The Analysis of Micro Amounts of Binapacryl, EPN, Methyl Parathion, and Parathion
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Additive Interactions of Some Reduced-Risk Biocides and Two
www.nature.com/scientificreports OPEN Additive interactions of some reduced‑risk biocides and two entomopathogenic nematodes suggest implications for integrated control of Spodoptera litura (Lepidoptera: Noctuidae) Rashad Rasool Khan 1,2*, Muhammad Arshad 1*, Asad Aslam 3 & Muhammad Arshad 4 Higher volumes of conventional and novel chemical insecticides are applied by farmers to control resistant strains of armyworm (Spodoperta litura) in Pakistan without knowing their risks to the environment and to public health. Ten reduced‑risk insecticides were tested for their compatibility with two entomopathogenic nematodes (EPNs); Heterorhabditis indica and Steinernema carpocapsae rd against S. litura. The insecticide emamectin benzoate was highly toxic (LC50 = 2.97 mg/l) against 3 instar S. litura larvae when applied alone whereas, novaluron and methoxyfenozide were the least toxic (LC50 = 29.56 mg/l and 21.06 mg/l), respectively. All the insecticides proved harmless against the two EPNs even 96 h after treatment. Indoxacarb, fubendiamide and spinetoram produced the greatest mortalities (72–76%) of S. litura larvae after 72 h when applied in mixtures with H. indica. Lowest mortalities (44.00 ± 3.74% and 48.00 ± 2.89) were observed for mixtures of H. indica with methoxyfenozide and chlorfenapyr, respectively. The positive control treatments with both EPNs (S. carpocapsae and H. indica) produced > 50% mortality 96 h after treatment. For insecticide mixtures with S. carpocapsae, only indoxacarb produced 90% mortality of larvae, whereas, indoxacarb, fubendiamide, emamectin benzoate, and spinetoram produced 90–92% mortality of larvae when applied in mixtures with H. indica. Additive interactions (Chi‑square < 3.84) of EPN mixtures with reduced volumes of reduced‑risk insecticides suggest opportunities to develop more environmentally favorable pest management programs for S. -
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 ..................................................................................................................................... -
Oxydemeton-Methyl (166) Demeton-S-Methyl (073
oxydemeton-methyl 993 OXYDEMETON-METHYL (166) DEMETON-S-METHYL (073) EXPLANATION Oxydemeton-methyl (ODM) was evaluated for residues by the JMPR in 1968, 1973, 1979, 1984, 1989, and 1992. The 1992 review was a complete re-evaluation. It reviewed extensive residue data from supervised trials on all major crops and associated data on use patterns, storage stability, processing, and methods of residue analysis were reviewed and numerous MRLs were recommended. The MRLs are expressed as the sum oxydemeton-methyl, demeton-S-methyl, and demeton-S- methylsulphon, expressed as oxydemeton-methyl. The ADI was established in 1989 at 0.0003 mg/kg body weight and is for the sum of the three compounds. Demeton-S-methyl is an insecticide. The sulfoxide of demeton-S-methyl is ODM. It currently has no MRLs. The 1995 CCPR scheduled ODM and demeton-S-methyl for periodic review of residue aspects by the 1997 JMPR (ALINORM 95/24A). This was changed by the 1997 CCPR, which scheduled ODM and demeton-S-methyl for periodic review by the 1998 JMPR. Bayer AG has submitted data in support of the Periodic Review which included information on crops and regions of interest to that company. The governments of Germany and The Netherlands have also submitted information. IDENTITY Common name (ISO): Oxydemeton-methyl Chemical name: IUPAC: S-2-ethylsulfinylethyl O,O-dimethyl phosphothioate CA: S-[2-ethylsulfinyl)ethyl] O,O-dimethyl phosphothioate CAS number: 301-12-2 EU-index number: 015-046-00-7 EINECS number: 206-110-7 CIPAC number: 171 Molecular formula: C6 H15 O4 P S2 Synonyms: Metasystox R Structural formula: . -
Method 8141B
METHOD 8141B ORGANOPHOSPHORUS COMPOUNDS BY GAS CHROMATOGRAPHY 1.0 SCOPE AND APPLICATION 1.1 This method provides procedures for the gas chromatographic (GC) determination of organophosphorus (OP) compounds. The compounds listed in the table below can be determined by GC using capillary columns with a flame photometric detector (FPD) or a nitrogen-phosphorus detector (NPD). Triazine herbicides can also be determined with this method when the NPD is used. Although performance data are presented for each of the listed chemicals, it is unlikely that all of them could be determined in a single analysis. This limitation results because the chemical and chromatographic behavior of many of these chemicals can result in co-elution. The analyst must select columns, detectors, and calibration procedures for the specific analytes of interest. Any listed chemical is a potential method interference when it is not a target analyte. Analyte CAS Registry No. Organophosphorus Pesticides Asponb 3244-90-4 Azinphos-methyl 86-50-0 Azinphos-ethyla 2642-71-9 Bolstar (Sulprofos) 35400-43-2 Carbophenothiona 786-19-6 Chlorfenvinphosa 470-90-6 Chlorpyrifos 2921-88-2 Chlorpyrifos methyla 5598-13-0 Coumaphos 56-72-4 Crotoxyphosa 7700-17-6 Demeton-Oc 8065-48-3 Demeton-Sc 8065-48-3 Diazinon 333-41-5 Dichlorofenthiona 97-17-6 Dichlorvos (DDVP) 62-73-7 Dicrotophosa 141-66-2 Dimethoate 60-51-5 Dioxathiona,c 78-34-2 Disulfoton 298-04-4 EPN 2104-64-5 Ethiona 563-12-2 Ethoprop 13194-48-4 Famphura 52-85-7 8141B - 1 Revision 2 November 2000 Analyte CAS Registry No. Fenitrothiona -
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. -
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 .......................................................................... -
Methyl-S-Demeton
Methyl-S-demeton (CAS No: 919-86-8) Health-based Reassessment of Administrative Occupational Exposure Limits Committee on Updating of Occupational Exposure Limits, a committee of the Health Council of the Netherlands No. 2000/15OSH/072, The Hague, 22 september 2003 Preferred citation: Health Council of the Netherlands: Committee on Updating of Occupational Exposure Limits. Methyl-S-demeton; Health-based Reassessment of Administrative Occupational Exposure Limits. The Hague: Health Council of the Netherlands, 2003; 2000/15OSH/072. all rights reserved 1 Introduction The present document contains the assessment of the health hazard of methyl-S- demeton by the Committee on Updating of Occupational Exposure Limits, a committee of the Health Council of the Netherlands. The first draft of this document was prepared by JAGM van Raaij, Ph.D. and WK de Raat, Ph.D. (OpdenKamp Registration & Notification, Zeist, the Netherlands) and J Krüse, Ph.D. (Kinetox, Vleuten, the Netherlands).* The evaluation of the toxicity of methyl-S-demeton has been based on reviews published in the ‘Handbook of pesticide toxicology’ (Gal91) and by the American Conference of Governmental Industrial Hygienists (ACG99). Where relevant, the original publications were reviewed and evaluated as will be indicated in the text. In addition, in December 1999, literature was searched in the on-line databases Toxline, Medline, Chemical Abstracts, covering the period of 1964-1966 until December 1999, and using the following key words: methyl demeton and 919-68-8. Data from unpublished studies were generally not taken into account. Exceptions were made for studies that were summarised and evaluated by international bodies such as the Food and Agricultural Organization/World Health Organization (FAO/WHO: Joint Meeting of the FAO Panel of Experts on Pesticides Residues on Food and the Environment and the WHO Expert Group on Pesticides Residues - JMPR) (FAO90, WHO85) and the International Programme on Chemical Safety/World Health Organization (IPCS/ WHO) (WHO97). -
744 Hydrolysis of Chiral Organophosphorus Compounds By
[Frontiers in Bioscience, Landmark, 26, 744-770, Jan 1, 2021] Hydrolysis of chiral organophosphorus compounds by phosphotriesterases and mammalian paraoxonase-1 Antonio Monroy-Noyola1, Damianys Almenares-Lopez2, Eugenio Vilanova Gisbert3 1Laboratorio de Neuroproteccion, Facultad de Farmacia, Universidad Autonoma del Estado de Morelos, Morelos, Mexico, 2Division de Ciencias Basicas e Ingenierias, Universidad Popular de la Chontalpa, H. Cardenas, Tabasco, Mexico, 3Instituto de Bioingenieria, Universidad Miguel Hernandez, Elche, Alicante, Spain TABLE OF CONTENTS 1. Abstract 2. Introduction 2.1. Organophosphorus compounds (OPs) and their toxicity 2.2. Metabolism and treatment of OP intoxication 2.3. Chiral OPs 3. Stereoselective hydrolysis 3.1. Stereoselective hydrolysis determines the toxicity of chiral compounds 3.2. Hydrolysis of nerve agents by PTEs 3.2.1. Hydrolysis of V-type agents 3.3. PON1, a protein restricted in its ability to hydrolyze chiral OPs 3.4. Toxicity and stereoselective hydrolysis of OPs in animal tissues 3.4.1. The calcium-dependent stereoselective activity of OPs associated with PON1 3.4.2. Stereoselective hydrolysis commercial OPs pesticides by alloforms of PON1 Q192R 3.4.3. PON1, an enzyme that stereoselectively hydrolyzes OP nerve agents 3.4.4. PON1 recombinants and stereoselective hydrolysis of OP nerve agents 3.5. The activity of PTEs in birds 4. Conclusions 5. Acknowledgments 6. References 1. ABSTRACT Some organophosphorus compounds interaction of the racemic OPs with these B- (OPs), which are used in the manufacturing of esterases (AChE and NTE) and such interactions insecticides and nerve agents, are racemic mixtures have been studied in vivo, ex vivo and in vitro, using with at least one chiral center with a phosphorus stereoselective hydrolysis by A-esterases or atom. -
Enzymatic Degradation of Organophosphorus Pesticides and Nerve Agents by EC: 3.1.8.2
catalysts Review Enzymatic Degradation of Organophosphorus Pesticides and Nerve Agents by EC: 3.1.8.2 Marek Matula 1, Tomas Kucera 1 , Ondrej Soukup 1,2 and Jaroslav Pejchal 1,* 1 Department of Toxicology and Military Pharmacy, Faculty of Military Health Sciences, University of Defence, Trebesska 1575, 500 01 Hradec Kralove, Czech Republic; [email protected] (M.M.); [email protected] (T.K.); [email protected] (O.S.) 2 Biomedical Research Center, University Hospital Hradec Kralove, Sokolovska 581, 500 05 Hradec Kralove, Czech Republic * Correspondence: [email protected] Received: 26 October 2020; Accepted: 20 November 2020; Published: 24 November 2020 Abstract: The organophosphorus substances, including pesticides and nerve agents (NAs), represent highly toxic compounds. Standard decontamination procedures place a heavy burden on the environment. Given their continued utilization or existence, considerable efforts are being made to develop environmentally friendly methods of decontamination and medical countermeasures against their intoxication. Enzymes can offer both environmental and medical applications. One of the most promising enzymes cleaving organophosphorus compounds is the enzyme with enzyme commission number (EC): 3.1.8.2, called diisopropyl fluorophosphatase (DFPase) or organophosphorus acid anhydrolase from Loligo Vulgaris or Alteromonas sp. JD6.5, respectively. Structure, mechanisms of action and substrate profiles are described for both enzymes. Wild-type (WT) enzymes have a catalytic activity against organophosphorus compounds, including G-type nerve agents. Their stereochemical preference aims their activity towards less toxic enantiomers of the chiral phosphorus center found in most chemical warfare agents. Site-direct mutagenesis has systematically improved the active site of the enzyme. These efforts have resulted in the improvement of catalytic activity and have led to the identification of variants that are more effective at detoxifying both G-type and V-type nerve agents. -
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. -
(074) EXPLANATION Residue Aspects of Disulfoton Were Reviewed
disulfoton 587 DISULFOTON (074) EXPLANATION Residue aspects of disulfoton were reviewed by the JMPR in 1973, 1975, 1979, 1981, 1984, 1991 and 1994. At the 1996 CCPR MRLs set "at or about the limit of determination" were amended from 0.01 to 0.02 mg/kg after a recommendation from the Ad Hoc Working Group On Methods of Analysis (ALINORM 97/24 para. 52). Several delegations expressed concern at the high levels of estimated intakes relative to the ADI and it was noted that processing data were not available for refinement of the estimation of intake. The Committee requested revised intake calculations and decided to keep all other proposals at step 7C (ALINORM 97/24, paras. 53 and 54). In 1997, the CCPR was informed that additional data would be available for the 1998 JMPR and disulfoton MRLs were kept at Step 7B pending the 1998 evaluation. The present Meeting received new residue data on lima beans, cotton, lettuce and potatoes, as well as reports of recent processing studies on coffee, cotton seed, maize, sorghum and wheat. Processing data on potatoes were also submitted, although minimal information was provided on the field conditions and the analytical methods used. The Meeting received summaries of data reviewed in the previous monographs on disulfoton for the estimation of STMRs and refinement of the dietary intake calculations. IDENTITY ISO Common name: disulfoton Chemical name IUPAC: O,O-diethyl S-2-ethylthioethyl phosphorodithioate CA: O,O-diethyl S-[2-(ethylthio)ethyl] phosphorodithioate CAS no: [298-04-4] Synonyms: disyston Structural formula: S CH 3 CH 2 O P S S CH 3 CH 3 CH 2 O Molecular formula: C8H19O2PS3 Molecular weight: 274.4 Physical and chemical properties Pure active ingredient Appearance: colourless oil with a characteristic odour 588 disulfoton Vapour pressure: 7.2 mPa (20°C), 13 mPa (25°C), 22 mPa (30°C) Melting point: <-25°C Boiling point: 128°C at 1 mm Hg Octanol/water partition coefficient: log Pow = 3.95 Solubility: water 12 mg/l (20°C).