ELECTRONIC SUPPLEMENTARY MATERIAL a Reliable LC-MS/MS
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Global Insecticide Use for Vector-Borne Disease Control
WHO/CDS/NTD/WHOPES/GCDPP/2007.2 GLOBAL INSECTICIDE USE FOR VECTOR-BORNE DISEASE CONTROL M. Zaim & P. Jambulingam DEPARTMENT OF CONTROL OF NEGLECTED TROPICAL DISEASES (NTD) WHO PESTICIDE EVALUATION SCHEME (WHOPES) First edition, 2002 Second edition, 2004 Third edition, 2007 © World Health Organization 2007 All rights reserved. The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the World Health Organization concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. Dotted lines on maps represent approximate border lines for which there may not yet be full agreement. The mention of specific companies or of certain manufacturers’ products does not imply that they are endorsed or recommended by the World Health Organization in preference to others of a similar nature that are not mentioned. Errors and omissions excepted, the names of proprietary products are distinguished by initial capital letters. All reasonable precautions have been taken by the World Health Organization to verify the information contained in this publication. However, the published material is being distributed without warranty of any kind, either express or implied. The responsibility for the interpretation and use of the material lies with the reader. In no event shall the World Health Organization be liable for damages arising from its use. The named authors alone are responsible for the views expressed in this publication. CONTENTS Page Acknowledgements i Introduction 1 Collection of information 2 Data analysis and observations on reporting 3 All uses in vector control 6 Malaria vector control 22 Dengue vector control 38 Chagas disease vector control 48 Leishmaniasis vector control 52 Other vector-borne disease control 56 Selected insecticides – DDT 58 Selected insecticides – Insect growth regulators 60 Selected insecticides – Bacterial larvicides 62 Country examples 64 Annex 1. -
2,4-Dichlorophenoxyacetic Acid
2,4-Dichlorophenoxyacetic acid 2,4-Dichlorophenoxyacetic acid IUPAC (2,4-dichlorophenoxy)acetic acid name 2,4-D Other hedonal names trinoxol Identifiers CAS [94-75-7] number SMILES OC(COC1=CC=C(Cl)C=C1Cl)=O ChemSpider 1441 ID Properties Molecular C H Cl O formula 8 6 2 3 Molar mass 221.04 g mol−1 Appearance white to yellow powder Melting point 140.5 °C (413.5 K) Boiling 160 °C (0.4 mm Hg) point Solubility in 900 mg/L (25 °C) water Related compounds Related 2,4,5-T, Dichlorprop compounds Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa) 2,4-Dichlorophenoxyacetic acid (2,4-D) is a common systemic herbicide used in the control of broadleaf weeds. It is the most widely used herbicide in the world, and the third most commonly used in North America.[1] 2,4-D is also an important synthetic auxin, often used in laboratories for plant research and as a supplement in plant cell culture media such as MS medium. History 2,4-D was developed during World War II by a British team at Rothamsted Experimental Station, under the leadership of Judah Hirsch Quastel, aiming to increase crop yields for a nation at war.[citation needed] When it was commercially released in 1946, it became the first successful selective herbicide and allowed for greatly enhanced weed control in wheat, maize (corn), rice, and similar cereal grass crop, because it only kills dicots, leaving behind monocots. Mechanism of herbicide action 2,4-D is a synthetic auxin, which is a class of plant growth regulators. -
Novel Approach to Fast Determination of 64 Pesticides Using of Ultra-Performance Liquid Chromatography-Tandem Mass Spectrometry
Novel approach to fast determination of 64 pesticides using of ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS) Tomas Kovalczuk, Ondrej Lacina, Martin Jech, Jan Poustka, Jana Hajslova To cite this version: Tomas Kovalczuk, Ondrej Lacina, Martin Jech, Jan Poustka, Jana Hajslova. Novel approach to fast determination of 64 pesticides using of ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS). Food Additives and Contaminants, 2008, 25 (04), pp.444-457. 10.1080/02652030701570156. hal-00577414 HAL Id: hal-00577414 https://hal.archives-ouvertes.fr/hal-00577414 Submitted on 17 Mar 2011 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. Food Additives and Contaminants For Peer Review Only Novel approach to fast determination of 64 pesticides using of ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS) Journal: Food Additives and Contaminants Manuscript ID: TFAC-2007-065.R1 Manuscript Type: Original Research Paper Date Submitted by the 07-Jul-2007 Author: Complete List of Authors: -
Exposure to Herbicides in House Dust and Risk of Childhood Acute Lymphoblastic Leukemia
Journal of Exposure Science and Environmental Epidemiology (2013) 23, 363–370 & 2013 Nature America, Inc. All rights reserved 1559-0631/13 www.nature.com/jes ORIGINAL ARTICLE Exposure to herbicides in house dust and risk of childhood acute lymphoblastic leukemia Catherine Metayer1, Joanne S. Colt2, Patricia A. Buffler1, Helen D. Reed3, Steve Selvin1, Vonda Crouse4 and Mary H. Ward2 We examine the association between exposure to herbicides and childhood acute lymphoblastic leukemia (ALL). Dust samples were collected from homes of 269 ALL cases and 333 healthy controls (o8 years of age at diagnosis/reference date and residing in same home since diagnosis/reference date) in California, using a high-volume surface sampler or household vacuum bags. Amounts of agricultural or professional herbicides (alachlor, metolachlor, bromoxynil, bromoxynil octanoate, pebulate, butylate, prometryn, simazine, ethalfluralin, and pendimethalin) and residential herbicides (cyanazine, trifluralin, 2-methyl-4- chlorophenoxyacetic acid (MCPA), mecoprop, 2,4-dichlorophenoxyacetic acid (2,4-D), chlorthal, and dicamba) were measured. Odds ratios (OR) and 95% confidence intervals (CI) were estimated by logistic regression. Models included the herbicide of interest, age, sex, race/ethnicity, household income, year and season of dust sampling, neighborhood type, and residence type. The risk of childhood ALL was associated with dust levels of chlorthal; compared to homes with no detections, ORs for the first, second, and third tertiles were 1.49 (95% CI: 0.82–2.72), 1.49 (95% CI: 0.83–2.67), and 1.57 (95% CI: 0.90–2.73), respectively (P-value for linear trend ¼ 0.05). The magnitude of this association appeared to be higher in the presence of alachlor. -
The Impact of the Nation's Most Widely Used Insecticides on Birds
The Impact of the Nation’s Most Widely Used Insecticides on Birds Neonicotinoid Insecticides and Birds The Impact of the Nation’s Most Widely Used Insecticides on Birds American Bird Conservancy, March 2013 Grasshopper Sparrow by Luke Seitz Cover photos: Horned Lark and chicks by Middleton Evans; Corn field, stock.xchng, sxc.hu; Calico Pennant dragonfly by David Cappaert, Michigan State University, Bugwood.org 1 Neonicotinoid Insecticides and Birds American Bird Conservancy would like to thank the Turner Foundation, Wallace Genetic Foundation, Jeff and Connie Woodman, Cornell Douglas Foundation and A.W. Berry Foundation for their ongoing support for American Bird Conservancy’s Pesticides Program. Written by Dr. Pierre Mineau and Cynthia Palmer Designed by Stephanie von Blackwood About the Authors Dr. Pierre Mineau began his long and distinguished scientific career studying the effects of persistent organochlorine compounds, like DDT and PCBs, on fish-eating birds. He then became responsible for the Canadian assessment of new and existing pesticides to determine their adverse impacts on wildlife. In 1994 he transitioned from regulatory reviews to full-time research on the environmental impacts of pesticides, achieving the rank of Senior Research Scientist at Environment Canada. Working with international collaborators and graduate students, he works on assessing globally the environmental footprint of pesticides. He also studies how birds are exposed to pesticides and how bird populations respond to pesticide use and agricultural practices. His work includes defining the ecological values of birds in cropland as well as estimating the incidental take of birds from various other human activities. He has written more than 100 peer-reviewed publications and has authored some 200 presentations. -
Review of the Mammalian Toxicology
REVIEW OF THE MAMMALIAN TOXICOLOGY AND METABOLISM/TOXICOKINETICS OF FENTHION The APVMA Review of Fenthion © Australian Pesticides and Veterinary Medicines Authority 2012 ISBN 978-0-9873591-5-5 (electronic) This document was originally published in 2005 as part of the preliminary review findings report for Part 1 of the fenthion review. It was subsequently updated in 2007, and revised in 2008. Ownership of intellectual property rights in this publication Unless otherwise noted, copyright (and any other intellectual property rights, if any) in this publication is owned by the Australian Pesticides and Veterinary Medicines Authority (APVMA). Creative Commons licence With the exception of the Coat of Arms, this publication is licensed under a Creative Commons Attribution 3.0 Australia Licence. This is a standard form agreement that allows you to copy, distribute, transmit and adapt this publication provided that you attribute the work. A summary of the licence terms is available from www.creativecommons.org/licenses/by/3.0/au/deed.en. The full licence terms are available from www.creativecommons.org/licenses/by/3.0/au/legalcode. The APVMA’s preference is that you attribute this publication (and any approved material sourced from it) using the following wording: Source: Licensed from the Australian Pesticides and Veterinary Medicines Authority (APVMA) under a Creative Commons Attribution 3.0 Australia Licence. This report was prepared for the APVMA by the Department of Health and Aging Office of Chemical Safety. In referencing this document the Department of Health and Aging Office of Chemical Safety should be cited as the author and the Australian Pesticides and Veterinary Medicines Authority as the publisher and copyright owner. -
Development of a CEN Standardised Method for Liquid Chromatography Coupled to Accurate Mass Spectrometry
Development of a CEN standardised method for liquid chromatography coupled to accurate mass spectrometry CONTENTS 1. Aim and scope ................................................................................................................. 2 2. Short description ................................................................................................................ 2 3. Apparatus and consumables ......................................................................................... 2 4. Chemicals ........................................................................................................................... 2 5. Procedure ........................................................................................................................... 3 5.1. Sample preparation ................................................................................................... 3 5.2. Recovery experiments for method validation ...................................................... 3 5.3. Extraction method ...................................................................................................... 3 5.4. Measurement .............................................................................................................. 3 5.5. Instrumentation and analytical conditions ............................................................ 4 5.5.1. Dionex Ultimate 3000 .......................................................................................... 4 5.5.2. QExactive Focus HESI source parameters ..................................................... -
Quantification of Neonicotinoid Pesticides in Six Cultivable Fish Species from the River Owena in Nigeria and a Template For
water Article Quantification of Neonicotinoid Pesticides in Six Cultivable Fish Species from the River Owena in Nigeria and a Template for Food Safety Assessment Ayodeji O. Adegun 1, Thompson A. Akinnifesi 1, Isaac A. Ololade 1 , Rosa Busquets 2 , Peter S. Hooda 3 , Philip C.W. Cheung 4, Adeniyi K. Aseperi 2 and James Barker 2,* 1 Department of Chemical Sciences, Adekunle Ajasin University, Akungba Akoko P.M.B. 001, Ondo State, Nigeria; [email protected] (A.O.A.); [email protected] (T.A.A.); [email protected] (I.A.O.) 2 School of Life Sciences, Pharmacy and Chemistry, Kingston University, Kingston-upon-Thames KT1 2EE, UK; [email protected] (R.B.); [email protected] (A.K.A.) 3 School of Engineering and the Environment, Kingston University, Kingston-on-Thames KT1 2EE, UK; [email protected] 4 Department of Chemical Engineering, Imperial College, London SW7 2AZ, UK; [email protected] * Correspondence: [email protected] Received: 17 June 2020; Accepted: 24 August 2020; Published: 28 August 2020 Abstract: The Owena River Basin in Nigeria is an area of agricultural importance for the production of cocoa. To optimise crop yield, the cocoa trees require spraying with neonicotinoid insecticides (Imidacloprid, Thiacloprid Acetamiprid and Thiamethoxam). It is proposed that rainwater runoff from the treated area may pollute the Owena River and that these pesticides may thereby enter the human food chain via six species of fish (Clarias gariepinus, Clarias anguillaris, Sarotherodon galilaeus, Parachanna obscura, Oreochromis niloticus and Gymnarchus niloticus) which are cultured in the river mostly for local consumption. -
162998571.Pdf
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by University of Liverpool Repository Please do not adjust margins Investigating the breakdown of the nerve agent simulant methyl paraoxon and chemical warfare agents GB and VX using nitrogen containing bases Received 00th January 20xx, Accepted 00th January 20xx Craig Wilson,a Nicholas J. Cooper,b Michael E. Briggs,a Andrew I. Cooper,*a and Dave J. Adams*c DOI: 10.1039/x0xx00000x A range of nitrogen containing bases was tested for the hydrolysis of a nerve agent simulant, methyl paraoxon (MP), and www.rsc.org/ the chemical warfare agents, GB and VX. The product distribution was found to be highly dependant on the basicity of the base and the quantity of water used for the hydrolysis. This study is important in the design of decontamination technology, which often involve mimics of CWAs. production of EA-2192 Introduction (S-(2-diisopropylaminoethyl) methylphosphonothioic acid), which exhibits roughly the same toxicity as VX itself.12 The Chemical warfare agents (CWAs) have a devastating effect on blister agent HD (Fig. 1d) can also undergo deactivation via the body and will disable or kill on exposure. Blister agents, such hydrolysis.13 However, its poor water solubility reduces the as sulfur mustard (HD, bis(2-chloroethyl) sulfide), target the skin efficiency of this decontamination method.14 As a result, and respiratory system causing severe pain and damage to the oxidation to the sulfoxide, or the addition of a co-solvent is most body whereas nerve agents, such as sarin (GB, isopropyl commonly used for HD deactivation.15-17 methylphosphonofluoridate) and VX (O-ethyl The high toxicity of CWAs means that research into their S-[2-(diisopropylamino)ethyl] methylphosphonothioate), target deactivation is often carried out using simulants. -
2002 NRP Section 6, Tables 6.1 Through
Table 6.1 Scoring Table for Pesticides 2002 FSIS NRP, Domestic Monitoring Plan } +1 0.05] COMPOUND/COMPOUND CLASS * ) (EPA) (EPA) (EPA) (EPA) (EPA) (FSIS) (FSIS) PSI (P) TOX.(T) L-1 HIST. VIOL. BIOCON. (B) {[( (2*R+P+B)/4]*T} REG. CON. (R) * ENDO. DISRUP. LACK INFO. (L) LACK INFO. {[ Benzimidazole Pesticides in FSIS Benzimidazole MRM (5- 131434312.1 hydroxythiabendazole, benomyl (as carbendazim), thiabendazole) Carbamates in FSIS Carbamate MRM (aldicarb, aldicarb sulfoxide, NA44234416.1 aldicarb sulfone, carbaryl, carbofuran, carbofuran 3-hydroxy) Carbamates NOT in FSIS Carbamate MRM (carbaryl 5,6-dihydroxy, chlorpropham, propham, thiobencarb, 4-chlorobenzylmethylsulfone,4- NT 4 1 3 NV 4 4 13.8 chlorobenzylmethylsulfone sulfoxide) CHC's and COP's in FSIS CHC/COP MRM (HCB, alpha-BHC, lindane, heptachlor, dieldrin, aldrin, endrin, ronnel, linuron, oxychlordane, chlorpyrifos, nonachlor, heptachlor epoxide A, heptachlor epoxide B, endosulfan I, endosulfan I sulfate, endosulfan II, trans- chlordane, cis-chlordane, chlorfenvinphos, p,p'-DDE, p, p'-TDE, o,p'- 3444NV4116.0 DDT, p,p'-DDT, carbophenothion, captan, tetrachlorvinphos [stirofos], kepone, mirex, methoxychlor, phosalone, coumaphos-O, coumaphos-S, toxaphene, famphur, PCB 1242, PCB 1248, PCB 1254, PCB 1260, dicofol*, PBBs*, polybrominated diphenyl ethers*, deltamethrin*) (*identification only) COP's and OP's NOT in FSIS CHC/COP MRM (azinphos-methyl, azinphos-methyl oxon, chlorpyrifos, coumaphos, coumaphos oxon, diazinon, diazinon oxon, diazinon met G-27550, dichlorvos, dimethoate, dimethoate -
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RESISTANCE TO MALATHION, PIRIMIPHOS-METHYL AND FENITROTHION IN COLEOPTERA FROM STORED GRAINS. Ivania A. PACHECO; M. Regina SARTORI; Scheilla BOLONHEZI Instituto de Tecnologia de Alimentos Avenida Brasil, 2880 - Caixa Postal 139 Campinas - Sao Paulo - Brasil - CEP 13073 SUMMARY The objectives of this paper were:l) to verify the occurrance of resistance to malathion, pirimiphos-methyl and fenitrothion in populations of coleoptera from stored grains and 2) to obtain data that could contribute to the adequate control of these insects during storage, thus reducing losses. Populations of Sitophilus oryzae, ~. zeamais, Tribolium castaneum and Rhyzopertha dominica were collected from storage facilities located in different regions of Brazil, and tested for resistance to the tree insecticides according to the FAO Standard Method (FAO, 1975). Insects were collected in the States of Sao Paulo, Rio Grande do SuI, Santa Catarina, Goias, Acre and Rondonia. Twenty populations of S. oryzae, ten of S. zeamais, twenty of R. dominica and twenty -five of T. castan~ad already been tested for - resistance to the three insecticides. Seven populations of S. oryzae, six of R. dominica and ten of S. zean~is were susceptible 'to the th~ee insecticides. Resistance to malathion was showed in thirteen populations of S. oryzae, fourteen of ~. dominica and twenty-five of !. castaneum. Simultaneous cross-resistance to pirimiphos-methyl and fenitrothion was indicated in one population of ~. oryzae and eight of !. castaneum. Cross resistance only to pirimiphos-methyl was indicated in two populations of ~. oryzae, one of ~. dominica and one of !. castaneum and only to fenitrothion in two of R. dominica and two of T. -
Chemical Name Federal P Code CAS Registry Number Acutely
Acutely / Extremely Hazardous Waste List Federal P CAS Registry Acutely / Extremely Chemical Name Code Number Hazardous 4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- P059 76-44-8 Acutely Hazardous 6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9,10,10- hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide P050 115-29-7 Acutely Hazardous Methanimidamide, N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]- P197 17702-57-7 Acutely Hazardous 1-(o-Chlorophenyl)thiourea P026 5344-82-1 Acutely Hazardous 1-(o-Chlorophenyl)thiourea 5344-82-1 Extremely Hazardous 1,1,1-Trichloro-2, -bis(p-methoxyphenyl)ethane Extremely Hazardous 1,1a,2,2,3,3a,4,5,5,5a,5b,6-Dodecachlorooctahydro-1,3,4-metheno-1H-cyclobuta (cd) pentalene, Dechlorane Extremely Hazardous 1,1a,3,3a,4,5,5,5a,5b,6-Decachloro--octahydro-1,2,4-metheno-2H-cyclobuta (cd) pentalen-2- one, chlorecone Extremely Hazardous 1,1-Dimethylhydrazine 57-14-7 Extremely Hazardous 1,2,3,4,10,10-Hexachloro-6,7-epoxy-1,4,4,4a,5,6,7,8,8a-octahydro-1,4-endo-endo-5,8- dimethanonaph-thalene Extremely Hazardous 1,2,3-Propanetriol, trinitrate P081 55-63-0 Acutely Hazardous 1,2,3-Propanetriol, trinitrate 55-63-0 Extremely Hazardous 1,2,4,5,6,7,8,8-Octachloro-4,7-methano-3a,4,7,7a-tetra- hydro- indane Extremely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]- 51-43-4 Extremely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]-, P042 51-43-4 Acutely Hazardous 1,2-Dibromo-3-chloropropane 96-12-8 Extremely Hazardous 1,2-Propylenimine P067 75-55-8 Acutely Hazardous 1,2-Propylenimine 75-55-8 Extremely Hazardous 1,3,4,5,6,7,8,8-Octachloro-1,3,3a,4,7,7a-hexahydro-4,7-methanoisobenzofuran Extremely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime 26419-73-8 Extremely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime.