Recent Advances on Detection of Insecticides Using Optical Sensors
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Restricted Use Product Summary Report
Page 1 of 17 Restricted Use Product Summary Report (January 19, 2016) Percent Active Registration # Name Company # Company Name Active Ingredient(s) Ingredient 4‐152 BONIDE ORCHARD MOUSE BAIT 4 BONIDE PRODUCTS, INC. 2 Zinc phosphide (Zn3P2) 70‐223 RIGO EXOTHERM TERMIL 70 VALUE GARDENS SUPPLY, LLC 20 Chlorothalonil 100‐497 AATREX 4L HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 42.6 Atrazine 100‐585 AATREX NINE‐O HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 88.2 Atrazine 100‐669 CURACRON 8E INSECTICIDE‐MITICIDE 100 SYNGENTA CROP PROTECTION, LLC 73 Profenofos 100‐817 BICEP II MAGNUM HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 33; 26.1 Atrazine; S‐Metolachlor 100‐827 BICEP LITE II MAGNUM HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 28.1; 35.8 Atrazine; S‐Metolachlor 100‐886 BICEP MAGNUM 100 SYNGENTA CROP PROTECTION, LLC 33.7; 26.1 Atrazine; S‐Metolachlor 100‐898 AGRI‐MEK 0.15 EC MITICIDE/INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 2 Abamectin 100‐903 DENIM INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 2.15 Emamectin benzoate 100‐904 PROCLAIM INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 5 Emamectin benzoate 100‐998 KARATE 1EC 100 SYNGENTA CROP PROTECTION, LLC 13.1 lambda‐Cyhalothrin 100‐1075 FORCE 3G INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 3 Tefluthrin Acetochlor; Carbamothioic acid, dipropyl‐ 100‐1083 DOUBLEPLAY SELECTIVE HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 16.9; 67.8 , S‐ethyl ester 100‐1086 KARATE EC‐W INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 13.1 lambda‐Cyhalothrin 100‐1088 SCIMITAR GC INSECTICIDE 100 SYNGENTA CROP PROTECTION, -
Propoxur United States Environmental Protection Agency
United States Prevention, Pesticides EPA738-R-97-009 Environmental Protection And Toxic Substances August 1997 Agency (7508W) Reregistration Eligibility Decision (RED) PROPOXUR UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C. 20460 OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES CERTIFIED MAIL Dear Registrant: I am pleased to announce that the Environmental Protection Agency has completed its reregistration eligibility review and decisions on the pesticide chemical case propoxur. The enclosed Reregistration Eligibility Decision (RED) contains the Agency's evaluation of the data base of this chemical, its conclusions of the potential human health and environmental risks of the current product uses, and its decisions and conditions under which these uses and products will be eligible for reregistration. The RED includes the data and labeling requirements for products for reregistration. It may also include requirements for additional data (generic) on the active ingredient to confirm the risk assessments. To assist you with a proper response, read the enclosed document entitled "Summary of Instructions for Responding to the RED." This summary also refers to other enclosed documents which include further instructions. You must follow all instructions and submit complete and timely responses. The first set of required responses is due 90 days from the receipt of this letter. The second set of required responses is due 8 months from the date of receipt of this letter. Complete and timely responses will avoid the Agency taking the enforcement action of suspension against your products. If you have questions on the product specific data requirements or wish to meet with the Agency, please contact the Special Review and Reregistration Division representative Bonnie Adler (703) 308-8523. -
Chem7988.Pdf
This article was originally published in a journal published by Elsevier, and the attached copy is provided by Elsevier for the author’s benefit and for the benefit of the author’s institution, for non-commercial research and educational use including without limitation use in instruction at your institution, sending it to specific colleagues that you know, and providing a copy to your institution’s administrator. All other uses, reproduction and distribution, including without limitation commercial reprints, selling or licensing copies or access, or posting on open internet sites, your personal or institution’s website or repository, are prohibited. For exceptions, permission may be sought for such use through Elsevier’s permissions site at: http://www.elsevier.com/locate/permissionusematerial Chemosphere 67 (2007) 2184–2191 www.elsevier.com/locate/chemosphere Assessment of pesticide contamination in three Mississippi Delta oxbow lakes using Hyalella azteca M.T. Moore *, R.E. Lizotte Jr., S.S. Knight, S. Smith Jr., C.M. Cooper USDA-ARS National Sedimentation Laboratory, P.O. Box 1157, Oxford, MS 38655, United States Received 8 September 2006; received in revised form 27 November 2006; accepted 8 December 2006 Available online 26 January 2007 Abstract Three oxbow lakes in northwestern Mississippi, USA, an area of intensive agriculture, were assessed for biological impairment from historic and current-use pesticide contamination using the amphipod, Hyalella azteca. Surface water and sediment samples from three sites in each lake were collected from Deep Hollow, Beasley, and Thighman Lakes from September 2000 to February 2001. Samples were analyzed for 17 historic and current-use pesticides and selected metabolites. -
Carbamate Pesticides Aldicarb Aldicarb Sulfoxide Aldicarb Sulfone
Connecticut General Statutes Sec 19a-29a requires the Commissioner of Public Health to annually publish a list setting forth all analytes and matrices for which certification for testing is required. Connecticut ELCP Drinking Water Analytes Revised 05/31/2018 Microbiology Total Coliforms Fecal Coliforms/ E. Coli Carbamate Pesticides Legionella Aldicarb Cryptosporidium Aldicarb Sulfoxide Giardia Aldicarb Sulfone Carbaryl Physicals Carbofuran Turbidity 3-Hydroxycarbofuran pH Methomyl Conductivity Oxamyl (Vydate) Minerals Chlorinated Herbicides Alkalinity, as CaCO3 2,4-D Bromide Dalapon Chloride Dicamba Chlorine, free residual Dinoseb Chlorine, total residual Endothall Fluoride Picloram Hardness, Calcium as Pentachlorophenol CaCO3 Hardness, Total as CaCO3 Silica Chlorinated Pesticides/PCB's Sulfate Aldrin Chlordane (Technical) Nutrients Dieldrin Endrin Ammonia Heptachlor Nitrate Heptachlor Epoxide Nitrite Lindane (gamma-BHC) o-Phosphate Metolachlor Total Phosphorus Methoxychlor PCB's (individual aroclors) Note 1 PCB's (as decachlorobiphenyl) Note 1 Demands Toxaphene TOC Nitrogen-Phosphorus Compounds Alachlor Metals Atrazine Aluminum Butachlor Antimony Diquat Arsenic Glyphosate Barium Metribuzin Beryllium Paraquat Boron Propachlor Cadmium Simazine Calcium Chromium Copper SVOC's Iron Benzo(a)pyrene Lead bis-(2-ethylhexyl)phthalate Magnesium bis-(ethylhexyl)adipate Manganese Hexachlorobenzene Mercury Hexachlorocyclopentadiene Molybdenum Nickel Potassium Miscellaneous Organics Selenium Dibromochloropropane (DBCP) Silver Ethylene Dibromide (EDB) -
Determination of the Residual Efficacy of Carbamate and Organophosphate
Yewhalaw et al. Malar J (2017) 16:471 DOI 10.1186/s12936-017-2122-3 Malaria Journal RESEARCH Open Access Determination of the residual efcacy of carbamate and organophosphate insecticides used for indoor residual spraying for malaria control in Ethiopia Delenasaw Yewhalaw1,2†, Meshesha Balkew3†, Josephat Shililu4, Sultan Suleman5, Alemayehu Getachew4, Gedeon Ashenbo4, Sheleme Chibsa6, Gunawardena Dissanayake6, Kristen George7, Dereje Dengela8, Yemane Ye‑Ebiyo4 and Seth R. Irish9* Abstract Background: Indoor residual spraying is one of the key vector control interventions for malaria control in Ethiopia. As malaria transmission is seasonal in most parts of Ethiopia, a single round of spraying can usually provide efective protection against malaria, provided the insecticide remains efective over the entire malaria transmission season. This experiment was designed to evaluate the residual efcacy of bendiocarb, pirimiphos-methyl, and two doses of pro‑ poxur on four diferent wall surfaces (rough mud, smooth mud, dung, and paint). Filter papers afxed to wall surfaces prior to spraying were analyzed to determine the actual concentration applied. Cone bioassays using a susceptible Anopheles arabiensis strain were done monthly to determine the time for which insecticides were efective in killing mosquitoes. Results: The mean insecticide dosage of bendiocarb applied to walls was 486 mg/m2 (target 400/mg). This treat‑ ment lasted 1 month or less on rough mud, smooth mud, and dung, but 4 months on painted surfaces. Pirimiphos- methyl was applied at 1854 mg/m2 (target 1000 mg/m2), and lasted between 4 and 6 months on all wall surfaces. Propoxur with a target dose of 1000 mg/m2 was applied at 320 mg/m2, and lasted 2 months or less on all surfaces, except painted surfaces (4 months). -
"U/^ ((*.U \ BIBLIOTHEEK STARINGGEBOUW Volatilization of Tri-Allate, Ethoprophos and Parathion Measured with Four Methods After Spraying on a Sandy Soil
"u/^ ((*.u \ BIBLIOTHEEK STARINGGEBOUW Volatilization of tri-allate, ethoprophos and parathion measured with four methods after spraying on a sandy soil G. Bor F. van den Berg J.H. Smelt R.A. Smidt A.E. van de Peppel-Groen M. Leistra Report 104 DLO Winand Staring Centre, Wageningen (The Netherlands), 1995 1 h FEB. 1998 0000' ABSTRACT Bor, G., F. van den Berg, J.H. Smelt, R.A. Smidt, A.E. van de Peppel-Groen, M. Leistra, 1995. Volatilization of tri-allate, ethoprophos and parathion measured withfour methods after spraying on a sandy soil. Wageningen (The Netherlands), DLO Winand Staring Centre. Report 104. 62 pp.; 9 Figs; 6 Tables; 14 Refs; 3 Annex. At about eleven times after application of tri-allate, ethoprophos and parathion to a sandy soil, their rates of volatilization were determined with the aerodynamic method (AD),th e Bowen-ratio method (BR), the theoretical-profile method (TP) and the Box method (B). The volatilization was highest for tri-allate and lowest for parathion. On the first day after application, the volatilization rate decreased sharply,bu tthereafte r the decreasewa smor egradual .Th edifference s involatilizatio n rate asdetermine d withth eAD ,B R andT Pmethod s werecomparativel y small.Th erate sdetermine d with the Box method were mostly lower than those determined with the other methods. Keywords: aerodynamic method, air quality, air sampling, Bowen ratio method, Box method, field experiment, gas chromatography, pesticide, polystyrene, theoretical-profile method, XAD ISSN 0927-4537 ©1995 DLO Winand Staring Centre for Integrated Land, Soil and Water Research (SC-DLO) P.O. -
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. -
Pesticides May Reduce Lettuce Yield Frank V
High-value crops such as strawberries, tain classes of insecticides on lettuce photo- usually clearly visible. Insecticides applied at broccoli, and iceberg lettuce often receive synthesis, transpiration, and productivity. normal rates and under the right environ- “preventive” or “insurance” pesticide treat- mental conditions may subtly damage a plant ments, which may result in weekly scheduled Insecticides but remain unobserved, because symptoms applications of insecticides. Many times such Insecticides in the various “classes,” such are not visible. treatments are unwarranted economically as chlorinated hydrocarbons (DDT, endrin, During the last few years, plant physiolo- and may reduce yields by detrimental effects and methoxychlor), organophosphates gists at University of California, Riverside, on the plants. Decreases in strawberry yields (guthion, parathion, and methyl-parathion), have developed the dual isotope porometer, due to preventive insecticide treatments in the carbamates (malathion and methomyl), and which provides accurate, simultaneous mea- absence of economically significant pest synthetic pyrethroids (fenvalerate and per- surements of a plant’s photosynthesis and populations have been reported. Research methrin), differ in their effects on plants. Ad- transpiration rates in the field. Entomologists supported by the California Iceberg Lettuce ditionally, the rates, number, and timing of have used the instrument to measure effects Research Advisory Board indicated that head applications may alter a compound’s effect -
B Commission Regulation (Eu)
02010R0037 — EN — 29.09.2018 — 035.001 — 1 This text is meant purely as a documentation tool and has no legal effect. The Union's institutions do not assume any liability for its contents. The authentic versions of the relevant acts, including their preambles, are those published in the Official Journal of the European Union and available in EUR-Lex. Those official texts are directly accessible through the links embedded in this document ►B COMMISSION REGULATION (EU) No 37/2010 of 22 December 2009 on pharmacologically active substances and their classification regarding maximum residue limits in foodstuffs of animal origin (Text with EEA relevance) (OJ L 15, 20.1.2010, p. 1) Amended by: Official Journal No page date ►M1 Commission Regulation (EU) No 758/2010 of 24 August 2010 L 223 37 25.8.2010 ►M2 Commission Regulation (EU) No 759/2010 of 24 August 2010 L 223 39 25.8.2010 ►M3 Commission Regulation (EU) No 761/2010 of 25 August 2010 L 224 1 26.8.2010 ►M4 Commission Regulation (EU) No 890/2010 of 8 October 2010 L 266 1 9.10.2010 ►M5 Commission Regulation (EU) No 914/2010 of 12 October 2010 L 269 5 13.10.2010 ►M6 Commission Regulation (EU) No 362/2011 of 13 April 2011 L 100 26 14.4.2011 ►M7 Commission Regulation (EU) No 363/2011 of 13 April 2011 L 100 28 14.4.2011 ►M8 Commission Implementing Regulation (EU) No 84/2012 of 1 L 30 1 2.2.2012 February 2012 ►M9 Commission Implementing Regulation (EU) No 85/2012 of 1 L 30 4 2.2.2012 February 2012 ►M10 Commission Implementing Regulation (EU) No 86/2012 of 1 L 30 6 2.2.2012 February 2012 ►M11 Commission -
Neurotoxicity in Preclinical Models of Occupational Exposure to Organophosphorus Compounds
CORE Metadata, citation and similar papers at core.ac.uk Provided by Frontiers - Publisher Connector REVIEW published: 18 January 2017 doi: 10.3389/fnins.2016.00590 Neurotoxicity in Preclinical Models of Occupational Exposure to Organophosphorus Compounds Jaymie R. Voorhees 1, 2*, Diane S. Rohlman 2, 3, Pamela J. Lein 4 and Andrew A. Pieper 1, 2, 5, 6, 7, 8, 9* 1 Department of Psychiatry, University of Iowa Carver College of Medicine, Iowa City, IA, USA, 2 Interdisciplinary Graduate Program in Human Toxicology, University of Iowa Carver College of Medicine, Iowa City, IA, USA, 3 Department of Occupational and Environmental Health, University of Iowa College of Public Health, Iowa City, IA, USA, 4 Department of Molecular Biosciences, School of Veterinary Medicine, University of California, Davis, Davis, CA, USA, 5 Department of Neurology, University of Iowa Carver College of Medicine, Iowa City, IA, USA, 6 Department of Free Radical and Radiation Biology Program, University of Iowa Carver College of Medicine, Iowa City, IA, USA, 7 Department of Radiation Oncology Holden Comprehensive Cancer Center, University of Iowa Carver College of Medicine, Iowa City, IA, USA, 8 Department of Veteran Affairs, University of Iowa Carver College of Medicine, Iowa City, IA, USA, 9 Weill Cornell Autism Research Program, Weill Cornell Medical College, New York, NY, USA Organophosphorus (OPs) compounds are widely used as insecticides, plasticizers, and fuel additives. These compounds potently inhibit acetylcholinesterase (AChE), the enzyme that inactivates acetylcholine at neuronal synapses, and acute exposure to high Edited by: OP levels can cause cholinergic crisis in humans and animals. Evidence further suggests Stefano L. -
Report Name:Ukraine's Mrls for Veterinary Drugs
Voluntary Report – Voluntary - Public Distribution Date: November 05,2020 Report Number: UP2020-0051 Report Name: Ukraine's MRLs for Veterinary Drugs Country: Ukraine Post: Kyiv Report Category: FAIRS Subject Report Prepared By: Oleksandr Tarassevych Approved By: Robin Gray Report Highlights: Ukraine adopted several maximum residue levels (MRLs) for veterinary drugs, coccidiostats and histomonostats in food products of animal origin. Ukraine also adopted a list of drugs residues that are not allowed in food products. THIS REPORT CONTAINS ASSESSMENTS OF COMMODITY AND TRADE ISSUES MADE BY USDA STAFF AND NOT NECESSARILY STATEMENTS OF OFFICIAL U.S. GOVERNMENT POLICY The Office of Agricultural Affairs of USDA/Foreign Agricultural Service in Kyiv, Ukraine prepared this report for U.S. exporters of domestic food and agricultural products. While every possible care was taken in the preparation of this report, information provided may not be completely accurate either because policies have changed since the time this report was written, or because clear and consistent information about these policies was not available. It is highly recommended U.S. exporters verify the full set of import requirements with their foreign customers, who are normally best equipped to research such matters with local authorities, before any goods are shipped. This FAIRS Subject Report accompanies other reports on Maximum, Residue Limits established by Ukraine in 2020. Related reports could be found under the following links: 1.) Ukraine's MRLs for Microbiological Contaminants_Kyiv_Ukraine_04-27-2020 2.) Ukraine's MRLs for Certain Contaminants_Kyiv_Ukraine_03-06-2020 Food Products of animal origin and/or ingredients of animal origin are not permitted in the Ukrainian market if they contain certain veterinary drugs residues in excess of the maximum residue levels established in Tables 1 and 2. -
Phytotoxicity of Some Organophosphate Insecticides to Oughly with Air Dry, Sieved Soil, to Pro Duce Rates of 37.5, 75 and ISO Mg Aj
Plant Protection Quarterly VoI.7(1} 1992 23 -------------------------------- ties of each pesticide were shaken thor Phytotoxicity of some organophosphate insecticides to oughly with air dry, sieved soil, to pro duce rates of 37.5, 75 and ISO mg aj. L-' onions and carrots during germination and emergence soil. Each pot constituted one plot. If it is assumed that in a field situation, P.J. Sinclair, New South Wales Agriculture, Horticultural Research and band-in-furrow treatment would treat a Advisory Station, Griffith, New South Wales 2680, Australia. strip 50 mm wide by 20 mm deep, the rates tested would correspond to 37.5, 75 R.J. Neeson and P.A. Williams, New South Wales Agriculture, Agricultural and 150 mg a.i. m" row, or 0.5,1.0 and 2.0 institute, Yanco, New South Wales 2703, Australia. kg a.i. ha" at a row spacing of 75 cm. The low and medium rates are then compara Summary ble to ra tes used in the field by Getzin The phytotoxicity of some commonly phytotoxicity from carbofuran applied to (1973), Thompson et al. (1981) and used insecticides to onions (Allium cepa) onions as a seed dressing. Chlorpyrifos is Goodyer et al. (1989) . and carrots (Daucus carota) during es generally non-phytotoxic at recom Daily counts of emerged seedlings were tablishment was assessed in pot trials. mended rates and methods of application, made at 7 to 18 days and at 21 days after Terbufos, ethoprophos, phoxirn and but some crops are especially sensitive to first watering. These data were used to de carbofuran (all 10% a.L granular fonnu it during the seedling stage or if the termine the total number of seedlings lations) and chlorpyrifos (25% a.i.