Threat by Nerve Agents: Update of Diagnostic and Therapeutic Strategies!
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Dimethoate 4EC Systemic Insecticide – Miticide ACTIVE INGREDIENT: PRECAUTIONARY STATEMENTS (Cont.) Dimethoate*
GROUP 1B INSECTICIDE Dimethoate 4EC Systemic Insecticide – Miticide ACTIVE INGREDIENT: PRECAUTIONARY STATEMENTS (Cont.) Dimethoate* .......................................................... 43.5% Mixers, loaders, applicators, flaggers, and other handlers must OTHER INGREDIENTS: .......................................... 56.5% wear: Long-sleeved shirt and long pants, shoes plus socks, goggles TOTAL: .............................................................. 100.0% or face shield, chemical-resistant gloves, a NIOSH-approved * This product contains 4 pounds of dimethoate per gallon. dust/mist filtering respirator with MSHA/NIOSH approval number prefix TC-21C or a NIOSH-approved respirator with any N, R, P, or KEEP OUT OF REACH OF CHILDREN HE filter, and chemical-resistant apron when mixing, loading, clean- ing up spills, or equipment. WARNING See Engineering Controls for additional requirements and excep- Si usted no entiende la etiqueta, busque a alguien para que se la ex- tions. plique a usted en detalle. (If you do not understand the label, find Follow manufacturer’s instructions for cleaning/maintaining PPE. If someone to explain it to you in detail.) no such instructions for washables exist, use detergent and hot water. Keep and wash PPE separately from other laundry. See FIRST AID Below Discard clothing and other absorbent materials that have been EPA Reg. No. 19713-231 Net Content: drenched or heavily contaminated with this product’s concentrate. EPA Est. No. 19713-GA-001 2.5 Gals. (9.46 L) Do not reuse them. ENGINEERING CONTROLS FIRST AID Mixers and loaders supporting aerial application to alfalfa, cotton, IF SWALLOWED: soybeans, corn, safflower, sorghum, and wheat, must use a closed • Call a poison control center or doctor immediately for treatment system that meets the requirements listed in the Worker Protections advice. -
Novichok Agent - Wikipedia
18-3-2018 Novichok agent - Wikipedia Novichok agent Novichok (Russian: Новичо́к, "newcomer") is a series of nerve agents the Soviet Union and Russia developed between 1971 and 1993.[a][2][3] Russian scientists who developed the agents claim they are the deadliest nerve agents ever made, with some variants possibly five to eight times more potent than VX,[4][5] and others up to ten times more potent than soman.[6] They were designed as part of a Soviet program codenamed "FOLIANT".[7][1] Five Novichok variants are believed to have been weaponised for military use.[8] The most versatile was A-232 (Novichok-5).[9] Novichok agents have never been used on the battlefield. Theresa May, Prime Minister of the United Kingdom, said that one such agent was used in the poisoning of Sergei and Yulia Skripal in England in March 2018.[10] Russia officially denies producing or researching Novichok agents.[11] In 2013, the Organisation for the Prohibition of Chemical Weapons Scientific Advisory Board reported that it had insufficient information to comment on the existence or properties of Novichok agents,[12] and in 2011 it noted there was no peer reviewed paper on Novichok agents in scientific literature.[13] Contents Design objectives Disclosure Development and test sites Description of Novichok agents Chemistry Effects Use Poisoning of Kivelidi Poisoning of Sergei and Yulia Skripal See also References Further reading External links Design objectives These agents were designed to achieve four objectives:[14][15] To be undetectable using standard 1970s and 1980s NATO chemical detection equipment; To defeat NATO chemical protective gear; To be safer to handle; To circumvent the Chemical Weapons Convention list of controlled precursors, classes of chemical and physical form. -
Validation Report 20
EURL for Cereals and Feeding stuff National Food Institute Technical University of Denmark Validation Report 20 Determination of pesticide residues in rice baby food by GC-MS/MS and LC-MS/MS (QuEChERS method) Parvaneh Hajeb Susan Strange Herrmann Mette Erecius Poulsen December 2015 Page 2 of 18 CONTENT: 1. Introduction ...................................................................................................................................... 3 2. Principle of analysis......................................................................................................................... 3 3. Validation design ............................................................................................................................. 4 4. Chromatograms and calibration curves .......................................................................................... 5 5. Validation parameters...................................................................................................................... 9 6. Criteria for the acceptance of validation results ........................................................................... 10 7. Results and discussion ................................................................................................................... 10 8. Conclusions .................................................................................................................................... 12 9. References ..................................................................................................................................... -
Verification of Chemical Warfare Agent Exposure in Human Samples
Toxichem Krimtech 2013;80(Special Issue):288 Verification of chemical warfare agent exposure in human samples Paul W. Elsinghorst, Horst Thiermann, Marianne Koller Institut für Pharmakologie und Toxikologie der Bundeswehr, München Abstract Aim: This brief presentation provides an overview of methods that have been developed for the verification of human exposure to chemical warfare agents. Methods: GC–MS detection of nerve agents (V- and G-type) has been carried out with respect to unreacted agents as well as enzyme-bound species and metabolites. Methods involving di- rect SPE from plasma, fluoride-induced release of protein-bound nerve agents in plasma and analysis of their metabolites in plasma and urine have been developed. Exposure to blistering agents, i.e., sulfur mustard, has been verified by GC–MS detection of the unreacted agent in plasma and by LC– and GC–MS analysis of its metabolites in urine. Results: After incorporation nerve agents quickly bind to proteins, e.g., acetylcholinesterase, butyrylcholinesterase or serum albumin, and only small parts remain freely circulating for a few hours (G-type) or up to 2 days (V-type). Concurrently they are converted to O-alkyl methylphosphonic acids by phosphotriesterases and/or simply by aqueous hydrolysis. As a re- sult, different biomarkers can be detected depending on the time passed between exposure and sampling. Unreacted V-type agents can be detected in plasma for 2 days, the O-alkyl methyl- phosphonic acids in plasma for about 2–4 days and in urine for up to 1 week. Fluoride-indu- ced release of protein-bound nerve agents can be carried out until 3 weeks post exposure. -
Guide No. 1 – October 2020 2/12 the CONCEPT and IMPLEMENTATION of CPA GUIDANCE RESIDUE LEVELS
Cooperation Centre for Scientific Research Relative to Tobacco CORESTA GUIDE N° 1 The Concept and Implementation of CPA Guidance Residue Levels October 2020 Agro-Chemical Advisory Committee CORESTA TECHNICAL GUIDE N° 1 Title: The Concept and Implementation of CPA Guidance Residue Levels Status: Valid Note: This document will be periodically reviewed by CORESTA Document history: Date of review Information July 2003 Version 1 GRL for Pyrethrins () and Terbufos corrected. December 2003 CPA terminology corrected. June 2008 Version 2 – GRLs revised and residue definitions added Provisional GRL of 2.00 ppm for Cyfluthrin to replace previous June 2010 GRL of 0.50 ppm July 2013 Version 3 – GRLs revised October 2013 Note for Maleic Hydrazide revised Version 4 – GRLs revised + clarification that scope of GRLs July 2016 applies predominantly to the production of traditional cigarette tobaccos and GAP associated with their cultivation. June 2018 Fluopyram GRL of 5 ppm added to GRL list Version 5 – Nine new CPAs with GRL added to list. November 2019 Revision of GRLs for Chlorantraniliprole and Indoxacarb. Updated web links. October 2020 Version 6 – Flupyradifurone GRL of 21 ppm added to GRL list. CORESTA Guide No. 1 – October 2020 2/12 THE CONCEPT AND IMPLEMENTATION OF CPA GUIDANCE RESIDUE LEVELS Executive Summary • Guidance Residue Levels (GRLs) are in the remit of the Agro-Chemical Advisory Committee (ACAC) of CORESTA. Their development is a joint activity of all ACAC members, who represent the leaf production, processing and manufacturing sectors of the Tobacco Industry. The concept of GRLs and their implementation are described in this guide. • GRLs provide guidance to tobacco growers and assist with interpretation and evaluation of results from analyses of residues of Crop Protection Agents (CPAs*). -
Warning: the Following Lecture Contains Graphic Images
What the новичок (Novichok)? Why Chemical Warfare Agents Are More Relevant Than Ever Matt Sztajnkrycer, MD PHD Professor of Emergency Medicine, Mayo Clinic Medical Toxicologist, Minnesota Poison Control System Medical Director, RFD Chemical Assessment Team @NoobieMatt #ITLS2018 Disclosures In accordance with the Accreditation Council for Continuing Medical Education (ACCME) Standards, the American Nurses Credentialing Center’s Commission (ANCC) and the Commission on Accreditation for Pre-Hospital Continuing Education (CAPCE), states presenters must disclose the existence of significant financial interests in or relationships with manufacturers or commercial products that may have a direct interest in the subject matter of the presentation, and relationships with the commercial supporter of this CME activity. The presenter does not consider that it will influence their presentation. Dr. Sztajnkrycer does not have a significant financial relationship to report. Dr. Sztajnkrycer is on the Editorial Board of International Trauma Life Support. Specific CW Agents Classes of Chemical Agents: The Big 5 The “A” List Pulmonary Agents Phosgene Oxime, Chlorine Vesicants Mustard, Phosgene Blood Agents CN Nerve Agents G, V, Novel, T Incapacitating Agents Thinking Outside the Box - An Abbreviated List Ammonia Fluorine Chlorine Acrylonitrile Hydrogen Sulfide Phosphine Methyl Isocyanate Dibotane Hydrogen Selenide Allyl Alcohol Sulfur Dioxide TDI Acrolein Nitric Acid Arsine Hydrazine Compound 1080/1081 Nitrogen Dioxide Tetramine (TETS) Ethylene Oxide Chlorine Leaks Phosphine Chlorine Common Toxic Industrial Chemical (“TIC”). Why use it in war/terror? Chlorine Density of 3.21 g/L. Heavier than air (1.28 g/L) sinks. Concentrates in low-lying areas. Like basements and underground bunkers. Reacts with water: Hypochlorous acid (HClO) Hydrochloric acid (HCl). -
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. -
Lifetime Organophosphorous Insecticide Use Among Private Pesticide Applicators in the Agricultural Health Study
Journal of Exposure Science and Environmental Epidemiology (2012) 22, 584 -- 592 & 2012 Nature America, Inc. All rights reserved 1559-0631/12 www.nature.com/jes ORIGINAL ARTICLE Lifetime organophosphorous insecticide use among private pesticide applicators in the Agricultural Health Study Jane A. Hoppin1, Stuart Long2, David M. Umbach3, Jay H. Lubin4, Sarah E. Starks5, Fred Gerr5, Kent Thomas6, Cynthia J. Hines7, Scott Weichenthal8, Freya Kamel1, Stella Koutros9, Michael Alavanja9, Laura E. Beane Freeman9 and Dale P. Sandler1 Organophosphorous insecticides (OPs) are the most commonly used insecticides in US agriculture, but little information is available regarding specific OP use by individual farmers. We describe OP use for licensed private pesticide applicators from Iowa and North Carolina in the Agricultural Health Study (AHS) using lifetime pesticide use data from 701 randomly selected male participants collected at three time periods. Of 27 OPs studied, 20 were used by 41%. Overall, 95% had ever applied at least one OP. The median number of different OPs used was 4 (maximum ¼ 13). Malathion was the most commonly used OP (74%) followed by chlorpyrifos (54%). OP use declined over time. At the first interview (1993--1997), 68% of participants had applied OPs in the past year; by the last interview (2005--2007), only 42% had. Similarly, median annual application days of OPs declined from 13.5 to 6 days. Although OP use was common, the specific OPs used varied by state, time period, and individual. Much of the variability in OP use was associated with the choice of OP, rather than the frequency or duration of application. -
Bayesian Nonparametric Model for Clustering Individual Co-Exposure to Pesticides Found in the French Diet
Bayesian nonparametric model for clustering individual co-exposure to pesticides found in the French diet. Amélie Crépet, Jessica Tressou To cite this version: Amélie Crépet, Jessica Tressou. Bayesian nonparametric model for clustering individual co-exposure to pesticides found in the French diet.. 2009. hal-00438796v2 HAL Id: hal-00438796 https://hal.archives-ouvertes.fr/hal-00438796v2 Preprint submitted on 12 Jan 2011 (v2), last revised 4 Feb 2011 (v3) 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. Bayesian nonparametric model for clustering individual co-exposure to pesticides found in the French diet. Am´elieCr´epet a & Jessica Tressoub January 12, 2011 aANSES, French Agency for Food, Environmental and Occupational Health Safety, 27-31 Av. G´en´eralLeclerc, 94701 Maisons-Alfort, France bINRA-Met@risk, Food Risk Analysis Methodologies, National Institute for Agronomic Re- search, 16 rue Claude Bernard, 75231 Paris, France Keywords Dirichlet process; Bayesian nonparametric modeling; multivariate Normal mixtures; clustering; multivariate exposure; food risk analysis. Abstract This work introduces a specific application of Bayesian nonparametric statistics to the food risk analysis framework. The goal was to determine the cocktails of pesticide residues to which the French population is simultaneously exposed through its current diet in order to study their possible combined effects on health through toxicological experiments. -
Dimethoate in Drinking-Water
WHO/SDE/WSH/03.04/90 English only Dimethoate in Drinking-water Background document for development of WHO Guidelines for Drinking-water Quality © World Health Organization 2004 Requests for permission to reproduce or translate WHO publications - whether for sale of for non- commercial distribution - should be addressed to Publications (Fax: +41 22 791 4806; e-mail: [email protected]. 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. 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. The World Health Organization does not warrant that the information contained in this publication is complete and correct and shall not be liable for any damage incurred as a results of its use. Preface One of the primary goals of WHO and its member states is that “all people, whatever their stage of development and their social and economic conditions, have the right to have access to an adequate supply of safe drinking water.” A major WHO function to achieve such goals is the responsibility “to propose ... regulations, and to make recommendations with respect to international health matters ....” The first WHO document dealing specifically with public drinking-water quality was published in 1958 as International Standards for Drinking-water. -
2020) XXX Draft COMMISSION REGULATION (EU
EUROPEAN COMMISSION Brussels, XXX SANTE/10482/2020 […](2020) XXX draft COMMISSION REGULATION (EU) …/… of XXX amending Annexes II, III and V to Regulation (EC) No 396/2005 of the European Parliament and of the Council as regards maximum residue levels for carbon tetrachloride, chlorothalonil, chlorpropham, dimethoate, ethoprophos, fenamidone, methiocarb, omethoate, propiconazole and pymetrozine in or on certain products (Text with EEA relevance) EN EN COMMISSION REGULATION (EU) …/… of XXX amending Annexes II, III and V to Regulation (EC) No 396/2005 of the European Parliament and of the Council as regards maximum residue levels for carbon tetrachloride, chlorothalonil, chlorpropham, dimethoate, ethoprophos, fenamidone, methiocarb, omethoate, propiconazole and pymetrozine in or on certain products (Text with EEA relevance) THE EUROPEAN COMMISSION, Having regard to the Treaty on the Functioning of the European Union, Having regard to Regulation (EC) No 396/2005 of the European Parliament and of the Council of 23 February 2005 on maximum residue levels of pesticides in or on food and feed of plant and animal origin and amending Council Directive 91/414/EEC1, and in particular Article 14(1)(a) and Article 18(1)(b) thereof, Whereas: (1) For chlorothalonil, chlorpropham, dimethoate, fenamidone, omethoate, propiconazole and pymetrozine maximum residue levels (MRLs) were set in Annex II to Regulation (EC) No 396/2005. For carbon tetrachloride, MRLs were set in Annex II and Part B of Annex III to that Regulation. For ethoprophos and methiocarb, MRLs were set in Part A of Annex III to that Regulation. (2) The approval of the active substance chlorothalonil was not renewed by Commission Implementing Regulation (EU) 2019/6772. -
Chemical Warfare Agents
Manuscript for Kirk-Othmer Encyclopedia of Chemical Technology August 2019 CHEMICAL WARFARE AGENTS This is the pre-print manuscript of an article published in the Kirk-Othmer Encyclopedia of Chemical Technology: https://onlinelibrary.wiley.com/doi/book/10.1002/0471238961 The published version of the article is available at the Wiley website: https://onlinelibrary.wiley.com/doi/10.1002/0471238961.0308051308011818.a01.pub3 How to cite: Costanzi, S. (2020). Chemical Warfare Agents. In Kirk‐Othmer Encyclopedia of Chemical Technology, (Ed.). doi:10.1002/0471238961.0308051308011818.a01.pub3 Stefano Costanzi Department of Chemistry and Center for Behavioral Neuroscience American University, Washington, D.C. [email protected] Chemical weapons are weapons that exploit the toxicity of chemicals to bring about death or harm. The toxic chemicals on which chemical weapons are based are known as chemical warfare agents. The elimination of this entire category of weapons is the aim of the Convention on the Prohibition of the Development, Production, Stockpiling and Use of Chemical Weapons and on their Destruction, also known as Chemical Weapons Convention or CWC, which was opened for signature in 1993 and entered into force in 1997. Administered and implemented by the Hague- based Organisation for the Prohibition of Chemical Weapons (OPCW), the CWC is an international treaty that enjoys almost universal embracement, having been ratified or acceded by 193 States Parties. Importantly, the CWC poses a complete and absolute ban on chemical weapons, mandating State Parties to renounce “(a) to develop, produce, otherwise acquire, stockpile or retain chemical weapons, or transfer, directly or indirectly, chemical weapons to anyone; (b) to use chemical weapons; (c) to engage in any military preparations to use chemical weapons; (d) to assist, encourage or induce, in any way, anyone to engage in any activity prohibited to a State Party” under the Convention (CWC Article II, Paragraph 1) (1-3).