Catalytic Efficiencies of Directly Evolved Phosphotriesterase Variants with Structurally Different Organophosphorus Compounds in Vitro
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Physical Study by Surface Characteriza4ons of Sarin Sensor on the Basis of Chem
Physical Study by Surface Characterizaons of Sarin Sensor on the Basis of Chemically Func4onalized Silicon Nanoribbon Field Effect Transistor K. Smaali1,§, D. Guérin1, V. Passi1, L. Ordronneau2, A. Carella2, T. Mélin1, E. Dubois1, D. Vuillaume1, J.P. Simonato2 and S. Lenfant1,* 1 IEMN, CNRS, Avenue Poincaré, Villeneuve d'Ascq, F-59652 cedex, France. 2. CEA, LITEN/DTNM/SEN/LSIN, Univ. Grenoble Alpes, MINATEC Campus, F-38054 Grenoble, France. ABSTRACT : Surface characteriZa[ons of an organophosphorus (OP) gas detector based on chemically func[onaliZed silicon nanoribbon field-effect transistor (SiNR-FET) were performed by Kelvin Probe Force Microscopy (KPFM) and ToF-SIMS, and correlated with changes in the current-voltage characteris[cs of the devices. KPFM measurements on FETs allow (i) to inves[gate the contact poten[al difference (CPD) distribu[on of the polariZed device as func[on of the gate voltage and the exposure to OP traces and; (ii) to analyZe the CPD hysteresis associated to the presence of mobile ions on the surface. The CPD measured by KPFM on the silicon nanoribbon was corrected due to side capacitance effects in order to determine the real quan[ta[ve surface poten[al. Comparison with macroscopic Kelvin probe (KP) experiments on larger surfaces was carried out. These two approaches were quan[ta[vely consistent. An important increase of the CPD values (between + 399 mV and + 302 mV) was observed aeer the OP sensor graeing, corresponding to a decrease of the work func[on, and a weaker varia[on aeer exposure to OP (between - 14 mV and - 61 mV) was measured. -
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. -
Development and Validation of a Method for the Simultaneous
CORE Metadata, citation and similar papers at core.ac.uk Provided by UGD Academic Repository American Journal of Applie d Chemistry 2014; 2(4): 46-54 Published online August 10, 2014 (http://www.sciencepublishinggroup.com/j/ajac) doi: 10.11648/j.ajac.20140204.11 ISSN: 2330-8753 (Print); ISSN: 2330-8745 (Online) Development and validation of a method for the simultaneous determination of 20 organophosphorus pesticide residues in corn by accelerated solvent extraction and gas chromatography with nitrogen phosphorus detection Vesna Kostik *, Biljana Gjorgeska, Bistra Angelovska Medical Faculty, Department of Pharmacy, University “Goce Delchev”, Shtip, Republic of Macedonia Email address: [email protected] (V. Kostik), [email protected] (B. Gjorgeska), [email protected] (B. Angelovska) To cite this article: Vesna Kostik, Biljana Gjorgeska, Bistra Angelovska. Development and Validation of a Method for the Simultaneous Determination of 20 Organophosphorus Pesticide Residues in Corn by Accelerated Solvent Extraction and Gas Chromatography with Nitrogen Phosphorus Detection. American Journal of Applied Chemistry. Vol. 2, No. 4, 2014, pp. 46-54. doi: 10.11648/j.ajac.20140204.11 Abstract: The method for simultaneous determination of 20 organophosphorus pesticide residues in corn samples has been developed and validated. For the extraction of organophosporus pesticide residues from the samples, the accelerated solvent technique with the mixture of dichloromethane: acetone (1:1, V/V ) was used. Clean up was done using liquid – liquid extraction with n – hexane, followed by solid phase extraction on primary secondary amine adsorbent, and elution with the mixture of acetone: toluene (65:35). The determination of the pesticides was carried out by gas chromatography with nitrogen phosphorus detection. -
Use of Chlorofluorocarbons in Hydrology : a Guidebook
USE OF CHLOROFLUOROCARBONS IN HYDROLOGY A Guidebook USE OF CHLOROFLUOROCARBONS IN HYDROLOGY A GUIDEBOOK 2005 Edition The following States are Members of the International Atomic Energy Agency: AFGHANISTAN GREECE PANAMA ALBANIA GUATEMALA PARAGUAY ALGERIA HAITI PERU ANGOLA HOLY SEE PHILIPPINES ARGENTINA HONDURAS POLAND ARMENIA HUNGARY PORTUGAL AUSTRALIA ICELAND QATAR AUSTRIA INDIA REPUBLIC OF MOLDOVA AZERBAIJAN INDONESIA ROMANIA BANGLADESH IRAN, ISLAMIC REPUBLIC OF RUSSIAN FEDERATION BELARUS IRAQ SAUDI ARABIA BELGIUM IRELAND SENEGAL BENIN ISRAEL SERBIA AND MONTENEGRO BOLIVIA ITALY SEYCHELLES BOSNIA AND HERZEGOVINA JAMAICA SIERRA LEONE BOTSWANA JAPAN BRAZIL JORDAN SINGAPORE BULGARIA KAZAKHSTAN SLOVAKIA BURKINA FASO KENYA SLOVENIA CAMEROON KOREA, REPUBLIC OF SOUTH AFRICA CANADA KUWAIT SPAIN CENTRAL AFRICAN KYRGYZSTAN SRI LANKA REPUBLIC LATVIA SUDAN CHAD LEBANON SWEDEN CHILE LIBERIA SWITZERLAND CHINA LIBYAN ARAB JAMAHIRIYA SYRIAN ARAB REPUBLIC COLOMBIA LIECHTENSTEIN TAJIKISTAN COSTA RICA LITHUANIA THAILAND CÔTE D’IVOIRE LUXEMBOURG THE FORMER YUGOSLAV CROATIA MADAGASCAR REPUBLIC OF MACEDONIA CUBA MALAYSIA TUNISIA CYPRUS MALI TURKEY CZECH REPUBLIC MALTA UGANDA DEMOCRATIC REPUBLIC MARSHALL ISLANDS UKRAINE OF THE CONGO MAURITANIA UNITED ARAB EMIRATES DENMARK MAURITIUS UNITED KINGDOM OF DOMINICAN REPUBLIC MEXICO GREAT BRITAIN AND ECUADOR MONACO NORTHERN IRELAND EGYPT MONGOLIA UNITED REPUBLIC EL SALVADOR MOROCCO ERITREA MYANMAR OF TANZANIA ESTONIA NAMIBIA UNITED STATES OF AMERICA ETHIOPIA NETHERLANDS URUGUAY FINLAND NEW ZEALAND UZBEKISTAN FRANCE NICARAGUA VENEZUELA GABON NIGER VIETNAM GEORGIA NIGERIA YEMEN GERMANY NORWAY ZAMBIA GHANA PAKISTAN ZIMBABWE The Agency’s Statute was approved on 23 October 1956 by the Conference on the Statute of the IAEA held at United Nations Headquarters, New York; it entered into force on 29 July 1957. The Headquarters of the Agency are situated in Vienna. -
Nerve Agent - Lntellipedia Page 1 Of9 Doc ID : 6637155 (U) Nerve Agent
This document is made available through the declassification efforts and research of John Greenewald, Jr., creator of: The Black Vault The Black Vault is the largest online Freedom of Information Act (FOIA) document clearinghouse in the world. The research efforts here are responsible for the declassification of MILLIONS of pages released by the U.S. Government & Military. Discover the Truth at: http://www.theblackvault.com Nerve Agent - lntellipedia Page 1 of9 Doc ID : 6637155 (U) Nerve Agent UNCLASSIFIED From lntellipedia Nerve Agents (also known as nerve gases, though these chemicals are liquid at room temperature) are a class of phosphorus-containing organic chemicals (organophosphates) that disrupt the mechanism by which nerves transfer messages to organs. The disruption is caused by blocking acetylcholinesterase, an enzyme that normally relaxes the activity of acetylcholine, a neurotransmitter. ...--------- --- -·---- - --- -·-- --- --- Contents • 1 Overview • 2 Biological Effects • 2.1 Mechanism of Action • 2.2 Antidotes • 3 Classes • 3.1 G-Series • 3.2 V-Series • 3.3 Novichok Agents • 3.4 Insecticides • 4 History • 4.1 The Discovery ofNerve Agents • 4.2 The Nazi Mass Production ofTabun • 4.3 Nerve Agents in Nazi Germany • 4.4 The Secret Gets Out • 4.5 Since World War II • 4.6 Ocean Disposal of Chemical Weapons • 5 Popular Culture • 6 References and External Links --------------- ----·-- - Overview As chemical weapons, they are classified as weapons of mass destruction by the United Nations according to UN Resolution 687, and their production and stockpiling was outlawed by the Chemical Weapons Convention of 1993; the Chemical Weapons Convention officially took effect on April 291997. Poisoning by a nerve agent leads to contraction of pupils, profuse salivation, convulsions, involuntary urination and defecation, and eventual death by asphyxiation as control is lost over respiratory muscles. -
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). -
Chlorpyrifos (Dursban) Ddvp (Dichlorvos) Diazinon Malathion Parathion
CHLORPYRIFOS (DURSBAN) DDVP (DICHLORVOS) DIAZINON MALATHION PARATHION Method no.: 62 Matrix: Air Procedure: Samples are collected by drawing known volumes of air through specially constructed glass sampling tubes, each containing a glass fiber filter and two sections of XAD-2 adsorbent. Samples are desorbed with toluene and analyzed by GC using a flame photometric detector (FPD). Recommended air volume and sampling rate: 480 L at 1.0 L/min except for Malathion 60 L at 1.0 L/min for Malathion Target concentrations: 1.0 mg/m3 (0.111 ppm) for Dichlorvos (PEL) 0.1 mg/m3 (0.008 ppm) for Diazinon (TLV) 0.2 mg/m3 (0.014 ppm) for Chlorpyrifos (TLV) 15.0 mg/m3 (1.11 ppm) for Malathion (PEL) 0.1 mg/m3 (0.008 ppm) for Parathion (PEL) Reliable quantitation limits: 0.0019 mg/m3 (0.21 ppb) for Dichlorvos (based on the RAV) 0.0030 mg/m3 (0.24 ppb) for Diazinon 0.0033 mg/m3 (0.23 ppb) for Chlorpyrifos 0.0303 mg/m3 (2.2 ppb) for Malathion 0.0031 mg/m3 (0.26 ppb) for Parathion Standard errors of estimate at the target concentration: 5.3% for Dichlorvos (Section 4.6.) 5.3% for Diazinon 5.3% for Chlorpyrifos 5.6% for Malathion 5.3% for Parathion Status of method: Evaluated method. This method has been subjected to the established evaluation procedures of the Organic Methods Evaluation Branch. Date: October 1986 Chemist: Donald Burright Organic Methods Evaluation Branch OSHA Analytical Laboratory Salt Lake City, Utah 1 of 27 T-62-FV-01-8610-M 1. -
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. -
Malathion Human Health and Ecological Risk Assessment Final Report
SERA TR-052-02-02c Malathion Human Health and Ecological Risk Assessment Final Report Submitted to: Paul Mistretta, COR USDA/Forest Service, Southern Region 1720 Peachtree RD, NW Atlanta, Georgia 30309 USDA Forest Service Contract: AG-3187-C-06-0010 USDA Forest Order Number: AG-43ZP-D-06-0012 SERA Internal Task No. 52-02 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 5100 Highbridge St., 42C Fayetteville, New York 13066-0950 Fax: (315) 637-0445 E-Mail: [email protected] Home Page: www.sera-inc.com May 12, 2008 Table of Contents Table of Contents............................................................................................................................ ii List of Figures................................................................................................................................. v List of Tables ................................................................................................................................. vi List of Appendices ......................................................................................................................... vi List of Attachments........................................................................................................................ vi ACRONYMS, ABBREVIATIONS, AND SYMBOLS ............................................................... vii COMMON UNIT CONVERSIONS AND ABBREVIATIONS.................................................... x CONVERSION OF SCIENTIFIC NOTATION .......................................................................... -
Ambient Water Quality Criteria for Chlorpyrifos
United State. Office of Water EPA 440/5-86~05 Environmental Protection Regulations and Standards September 1986 Amy l. lea~erry Agency Criteria and Standards Division Washington DC 20460 Water &EPA Ambient Wat'er Quality Criteria for Chlorpyrifos - 1986 &~IENT AQUATIC LIFE WATER QUALITY CRITERIA FOR CHLORPYRIFOS U.S. ENVIRONMENTAL PROTECTION AGENCY OFFICE OF RESEARCH AND DEVELOPMENT ENVIRONMENTAL RESEARCH LABORATORIES DULUTH, MINNESOTA NARRAGANSETT, RHODE ISLAND NOTICES This document has been reviewed by the Criteria and Standards Division, Office of Water Regulations and Standards, U.S. Environmental Protection Agency, and approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. This document is availaryle to the public throu~h the National Technical Inf0rmation Service (NTIS), 5285 Port Royal Road, Springfield, VA 22161. 11 FOREWORD Section 304(a)(1) of the Clean Water Act of 1977 (P.L. 95-217) requires the Administrator of the Environmental Protection Agency to publish water quality criteria that accurately reflect the latest scientific knowledge on the kind and extent of all identifiable effects on health and welfare that might be expected from the presence of pollutants in any body of water~ including ground water. This document is a revision of proposed criteria based upon consideration of comments received from other Federal agencies~ State agencies~ special interest groups~ and individual scientists. Criteria contained in this document replace any previously published EPA aquatic life criteria for the same pollutant(s). The term "water quality criteria" is used in two sections of the Clean Water Act~ section 304(a)(1) and section 303(c)(2). -
Organic & Biomolecular Chemistry
Organic & Biomolecular Chemistry Accepted Manuscript This is an Accepted Manuscript, which has been through the Royal Society of Chemistry peer review process and has been accepted for publication. Accepted Manuscripts are published online shortly after acceptance, before technical editing, formatting and proof reading. Using this free service, authors can make their results available to the community, in citable form, before we publish the edited article. We will replace this Accepted Manuscript with the edited and formatted Advance Article as soon as it is available. You can find more information about Accepted Manuscripts in the Information for Authors. Please note that technical editing may introduce minor changes to the text and/or graphics, which may alter content. The journal’s standard Terms & Conditions and the Ethical guidelines still apply. In no event shall the Royal Society of Chemistry be held responsible for any errors or omissions in this Accepted Manuscript or any consequences arising from the use of any information it contains. www.rsc.org/obc Page 1 of 7 Organic & Biomolecular Chemistry Journal Name RSCPublishing ARTICLE Selective chromo-fluorogenic detection of DFP (a Sarin and Soman mimic) and DCNP (a Tabun mimic) Cite this: DOI: 10.1039/x0xx00000x with a unique probe based on a boron dipyrromethene (BODIPY) dye Manuscript Received 00th January 2012, Accepted 00th January 2012 Andrea Barba-Bon,a,b Ana M. Costero,a,b* Salvador Gil,a,b Ramón Martínez- a,c,d a,c,d DOI: 10.1039/x0xx00000x Máñez, * and Félix Sancenón www.rsc.org/ A novel colorimetric probe (P4) for the selective differential detection of DFP (a Sarin and Soman mimic) and DCNP (a Tabun mimic) was prepared. -
Probabilistic Assessment of the Cumulative Acute Exposure to Organophosphorus and Carbamate Insecticides in the Brazilian Diet E.D
Toxicology 222 (2006) 132–142 Probabilistic assessment of the cumulative acute exposure to organophosphorus and carbamate insecticides in the Brazilian diet E.D. Caldas a,∗, P.E. Boon b, J. Tressou c a Department of Pharmaceutical Sciences, College of Health Sciences, University of Bras´ılia, 70919-970 Bras´ılia, DF, Brazil b RIKILT, Institute of Food Safety, Wageningen University and Research Centre, 6708 PD Wageningen, The Netherlands c INRA, Unit´eM´et@risk, Methodologies d’analyse de risque alimentaire INA-PG, 75231 Paris, France Received 10 October 2005; received in revised form 1 February 2006; accepted 13 February 2006 Available online 6 March 2006 Abstract In the present study, the cumulative exposure of 25 acetylcholinesterase (AChE) inhibiting pesticides through the consumption of nine fruits and vegetables by the Brazilian population was assessed. Food consumption data were obtained from a household budget survey conducted in all Brazilian states from July 2002 to June 2003. Residue data from 4001 samples were obtained from the Brazilian national monitoring program on pesticide residues. Relative potency factors (RPF) were calculated with methamidophos or acephate as index compounds (IC), using BMD10 or NOAEL for AChE inhibition, mostly in rat brain, obtained from national and international pesticide evaluations. Monocrotophos and triazophos, in addition to aldicarb, had the highest calculated RPF in any scenario. The exposure to AChE inhibiting pesticides for the general population at P99.9, represented 33.6% of the ARfD as methamidophos and 70.2% ARfD as acephate. The exposure calculated as acephate could exceed the ARfD at the upper bound of the 95% confidence interval for this percentile.