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Monocrotophos Proposed AEGL Document
MONOCROTOPHOS Page 1 of 32 Proposed 10/2009 v.1 1 2 3 4 ACUTE EXPOSURE GUIDELINE LEVELS 5 (AEGLs) 6 7 8 PROPOSED 9 10 11 12 13 MONOCROTOPHOS 14 (CAS Reg. No. 6923-22-4) 15 16 17 18 19 20 MONOCROTOPHOS Page 2 of 32 Proposed 10/2009 v.1 1 2 PREFACE 3 4 Under the authority of the Federal Advisory Committee Act (FACA) P. L. 92-463 of 5 1972, the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous 6 Substances (NAC/AEGL Committee) has been established to identify, review and interpret 7 relevant toxicologic and other scientific data and develop AEGLs for high priority, acutely toxic 8 chemicals. 9 10 AEGLs represent threshold exposure limits for the general public and are applicable to 11 emergency exposure periods ranging from 10 minutes to 8 hours. Three levels C AEGL-1, 12 AEGL-2 and AEGL-3 C are developed for each of five exposure periods (10 and 30 minutes, 1 13 hour, 4 hours, and 8 hours) and are distinguished by varying degree of severity of toxic effects. 14 The three AEGLs are defined as follows: 15 16 AEGL-1 is the airborne concentration (expressed as parts per million or milligrams per 17 cubic meter [ppm or mg/m3]) of a substance above which it is predicted that the general 18 population, including susceptible individuals, could experience notable discomfort, irritation, or 19 certain asymptomatic, non-sensory effects. However, the effects are not disabling and are 20 transient and reversible upon cessation of exposure. -
Downloads/Pgm Hydrus1d/HYDRUS-4.16.Pdf (Accessed on 20 April 2019)
water Article Assessment of the Environmental Risk of Pesticides Leaching at the Watershed Scale under Arid Climatic Conditions and Low Recharge Rates Hesham M. Ibrahim 1,2,* and Ali M. Al-Turki 1 1 Department of Soil Science, College of Food and Agricultural Sciences, King Saud University, P.O. Box 2460, Riyadh 11451, Saudi Arabia; [email protected] 2 Department of Soils and Water, Faculty of Agriculture, Suez Canal University, Ismailia 41522, Egypt * Correspondence: [email protected]; Tel.: +966-501728656 Received: 5 January 2020; Accepted: 2 February 2020; Published: 5 February 2020 Abstract: The assessment of the vulnerability of soil and groundwater resources to pesticide contamination is important to reduce the risk of environmental pollution. The applicability of the expanded attenuation factor (EAF) to assess leaching potential of 30 pesticides was investigated under 1 four recharge rates (0.0003–0.002 m d− ) in the arid environment of the Jazan watershed. EAF results revealed that Picloram, Carbofuran, Monocrotophos, and 2,4-D pesticides showed high leaching potential, mainly because of their low KOC, and relatively longer t1/2. In addition, medium leaching potential was observed with six more pesticides (Atrazine, Aldicarb, Simazine, Methomyl, Oxamyl, and Lindane). Regardless of the recharge rate, all other pesticides showed a very low leaching potential in the Jazan watershed. Sensitivity analysis revealed that the output of the EAF index is most sensitive to the fraction of organic carbon ( foc), water content at field capacity (θFC ), recharge rate (q), and partition coefficient (KOC), and least sensitive to soil bulk density (ρb) and air-filled porosity (na). -
Florida State Emergency Response Commission
Florida State Emergency Response Commission Sub-Committee on Training (SOT) HAZARDOUS MATERIALS MEDICAL TREATMENT PROTOCOLS Version 3.3 TOXIDROMES Toxidromes are clinical syndromes that the patient presents with. These patterns of signs and symptoms are essential for the successful recognition of chemical exposure. The toxidromes identified in this protocol are chemical exposure based while others such as the opioids are found within general medical protocol. These chemical toxidromes are identified clinically into five syndromes: Irritant Gas Toxidrome Asphyxiant Toxidrome Corrosive Toxidrome Hydrocarbon and Halogenated Hydrocarbons Toxidrome Cholinergic Toxidrome Each can present as a clinical manifestation of the chemical/poisoning involved with some cross-over between toxidromes. This list combines the toxic syndromes found within NFPA 473 (A.5.4.1(2) and traditional syndromes. Toxidrome Correlation to NFPA Standard 473 and Traditional Syndromes Toxidrome NFPA 473 A.5.4.1(2) Hazardous Materials Protocol Correlation Irritant Gas (j) Irritants Bronchospasm OC Pepper spray & lacrimants Asphyxiant (c) Chemical asphyxiants Carbon Monoxide (d) Simple asphyxiants Aniline dyes, Nitriles, Nitrares (h) Blood Agents Cyanide & Hydrogen Sulfide (n) Nitrogen Compounds Closed Space Fires Simple Asphyxants Corrosive (a) Corrosives Hydrofluroic Acid (g) Vesicants Chemical burns to the eye Choramine and Chlorine Hydrocarbon (e) Organic solvents Phenol and (q) Phenolic Compounds Halogenated Hydrocarbons Halogenated Hydrocarbons Cholinergic (b) Pesticides -
Photocatalytic Degradation of Monocrotophos and Chlorpyrifos In
Journal of Water Process Engineering 7 (2015) 94–101 Contents lists available at ScienceDirect Journal of Water Process Engineering journa l homepage: www.elsevier.com/locate/jwpe Photocatalytic degradation of monocrotophos and chlorpyrifos in aqueous solution using TiO2 under UV radiation ∗ Augustine Amalraj, Anitha Pius Department of Chemistry, The Gandhigram Rural Institute – Deemed University, Gandhigram, Dindigul 624 302, Tamil Nadu, India a r t i c l e i n f o a b s t r a c t Article history: Monocrotophos (MCP) and chlorpyrifos (CPS) are most popular and broadly used organophosphorous Received 6 November 2014 pesticides owing to its low cost and high efficiency in controlling pests in agriculture. Presence of Received in revised form 2 June 2015 pesticides in aquatic environments causes serious problems to human beings and other organisms. Photo- Accepted 2 June 2015 catalytic degradation has been proved to be a promising method for the treatment of water. In view of this, Available online 17 June 2015 TiO2 photocatalyst was prepared by sol–gel method and characterized by SEM with EDAX, XRD, BET and FTIR. The photocatalytic degradation of MCP and CPS was carried out using prepared TiO2 photocatalyst Keywords: irradiated with 16 W UV light source. The effect of various parameters, i.e., photocatalyst concentration, TiO2 nanoparticles Pesticides pesticide concentration and pH of the solution on the percentage of degradation of selected pesticides Monocrotophos had been examined. The kinetic analysis of photodegradation of MCP and CPS under different initial con- Chlorpyrifos centration followed the Langmuir–Hinshelwood model. TiO2 found to be an excellent photocatalyst for Langmuir–Hinshelwood model the degradation of MCP and CPS under UV light irradiation. -
Pesticide Residue Monitoring in Sediment and Surface Water Within the South Florida Water Management District Volume 2
Technical Publication 91-01 Pesticide Residue Monitoring in Sediment and Surface Water Within the South Florida Water Management District Volume 2 by Richard J. Pfeuffer January 1991 This publication was produced at an annual cost of $243.75 or $.49 per copy to inform the public. 500 191 Produced on recycled paper. Water Quality Division Research and Evaluation Department South Florida Water Management District West Palm Beach, Florida A IBSTRAC'I' Pesticide monitoring data are collected under the requirements of several permits and agreements as an indicator of water quality. The monitoring provides data to determine shifts or adverse trends in the quality of water being delivered to Lake Okeechobee, Everglades National Park, and the Water Conservation Areas. In addition, pesticide residue data are collected throughout the South Florida Water Management District at locations selected to determine water quality conditions at the major water control points. Special investigations are performed on selected pesticides as required and follow-up sampling is conducted based on the pesticides detected. Data were collected from 13 stations in 1984. By 1988, the network was expanded to 29 stations. Currently, water and sediment samples are collected quarterly and analyzed for 67 pesticides, herbicides and degradation products. Out of a total of 197 surface water samples, 13 percent had detectable residues, while 25 percent of the 208 sediment samples had detectable residues. The compounds detected in the water samples included atrazine and zinc phosphide while a variety of compounds, including DDT, have been detected in the sediment. None of the residues detected are considered to have adverse health or environmental effects. -
Review of Azinphos-Methyl Was Undertaken by the Office of Chemical Safety (OCS), Which Considered All the Toxicological Data and Information Submitted for the Review
The reconsideration of the active constituent azinphos-methyl, registrations of products containing azinphos-methyl and approvals of their associated labels PRELIMINARY REVIEW FINDINGS Volume 1: Review Summary OCTOBER 2006 Canberra Australia Azinphos-methyl review – Preliminary Review Findings © Australian Pesticides & Veterinary Medicines Authority 2006 This work is copyright. Apart from any use permitted under the Copyright Act 1968, no part may be reproduced without permission from the Australian Pesticides & Veterinary Medicines Authority. The Australian Pesticides & Veterinary Medicines Authority publishes this preliminary review findings report for the active constituent azinphos-methyl and products containing azinphos- methyl. For further information about this review or the Pesticides Review Program, contact: Manager Chemical Review Australian Pesticides & Veterinary Medicines Authority PO Box E 240 KINGSTON ACT 2604 Australia Telephone: 61 2 6272 3213 Facsimile: 61 2 6272 3218 Email: [email protected] APVMA web site: http://www.apvma.gov.au i Azinphos-methyl review – Preliminary Review Findings FOREWORD The Australian Pesticides & Veterinary Medicines Authority (APVMA) is an independent statutory authority with responsibility for the regulation of agricultural and veterinary chemicals in Australia. Its statutory powers are provided in the Agvet Codes scheduled to the Agricultural and Veterinary Chemicals Code Act 1994. The APVMA can reconsider the approval of an active constituent, the registration of a chemical product or -
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. -
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. -
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 .......................................................................... -
Organophosphate Insecticides
CHAPTER 4 HIGHLIGHTS Organophosphate Insecticides Acts through phosphorylation of the acetylcholinesterase enzyme Since the removal of organochlorine insecticides from use, organophosphate at nerve endings insecticides have become the most widely used insecticides available today. More Absorbed by inhalation, than forty of them are currently registered for use and all run the risk of acute ingestion, and skin and subacute toxicity. Organophosphates are used in agriculture, in the home, penetration in gardens, and in veterinary practice. All apparently share a common mecha- Muscarinic, nicotinic & CNS nism of cholinesterase inhibition and can cause similar symptoms. Because they effects share this mechanism, exposure to the same organophosphate by multiple routes or to multiple organophosphates by multiple routes can lead to serious additive Signs and Symptoms: toxicity. It is important to understand, however, that there is a wide range of Headache, hypersecretion, toxicity in these agents and wide variation in cutaneous absorption, making muscle twitching, nausea, specific identification and management quite important. diarrhea Respiratory depression, seizures, loss of consciousness Toxicology Miosis is often a helpful Organophosphates poison insects and mammals primarily by phosphory- diagnostic sign lation of the acetylcholinesterase enzyme (AChE) at nerve endings. The result is a loss of available AChE so that the effector organ becomes overstimulated by Treatment: the excess acetylcholine (ACh, the impulse-transmitting substance) in the nerve Clear airway, improve tissue ending. The enzyme is critical to normal control of nerve impulse transmission oxygenation from nerve fibers to smooth and skeletal muscle cells, glandular cells, and Administer atropine sulfate autonomic ganglia, as well as within the central nervous system (CNS). -
Evaluation of Genotoxicity of Monocrotophos and Quinalphos In
Integrative Pharmacology, Toxicology and Genotoxicology Research Article ISSN: 2058-8496 Evaluation of genotoxicity of monocrotophos and quinalphos in rats and protective effects of melatonin Vibhuti Mishra, Sapneh Sharma, Shilpa Khatri and Nalini Srivastava* School of Studies in Biochemistry, Jiwaji University, Gwalior 474 011, India Abstract Monocrotophos [dimethyl-[E]-1-methyl-2-(methyl carbamoyl) vinyl phosphate, MCP] and quinalphos [O,O-diethyl-o-(2-quinoxymethyl)-phosphorothionate, QNP] are highly toxic, broad spectrum and cholinesterase inhibiting pesticides which are extensively used in agriculture and household. Acute and chronic exposure of these pesticides has adverse effects on living organisms. Present study was carried out to evaluate the genotoxic potential of these pesticides using comet assay and micronucleus assay in rats and also to analyze the protective effects of melatonin. Both acute and chronic exposure caused DNA damage in rat tissues and lymphocytes as evident from the statistically significant increase in DNA damage index on pesticide exposure. However the co-treatment of melatonin decreased the damage index to significant levels. At the same time, statistically significant number of micronuclei was observed in polychromatic erythrocytes (PCE) in the bone marrow of rats treated with pesticides when compared to control group but the co-treatment of melatonin decreased the number of micronucleated PCE in the pesticide treated rats. Hence, the co treatment of melatonin has the ability to reduce the genotoxic potential of MCP and QNP under the experimental conditions applied in the present study. Introduction is an inevitable consequence of cellular metabolism, with a propensity for increased levels following toxic insults due to exposure with Pesticides are highly toxic compounds extensively used for the various environmental chemicals, radiations, metals and pesticides. -
Acutely / Extremely Hazardous Waste List
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 Extemely Hazardous 1,1,1-Trichloro-2, -bis(p-methoxyphenyl)ethane Extemely Hazardous 1,1a,2,2,3,3a,4,5,5,5a,5b,6-Dodecachlorooctahydro-1,3,4-metheno-1H-cyclobuta (cd) pentalene, Dechlorane Extemely Hazardous 1,1a,3,3a,4,5,5,5a,5b,6-Decachloro--octahydro-1,2,4-metheno-2H-cyclobuta (cd) pentalen-2- one, chlorecone Extemely Hazardous 1,1-Dimethylhydrazine 57-14-7 Extemely 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 Extemely Hazardous 1,2,3-Propanetriol, trinitrate P081 55-63-0 Acutely Hazardous 1,2,3-Propanetriol, trinitrate 55-63-0 Extemely Hazardous 1,2,4,5,6,7,8,8-Octachloro-4,7-methano-3a,4,7,7a-tetra- hydro- indane Extemely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]- 51-43-4 Extemely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]-, P042 51-43-4 Acutely Hazardous 1,2-Dibromo-3-chloropropane 96-12-8 Extemely Hazardous 1,2-Propylenimine P067 75-55-8 Acutely Hazardous 1,2-Propylenimine 75-55-8 Extemely Hazardous 1,3,4,5,6,7,8,8-Octachloro-1,3,3a,4,7,7a-hexahydro-4,7-methanoisobenzofuran Extemely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime 26419-73-8 Extemely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime.