An Overview on the Potential Hazards of Pyrethroid Insecticides in Fish, with Special Emphasis on Cypermethrin Toxicity
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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 -
Exposure of Phlebotomus Argentipes to Alpha-Cypermethrin, Permethrin, and DDT Using CDC Bottle Bioassays to Assess Insecticide Susceptibility
Utah State University DigitalCommons@USU Undergraduate Honors Capstone Projects Honors Program 5-2020 Exposure of Phlebotomus Argentipes to Alpha-Cypermethrin, Permethrin, and DDT Using CDC Bottle Bioassays to Assess Insecticide Susceptibility Jacob Rex Andersen Utah State University Follow this and additional works at: https://digitalcommons.usu.edu/honors Part of the Biology Commons Recommended Citation Andersen, Jacob Rex, "Exposure of Phlebotomus Argentipes to Alpha-Cypermethrin, Permethrin, and DDT Using CDC Bottle Bioassays to Assess Insecticide Susceptibility" (2020). Undergraduate Honors Capstone Projects. 485. https://digitalcommons.usu.edu/honors/485 This Thesis is brought to you for free and open access by the Honors Program at DigitalCommons@USU. It has been accepted for inclusion in Undergraduate Honors Capstone Projects by an authorized administrator of DigitalCommons@USU. For more information, please contact [email protected]. © 2020 Jacob Rex Andersen All Rights Reserved i Abstract Background: Insecticide resistance for sand flies is a concern since sand flies are vectors for Leishmania spp. parasites which cause leishmaniasis affecting millions of people each year. The CDC bottle bioassay is used to assess resistance by comparing known insecticide diagnostic doses and diagnostic times from an insecticide-susceptible population. The objective of this study was to determine diagnostic doses and diagnostic times for α-cypermethrin and the lethal dose for 50% and 90% mortality for α- cypermethrin, permethrin, and DDT for Phlebotomus argentipes. Methods: The CDC bottle bioassays were performed in 1,000 mL glass bottles with 15- 25 sand flies from a laboratory strain of insecticide-susceptible P. argentipes. A range of concentrations of α-cypermethrin, permethrin, and DDT were evaluated. -
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). -
Evaluation of Fluralaner and Afoxolaner Treatments to Control Flea
Dryden et al. Parasites & Vectors (2016) 9:365 DOI 10.1186/s13071-016-1654-7 RESEARCH Open Access Evaluation of fluralaner and afoxolaner treatments to control flea populations, reduce pruritus and minimize dermatologic lesions in naturally infested dogs in private residences in west central Florida USA Michael W. Dryden1*, Michael S. Canfield2, Kimberly Kalosy1, Amber Smith1, Lisa Crevoiserat1, Jennifer C. McGrady1, Kaitlin M. Foley1, Kathryn Green2, Chantelle Tebaldi2, Vicki Smith1, Tashina Bennett1, Kathleen Heaney3, Lisa Math3, Christine Royal3 and Fangshi Sun3 Abstract Background: A study was conducted to evaluate and compare the effectiveness of two different oral flea and tick products to control flea infestations, reduce pruritus and minimize dermatologic lesions over a 12 week period on naturally infested dogs in west central FL USA. Methods: Thirty-four dogs with natural flea infestations living in 17 homes were treated once with a fluralaner chew on study day 0. Another 27 dogs living in 17 different homes were treated orally with an afoxolaner chewable on day 0, once between days 28–30 and once again between days 54–60. All products were administered according to label directions by study investigators. Flea populations on pets were assessed using visual area counts and premise flea infestations were assessed using intermittent-light flea traps on days 0, 7, 14, 21, and once between days 28–30, 40–45, 54–60 and 82–86. Dermatologic assessments were conducted on day 0 and once monthly. Pruritus assessments were conducted by owners throughout the study. No concurrent treatments for existing skin disease (antibiotics, anti-inflammatories, anti-fungals) were allowed. -
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. -
4. Chemical and Physical Information
PYRETHRINS AND PYRETHROIDS 131 4. CHEMICAL AND PHYSICAL INFORMATION 4.1 CHEMICAL IDENTITY The naturally-occurring pyrethrins, extracted from chrysanthemum flowers, are esters of chrysanthemic acid (Pyrethrin I, Cinerin I, and Jasmolin I) and esters of pyrethric acid (Pyrethrin II, Cinerin II, and Jasmolin II). In the United States, the pyrethrum extract is standardized as 45–55% w/w total pyrethrins. The typical proportion of Pyrethrins I to II is 0.2:2.8, while the ratio of pyrethrins:cinerins:jasmolins is 71:21:7 (Tomlin 1997). Information regarding the chemical identity of the pyrethrins is presented in Table 4-1. Pyrethroids are synthetic esters derived from the naturally-occurring pyrethrins. One exception to the axiom that all pyrethroids are esters of carboxylic acids is noteworthy. There is a group of oxime ethers that exhibits insecticidal activity similar in nature to the pyrethrins and pyrethroid esters (Davies 1985). Little data exist regarding these compounds, and no commercial products have been produced. Commercially available pyrethroids include allethrin, bifenthrin, bioresmethrin, cyfluthrin, cyhalothrin, cypermethrin, deltamethrin, esfenvalerate (fenvalerate), flucythrinate, flumethrin, fluvalinate, fenpropathrin, permethrin, phenothrin, resmethrin, tefluthrin, tetramethrin, and tralomethrin. Information regarding the chemical identity of pyrethroids is shown in Table 4-2. With the exception of deltamethrin, pyrethroids are a complex mixture of isomers rather than one single pure compound. For pyrethroids possessing the cyclopropane moiety, isomerism about the cyclopropane ring greatly influences the toxicity of these insecticides. The presence of two chiral centers in the ring results in two pairs of diastereomers. The diastereomers and their nonsuperimposable mirror images (enantiomers) are illustrated in Figure 4-1. -
Interim Review of Chlorfenvinphos
National Registration Authority for Agricultural and Veterinary Chemicals Section 3 AGRICULTURAL ASSESSMENT 1. INTRODUCTION........................................................................................................................ 6 1.1 Registration Status...................................................................................................................... 6 1.2 Methods of Application.............................................................................................................. 8 1.3 Permits..................................................................................................................................... 11 1.4 Performance Questionnaires ..................................................................................................... 11 2. EFFICACY ASSESSMENT....................................................................................................... 16 2.1 Background ............................................................................................................................. 16 2.2 Evaluation of Efficacy............................................................................................................... 16 2.3 Alternatives.............................................................................................................................. 16 2.4 Side Effects.............................................................................................................................. 18 2.5 Resistance Management .......................................................................................................... -
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 . -
MP144: Ornamental Insect Control for Homeowners
ORNAMENTAL INSECT CONTROL FOR HOMEOWNERS OUTDOOR ORNAMENTAL INSECT CONTROL Amount Formulation Pest Insecticide and Formulation* Per Gallon Spray Remarks and Precautions Aphid acephate Follow label directions. acetamiprid Follow label directions. beta-cyfluthrin 0.0015% + imidacloprid 0.012% ready to use Follow label directions. (Bayer Advanced Dual Action Rose & Flower Insect Killer Ready-To-Use) bifenthrin Follow label directions. cyfluthrin Follow label directions. dinotefuran (Ortho Tree & Shrub Insect Control Plus Per label directions. Miracle-Gro Plant Food Concentrate 0.43%, Ortho Tree & Shrub Insect Control Granules 2.0%) horticultural oils 1%-2% Follow label directions. imidacloprid (Bayer Advanced) Follow label directions. insecticidal soap 1%-2% Thorough coverage is necessary. Spray must contact pests to be effective. Repeat spray three times at 5- to 7-day intervals. malathion (various) Follow label directions. pyrethrin/pyrethrum Follow label directions. pyrethroids (various) ready to use and concentrate Follow label directions. Azalea Leaf Miner acephate (Orthene TTO) 1 tsp Per label directions. beta-cyfluthrin 0.0015% + imidacloprid 0.012% ready to use Follow label directions. (Bayer Advanced Dual Action Rose & Flower Insect Killer Ready-To-Use) dinotefuran (Ortho Tree & Shrub Insect Control Plus Per label directions. Miracle-Gro Plant Food Concentrate 0.43%, Ortho Tree & Shrub Insect Control Granules 2.0%) imidacloprid (Bayer Advanced) Bagworm Bacillus thuringiensis 2 tsp Per label directions. (Biotrol WP, Thuricide, Sok-Bt) beta-cyfluthrin 0.0015% + imidacloprid 0.012% ready to use Follow label directions. (Bayer Advanced Dual Action Rose & Flower Insect Killer Ready-To-Use) malathion (various) Per label directions. In winter, hand-pick and burn if only a few bagworms are present. -
Pyrethroid and DDT Resistance and Organophosphate Susceptibility Among Anopheles Spp
DISPATCHES Pyrethroid and DDT Resistance and Organophosphate Susceptibility among Anopheles spp. Mosquitoes, Western Kenya Christine L. Wanjala, Jernard P. Mbugi, western Kenya (Figure 1). Malaria vector dynamics and Edna Ototo, Maxwell Gesuge, Yaw A. Afrane, parasite prevalence have been studied in 3 sites (9), and Harrysone E. Atieli, Guofa Zhou, ITN coverage was generally >80% (10). Bungoma, Emu- Andrew K. Githeko, Guiyun Yan tete, Iguhu, and Emakakha are in the highland-fringe ma- laria epidemic area; Chulaimbo, Ahero, and Kisian are in We conducted standard insecticide susceptibility testing the malaria-endemic basin region of Lake Victoria (low- across western Kenya and found that the Anopheles gam- land). All sample sites were in rural or suburban areas. biae mosquito has acquired high resistance to pyrethroids Agricultural and public health use of insecticides in and DDT, patchy resistance to carbamates, but no resis- tance to organophosphates. Use of non–pyrethroid-based each study site was surveyed by using questionnaire sur- vector control tools may be preferable for malaria preven- veys in 30 randomly selected households per site. Mos- tion in this region. quito larvae were collected from each study site, fed with TetraMin fish food (Spectrum Brands, Inc., Blacksburg, VA, USA), and raised to adults in the insectary at the Ke- uring the past decade, a massive scale-up of insecticide- nya Medical Research Institute in Kisumu. The insectary Dtreated nets (ITNs) and indoor residual spraying (IRS) was not regulated for temperature and humidity; ambient of insecticides in malaria-endemic areas worldwide have led temperature (average ≈24°C) and humidity (≈75% rela- to a substantial reduction in mosquitoes and, paired with the tive humidity) were used for the study. -
Using Liver Mirna Profiles to Predict Chemical Hepatocarcinogenesis”
“Using liver miRNA profiles to predict chemical hepatocarcinogenesis” By Costas Koufaris A thesis submitted to Imperial College London for the degree of Doctor of Philosophy Department of Surgery and Cancer Biomolecular Medicine Imperial College London April- 12011 - ABSTRACT Industrial, agricultural, and pharmaceutical requirements drive the development of a plethora of new chemical entities each year, many of which -for example drugs, pesticides, and food additives- have to be assessed for potential human health hazard. The current benchmark for risk assessement is the lifetime rodent bioassay which is expensive, time-consuming, laborious, requires the sacrifice of numerous animals, and is often irrelevant to humans. Hence alternative strategies to the rodent lifetime bioassay for prediction of chemical carcinogens are being pursued, especially for the liver which is an organ frequently affected by exogenous chemicals due to its detoxifying and metabolic roles. Numerous studies in recent years support the important role of microRNAs in cancer development, including hepatocellular carcinoma. The principal hypothesis of this project was that hepatic microRNA signatures can contribute to the earlier prediction of chemical hepatocarcinogens. Examination of livers from male Fischer rats treated with six chemical hepatocarcinogens, with diverse mode of actions for 90 days revealed that all the tested hepatocarcinogens affected the liver miRNAome from that early stage. Interestingly, a small set of microRNAs were identified whose expression -
Download Report
final report Project Code: AHW.003 Prepared by: Agrisearch Services Pty Ltd Date published: July 2000 PUBLISHED BY Meat and Livestock Australia Limited Locked Bag 991 NORTH SYDNEY NSW 2059 Monitoring of insecticide resistance in field sampled buffalo flies Meat & Livestock Australia acknowledges the matching funds provided by the Australian Government to support the research and development detailed in this publication. This publication is published by Meat & Livestock Australia Limited ABN 39 081 678 364 (MLA). Care is taken to ensure the accuracy of the information contained in this publication. However MLA cannot accept responsibility for the accuracy or completeness of the information or opinions contained in the publication. You should make your own enquiries before making decisions concerning your interests. Reproduction in whole or in part of this publication is prohibited without prior written consent of MLA. Table Of Contents 1. SUMMARy ................................................................................................................2 2. INTRODUCTION .......................................................................................................5 3. EXPERIMENTAL DETAILS .......................................................................................5 3.1 BIOASSAY METHOD .................................................................................................5 3.2 FARMS AND REGIONS SURVEyED .............................................................................6 3.3 QUESTIONNAIRE .....................................................................................................7