Environmental Health Criteria 63 ORGANOPHOSPHORUS
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US EPA Environmental Technology Verification Statement Removal of Chemical Contaminants in Drinking Water Watts Premier Inc
THE ENVIRONMENTAL TECHNOLOGY VERIFICATION PROGRAM U.S. Environmental Protection Agency NSF International ETV Joint Verification Statement TECHNOLOGY TYPE: POINT-OF-USE DRINKING WATER TREATMENT SYSTEM APPLICATION: REMOVAL OF CHEMICAL CONTAMINANTS IN DRINKING WATER PRODUCT NAME: WATTS PREMIER WP-4V COMPANY: WATTS PREMIER, INC. ADDRESS: 1725 WEST WILLIAMS DR. SUITE C-20 PHOENIX, AZ 85027 PHONE: 800-752-5582 NSF International (NSF) manages the Drinking Water Systems (DWS) Center under the U.S. Environmental Protection Agency’s (EPA) Environmental Technology Verification (ETV) Program. The DWS Center recently evaluated the performance of the Watts Premier WP-4V point-of-use (POU) drinking water treatment system. NSF performed all of the testing activities, and also authored the verification report and this verification statement. The verification report contains a comprehensive description of the test. EPA created the ETV Program to facilitate the deployment of innovative or improved environmental technologies through performance verification and dissemination of information. The goal of the ETV Program is to further environmental protection by accelerating the acceptance and use of improved and more cost-effective technologies. ETV seeks to achieve this goal by providing high-quality, peer- reviewed data on technology performance to those involved in the design, distribution, permitting, purchase, and use of environmental technologies. ETV works in partnership with recognized standards and testing organizations, stakeholder groups (consisting of buyers, vendor organizations, and permitters), and with the full participation of individual technology developers. The program evaluates the performance of innovative technologies by developing test plans that are responsive to the needs of stakeholders, conducting field or laboratory tests (as appropriate), collecting and analyzing data, and preparing peer reviewed reports. -
Adverse Effects of Organophosphorus Pesticides on the Liver: a Brief Summary of Four Decades of Research
Karami-Mohajeri S, et al. Adverse effects of OPs on the liver: a brief research summary Arh Hig Rada Toksikol 2017;68:261-275 261 Review DOI: 10.1515/aiht-2017-68-2989 Adverse effects of organophosphorus pesticides on the liver: a brief summary of four decades of research Somayyeh Karami-Mohajeri1,2, Ahmad Ahmadipour2, Hamid-Reza Rahimi1,2, and Mohammad Abdollahi3,4 Pharmaceutics Research Center, Institute of Neuropharmacology1, Department of Toxicology and Pharmacology, Faculty of Pharmacy2, Kerman University of Medical Sciences, Kerman, Pharmaceutical Sciences Research Center3, Department of Toxicology and Pharmacology4, Faculty of Pharmacy, Tehran University of Medical Sciences, Tehran, Iran [Received in May 2017; Similarity Check in May 2017; Accepted in December 2017] Organophosphorus pesticides (OPs) are widely used volatile pesticides that have harmful effects on the liver in acute and chronic exposures. This review article summarises and discusses a wide collection of studies published over the last 40 years reporting on the effects of OPs on the liver, in an attempt to propose general mechanisms of OP hepatotoxicity and possible treatment. Several key biological processes have been reported as involved in OP-induced hepatotoxicity such as disturbances in the antioxidant defence system, oxidative stress, apoptosis, and mitochondrial and microsomal metabolism. Most studies show that antioxidants can attenuate oxidative stress and the consequent changes in liver function. However, few studies have examined the relationship between OP structures and the severity and mechanism of their action. We hope that future in vitro, in vivo, and clinical trials will answer the remaining questions about the mechanisms of OP hepatotoxicity and its management. -
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 -
"U/^ ((*.U \ BIBLIOTHEEK STARINGGEBOUW Volatilization of Tri-Allate, Ethoprophos and Parathion Measured with Four Methods After Spraying on a Sandy Soil
"u/^ ((*.u \ BIBLIOTHEEK STARINGGEBOUW Volatilization of tri-allate, ethoprophos and parathion measured with four methods after spraying on a sandy soil G. Bor F. van den Berg J.H. Smelt R.A. Smidt A.E. van de Peppel-Groen M. Leistra Report 104 DLO Winand Staring Centre, Wageningen (The Netherlands), 1995 1 h FEB. 1998 0000' ABSTRACT Bor, G., F. van den Berg, J.H. Smelt, R.A. Smidt, A.E. van de Peppel-Groen, M. Leistra, 1995. Volatilization of tri-allate, ethoprophos and parathion measured withfour methods after spraying on a sandy soil. Wageningen (The Netherlands), DLO Winand Staring Centre. Report 104. 62 pp.; 9 Figs; 6 Tables; 14 Refs; 3 Annex. At about eleven times after application of tri-allate, ethoprophos and parathion to a sandy soil, their rates of volatilization were determined with the aerodynamic method (AD),th e Bowen-ratio method (BR), the theoretical-profile method (TP) and the Box method (B). The volatilization was highest for tri-allate and lowest for parathion. On the first day after application, the volatilization rate decreased sharply,bu tthereafte r the decreasewa smor egradual .Th edifference s involatilizatio n rate asdetermine d withth eAD ,B R andT Pmethod s werecomparativel y small.Th erate sdetermine d with the Box method were mostly lower than those determined with the other methods. Keywords: aerodynamic method, air quality, air sampling, Bowen ratio method, Box method, field experiment, gas chromatography, pesticide, polystyrene, theoretical-profile method, XAD ISSN 0927-4537 ©1995 DLO Winand Staring Centre for Integrated Land, Soil and Water Research (SC-DLO) P.O. -
Effect of Chlorpyrifos Oxon on M2 Muscarinic Acetylcholine Receptor Trafficking”
EFFECT OF CHLORPYRIFOS OXON ON M2 MUSCARINIC ACETYLCHOLINE RECEPTOR REGULATION BY ELMAR MABUNGA UDARBE Doctor of Veterinary Medicine University of the Philippines Los Baños College, Laguna, Philippines 1999 Submitted to the Faculty of the Graduate College of Oklahoma State University in partial fulfillment of the requirements for the Degree of MASTER OF SCIENCE July, 2004 EFFECT OF CHLORPYRIFOS OXON ON M2 MUSCARINIC ACETYLCHOLINE RECEPTOR REGULATION Thesis Approved: DR. CAREY N. POPE Thesis Advisor DR. CYRIL C. CLARKE DR. CHARLOTTE C. OWNBY DR. DORIS K. PATNEAU DR. AL CARLOZI Dean of Graduate College ii ACKNOWLEDGMENTS My sincerest gratitude goes to my major advisor, Dr. Carey N. Pope for the intelligent supervision, for providing inspiration to do this work. I am also thankful to my committee members, Dr. Cyril Clarke, Dr. Charlotte Ownby and Dr. Doris Patneau for helpful comments on the content and form of this manuscript. I am indebted to the Fulbright-Philippine Agriculture Scholarship Program (FPASP) and the Philippine American Education Foundation (PAEF) whose exchange program deepened my understanding of the U.S. culture and its people and allowed me to promote mutual understanding between the U.S. and the Philippines. I am grateful to the University of the Philippines in Mindanao (UPMINDANAO) for supporting my pursuit for graduate studies, the National Institute of Environmental Health Sciences (NIEHS), Oklahoma State University Board of Regents and Dr. Sidney Ewing, Wendell H. and Nellie G. Krull Endowed professor for the financial assistance. I am also thankful to the following: Ms. Sharon Baker for doing the preliminary work on the project; Dr. -
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 ..................................................................................................................................... -
Environmental Properties of Chemicals Volume 2
1 t ENVIRONMENTAL 1 PROTECTION Esa Nikunen . Riitta Leinonen Birgit Kemiläinen • Arto Kultamaa Environmental properties of chemicals Volume 2 1 O O O O O O O O OO O OOOOOO Ol OIOOO FINNISH ENVIRONMENT INSTITUTE • EDITA Esa Nikunen e Riitta Leinonen Birgit Kemiläinen • Arto Kultamaa Environmental properties of chemicals Volume 2 HELSINKI 1000 OlO 00000001 00000000000000000 Th/s is a second revfsed version of Environmental Properties of Chemica/s, published by VAPK-Pub/ishing and Ministry of Environment, Environmental Protection Department as Research Report 91, 1990. The pubiication is also available as a CD ROM version: EnviChem 2.0, a PC database runniny under Windows operating systems. ISBN 951-7-2967-2 (publisher) ISBN 952-7 1-0670-0 (co-publisher) ISSN 1238-8602 Layout: Pikseri Julkaisupalvelut Cover illustration: Jussi Hirvi Edita Ltd. Helsinki 2000 Environmental properties of chemicals Volume 2 _____ _____________________________________________________ Contents . VOLUME ONE 1 Contents of the report 2 Environmental properties of chemicals 3 Abbreviations and explanations 7 3.1 Ways of exposure 7 3.2 Exposed species 7 3.3 Fffects________________________________ 7 3.4 Length of exposure 7 3.5 Odour thresholds 8 3.6 Toxicity endpoints 9 3.7 Other abbreviations 9 4 Listofexposedspecies 10 4.1 Mammais 10 4.2 Plants 13 4.3 Birds 14 4.4 Insects 17 4.5 Fishes 1$ 4.6 Mollusca 22 4.7 Crustaceans 23 4.8 Algae 24 4.9 Others 25 5 References 27 Index 1 List of chemicals in alphabetical order - 169 Index II List of chemicals in CAS-number order -
Neuroactive Insecticides: Targets, Selectivity, Resistance, and Secondary Effects
EN58CH06-Casida ARI 5 December 2012 8:11 Neuroactive Insecticides: Targets, Selectivity, Resistance, and Secondary Effects John E. Casida1,∗ and Kathleen A. Durkin2 1Environmental Chemistry and Toxicology Laboratory, Department of Environmental Science, Policy, and Management, 2Molecular Graphics and Computational Facility, College of Chemistry, University of California, Berkeley, California 94720; email: [email protected], [email protected] Annu. Rev. Entomol. 2013. 58:99–117 Keywords The Annual Review of Entomology is online at acetylcholinesterase, calcium channels, GABAA receptor, nicotinic ento.annualreviews.org receptor, secondary targets, sodium channel This article’s doi: 10.1146/annurev-ento-120811-153645 Abstract Copyright c 2013 by Annual Reviews. Neuroactive insecticides are the principal means of protecting crops, people, All rights reserved livestock, and pets from pest insect attack and disease transmission. Cur- ∗ Corresponding author rently, the four major nerve targets are acetylcholinesterase for organophos- phates and methylcarbamates, the nicotinic acetylcholine receptor for neonicotinoids, the γ-aminobutyric acid receptor/chloride channel for by Public Health Information Access Project on 04/29/14. For personal use only. Annu. Rev. Entomol. 2013.58:99-117. Downloaded from www.annualreviews.org polychlorocyclohexanes and fiproles, and the voltage-gated sodium channel for pyrethroids and dichlorodiphenyltrichloroethane. Species selectivity and acquired resistance are attributable in part to structural differences in binding subsites, receptor subunit interfaces, or transmembrane regions. Additional targets are sites in the sodium channel (indoxacarb and metaflumizone), the glutamate-gated chloride channel (avermectins), the octopamine receptor (amitraz metabolite), and the calcium-activated calcium channel (diamides). Secondary toxic effects in mammals from off-target serine hydrolase inhibi- tion include organophosphate-induced delayed neuropathy and disruption of the cannabinoid system. -
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: . -
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 -
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. -
Appendix H EPA Hazardous Waste Law
Appendix H EPA Hazardous Waste Law This Appendix is intended to give you background information on hazardous waste laws and how they apply to you. For most U.S. Environmental Protection Agency (EPA) requirements that apply to the University, the Safety Department maintains compliance through internal inspections, record keeping and proper disposal. In Wisconsin, the Department of Natural Resources (DNR) has adopted the EPA regulations, consequently EPA and DNR regulations are nearly identical. EPA defines This Appendix only deals with "hazardous waste" as defined by the EPA. hazardous waste as Legally, EPA defines hazardous waste as certain hazardous chemical waste. This hazardous chemical Appendix does not address other types of regulated laboratory wastes, such as waste; radioactive, infectious, biological, radioactive or sharps. Chapter 8 descibes disposal procedures infectious and biohazardous waste for animals. Chapter 9 describes disposal procedures for sharps and other waste that are regulated by can puncture tissue. Chapter 11 discusses Radiation and the Radiation Safety for other agencies. Radiation Workers provides guidelines for the disposal of radioactive waste. Procedures for medical waste are written by the UW Hospital Safety Officer. The Office of Biological Safety can provide guidance for the disposal of infectious and biological waste. EPA regulations focus on industrial waste streams. As a result, many laboratory chemical wastes are not regulated by EPA as hazardous chemical waste. However, many unregulated chemical wastes do merit special handling and disposal If a waste can be procedures. Thus, Chapter 7 and Appendix A of this Guide recommend disposal defined as: procedures for many unregulated wastes as if they were EPA hazardous waste.