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Neuroactive Insecticides: Targets, Selectivity, Resistance, and Secondary Effects
EN58CH06-Casida ARI 5 December 2012 8:11 Neuroactive Insecticides: Targets, Selectivity, Resistance, and Secondary Effects John E. Casida1,∗ and Kathleen A. Durkin2 1Environmental Chemistry and Toxicology Laboratory, Department of Environmental Science, Policy, and Management, 2Molecular Graphics and Computational Facility, College of Chemistry, University of California, Berkeley, California 94720; email: [email protected], [email protected] Annu. Rev. Entomol. 2013. 58:99–117 Keywords The Annual Review of Entomology is online at acetylcholinesterase, calcium channels, GABAA receptor, nicotinic ento.annualreviews.org receptor, secondary targets, sodium channel This article’s doi: 10.1146/annurev-ento-120811-153645 Abstract Copyright c 2013 by Annual Reviews. Neuroactive insecticides are the principal means of protecting crops, people, All rights reserved livestock, and pets from pest insect attack and disease transmission. Cur- ∗ Corresponding author rently, the four major nerve targets are acetylcholinesterase for organophos- phates and methylcarbamates, the nicotinic acetylcholine receptor for neonicotinoids, the γ-aminobutyric acid receptor/chloride channel for by Public Health Information Access Project on 04/29/14. For personal use only. Annu. Rev. Entomol. 2013.58:99-117. Downloaded from www.annualreviews.org polychlorocyclohexanes and fiproles, and the voltage-gated sodium channel for pyrethroids and dichlorodiphenyltrichloroethane. Species selectivity and acquired resistance are attributable in part to structural differences in binding subsites, receptor subunit interfaces, or transmembrane regions. Additional targets are sites in the sodium channel (indoxacarb and metaflumizone), the glutamate-gated chloride channel (avermectins), the octopamine receptor (amitraz metabolite), and the calcium-activated calcium channel (diamides). Secondary toxic effects in mammals from off-target serine hydrolase inhibi- tion include organophosphate-induced delayed neuropathy and disruption of the cannabinoid system. -
U.S. Geological Survey National Water-Quality Assessment Program
U.S. Geological Survey National Water-Quality Assessment Program Stream water-quality analytes Major ions and trace elementsschedule 998 (20 constituents) Pesticides schedule 2437 (229 compounds) Alkalinity 1H1,2,4Triazole Arsenic 2,3,3Trichloro2propene1sulfonic acid (TCPSA) Boron 2,4D Calcium 2(1Hydroxyethyl)6methylaniline Chloride 2[(2Ethyl6methylphenyl)amino]1propanol Fluoride 2AminoNisopropylbenzamide Iron 2Aminobenzimidazole Lithium 2Chloro2',6'diethylacetanilide 2Chloro4,6diaminostriazine {CAAT} Magnesium (Didealkylatrazine) pH 2Chloro4isopropylamino6aminostriazine Potassium 2Chloro6ethylamino4aminostriazine {CEAT} Total dissolved solids 2ChloroN(2ethyl6methylphenyl)acetamide Selenium 2Hydroxy4isopropylamino6aminostriazine 2Hydroxy4isopropylamino6ethylaminostriazin Silica e {OIET} Sodium 2Hydroxy6ethylamino4aminostriazine Specific conductance 2Isopropyl6methyl4pyrimidinol Strontium 3,4Dichlorophenylurea Sulfate 3Hydroxycarbofuran Turbidity 3Phenoxybenzoic acid Vanadium 4(Hydroxymethyl)pendimethalin 4Chlorobenzylmethyl sulfoxide Suspended sediment 4Hydroxy molinate 4Hydroxychlorothalonil Nutrientsschedule 2430 (18 constituents) 4Hydroxyhexazinone A Inorganic carbon, suspended Acephate Dissolved inorganic carbon Acetochlor ammonia + organic nitrogen (unfilteredKjeldahl) Acetochlor oxanilic acid ammonia + organic nitrogen (filteredKjeldahl) Acetochlor sulfonic acid Ammonia as N, filtered Acetochlor sulfynilacetic acid nitrite, filtered Alachlor -
Appendix H EPA Hazardous Waste Law
Appendix H EPA Hazardous Waste Law This Appendix is intended to give you background information on hazardous waste laws and how they apply to you. For most U.S. Environmental Protection Agency (EPA) requirements that apply to the University, the Safety Department maintains compliance through internal inspections, record keeping and proper disposal. In Wisconsin, the Department of Natural Resources (DNR) has adopted the EPA regulations, consequently EPA and DNR regulations are nearly identical. EPA defines This Appendix only deals with "hazardous waste" as defined by the EPA. hazardous waste as Legally, EPA defines hazardous waste as certain hazardous chemical waste. This hazardous chemical Appendix does not address other types of regulated laboratory wastes, such as waste; radioactive, infectious, biological, radioactive or sharps. Chapter 8 descibes disposal procedures infectious and biohazardous waste for animals. Chapter 9 describes disposal procedures for sharps and other waste that are regulated by can puncture tissue. Chapter 11 discusses Radiation and the Radiation Safety for other agencies. Radiation Workers provides guidelines for the disposal of radioactive waste. Procedures for medical waste are written by the UW Hospital Safety Officer. The Office of Biological Safety can provide guidance for the disposal of infectious and biological waste. EPA regulations focus on industrial waste streams. As a result, many laboratory chemical wastes are not regulated by EPA as hazardous chemical waste. However, many unregulated chemical wastes do merit special handling and disposal If a waste can be procedures. Thus, Chapter 7 and Appendix A of this Guide recommend disposal defined as: procedures for many unregulated wastes as if they were EPA hazardous waste. -
For Methyl Parathion
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON D.C., 20460 OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES MEMORANDUM DATE: July 31, 2006 SUBJECT: Finalization of Interim Reregistration Eligibility Decisions (IREDs) and Interim Tolerance Reassessment and Risk Management Decisions (TREDs) for the Organophosphate Pesticides, and Completion of the Tolerance Reassessment and Reregistration Eligibility Process for the Organophosphate Pesticides FROM: Debra Edwards, Director Special Review and Reregistration Division Office of Pesticide Programs TO: Jim Jones, Director Office of Pesticide Programs As you know, EPA has completed its assessment of the cumulative risks from the organophosphate (OP) class of pesticides as required by the Food Quality Protection Act of 1996. In addition, the individual OPs have also been subject to review through the individual- chemical review process. The Agency’s review of individual OPs has resulted in the issuance of Interim Reregistration Eligibility Decisions (IREDs) for 22 OPs, interim Tolerance Reassessment and Risk Management Decisions (TREDs) for 8 OPs, and a Reregistration Eligibility Decision (RED) for one OP, malathion.1 These 31 OPs are listed in Appendix A. EPA has concluded, after completing its assessment of the cumulative risks associated with exposures to all of the OPs, that: (1) the pesticides covered by the IREDs that were pending the results of the OP cumulative assessment (listed in Attachment A) are indeed eligible for reregistration; and 1 Malathion is included in the OP cumulative assessment. However, the Agency has issued a RED for malathion, rather than an IRED, because the decision was signed on the same day as the completion of the OP cumulative assessment. -
Acute Exposure to a Sublethal Dose of Imidacloprid and Coumaphos Enhances Olfactory Learning and Memory in the Honeybee Apis Mellifera
Invert Neurosci DOI 10.1007/s10158-012-0144-7 ORIGINAL PAPER Acute exposure to a sublethal dose of imidacloprid and coumaphos enhances olfactory learning and memory in the honeybee Apis mellifera Sally M. Williamson • Daniel D. Baker • Geraldine A. Wright Received: 8 October 2012 / Accepted: 5 November 2012 Ó The Author(s) 2012. This article is published with open access at Springerlink.com Abstract The decline of honeybees and other pollinating agricultural chemicals used to combat pests and fungi that insects is a current cause for concern. A major factor bees experience when they pollinate flowering crops or implicated in their decline is exposure to agricultural plants near agricultural land (Dainat et al. 2011; Neumann chemicals, in particular the neonicotinoid insecticides such and Carreck 2010; vanEngelsdorp et al. 2009). Systemic as imidacloprid. Honeybees are also subjected to additional insecticides, such as the neonicotinoids, are of particular chemical exposure when beekeepers treat hives with aca- concern as they persist in pollen and nectar long after ricides to combat the mite Varroa destructor. Here, we application (Rortais et al. 2005). Domesticated honeybees assess the effects of acute sublethal doses of the neoni- are also exposed to chemical acaricides administered by cotinoid imidacloprid, and the organophosphate acaricide beekeepers within the colony to control infestations of the coumaphos, on honey bee learning and memory. Imida- parasitic mite Varroa destructor (Rosenkranz et al. 2010). cloprid had little effect on performance in a six-trial It has been suggested that combined exposure to both olfactory conditioning assay, while coumaphos caused a pesticides and acaricides may be more toxic to bees than modest impairment. -
Quantum Chemical Study of the Thermochemical Properties of Organophosphorous Compounds A
QUANTUM CHEMICAL STUDY OF THE THERMOCHEMICAL PROPERTIES OF ORGANOPHOSPHOROUS COMPOUNDS A. Khalfa, M. Ferrari, R. Fournet, B. Sirjean, L. Verdier, Pierre-Alexandre Glaude To cite this version: A. Khalfa, M. Ferrari, R. Fournet, B. Sirjean, L. Verdier, et al.. QUANTUM CHEMICAL STUDY OF THE THERMOCHEMICAL PROPERTIES OF ORGANOPHOSPHOROUS COMPOUNDS. Journal of Physical Chemistry A, American Chemical Society, 2015, 119 (42), pp.10527-10539. 10.1021/acs.jpca.5b07071. hal-01241498 HAL Id: hal-01241498 https://hal.archives-ouvertes.fr/hal-01241498 Submitted on 10 Dec 2015 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. QUANTUM CHEMICAL STUDY OF THE THERMOCHEMICAL PROPERTIES OF ORGANOPHOSPHOROUS COMPOUNDS A. Khalfa, M. Ferrari1, R. Fournet1, B. Sirjean1, L. Verdier2, P.A. Glaude1 1Laboratoire Réactions et Génie des Procédés, Université de Lorraine, CNRS, 1 rue Grandville, BP 20451, 54001 NANCY Cedex, France, 2DGA Maîtrise NRBC, Site du Bouchet, 5 rue Lavoisier, BP n°3, 91710 Vert le Petit, France Abstract Organophosphorous compounds are involved in many toxic compounds such as fungicides, pesticides, or chemical warfare nerve agents. The understanding of the decomposition chemistry of these compounds in the environment is largely limited by the scarcity of thermochemical data. -
NIOSH Method 5600: Organophosphorus Pesticides
ORGANOPHOSPHORUS PESTICIDES 5600 Formula: Table 1 MW: Table 1 CAS: Table 1 RTECS: Table 1 METHOD: 5600, Issue 1 EVALUATION: FULL Issue 1: 15 August 1994 OSHA : Table 2 PROPERTIES: Table 3 NIOSH: Table 2 ACGIH: Table 2 SYNONYMS: Table 4 SAMPLING MEASUREMENT SAMPLER: FILTER/SOLID SORBENT TUBE (OVS-2 tube: TECHNIQUE: GC, FLAME PHOTOMETRIC DETECTION 13-mm quartz filter; XAD-2, 270 mg/140 mg) (FPD) FLOW RATE: 0.2 to 1 L/min ANALYTE: organophosphorus pesticides, Table 1 VOL-MIN: 12 L EXTRACTION: 2-mL 90% toluene/10% acetone solution -MAX: 240 L; 60 L (Malathion, Ronnel) INJECTION SHIPMENT: cap both ends of tube VOLUME: 1-2 µL SAMPLE TEMPERATURE STABILITY: at least 10 days at 25 °C -INJECTION: 240 °C at least 30 days at 0 °C -DETECTOR: 180 °C to 215 °C (follow manufacturer's recommendation) BLANKS: 2 to 10 field blanks per set -COLUMN: Table 6 CARRIER GAS: He at 15 psi (104 kPa) ACCURACY COLUMN: fused silica capillary column; Table 6 RANGE STUDIED: Table 5, Column A DETECTOR: FPD (phosphorus mode) ACCURACY: Table 5, Column B CALIBRATION: standard solutions of organophosphorus compounds in toluene BIAS: Table 5, Column C RANGE: Table 8, Column C ˆ OVERALL PRECISION (S rT): Table 5, Column D ESTIMATED LOD: Table 8, Column F PRECISION (S r): Table 5, Column E APPLICABILITY: The working ranges are listed in Table 5. They cover a range of 1/10 to 2 times the OSHA PELs. This INTERFERENCES: Several organophosphates may co-elute method also is applicable to STEL measurements using 12-L with either target analyte or internal standard causing samples. -
Environmental Health Criteria 63 ORGANOPHOSPHORUS
Environmental Health Criteria 63 ORGANOPHOSPHORUS INSECTICIDES: A GENERAL INTRODUCTION Please note that the layout and pagination of this web version are not identical with the printed version. Organophophorus insecticides: a general introduction (EHC 63, 1986) INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY ENVIRONMENTAL HEALTH CRITERIA 63 ORGANOPHOSPHORUS INSECTICIDES: A GENERAL INTRODUCTION This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization World Health Orgnization Geneva, 1986 The International Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experimental laboratory, and risk-assessment methods that could produce internationally comparable results, and the development of manpower in the field of toxicology. Other activities carried out by the IPCS include the development of know-how for coping with chemical accidents, coordination -
Recent Advances on Detection of Insecticides Using Optical Sensors
sensors Review Recent Advances on Detection of Insecticides Using Optical Sensors Nurul Illya Muhamad Fauzi 1, Yap Wing Fen 1,2,*, Nur Alia Sheh Omar 1,2 and Hazwani Suhaila Hashim 2 1 Functional Devices Laboratory, Institute of Advanced Technology, Universiti Putra Malaysia, Serdang 43400, Selangor, Malaysia; [email protected] (N.I.M.F.); [email protected] (N.A.S.O.) 2 Department of Physics, Faculty of Science, Universiti Putra Malaysia, Serdang 43400, Selangor, Malaysia; [email protected] * Correspondence: [email protected] Abstract: Insecticides are enormously important to industry requirements and market demands in agriculture. Despite their usefulness, these insecticides can pose a dangerous risk to the safety of food, environment and all living things through various mechanisms of action. Concern about the environmental impact of repeated use of insecticides has prompted many researchers to develop rapid, economical, uncomplicated and user-friendly analytical method for the detection of insecticides. In this regards, optical sensors are considered as favorable methods for insecticides analysis because of their special features including rapid detection time, low cost, easy to use and high selectivity and sensitivity. In this review, current progresses of incorporation between recognition elements and optical sensors for insecticide detection are discussed and evaluated well, by categorizing it based on insecticide chemical classes, including the range of detection and limit of detection. Additionally, this review aims to provide powerful insights to researchers for the future development of optical sensors in the detection of insecticides. Citation: Fauzi, N.I.M.; Fen, Y.W.; Omar, N.A.S.; Hashim, H.S. Recent Keywords: insecticides; optical sensor; recognition element Advances on Detection of Insecticides Using Optical Sensors. -
Federal Register/Vol. 69, No. 188/Wednesday, September 29
Federal Register / Vol. 69, No. 188 / Wednesday, September 29, 2004 / Notices 58125 collected by CSREES contains sensitive on Tuesday, September 28, 2004, to organization facilitating fair information of an individual nature. provide information and receive public international trade in food and Estimate of Burden: Each year, the comments on agenda items that will be protecting the health and economic State 4–H office aggregates all electronic discussed at the Fifteenth Session of the interests of consumers. Through County 4–H enrollment reports into the Codex Committee on Residues in adoption of food standards, codes of State 4–H enrollment report, and Veterinary Drugs in Foods, which will practice, and other guidelines transmits it electronically to CSREES. be held in Alexandria, VA, October 26– developed by its committees, and by The applicable Territories similarly 29, 2004. The Under Secretary and CVM promoting their adoption and transmit aggregated information. This recognize the importance of providing implementation by governments, Codex requirement constitutes the Federal interested parties with information seeks to ensure that the world’s food burden CSREES imposes on the States about the Codex Committee on Residues supply is sound, wholesome, free from and Territories and is the only burden of Veterinary Drugs in Foods of the adulteration, and correctly labeled. In measured and accounted for in this Codex Alimentarius Commission and to the United States, USDA, FDA, and the estimate. CSREES estimates that it takes address items on the Agenda for the Environmental Protection Agency one State or Territory 31 hours to 15th Session of the Committee. manage and carry out U.S. -
Changes Highlighted Final Version Date of Issue: 23Rd December 2015
EPHMRA ANATOMICAL CLASSIFICATION GUIDELINES 2016 Section A Changed Classes/Guidelines: Changes Highlighted Final Version Date of issue: 23rd December 2015 1 A2B ANTIULCERANTS R1997r2 016 Combinations of specific antiulcerants with anti-infectives against Helicobacter pylori are classified according to the anti-ulcerant substance. For example, proton pump inhibitors in combination with these anti-infectives are classified in A2B2. A2B1 H2 antagonists R2002 Includes, for example, cimetidine, famotidine, nizatidine, ranitidine, roxatidine. Combinations of low dose H2 antagonists with antacids are classified with antacids in A2A6. A2B2 Acid Proton pump inhibitors R2003r2 016 Includes esomeprazole, lansoprazole, omeprazole, pantoprazole, rabeprazole. A2B3 Prostaglandin antiulcerants Includes misoprostol, enprostil. A2B4 Bismuth antiulcerants Includes combinations with antacids. A2B9 All other antiulcerants R2002r2 016 Includes all other products specifically stated to be antiulcerants even when containing antispasmodics (see A3). Combinations of low dose H2 antagonists with antacids are classified with antacids in A2A6. Included are, eg carbenoxolone, gefarnate, pirenzepine, proglumide, sucralfate and sofalcone. Herbal combinations are classified in A2C. In Japan, Korea and Taiwan only, sulpiride and other psycholeptics indicated for ulcer use are also included in this group, whilst in all other countries, these compounds are classified in N5A9. Products containing rebamipide for gastric mucosal protection are classified here. Products containing rebamipide and indicated for dry eye are classified in S1K9. A2C OTHER STOMACH DISORDER PREPARATIONS R1994 Includes herbal preparations and also plain alginic acid. Combinations of antacids with alginic acid are in A2A1. 2 A4 ANTIEMETICS AND ANTINAUSEANTS A4A ANTIEMETICS AND ANTINAUSEANTS R1996 Products indicated for vertigo and Meniere's disease are classified in N7C. Gastroprokinetics are classified in A3F. -
Target Pesticide List
EUPT-FV17- TARGET PESTICIDE LIST MRRL Pesticide (mg/Kg) 3-hydroxy-carbofuran 0.01 Acephate 0.01 Acetamiprid 0.01 Acrinathrin 0.01 Aldicarb 0.01 Aldicarb Sulfone 0.01 Aldicarb Sulfoxide 0.01 Azinphos-methyl 0.01 Azoxystrobin 0.01 Benfuracarb 0.01 Benomyl 0.01 Bifenthrin 0.01 Bitertanol 0.01 Boscalid 0.01 Bromopropylate 0.01 Bromuconazole 0.01 Bupirimate 0.01 Buprofezin 0.01 Cadusafos 0.006 Carbaryl 0.01 Carbendazim 0.01 Carbofuran 0.01 Carbosulfan 0.01 Chlorfenapyr 0.01 Chlorfenvinphos 0.01 Chlorobenzilate 0.01 Chlorothalonil 0.01 Chlorpropham (only parent compound) 0.01 Chlorpyrifos 0.01 Chlorpyrifos-methyl 0.01 Clofentezine (only parent compound) 0.01 Clothianidin 0.01 Cyfluthrin (cyfluthrin incl. other mixtures of constituent isomers (sum of isomers)) 0.01 Cypermethrin (cypermethrin incl. other mixtures of constituent isomers (sum of isomers)) 0.01 Cyproconazole 0.01 Cyprodinil 0.01 Deltamethrin 0.01 Demeton-S-methylsulfone 0.006 Desmethyl-pirimicarb 0.01 Diazinon 0.01 Dichlofluanid (only parent compound) 0.01 Dichlorvos 0.01 Dicloran 0.01 Dicofol 0.01 Diethofencarb 0.01 Difenoconazole 0.01 Diflubenzuron 0.01 Dimethoate 0.003 Dimethomorph 0.01 Dimethylaminosulfotoluidide (DMST) 0.01 Diniconazole 0.01 Diphenylamine 0.01 Endosulfan alpha 0.01 Endosulfan beta 0.01 Endosulfan sulfate 0.01 EPN 0.01 Epoxiconazole 0.01 Ethion 0.01 Ethirimol 0.01 Ethoprophos 0.008 Etofenprox 0.01 Fenamidone 0.01 Fenamiphos 0.01 Fenamiphos sulfone 0.01 Fenamiphos sulfoxide 0.01 Fenarimol 0.01 Fenazaquin 0.01 Fenbuconazole 0.01 Fenhexamid 0.01 Fenitrothion 0.01