Triameen® Y12D - High Performance, Broad Spectrum Biocide for Disinfection and Preservation R. Borgmann-Strahsen Introduction Control of harmful microorganisms is important in many application fields to ensure human and animal welfare and product integrity. The trend to more sustainable products/pro- cesses like use of natural based raw materials, reduction of Fig. 1 Molecular structure of Triameen® Y12D. solvents and increasing recycling of industrial water enhance the risk of microbial deterioration. Hence biocides play an important role in safeguarding our current standard of living plications. The molecular structure of Triameen® Y12D is shown and realizing a more sustainable future. in Fig. 1. As can be seen it has the shape of a “Y” with primary In Europe the making available on the market and use of bio- amine groups (blue circles) at the end of the 2 propyl groups and a cidal products is regulated by the Biocidal Products Regulation tertiary amine group (black circle) at the cross-point. (BPR, Regulation (EU) No 528/2012).