Spider Mites and Resistance 653 in Production and Better Flowers V/Ith Quired Dosages
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Novel Approach to Fast Determination of 64 Pesticides Using of Ultra-Performance Liquid Chromatography-Tandem Mass Spectrometry
Novel approach to fast determination of 64 pesticides using of ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS) Tomas Kovalczuk, Ondrej Lacina, Martin Jech, Jan Poustka, Jana Hajslova To cite this version: Tomas Kovalczuk, Ondrej Lacina, Martin Jech, Jan Poustka, Jana Hajslova. Novel approach to fast determination of 64 pesticides using of ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS). Food Additives and Contaminants, 2008, 25 (04), pp.444-457. 10.1080/02652030701570156. hal-00577414 HAL Id: hal-00577414 https://hal.archives-ouvertes.fr/hal-00577414 Submitted on 17 Mar 2011 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. Food Additives and Contaminants For Peer Review Only Novel approach to fast determination of 64 pesticides using of ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS) Journal: Food Additives and Contaminants Manuscript ID: TFAC-2007-065.R1 Manuscript Type: Original Research Paper Date Submitted by the 07-Jul-2007 Author: Complete List of Authors: -
COMBINED LIST of Particularly Hazardous Substances
COMBINED LIST of Particularly Hazardous Substances revised 2/4/2021 IARC list 1 are Carcinogenic to humans list compiled by Hector Acuna, UCSB IARC list Group 2A Probably carcinogenic to humans IARC list Group 2B Possibly carcinogenic to humans If any of the chemicals listed below are used in your research then complete a Standard Operating Procedure (SOP) for the product as described in the Chemical Hygiene Plan. Prop 65 known to cause cancer or reproductive toxicity Material(s) not on the list does not preclude one from completing an SOP. Other extremely toxic chemicals KNOWN Carcinogens from National Toxicology Program (NTP) or other high hazards will require the development of an SOP. Red= added in 2020 or status change Reasonably Anticipated NTP EPA Haz list COMBINED LIST of Particularly Hazardous Substances CAS Source from where the material is listed. 6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9,10,10- hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide Acutely Toxic Methanimidamide, N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]- Acutely Toxic 1-(2-Chloroethyl)-3-(4-methylcyclohexyl)-1-nitrosourea (Methyl-CCNU) Prop 65 KNOWN Carcinogens NTP 1-(2-Chloroethyl)-3-cyclohexyl-1-nitrosourea (CCNU) IARC list Group 2A Reasonably Anticipated NTP 1-(2-Chloroethyl)-3-cyclohexyl-1-nitrosourea (CCNU) (Lomustine) Prop 65 1-(o-Chlorophenyl)thiourea Acutely Toxic 1,1,1,2-Tetrachloroethane IARC list Group 2B 1,1,2,2-Tetrachloroethane Prop 65 IARC list Group 2B 1,1-Dichloro-2,2-bis(p -chloropheny)ethylene (DDE) Prop 65 1,1-Dichloroethane -
Features & Benefits
Click Here To Purchase Features & Benefits: • TAURUS SC is a water-based suspension concentrate of 9.1% Fipronil for Pre and Post-construction termite applications, and to control perimeter pests • Apply at a rate of 4 gallons of dilution per 10 linear feet per foot of depth for termites • TAURUS SC is labeled for barrier applications targeting listed occasional invaders around structures • Now with EP/LI applications PRECAUTIONARY STATEMENTS ® Hazards to Humans and Domestic Animals Caution TAURUS SC Harmful if swallowed, absorbed through skin or inhaled. Do not get in eyes, on skin Termiticide / Insecticide or on clothing. Do not breathe spray mist. Wash thoroughly with soap and water after handling and before eating, drinking, chewing gum, or using tobacco. Remove and It is a violation of federal law to use this product in a manner inconsistent wash contaminated clothing before reuse. with its labeling. Personal Protective Equipment (PPE): • For sale to, use and storage only by individuals/firms licensed or registered All pesticide handlers (mixers, loaders, and applicators) must wear long-sleeved by the state to apply termiticide and/or general pest control products. shirt and long pants, socks, shoes, and chemical-resistant gloves. All pesticide • DO NOT use this product for termite or other pest control indoors, except for handlers must wear a dust/mist filtering respirator (MSHA/NIOSH approval number label-specified applications for termite control and foam applications to wall prefix TC-21C), or a NIOSH approved respirator with any N, R, P or HE filter, when voids for control of other listed pests. working in a non-ventilated space, including but not limited to crawl-spaces and • DO NOT use on golf course turf. -
Development of a CEN Standardised Method for Liquid Chromatography Coupled to Accurate Mass Spectrometry
Development of a CEN standardised method for liquid chromatography coupled to accurate mass spectrometry CONTENTS 1. Aim and scope ................................................................................................................. 2 2. Short description ................................................................................................................ 2 3. Apparatus and consumables ......................................................................................... 2 4. Chemicals ........................................................................................................................... 2 5. Procedure ........................................................................................................................... 3 5.1. Sample preparation ................................................................................................... 3 5.2. Recovery experiments for method validation ...................................................... 3 5.3. Extraction method ...................................................................................................... 3 5.4. Measurement .............................................................................................................. 3 5.5. Instrumentation and analytical conditions ............................................................ 4 5.5.1. Dionex Ultimate 3000 .......................................................................................... 4 5.5.2. QExactive Focus HESI source parameters ..................................................... -
Historical Use of Lead Arsenate and Survey of Soil Residues in Former Apple Orchards in Virginia
HISTORICAL USE OF LEAD ARSENATE AND SURVEY OF SOIL RESIDUES IN FORMER APPLE ORCHARDS IN VIRGINIA by Therese Nowak Schooley Thesis submitted to the faculty of the Virginia Polytechnic Institute and State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE IN LIFE SCIENCES in Entomology Michael J. Weaver, Chair Donald E. Mullins, Co-Chair Matthew J. Eick May 4, 2006 Blacksburg, Virginia Keywords: arsenic, lead, lead arsenate, orchards, soil residues, historical pesticides HISTORICAL USE OF LEAD ARSENATE AND SURVEY OF SOIL RESIDUES IN FORMER APPLE ORCHARDS IN VIRGINIA Therese Nowak Schooley Abstract Inorganic pesticides including natural chemicals such as arsenic, copper, lead, and sulfur have been used extensively to control pests in agriculture. Lead arsenate (PbHAsO4) was first used in apple orchards in the late 1890’s to combat the codling moth, Cydia pomonella (Linnaeus). The affordable and persistent pesticide was applied in ever increasing amounts for the next half century. The persistence in the environment in addition to the heavy applications during the early 1900’s may have led to many of the current and former orchards in this country being contaminated. In this study, soil samples were taken from several apple orchards across the state, ranging from Southwest to Northern Virginia and were analyzed for arsenic and lead. Based on naturally occurring background levels and standards set by other states, two orchards sampled in this study were found to have very high levels of arsenic and lead in the soil, Snead Farm and Mint Spring Recreational Park. Average arsenic levels at Mint Spring Recreational Park and Snead Farm were found to be 65.2 ppm and 107.6 ppm, respectively. -
Safe Pest Control
SAFE PEST CONTROL U.S. Department of Housing and Urban Development • Office of Healthy Homes and Lead Hazard Control “For years, cockroaches have defeated our best efforts to get rid of them. We sprayed and sprayed, but they always came back. Now we under- stand there are better methods and products that really work” Environmental Health Watch Did you know...? ■ Many pesticides for home use are toxic? ■ There are alternative pest management methods that limit the use of toxic substances? ■ Mice, cockroaches, and cockroach "dust” can trigger asthma attack? What is it? Integrated pest management (IPM) is a way to remove pests, like cock- roaches, mice, and rats from a home. IPM is a common sense approach that: ■ Denies pests food, water, shelter and a way to enter the home. ■ Uses baits and powders, such as gel baits, traps and borate powder. Why use IPM? ■ IPM is safer. IPM does not use as many harmful pesticides as traditional pest control. - Avoiding pesticides is especially important in homes. Pesticides can contain long lasting, toxic chemicals or lung irritants that cause asthma attacks. Children are among those most vulnerable to exposure. IPM strategies apply pesticides only as needed and use the least hazardous pesticides to control pests. continued on back www.hud.gov/offices/lead U.S. Department of Housing and Urban Development SAFE PEST CONTROL Office of Healthy Homes and Lead Hazard Control Non-toxic traps can be part of an IPM strategy. If needed, call a pest control professional who uses IPM practices. If you have taken all the steps described above and still have a pest problem, you may need a professional to help. -
4-Cyano-3-Benzoylamino-N
(19) TZZ _T (11) EP 2 427 427 B1 (12) EUROPEAN PATENT SPECIFICATION (45) Date of publication and mention (51) Int Cl.: of the grant of the patent: C07C 255/60 (2006.01) 25.12.2013 Bulletin 2013/52 (86) International application number: (21) Application number: 10713937.0 PCT/EP2010/054862 (22) Date of filing: 14.04.2010 (87) International publication number: WO 2010/127926 (11.11.2010 Gazette 2010/45) (54) 4-CYANO-3-BENZOYLAMINO-N-PHENYL-BENZAMIDES FOR USE IN PEST CONTROL 4-CYANO-3-BENZOYLAMINO-N-PHENYL-BENZAMIDE ZUR VERWENDUNG IN DER SCHÄDLINGSBEKÄMPFUNG 4-CYANO-3-BENZOYLAMINO-N-PHÉNYL-BENZAMIDES DESTINÉS À ÊTRE UTILISÉS DANS LA LUTTE ANTIPARASITAIRE (84) Designated Contracting States: • HUETER, Ottmar Franz AT BE BG CH CY CZ DE DK EE ES FI FR GB GR CH-4332 Stein (CH) HR HU IE IS IT LI LT LU LV MC MK MT NL NO PL • MAIENFISCH, Peter PT RO SE SI SK SM TR CH-4332 Stein (CH) (30) Priority: 06.05.2009 GB 0907822 (74) Representative: Herrmann, Jörg et al 18.12.2009 GB 0922234 Syngenta Crop Protection Münchwilen AG (43) Date of publication of application: Intellectual Property Department 14.03.2012 Bulletin 2012/11 Schaffhauserstrasse CH-4332 Stein (CH) (73) Proprietor: Syngenta Participations AG 4058 Basel (CH) (56) References cited: EP-A1- 1 714 958 WO-A1-2008/000438 (72) Inventors: WO-A1-2008/074427 • JUNG, Pierre Joseph Marcel CH-4332 Stein (CH) Remarks: • GODFREY, Christopher Richard Ayles Thefile contains technical information submitted after CH-4332 Stein (CH) the application was filed and not included in this specification Note: Within nine months of the publication of the mention of the grant of the European patent in the European Patent Bulletin, any person may give notice to the European Patent Office of opposition to that patent, in accordance with the Implementing Regulations. -
Who Needs Chlorpyrifos and Why (By Crop)?
1 WHO NEEDS CHLORPYRIFOS AND WHY (BY CROP)? EXCERPTS OF COMMENTS SUBMITTED TO EPA AT EPA-HQ-OPP-2015-0653 GENERAL “Consumers I have visited with that do not have any ag background are easily swayed into the belief that farmers are polluting the environment and recklessly applying chemicals. Truth is our farmers are professionals and with today’s pricing cannot afford to be over- or misapplying inputs that affect their bottom lines…. I strongly suggest that you…allow producers of the world’s food source to continue using the product chlorpyrifos.” – North Dakota farmer. “Many food crop industries in the Pacific Northwest are concerned about the impacts to pest management based on EPA’s proposed tolerance revocation of chlorpyrifos, including several minor crop groups with limited pesticide options. These industries include processed vegetables, strawberry, grass seed, mint, and cranberry. For many of these industries, chlorpyrifos has unique properties that make it an essential part of their Integrated Pest Management program. It is also an important tool for resistance management. Several of these industries have conducted research to identify effective alternatives to chlorpyrifos, but currently there aren’t viable alternatives that match the efficacy and low risk of this product for managing a number of critical pests…. A revocation of all chlorpyrifos tolerances would eliminate a number of low-risk, critical uses in cases where few alternatives exist at present, and in many cases those alternatives (neonicotinoids, pyrethroids) would be less efficacious, more expensive and have greater impacts on nontarget species including pollinators and beneficial insects. Further, the economic impacts based on resulting crop damage would be substantial.” – Oregon State University Agronomist. -
Argonne Report.Pdf
CONTENTS NOTATION ........................................................................................................................... xi ABSTRACT ........................................................................................................................... 1 1 INTRODUCTION ........................................................................................................... 5 1.1 Overview of the Emergency Response Guidebook ................................................ 5 1.2 Organization of this Report ..................................................................................... 7 2 GENERAL METHODOLOGY ....................................................................................... 9 2.1 TIH List ................................................................................................................... 10 2.1.1 Background ................................................................................................. 10 2.1.2 Changes in the TIH List for the ERG2012 ................................................. 11 2.2 Shipment and Release Scenarios ............................................................................ 11 2.2.1 Shipment Profiles ........................................................................................ 12 2.2.2 Treatment of Chemical Agents ................................................................... 14 2.3 Generics, Mixtures, and Solutions .......................................................................... 17 2.4 Analysis of Water-Reactive -
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.