Litter Beetle Management in Poultry Barns by Danny L
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Cypermethrin
International Environmental Health Criteria 82 Cypermethrin Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization WORLD HEALTH ORGANIZATION GENEVA 1989 Other titles available in the ENVIRONMENTAL HEALTH CRITERIA series include: 1. Mercury 2. Polychlorinated Biphenyls and Terphenyls 3. Lead 4. Oxides of Nitrogen 5. Nitrates, Nitrites, and N-Nitroso Compounds 6. Principles and Methods for Evaluating the Toxicity of Chemicals, Part 1 7. Photochemical Oxidants 8. Sulfur Oxides and Suspended Particulate Matter 9. DDT and its Derivatives 10. Carbon Disulfide 11. Mycotoxins 12. Noise 13. Carbon Monoxide 14. Ultraviolet Radiation 15. Tin and Organotin Compounds 16. Radiofrequency and Microwaves 17. Manganese 18. Arsenic 19. Hydrogen Sulfide 20. Selected Petroleum Products 21. Chlorine and Hydrogen Chloride 22. Ultrasound 23. Lasers and Optical Radiation 24. Titanium 25. Selected Radionuclides 26. Styrene 27. Guidelines on Studies in Environmental Epidemiology 28. Acrylonitrile 29. 2,4-Dichlorophenoxyacetic Acid (2,4-D) 30. Principles for Evaluating Health Risks to Progeny Associated with Exposure to Chemicals during Pregnancy 31. Tetrachloroethylene 32. Methylene Chloride 33. Epichlorohydrin 34. Chlordane 35. Extremely Low Frequency (ELF) Fields 36. Fluorine and Fluorides 37. Aquatic (Marine and Freshwater) Biotoxins 38. Heptachlor 39. Paraquat and Diquat 40. Endosulfan 41. Quintozene 42. Tecnazene 43. Chlordecone 44. Mirex continued on p. 156 -
Characterization of Residential Pest Control Products Used in Inner City Communities in New York City
Journal of Exposure Science and Environmental Epidemiology (2010), 1–11 r 2010 Nature America, Inc. All rights reserved 1559-0631/10 www.nature.com/jes Characterization of residential pest control products used in inner city communities in New York City MEGAN K. HORTONa, J. BRYAN JACOBSONb, WENDY MCKELVEYb, DARRELL HOLMESa, BETTY FINCHERc, AUDREY QUANTANOc, BEINVENDIDA PAEZ DIAZc, FAYE SHABBAZZc, PEGGY SHEPARDc, ANDREW RUNDLEa AND ROBIN M. WHYATTa aColumbia Center for Children’s Environmental Health, Mailman School of Public Health, Columbia University, New York, New York, USA bNew York City Department of Health and Mental Hygiene, New York, New York, USA cWest Harlem Environmental Action, New York, New York, USA The Columbia Center for Children’s Environmental Health (CCCEH) previously reported widespread residential insecticide use in urban communities in New York City. Research suggests that pyrethroids are replacing organophosphates (OPs) in response to 2000–2001 US EPA pesticide regulations restricting OP use. A systematic assessment of active ingredients used for residential pest control is lacking. We queried a database of pesticide applications reported by licensed applicators between 1999 and 2005 and surveyed pest control products available in 145 stores within 29 zip codes in the CCCEH catchment area including Northern Manhattan and the South Bronx. Pyrethroids, pyrethrins, piperonyl butoxide, and hydramethylnon were the most common insecticide active ingredients reported as used by licensed pesticide applicators within the 29 zip codes of the CCCEH catchment area between 1999 and 2005. Use of certain pyrethroids and some non-spray insecticides such as fipronil and boric acid increased significantly by year (logistic regression, OR41.0, Po0.05), whereas use of OPs, including chlorpyrifos and diazinon decreased significantly by year (logistic regression, ORo1.0, Po0.05). -
Potential for Resistance to Pyriproxyfen: a Promising
SEPTEMBER 199I RnsrsreNcn PornNtrer, To PyRrpRoxyFEN POTENTIAL FOR RESISTANCETO PYRIPROXYFEN:A PROMISING NEW MOSQUITO LARVICIDE C. H. SCHAEFER eNo F. S. MULLIGAN III1 Mosquito Control Researchlnboratory, IJniuersity of California, 9240 S. Riuerbend,Auenue, Parli.er, CA 93648 ABSTRACT. An organophosphorus-resistantstrain of Culcx quin4u.efasciaturwas pressured with pyriproxyfen for 1? genbrations.Egg viability began declining in the F? generation and becamelower as the ielection procesi continued; by the F17generation egg viabilif was too low to proceed further. Susceptibility tests on larvae of the Fs, Fro, Frr, and Frz generationsshowed no indication of increased tolerance to pyriproxyfen. INTRODUCTION of chlorpyrifos and related compounds due to insecticide resistance(Stewart 1975). Pyriproxyfen, 2-[1-methyl-2-(4-phenoxy- Another consideration is the potential for phenoxy)ethoxyl pyridine, is also known as S- cross-resistanceof strains which have already 31183and by the trademark names Nylar@and been selectedfor insecticide resistance.For ex- [email protected] compound acts as a juvenile ample, when a new benzamide larvicide which hormone mimic; it doesnot producedirect larval had a high degreeof efficacy against mosquitoes toxicity but disrupts the normal processof insect was used to pressure an organophosphorus-re- development, which results in pupal mortality sistant (OP-R) strain of Cx. quirquefasciatu.s, or in the production of abnormal adults. Pyri- cross-resistancebecame apparent after only 4 proxyfen is highly active against a variety of generationsof selection (Schaeferet al. 1981). insects of public health importance including Information on how quickly insecticide-resist- cockroaches (Chow and Yang 1990), fleas ant strains might develop tolerance to pyri- (Palma and Meola 1990),the tsetsefly (Langley proxyfen was sought.Insecticide pressure exper- et al. -
Chemicals Implicated in Colony Collapse Disorder
Chemicals Implicated While research is underway to determine the cause of Colony Collapse Disorder (CCD), pesticides have emerged as one of the prime suspects. Recent bans in Europe attest to the growing concerns surrounding pesticide use and honeybee decline. Neonicotinoids Neonicotinoids are a relatively new class of insecticides that share a common mode of action that affect the central nervous system of insects, resulting in paralysis and death. They include imidacloprid, acetamiprid, clothianidin, dinotefuran, nithiazine, thiacloprid and thiamethoxam. According to the EPA, uncertainties have been identified since their initial registration regarding the potential environmental fate and effects of neonicotinoid pesticides, particularly as they relate to pollinators. Studies conducted in the late 1990s suggest that neonicotinic residues can accumulate in pollen and nectar of treated plants and represent a potential risk to pollinators. There is major concern that neonicotinoid pesticides may play a role in recent pollinator declines. Neonicotinoids can also be persistent in the environment, and when used as seed treatments, translocate to residues in pollen and nectar of treated plants. The potential for these residues to affect bees and other pollinators remain uncertain. Despite these uncertainties, neonicotinoids are beginning to dominate the market place, putting pollinators at risk. The case of the neonicotinoids exemplifies two critical problems with current registration procedures and risk assessment methods for pesticides: the reliance on industry-funded science that contradicts peer-reviewed studies and the insufficiency of current risk assessment procedures to account for sublethal effects of pesticides. • Imidacloprid Used in agriculture as foliar and seed treatments, for indoor and outdoor insect control, home gardening and pet products, imidacloprid is the most popular neonicotinoid, first registered in 1994 under the trade names Merit®, Admire®, Advantage TM. -
Historical Perspectives on Apple Production: Fruit Tree Pest Management, Regulation and New Insecticidal Chemistries
Historical Perspectives on Apple Production: Fruit Tree Pest Management, Regulation and New Insecticidal Chemistries. Peter Jentsch Extension Associate Department of Entomology Cornell University's Hudson Valley Lab 3357 Rt. 9W; PO box 727 Highland, NY 12528 email: [email protected] Phone 845-691-7151 Mobile: 845-417-7465 http://www.nysaes.cornell.edu/ent/faculty/jentsch/ 2 Historical Perspectives on Fruit Production: Fruit Tree Pest Management, Regulation and New Chemistries. by Peter Jentsch I. Historical Use of Pesticides in Apple Production Overview of Apple Production and Pest Management Prior to 1940 Synthetic Pesticide Development and Use II. Influences Changing the Pest Management Profile in Apple Production Chemical Residues in Early Insect Management Historical Chemical Regulation Recent Regulation Developments Changing Pest Management Food Quality Protection Act of 1996 The Science Behind The Methodology Pesticide Revisions – Requirements For New Registrations III. Resistance of Insect Pests to Insecticides Resistance Pest Management Strategies IV. Reduced Risk Chemistries: New Modes of Action and the Insecticide Treadmill Fermentation Microbial Products Bt’s, Abamectins, Spinosads Juvenile Hormone Analogs Formamidines, Juvenile Hormone Analogs And Mimics Insect Growth Regulators Azadirachtin, Thiadiazine Neonicotinyls Major Reduced Risk Materials: Carboxamides, Carboxylic Acid Esters, Granulosis Viruses, Diphenyloxazolines, Insecticidal Soaps, Benzoyl Urea Growth Regulators, Tetronic Acids, Oxadiazenes , Particle Films, Phenoxypyrazoles, Pyridazinones, Spinosads, Tetrazines , Organotins, Quinolines. 3 I Historical Use of Pesticides in Apple Production Overview of Apple Production and Pest Management Prior to 1940 The apple has a rather ominous origin. Its inception is framed in the biblical text regarding the genesis of mankind. The backdrop appears to be the turbulent setting of what many scholars believe to be present day Iraq. -
STRUCTURAL PEST CONTROL APPLICATOR: GUIDANCE DOCUMENT Label Changes for Pyrethroid Non-Agricultural Outdoor Products
Structural Pest Section 19 Martin Luther King, Jr. Dr. Atlanta, Georgia 30334-4201 Phone: (404) 656-3641 STRUCTURAL PEST CONTROL APPLICATOR: GUIDANCE DOCUMENT Label Changes for Pyrethroid Non-agricultural Outdoor Products Why are these labels being changed? Recently, pesticide products containing insecticides in the chemical class known as pyrethroids have undergone a series of label changes. These changes are in response to water quality monitoring studies that found significant amounts of pyrethroid insecticides in sediments of urban creeks. Pyrethroids are highly toxic to aquatic organisms, accumulate in sediments and thus produce an increased risk of causing harm to invertebrates and other creatures living within sediments. What is currently happening? The Environmental Protection Agency (EPA) is requiring revised “Environmental Hazard Statements” and general “Directions for Use” for pyrethroid pesticide products used in non-agricultural outdoor settings. These label changes are intended to reduce pyrethroid movement into non-target areas through runoff or spray drift that may occur during applications. Pyrethroid products containing the new label language are now in the marketplace. Both consumer products and those designed for use by pest management professionals (PMPs) are affected by these changes. These new requirements will result in changing use patterns for the prevention and control of general household pests, lawn and ornamental pests as well as termites and other wood-destroying organisms. New language will be found on pyrethroid products formulated as liquid concentrates, broadcast granules, dusts and ready-to-use liquid mixtures. Older products that do not have new label restrictions can continue to be used according to the attached label. Broadcast applications to large surfaces such as exterior walls of buildings, patios, or concrete walkways will no longer be allowed. -
Interim Reregistration Eligibility Decision (IRED) for Carbaryl Is Being Published in the Federal Register
CARBARYL IRED FACTS [Revised 10/22/04] Action and Rationale EPA has assessed the risks of carbaryl and, on June 30, 2003, reached an Interim Reregistration Eligibility Decision (IRED) for this carbamate pesticide. A revised IRED document is being released for public comment on October 27, 2004. A letter from EPA to registrants dated October 22, 2004 precedes the IRED document and explains the revisions made. Although all uses may not meet the current safety standard and some uses may pose unreasonable risks to human health and the environment, these effects can be mitigated by the measures identified in the Carbaryl IRED. Provided that these risk mitigation measures are adopted, aggregate risks for carbaryl alone will be within acceptable levels and the pesticide will be eligible for reregistration once EPA considers the cumulative risks of the carbamates. Carbaryl is one of the most widely used broad-spectrum insecticides in agriculture, professional turf management and ornamental production, and residential pet, lawn, and garden markets. Although dietary (food and drinking water) exposures are not of concern, carbaryl does pose risks of concern from uses in and around the home. With mitigation measures discussed in the IRED document, carbaryl will fit into its own “risk cup” and will not pose significant aggregate risk concerns. Carbaryl also poses risks of concern to occupational handlers who mix, load, and apply the pesticide in agricultural sites, and to workers who may be exposed upon re-entering treated agricultural areas. Carbaryl poses ecological risks, particularly to honey bees and aquatic invertebrates. With mitigation measures, these occupational and ecological risks also will not be of concern for reregistration. -
Pesticides EPA 738-R-06-004 Environmental Protection and Toxic Substances June 2006 Agency (7508C) ______Reregistration Eligibility Decision for Pyrethrins
United States Prevention, Pesticides EPA 738-R-06-004 Environmental Protection And Toxic Substances June 2006 Agency (7508C) _________________________________________________________________ Reregistration Eligibility Decision for Pyrethrins List B Case No. 2580 Reregistration Eligibility Decision (RED) Document for Pyrethrins Approved by: /S/ . Debra Edwards, Ph. D. Director Special Review and Reregistration Division Date: June 7, 2006 . Page 2 of 108 TABLE OF CONTENTS Executive Summary ....................................................................................................................... 7 I. Introduction......................................................................................................................... 11 II. Chemical Overview........................................................................................................... 12 A. Regulatory History...................................................................................................... 12 B. Chemical Identification .............................................................................................. 13 C. Use Profile.................................................................................................................... 16 1. Pyrethrins Use Profile................................................................................................. 16 III. Summary of Pyrethrins Risk Assessments ............................................................... 17 A. Human Health Risk Assessment............................................................................... -
Quantitative Determination of Pyrethroids, Pyrethrins, and Piperonyl Butoxide in Surface Water by High-Resolution Gas Chromatography/High-Resolution Mass Spectrometry
J. Agric. Food Chem. 2006, 54, 6957−6962 6957 Quantitative Determination of Pyrethroids, Pyrethrins, and Piperonyl Butoxide in Surface Water by High-Resolution Gas Chromatography/High-Resolution Mass Spectrometry MILLION BEKELE WOUDNEH* AXYS Analytical Services Ltd., 2045 Mills Road West, Sidney, British Columbia V8L 3S8, Canada DANIEL RAY OROS San Francisco Estuary Institute, 7770 Pardee Lane, 2nd Floor, Oakland, California 94621 A new method for determination of pyrethroids, pyrethrins, and piperonyl butoxide (PBO) by high- resolution gas chromatography/high-resolution mass spectrometry (HRGC/HRMS) was developed for surface water samples. The method is based on sampling 100 L of ambient surface water with a solid phase extraction (SPE) technique that uses both wound glass fiber filters for collecting the particulate-associated chemicals and XAD-2 resin for collecting the dissolved chemicals. The method detection limits of the analytes ranged from 0.58 to 8.16 ng/sample, which is equivalent to a detection limit range of 0.0058-0.082 ng/L for a 100 L water sample collected by the SPE technique. The SPE when coupled with HRGC/HRMS was a suitable match for detecting these chemicals at subnanogram per liter ranges that are toxicologically significant to aquatic organisms. To confirm the utility of this method for environmental applications, pyrethroids and PBO were found at subnanogram per liter concentrations in surface water samples collected from five tributaries (primarily urban creeks) of the San Francisco Bay, California. KEYWORDS: Pyrethroids; pesticides; XAD-2; HRGC/HRMS; San Francisco Bay INTRODUCTION by inhibiting a group of enzymes (mixed-function oxidases) that are involved in pyrethroid detoxification, which as a result The decision of the U.S. -
Thrips on Seedling Cotton: Related Problems and Control E Burris
Louisiana State University LSU Digital Commons LSU Agricultural Experiment Station Reports LSU AgCenter 1989 Thrips on seedling cotton: related problems and control E Burris Follow this and additional works at: http://digitalcommons.lsu.edu/agexp Recommended Citation Burris, E, "Thrips on seedling cotton: related problems and control" (1989). LSU Agricultural Experiment Station Reports. 881. http://digitalcommons.lsu.edu/agexp/881 This Article is brought to you for free and open access by the LSU AgCenter at LSU Digital Commons. It has been accepted for inclusion in LSU Agricultural Experiment Station Reports by an authorized administrator of LSU Digital Commons. For more information, please contact [email protected]. L. l NOV 011989 RA. Contents Page Introduction . 3 Materials and Methods . 6 General Experimental Design.. .. ... .... ........ .................... 6 Seed Treatments . 7 Soil Treatments . 7 Foliar Treatments . 7 Thrips Population Monitoring . 7 Measurements of Cotton Growth and Yield . 8 Results and Discussion ... .. ........ ... .... .. ..... ..... ... .............. .. 8 Potential [mpact of Thrips on Plant Height and Seed Cotton Yield . 9 Efficacy of Selected Insecticide . 9 Interactions of Insecticides U ed for Thrip Control with Other Pe ts and Pe ticide . 13 Summary and Conclusions ..... ..... ................... .. ....... ........ 16 Information on Chemicals U ed in Te t. .. .... .. ..................... 18 Literature Cited ........................... ... .. .. .. .... ........ .. ........ 19 The mention of a pesticide in thi publication i intended only as a report of research and does not constitute a guarantee or warranty by the Louisiana Agricultural Experiment Station nor an endor ement over other product of a similar nature not mentioned. Some uses of pesticide di cus ed here have not nece arily been registered. All consumer uses of pe ticides must be registered by appropriate late and federal agencie . -
US EPA, Pesticide Product Label, PYRIPROXYFEN 10% EC,06/24
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, DC 20460 OFFICE OF CHEMICAL SAFETY AND POLLUTION PREVENTION June 24, 2021 Lisa Adamson Regulatory Manager Control Solutions, Inc. 5903 Genoa-Red Bluff Pasadena, TX 77507-1041 Subject: Registration Review Label Mitigation for Pyriproxyfen Product Name: Pyriproxyfen 10% EC EPA Registration Number: 53883-280 Application Date: 02/21/2020 Decision Number: 560323 Dear Ms. Adamson: The Agency, in accordance with the Federal Insecticide, Fungicide and Rodenticide Act (FIFRA), as amended, has completed reviewing all the information submitted with your application to support the Registration Review of the above referenced product in connection with the Pyriproxyfen Interim Decision, and has concluded that your submission is acceptable. The label referred to above, submitted in connection with registration under FIFRA, as amended, is acceptable. Should you wish to add/retain a reference to the company’s website on your label, then please be aware that the website becomes labeling under the Federal Insecticide Fungicide and Rodenticide Act and is subject to review by the Agency. If the website is false or misleading, the product would be misbranded and unlawful to sell or distribute under FIFRA section 12(a)(1)(E). 40 CFR 156.10(a)(5) list examples of statements EPA may consider false or misleading. In addition, regardless of whether a website is referenced on your product’s label, claims made on the website may not substantially differ from those claims approved through the registration process. Therefore, should the Agency find or if it is brought to our attention that a website contains false or misleading statements or claims substantially differing from the EPA approved registration, the website will be referred to the EPA’s Office of Enforcement and Compliance. -
Colony Collapse Disorder in Relation to Human-Produced Toxins: What's
Colony Collapse Disorder in relation to human-produced toxins: What’s the buzz all about? Available at: http://www.sawyoo.com/postpic/2013/09/honey-bee-hives_77452.jpg Last accessed: 17/04/2017 Abstract: p2 Introduction: p3 Insecticides: p5 Herbicides & fungicides: p7 Miticides & other preventative measures: p9 “Inactive” ingredients: p10 Synergies between pesticides: p11 Conclusions: p12 Discussion: p12 References: p14 1 Abstract In recent years, the global population of pollinating animals has been in decline. The honey bee in particular is one of the most important and well known pollinators and is no exception.The Western honey bee Apis mellifera, the most globally spread honey bee species suffers from one problem in particular. Colony Collapse Disorder (CCD), which causes the almost all the worker bees to abandon a seemingly healthy and food rich hive during the winter. One possible explanation for this disorder is that it is because of the several human produced toxins, such as insecticides, herbicides, fungicides and miticides. So the main question is: Are human-produced toxins the primary cause of CCD? It seems that insecticides and, in particular, neonicotinoid insecticides caused increased mortality and even recreated CCD-like symptoms by feeding the bees with neonicotinoids. Herbicides seem relatively safe for bees, though they do indirectly reduce the pollen diversity, which can cause the hive to suffer from malnutrition. Fungicides are more dangerous, causing several sublethal effects, including a reduced immune response and changing the bacterial gut community. The levels of one fungicide in particular, chlorothalonil, tends to be high in hives. Miticides levels tend to be high in treated hives and can cause result in bees having a reduced lifespan.