Section 302 EHS TPQ List.Pdf
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Propoxur United States Environmental Protection Agency
United States Prevention, Pesticides EPA738-R-97-009 Environmental Protection And Toxic Substances August 1997 Agency (7508W) Reregistration Eligibility Decision (RED) PROPOXUR UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C. 20460 OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES CERTIFIED MAIL Dear Registrant: I am pleased to announce that the Environmental Protection Agency has completed its reregistration eligibility review and decisions on the pesticide chemical case propoxur. The enclosed Reregistration Eligibility Decision (RED) contains the Agency's evaluation of the data base of this chemical, its conclusions of the potential human health and environmental risks of the current product uses, and its decisions and conditions under which these uses and products will be eligible for reregistration. The RED includes the data and labeling requirements for products for reregistration. It may also include requirements for additional data (generic) on the active ingredient to confirm the risk assessments. To assist you with a proper response, read the enclosed document entitled "Summary of Instructions for Responding to the RED." This summary also refers to other enclosed documents which include further instructions. You must follow all instructions and submit complete and timely responses. The first set of required responses is due 90 days from the receipt of this letter. The second set of required responses is due 8 months from the date of receipt of this letter. Complete and timely responses will avoid the Agency taking the enforcement action of suspension against your products. If you have questions on the product specific data requirements or wish to meet with the Agency, please contact the Special Review and Reregistration Division representative Bonnie Adler (703) 308-8523. -
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. -
12.18 Carbofuran Carbofuran (CAS No
12. CHEMICAL FACT SHEETS WHO (2003) Cadmium in drinking-water. Background document for preparation of WHO Guidelines for drinking-water quality. Geneva, World Health Organization (WHO/SDE/WSH/03.04/80). 12.18 Carbofuran Carbofuran (CAS No. 1563-66-2) is used worldwide as a pesticide for many crops. Residues in treated crops are generally very low or not detectable. The physical and chemical properties of carbofuran and the few data on occurrence indicate that drink- ing-water from both groundwater and surface water sources is potentially the major route of exposure. Guideline value 0.007 mg/litre Occurrence Has been detected in surface water, groundwater and drinking-water, generally at levels of a few micrograms per litre or lower; highest concentration (30 mg/litre) measured in groundwater ADI 0.002 mg/kg of body weight based on a NOAEL of 0.22 mg/kg of body weight per day for acute (reversible) effects in dogs in a short-term (4- week) study conducted as an adjunct to a 13-week study in which inhibition of erythrocyte acetylcholinesterase activity was observed, and using an uncertainty factor of 100 Limit of detection 0.1 mg/litre by GC with a nitrogen–phosphorus detector; 0.9 mg/litre by reverse-phase HPLC with a fluorescence detector Treatment achievability 1 mg/litre should be achievable using GAC Guideline derivation • allocation to water 10% of ADI • weight 60-kg adult • consumption 2 litres/day Additional comments Use of a 4-week study was considered appropriate because the NOAEL is based on a reversible acute effect; the NOAEL will also be protective for chronic effects. -
Carbamate Pesticides Aldicarb Aldicarb Sulfoxide Aldicarb Sulfone
Connecticut General Statutes Sec 19a-29a requires the Commissioner of Public Health to annually publish a list setting forth all analytes and matrices for which certification for testing is required. Connecticut ELCP Drinking Water Analytes Revised 05/31/2018 Microbiology Total Coliforms Fecal Coliforms/ E. Coli Carbamate Pesticides Legionella Aldicarb Cryptosporidium Aldicarb Sulfoxide Giardia Aldicarb Sulfone Carbaryl Physicals Carbofuran Turbidity 3-Hydroxycarbofuran pH Methomyl Conductivity Oxamyl (Vydate) Minerals Chlorinated Herbicides Alkalinity, as CaCO3 2,4-D Bromide Dalapon Chloride Dicamba Chlorine, free residual Dinoseb Chlorine, total residual Endothall Fluoride Picloram Hardness, Calcium as Pentachlorophenol CaCO3 Hardness, Total as CaCO3 Silica Chlorinated Pesticides/PCB's Sulfate Aldrin Chlordane (Technical) Nutrients Dieldrin Endrin Ammonia Heptachlor Nitrate Heptachlor Epoxide Nitrite Lindane (gamma-BHC) o-Phosphate Metolachlor Total Phosphorus Methoxychlor PCB's (individual aroclors) Note 1 PCB's (as decachlorobiphenyl) Note 1 Demands Toxaphene TOC Nitrogen-Phosphorus Compounds Alachlor Metals Atrazine Aluminum Butachlor Antimony Diquat Arsenic Glyphosate Barium Metribuzin Beryllium Paraquat Boron Propachlor Cadmium Simazine Calcium Chromium Copper SVOC's Iron Benzo(a)pyrene Lead bis-(2-ethylhexyl)phthalate Magnesium bis-(ethylhexyl)adipate Manganese Hexachlorobenzene Mercury Hexachlorocyclopentadiene Molybdenum Nickel Potassium Miscellaneous Organics Selenium Dibromochloropropane (DBCP) Silver Ethylene Dibromide (EDB) -
The Calcium Arsenates
Station RuIletin 131. June, 1918 Oregon Agricultural College Experiment Station AGRICULTURAL CHEMISTRY DEPARTMENT The Calcium Arsenates By R. H. ROBINSON Acting Chemist, Oregon Agricultural Experiment Station. CORVALLIS, OREGON The regular huIlejne of the Station are sent free to the residents of Oregon who request them. THE CALCIUM ARSENATES By R. H. ROBINSON Acting Chemist, Oregon Agricultural Experiment Station INTRODUCTION Chemical investigations on the calcium arsenates relative to their economfic value and practicability as insecticides have been carried on by the department of Agricultural Chemistry of this Station during the past two years.The results obtained from these investigations are presented in this bulletin.The work was supported by the annual funds provided by the Adams Act of the United States Government.. Commercial calcium arsenate is an arsenical now being produced by reliable manufacturers of spray material and offered for sale as a sub- stitute for the arsenates of lead.The value of the latter as a stomachic insecticide has been demonstrated, and itis now used extensively for the successful controlof the codling moth, the destructionof the cotton boll worm., the tobacco worm, and the Colorado potato beetle. Previous inveatigations on the toxic values and killing power of calcium arsenate and lead arsenate indicate equal efficiency. A consideration of a few figures will show the economic advantages which might be gained if calcium arsenate could be substituted for lead arsenate.A conservative estimate of the quantity of lead arsenate used annually in the United States, as stated by one of the largest manufac- turers of spray materials, is probably more than 30,000,000 pounds. -
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. -
Teratogenicity and Embryotoxicity of Organophosphorus Compounds in Animal Models - a Short Review
Mil. Med. Sci. Lett. (Voj. Zdrav. Listy) 2012, vol. 81(1), p. 16-26 ISSN 0372-7025 DOI: 10.31482/mmsl.2012.003 REVIEW ARTICLE TERATOGENICITY AND EMBRYOTOXICITY OF ORGANOPHOSPHORUS COMPOUNDS IN ANIMAL MODELS - A SHORT REVIEW Syed M Nurulain and M Shafiullah Department of Pharmacology and Therapeutic, Faculty of Medicine and Health Sciences, UAE University, AlAin, UAE. P.O.Box 17666, Alain, UAE Received 9 th December 2011. Revised 12 th February 2012. Published 9 th March 2012. Summary Organophosphorus compounds (OPCs) are a wide group of compounds both structurally and functionally. Each OPC has a unique toxicological profile. The exposure to this type of poison is not limited only to certain occupationally exposed people but also to children, women, pregnant women; all have chances to be exposed to this poison. During the recent past years it has been reported in many poison epidemiological studies and case reports that exposure of OPCs during pregnancy caused malformed fetuses, neural tube defect (NTD) and shortening of pregnancy. The literature for animal models reveals inconclusive evidence. The generalized view is that they are neither teratogenic nor embryotoxic. But it is not true. There is a lack of systematic study and scarcity of reports on the topic. The present study was undertaken to investigate the teratogenicity induced by organophosphorus compounds in different animal models by literature review. Literature was searched by Toxicology Data NetWork (TOXNET), Developmental and Reproductive Toxicology Database (DART), Toxicology Literature Online (TOXLINE), Hazardous Substances Data Bank (HSDB), Pubmed Central, Entrez-Pubmed, Science Direct, Directory Of Open Access Journal (DOAJ), Google Scholar and International Program on Chemical Safety (IPCS-INCHEM), Embase. -
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 -
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 -
Organophosphate Poisoning : a Review
120 Sinha and Sharma Med J Indones Organophosphate poisoning : A review Parmod K. Sinha, Ashok Sharma Abstrak Pestisida organofosfat digunakan secara luas di seluruh dunia. Keracunan oleh bahan ini merupakan masalah kesehatan masyarakat, terutama di negara berkembang. Zat neurotoksik organofosfat merupakan bahan yang dianggap mengancam dalam bidang militer dan terorisme. Mekanisme toksisitas bahan ini adalah dengan cara menghambat asetilkolinesterase yang mengakibatkan menumpuknya neurotransmitor asetilkolin dan terjadi rangsangan terus-menerus pada reseptor asetilkolin pada sistem saraf sentral maupun perifer. Selain krisis kolinergik, organofosfat dapat menimbulkan berbagai sindrom neurologis, baik akut maupun kronik. Sedangkan gejala peralihan ( intermediate) terjadi 1-4 hari setelah krisis kolinergik teratasi. Pengobatan standar terdiri dari reaktivasi asetilkolinesterase dengan antidot golongan oksim (prolidoksim, oksidoksime, HI-6 dan HLo7), dan pengendalian efek biokimia asetilkolin dengan menggunakan atropin. Golongan oksim yang baru HI-6 dan Hlo7 merupakan reaktivator asetilkolinesterase yang lebih cocok dan efektif untuk keracunan akut dan berat dibandingkan dengan prolidoksim dan obidoksim. Penderita yang mendapat pengobatan segera, biasanya dapat sembuh dari toksisitas akut, namun gejala neurologis ikutan dapat saja terjadi. (Med J Indones 2003; 12: 120-6) Abstract Organophosphate pesticides are used extensively worldwide, and poisoning by these agents, particularly in developing nations is a public health problem. Organophosphorous -
Rapid HPLC Determination of Carbofuran and Carbaryl in Tap and Environmental Waters Using On-Line SPE
Application Update: 186 Rapid HPLC Determination of Carbofuran and Carbaryl in Tap and Environmental Waters Using On-Line SPE Xu Qun1 and Jeff Rohrer2 1Shanghai, Peoples Republic of China; 2Sunnyvale, CA, USA Introduction Method detection limits (MDLs) of the two Key Words N-methylcarbamates are widely used agricultural compounds were both ≤ 0.062 μg/L, which is lower than pesticides. Reversed-phase high-performance liquid the MDLs reported in EPA Method 8318 (2.0 μg/L for • Carbamates chromatography (RP-HPLC) with fluorescence detection carbofuran and 1.7 μg/L for carbaryl), and in the standard • U.S. EPA following postcolumn derivatization, per EPA Methods method enacted by the Chinese government (7 μg/L 531.2 and 8318,1,2 is the method typically used for the for carbofuran).5 The MDLs were also similar to those • Pesticides sensitive determination of carbamates. Thermo Scientific reported in EPA Method 531.2 (0.058 μg/L for carbofuran • Drinking Water has published a detailed method3,4 that is consistent with and 0.068 μg/L for carbaryl). The MDL for carbofuran is the EPA methods. When an HPLC with UV absorbance well under the 40 μg/L maximum allowable concentration • SolEx HRP detection method is used, a sample preparation in U.S. drinking water,6 and meets the general rule for • RSLC procedure—either liquid-liquid extraction or off-line pesticides in drinking water (98/83/EC) published by the solid-phase extraction (SPE)—is required to increase the European Union (the maximum admissible concentration detection sensitivity. However, these procedures are time- of each individual pesticide component is 0.1 μg/L).7 consuming, require large volumes of organic solvents, and Therefore this method would be universally appropriate are deficient in terms of process control. -
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