Parathion-Methyl
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ACEPHATE (Addendum)
3 ACEPHATE (addendum) First draft prepared by Professor P.K. Gupta 1 and Dr Angelo Moretto 2 1 Rajinder Nagar, Bareilly, UP, India; 2 Dipartimento Medicina Ambientale e Sanità Pubblica, Università di Padova, Padova, Italy Explanation..........................................................................................................3 Evaluation for acceptable daily intake.................................................................4 Biochemical aspects ......................................................................................4 Oral absorption, distribution, excretion and metabolism .......................4 Toxicological studies.....................................................................................5 Acute toxicity.........................................................................................5 Short-term studies of toxicity.................................................................6 Special studies........................................................................................7 Studies on inhibition of cholinesterase activity in vitro ..................7 Short-term study of neurotoxicity ...................................................7 Developmental neurotoxicity..........................................................9 Observations in humans ..............................................................................10 Comments..........................................................................................................12 Toxicological evaluation ...................................................................................13 -
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. -
The Spruce Budworm, Choristoneura Fumiferana
02-01370 Spruce Budworm Bro 10/10/02 11:09 AM Page 1 MORE INFORMATION The he spruce budworm, Choristoneura fumiferana For more information on Spruce Budworms call: The Tree Line Spruce (Clemens), is the most destructive and widely (204) 945-7866. Or write: Budworm distributed forest defoliator in North America. Manitoba Conservation Forestry Branch In Manitoba T Forest Health and Ecology The destructive phase of this pest is the larval or caterpillar 200 Saulteaux Crescent Winnipeg, Manitoba R3J 3W3 stage. Massive budworm outbreaks occur periodically, Web site: www.gov.mb.ca/natres/forestry/ destroying hundreds of thousands of hectares of valuable fir and spruce. Aerial view of budworm damage In eastern Canada the budworm’s preferred food is balsam fir, Photos courtesy of Canadian Forest Service, Great Lakes Forest Research Centre, white spruce and red spruce. In Manitoba, the budworm Sault Ste. Marie, Ontario and Northern Forest Research Centre, Edmonton, Alberta. feeds primarily on white spruce and balsam fir, and, less frequently, on black spruce. 02-01370 Spruce Budworm Bro 10/10/02 11:09 AM Page 2 DESCRIPTION OF LIFE STAGES LIFE CYCLE DAMAGE CONTROL The adult moth has a wingspread of The female moth lays In light and moderate infestations Various insecticides are used 21 to 30 mm. It is grey-brown in its eggs in July on the damage is restricted to a partial against the spruce budworm to colour with silvery white patches on underside of needles. loss of new foliage, particularly in protect valuable spruce and fir the forewings. Normally, the eggs the upper crown trees. -
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 -
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 -
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. -
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. -
Fate and Effects of Azinphos-Methyl in a Flow-Through Wetland in South
Environ. Sci. Technol. 2003, 37, 2139-2144 preventing it from entering downstream aquatic habitats (1, Fate and Effects of Azinphos-Methyl 2). The implementation of retention ponds in agricultural in a Flow-Through Wetland in South watersheds was mentioned by Scott et al. (3) as one strategy to reduce the amount and toxicity of runoff-related insecticide Africa pollution discharging into estuaries. The usefulness of aquatic plants for removal of insecticides from water has been shown ,² ² in an indoor microcosm study (4), and the effects of the RALF SCHULZ,* CHRISTINA HAHN, organophosphate phorate have been assessed using littoral ERIN R. BENNETT,² mesocosms in South Dakota wetlands (5). However, infor- JAMES M. DABROWSKI,² mation about the fate or effects of spray drift-borne GERALDINE THIERE,² AND SUE K. C. PEALL³ insecticide input in constructed wetlands is limited. Processes important for removal of nonpoint-source Department of Zoology, Private Bag X1, University of pesticide pollution in wetlands may include adsorption, Stellenbosch, Matieland 7602, South Africa, and Forensic Chemistry Laboratory, Department of Health, decomposition, hydrolysis, microbial metabolism, photolysis, Cape Town 8000, South Africa and volatilization (6). The macrophytes present in the wetland may play an important role in providing an increased surface area for sorption as well as for microbial activity (7). Further- more, they may contribute directly to metabolism (8). Our knowledge about the effectiveness of constructed Spray drift is an important route for nonpoint-source wetlands in retaining agricultural nonpoint-source pesticide pesticide pollution of aquatic habitats (9, 10). Specifically, pollution is limited. A 0.44-ha vegetated wetland built orchard applications result in a large amount of drift due to small droplet size and the trajectory of release (11). -
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 .......................................................................... -
Consequences of Linguistic Uncertainty for Insect Management
WATCH YOUR LANGUAGE Consequences of Linguistic Uncertainty for Insect Management THERESA M. CIRA, KATHY QUICK, AND ROBERT C. VENETTE JA'CRISPY/ISTOCK 258 AMERICAN ENTOMOLOGIST | WINTER 2019 his is a call to entomologists to consider the un- certainty introduced into our works through the language we use. Albert Einstein remarked, “Every- thing depends on the degree to which words and word-combinations correspond to the world of im- Tpression,” which makes language a “dangerous source of error and deception” (Hawking 2007). Scientists usually research and deliberately choose the language they use to propose new concepts or terminology. Often, however, terms slip into the lexicon through less systematic means. Words may seem to have meanings so obvious that broad understanding of the term may be taken for granted, but individual contexts are diverse, and to assume that a word’s meaning is unchanging across time and space is to overlook the uncertainties of lan- guage. Thus, communication through even the most common entomological vocabulary can fail. Language is a mutable, un- certain, and imperfect way of representing the world. Because language is integral to science and yet inherently imprecise, it is important for scientists to recognize and address uncertain- ty in the language of our works. Uncertainty, as defined by the Society a phenomenon is repeatedly observed and for Risk Analysis (2015), is “not knowing the individuals agree that measurements con- true value of a quantity or the future con- verge, to some degree, on a specific point, sequences of an activity,” or “imperfect or more certainty about the true nature of the incomplete information/knowledge about phenomenon can be asserted.