RED) AL & MG Phosphide UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C
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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). -
Features & Benefits
Click Here To Purchase Features & Benefits: • TAURUS SC is a water-based suspension concentrate of 9.1% Fipronil for Pre and Post-construction termite applications, and to control perimeter pests • Apply at a rate of 4 gallons of dilution per 10 linear feet per foot of depth for termites • TAURUS SC is labeled for barrier applications targeting listed occasional invaders around structures • Now with EP/LI applications PRECAUTIONARY STATEMENTS ® Hazards to Humans and Domestic Animals Caution TAURUS SC Harmful if swallowed, absorbed through skin or inhaled. Do not get in eyes, on skin Termiticide / Insecticide or on clothing. Do not breathe spray mist. Wash thoroughly with soap and water after handling and before eating, drinking, chewing gum, or using tobacco. Remove and It is a violation of federal law to use this product in a manner inconsistent wash contaminated clothing before reuse. with its labeling. Personal Protective Equipment (PPE): • For sale to, use and storage only by individuals/firms licensed or registered All pesticide handlers (mixers, loaders, and applicators) must wear long-sleeved by the state to apply termiticide and/or general pest control products. shirt and long pants, socks, shoes, and chemical-resistant gloves. All pesticide • DO NOT use this product for termite or other pest control indoors, except for handlers must wear a dust/mist filtering respirator (MSHA/NIOSH approval number label-specified applications for termite control and foam applications to wall prefix TC-21C), or a NIOSH approved respirator with any N, R, P or HE filter, when voids for control of other listed pests. working in a non-ventilated space, including but not limited to crawl-spaces and • DO NOT use on golf course turf. -
Historical Use of Lead Arsenate and Survey of Soil Residues in Former Apple Orchards in Virginia
HISTORICAL USE OF LEAD ARSENATE AND SURVEY OF SOIL RESIDUES IN FORMER APPLE ORCHARDS IN VIRGINIA by Therese Nowak Schooley Thesis submitted to the faculty of the Virginia Polytechnic Institute and State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE IN LIFE SCIENCES in Entomology Michael J. Weaver, Chair Donald E. Mullins, Co-Chair Matthew J. Eick May 4, 2006 Blacksburg, Virginia Keywords: arsenic, lead, lead arsenate, orchards, soil residues, historical pesticides HISTORICAL USE OF LEAD ARSENATE AND SURVEY OF SOIL RESIDUES IN FORMER APPLE ORCHARDS IN VIRGINIA Therese Nowak Schooley Abstract Inorganic pesticides including natural chemicals such as arsenic, copper, lead, and sulfur have been used extensively to control pests in agriculture. Lead arsenate (PbHAsO4) was first used in apple orchards in the late 1890’s to combat the codling moth, Cydia pomonella (Linnaeus). The affordable and persistent pesticide was applied in ever increasing amounts for the next half century. The persistence in the environment in addition to the heavy applications during the early 1900’s may have led to many of the current and former orchards in this country being contaminated. In this study, soil samples were taken from several apple orchards across the state, ranging from Southwest to Northern Virginia and were analyzed for arsenic and lead. Based on naturally occurring background levels and standards set by other states, two orchards sampled in this study were found to have very high levels of arsenic and lead in the soil, Snead Farm and Mint Spring Recreational Park. Average arsenic levels at Mint Spring Recreational Park and Snead Farm were found to be 65.2 ppm and 107.6 ppm, respectively. -
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. -
Safe Pest Control
SAFE PEST CONTROL U.S. Department of Housing and Urban Development • Office of Healthy Homes and Lead Hazard Control “For years, cockroaches have defeated our best efforts to get rid of them. We sprayed and sprayed, but they always came back. Now we under- stand there are better methods and products that really work” Environmental Health Watch Did you know...? ■ Many pesticides for home use are toxic? ■ There are alternative pest management methods that limit the use of toxic substances? ■ Mice, cockroaches, and cockroach "dust” can trigger asthma attack? What is it? Integrated pest management (IPM) is a way to remove pests, like cock- roaches, mice, and rats from a home. IPM is a common sense approach that: ■ Denies pests food, water, shelter and a way to enter the home. ■ Uses baits and powders, such as gel baits, traps and borate powder. Why use IPM? ■ IPM is safer. IPM does not use as many harmful pesticides as traditional pest control. - Avoiding pesticides is especially important in homes. Pesticides can contain long lasting, toxic chemicals or lung irritants that cause asthma attacks. Children are among those most vulnerable to exposure. IPM strategies apply pesticides only as needed and use the least hazardous pesticides to control pests. continued on back www.hud.gov/offices/lead U.S. Department of Housing and Urban Development SAFE PEST CONTROL Office of Healthy Homes and Lead Hazard Control Non-toxic traps can be part of an IPM strategy. If needed, call a pest control professional who uses IPM practices. If you have taken all the steps described above and still have a pest problem, you may need a professional to help. -
4-Cyano-3-Benzoylamino-N
(19) TZZ _T (11) EP 2 427 427 B1 (12) EUROPEAN PATENT SPECIFICATION (45) Date of publication and mention (51) Int Cl.: of the grant of the patent: C07C 255/60 (2006.01) 25.12.2013 Bulletin 2013/52 (86) International application number: (21) Application number: 10713937.0 PCT/EP2010/054862 (22) Date of filing: 14.04.2010 (87) International publication number: WO 2010/127926 (11.11.2010 Gazette 2010/45) (54) 4-CYANO-3-BENZOYLAMINO-N-PHENYL-BENZAMIDES FOR USE IN PEST CONTROL 4-CYANO-3-BENZOYLAMINO-N-PHENYL-BENZAMIDE ZUR VERWENDUNG IN DER SCHÄDLINGSBEKÄMPFUNG 4-CYANO-3-BENZOYLAMINO-N-PHÉNYL-BENZAMIDES DESTINÉS À ÊTRE UTILISÉS DANS LA LUTTE ANTIPARASITAIRE (84) Designated Contracting States: • HUETER, Ottmar Franz AT BE BG CH CY CZ DE DK EE ES FI FR GB GR CH-4332 Stein (CH) HR HU IE IS IT LI LT LU LV MC MK MT NL NO PL • MAIENFISCH, Peter PT RO SE SI SK SM TR CH-4332 Stein (CH) (30) Priority: 06.05.2009 GB 0907822 (74) Representative: Herrmann, Jörg et al 18.12.2009 GB 0922234 Syngenta Crop Protection Münchwilen AG (43) Date of publication of application: Intellectual Property Department 14.03.2012 Bulletin 2012/11 Schaffhauserstrasse CH-4332 Stein (CH) (73) Proprietor: Syngenta Participations AG 4058 Basel (CH) (56) References cited: EP-A1- 1 714 958 WO-A1-2008/000438 (72) Inventors: WO-A1-2008/074427 • JUNG, Pierre Joseph Marcel CH-4332 Stein (CH) Remarks: • GODFREY, Christopher Richard Ayles Thefile contains technical information submitted after CH-4332 Stein (CH) the application was filed and not included in this specification Note: Within nine months of the publication of the mention of the grant of the European patent in the European Patent Bulletin, any person may give notice to the European Patent Office of opposition to that patent, in accordance with the Implementing Regulations. -
Who Needs Chlorpyrifos and Why (By Crop)?
1 WHO NEEDS CHLORPYRIFOS AND WHY (BY CROP)? EXCERPTS OF COMMENTS SUBMITTED TO EPA AT EPA-HQ-OPP-2015-0653 GENERAL “Consumers I have visited with that do not have any ag background are easily swayed into the belief that farmers are polluting the environment and recklessly applying chemicals. Truth is our farmers are professionals and with today’s pricing cannot afford to be over- or misapplying inputs that affect their bottom lines…. I strongly suggest that you…allow producers of the world’s food source to continue using the product chlorpyrifos.” – North Dakota farmer. “Many food crop industries in the Pacific Northwest are concerned about the impacts to pest management based on EPA’s proposed tolerance revocation of chlorpyrifos, including several minor crop groups with limited pesticide options. These industries include processed vegetables, strawberry, grass seed, mint, and cranberry. For many of these industries, chlorpyrifos has unique properties that make it an essential part of their Integrated Pest Management program. It is also an important tool for resistance management. Several of these industries have conducted research to identify effective alternatives to chlorpyrifos, but currently there aren’t viable alternatives that match the efficacy and low risk of this product for managing a number of critical pests…. A revocation of all chlorpyrifos tolerances would eliminate a number of low-risk, critical uses in cases where few alternatives exist at present, and in many cases those alternatives (neonicotinoids, pyrethroids) would be less efficacious, more expensive and have greater impacts on nontarget species including pollinators and beneficial insects. Further, the economic impacts based on resulting crop damage would be substantial.” – Oregon State University Agronomist. -
Chlorpyrifos, Part 1: Toxicology
JOURNAL OF PESTICIDE REFORM/ WINTER 1994 • VOL.14, NO. 4 ■ INSECTICIDE FACTSHEET CHLORPYRIFOS, PART 1: TOXICOLOGY The broad spectrum organophosphate insecticide chlorpyrifos is the most widely used insecticide in the U.S. Total use is estimated at almost 30 million pounds per year. Like all organophosphate insecticides, chlorpyrifos affects the nervous system by inhibiting an enzyme that is important in the transmission of nerve impulses. Symptoms of acute poisoning include headache, nausea, muscle twitching, and convulsions. Chlorpyrifos poisonings are reported to state and federal agencies more often than poisonings of almost every other insecticide. In both laboratory animals and humans, chlorpyrifos can also cause delayed effects on the nervous system. Some effects have been measured years after exposure. Human birth defects have been associated with exposure to chlorpyrifos products. In pregnant laboratory animals, chlorpyrifos exposure caused fetal death. Pups that did survive were smaller pups and did not survive as well as pups from unexposed mothers. Chlorpyrifos also affects the male reproductive system; exposure to a chlorpyrifos product has caused death of cells in male rat testes and a decrease in sperm production in cattle. Chlorpyrifos has caused genetic damage in human blood and lymph cells, mice spleen cells, and hamster bone marrow cells. Immune system abnormalities have been reported from patients exposed to chlorpyrifos. Many individuals report developing sensitivities to a broad array of substances following chlorpyrifos exposure. The second part of this factsheet will discuss human exposure to chlorpyrifos and the ecological effects of chlorpyrifos. BY CAROLINE COX mary agricultural uses are for oranges, al- plications are made annually. -
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. -
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 -
Contracting for Pest Control Service in Public Buildings ______A
Contracting for Pest Control Service in Public Buildings _____________________________________________________ A. Greene Regional Entomologist U. S. General Services Administration Three Core Principles of Public Sector Contracting ______________________________________________________ Contracting is Law The Principle of Fairness Competition must be maximized No bidder can be unfairly excluded The Principle of Frugality Minimum requirements only The goal should be greatest value The Six Principal Components of Service Contracting ______________________________________________________ Program management Type of contract Estimating cost Method of award Statement of work Quality assurance 1. Program Management ______________________________________________________ Who will be the Integrated Pest MANAGER? IPM = Integrated Procurement Mission 2. Type of Contract ________________________________________________________ Janitorial service or separate contract? How will the work be ordered & paid for? Firm-Fixed Price Indefinite Delivery __________________________________________________________The Firm-Fixed-Price Contract Advantages: Minimum administrative burden Easiest type of contract to budget for Disadvantages: Highly inflated prices if bidders feel there are high cost risks, e.g.: Excessive monitoring/recordkeeping requirements High-cost, indeterminate specialty work included (e.g. termites, bird deterrence, wildlife trapping) __________________________________________________________The Firm-Fixed-Price Contract Needless (& Expensive) -
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.