EPA “P-LISTED CHEMICALS” (Acutely Toxic)
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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. -
Dimethoate 4EC Systemic Insecticide – Miticide ACTIVE INGREDIENT: PRECAUTIONARY STATEMENTS (Cont.) Dimethoate*
GROUP 1B INSECTICIDE Dimethoate 4EC Systemic Insecticide – Miticide ACTIVE INGREDIENT: PRECAUTIONARY STATEMENTS (Cont.) Dimethoate* .......................................................... 43.5% Mixers, loaders, applicators, flaggers, and other handlers must OTHER INGREDIENTS: .......................................... 56.5% wear: Long-sleeved shirt and long pants, shoes plus socks, goggles TOTAL: .............................................................. 100.0% or face shield, chemical-resistant gloves, a NIOSH-approved * This product contains 4 pounds of dimethoate per gallon. dust/mist filtering respirator with MSHA/NIOSH approval number prefix TC-21C or a NIOSH-approved respirator with any N, R, P, or KEEP OUT OF REACH OF CHILDREN HE filter, and chemical-resistant apron when mixing, loading, clean- ing up spills, or equipment. WARNING See Engineering Controls for additional requirements and excep- Si usted no entiende la etiqueta, busque a alguien para que se la ex- tions. plique a usted en detalle. (If you do not understand the label, find Follow manufacturer’s instructions for cleaning/maintaining PPE. If someone to explain it to you in detail.) no such instructions for washables exist, use detergent and hot water. Keep and wash PPE separately from other laundry. See FIRST AID Below Discard clothing and other absorbent materials that have been EPA Reg. No. 19713-231 Net Content: drenched or heavily contaminated with this product’s concentrate. EPA Est. No. 19713-GA-001 2.5 Gals. (9.46 L) Do not reuse them. ENGINEERING CONTROLS FIRST AID Mixers and loaders supporting aerial application to alfalfa, cotton, IF SWALLOWED: soybeans, corn, safflower, sorghum, and wheat, must use a closed • Call a poison control center or doctor immediately for treatment system that meets the requirements listed in the Worker Protections advice. -
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) -
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 -
Pesticides May Reduce Lettuce Yield Frank V
High-value crops such as strawberries, tain classes of insecticides on lettuce photo- usually clearly visible. Insecticides applied at broccoli, and iceberg lettuce often receive synthesis, transpiration, and productivity. normal rates and under the right environ- “preventive” or “insurance” pesticide treat- mental conditions may subtly damage a plant ments, which may result in weekly scheduled Insecticides but remain unobserved, because symptoms applications of insecticides. Many times such Insecticides in the various “classes,” such are not visible. treatments are unwarranted economically as chlorinated hydrocarbons (DDT, endrin, During the last few years, plant physiolo- and may reduce yields by detrimental effects and methoxychlor), organophosphates gists at University of California, Riverside, on the plants. Decreases in strawberry yields (guthion, parathion, and methyl-parathion), have developed the dual isotope porometer, due to preventive insecticide treatments in the carbamates (malathion and methomyl), and which provides accurate, simultaneous mea- absence of economically significant pest synthetic pyrethroids (fenvalerate and per- surements of a plant’s photosynthesis and populations have been reported. Research methrin), differ in their effects on plants. Ad- transpiration rates in the field. Entomologists supported by the California Iceberg Lettuce ditionally, the rates, number, and timing of have used the instrument to measure effects Research Advisory Board indicated that head applications may alter a compound’s effect -
Impact of Pesticide Use on Health in Developing Countries
Impact of pesticide use on health in developing countries Proceedings of a symposium held in Ottawa, Canada, 1 7-20 September 1990 IDRC CRDI International Development Research Centre Centre de recherches pour le devetoppement international 1 March 1993 Dear Reader/Librarian, IDRC is a public corporation created by the Canadian parliament in 1970 to help developing countries find viable solutions to their problems through research. At the 1992 Earth Summit, IDRC's mandate was broadened to emphasize sustainable development issues. As part of IDRC's strengthened commitment to global action and harüony, we are pleased to send you a complimentary copy of our most recent publication: The impact of pesticide use on health in developing countries (March 1993, 352 pages, 0-88936-560-1, $17.95). The first part of this book presents a brief survey of the global situation and the results of twelve epidemiological studies carried out by researchers from Africa, Latin America, Asia and the Middle East. These focus on poisonings resulting from organophosphates, herbicides, and pyrethroids. The second part illustrates the role of the process of development, production, spraying techniques and legislation in protecting the health of workers. A discussion of the benefits and modalities of access to pertinent information for the prevention of pesticide poisonings is provided in the third section. Finally, in the fourth section, consideration is given to the advantages and disadvantages of certain alternatives to the use of synthetic pesticides in agriculture and public health, such as botanical pesticides and integrated pest management strategies. We hope this book is a valuable addition to your collection. -
A COMPARATIVE STUDY of the CYTOGENETIC EFFECTS of the INSECTICIDES HEPTACHLOR, MALATHION, and METHYL PARATHION in Vicia Faba
Contam. Amb. 1, 7-16, 1985 A COMPARATIVE STUDY OF THE CYTOGENETIC EFFECTS OF THE INSECTICIDES HEPTACHLOR, MALATHION, AND METHYL PARATHION IN Vicia faba SANDRAGOMEZ-ARROYO, ANA MAR~ABAIZA, GRA~IELALOPEZ AND RAFAELVILLALOBOS- PIETRINI Laboratorio de Citogenética y Mutagénesis Am- bientales, Centro de Ciencias de la Atmósfera, Universidad Nacional Autónoma de México, Co- yoacán 04510, México, D. F. y Centro de Inves- tigación y Reproducción Animal, Universidad Au- tónoma de Tlaxcala. ABSTRACT In order to determine the potential cytogenetic effects of Heptachlor, Malathion and Methyl Parathion, meristems of broad bean root tips were treated with se- vera1 concentrations o£ these insecticides for different periods of treatment and recovery. Heptachlor and Malathion induced chromosomal alterations in anaphase cells as fragments and bridges, chromosomes with inactivated centromeres and isochroinosomes, and as micronuclei in interphase cells. Multipolar anaphases also appeared when the mitotic spindle was damaged. Heptachlor induced pycnosis but Malathion did not. Chromosomal aberrations caused by Methyl Parathion were observed in cells only during metaphase, since a strong c-mitotic effect was induced mostly in the form of fragments. Longer recovery periods (42 and 44 h) revealed tetraploid and pycnotic cells. Only in the case of Malation was there an increase in chromosome altera- tions with higher concentrations. However, no such dose response relationship was observed for micronuclei frequency. RESUMEN Con el fin de establecer el daño genético que ocasionan el Heptacloro, el Mala- tión y el Metil Paratión, se realizaron tratamientos sobre las células meristemá- ticas de la raíz de haba con diversas concentraciones de estos insecticidas y dife- rentes tiempos de tratamiento y recuperación. -
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 -
TOXICOLOGICAL PROFILE for HEPTACHLOR and HEPTACHLOR EPOXIDE
TOXICOLOGICAL PROFILE FOR HEPTACHLOR and HEPTACHLOR EPOXIDE Prepared by: Syracuse Research Corporation Under Contract No. 200-2004-09793 Prepared for: U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry November 2007 HEPTACHLOR AND HEPTACHLOR EPOXIDE ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. HEPTACHLOR AND HEPTACHLOR EPOXIDE iii UPDATE STATEMENT A Toxicological Profile for Heptachlor/Heptachlor Epoxide, Draft for Public Comment was released in September 2005. This edition supersedes any previously released draft or final profile. Toxicological profiles are revised and republished as necessary. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology and Environmental Medicine/Applied Toxicology Branch 1600 Clifton Road NE Mailstop F-32 Atlanta, Georgia 30333 HEPTACHLOR AND HEPTACHLOR EPOXIDE iv This page is intentionally blank. v FOREWORD This toxicological profile is prepared in accordance with guidelines developed by the Agency for Toxic Substances and Disease Registry (ATSDR) and the Environmental Protection Agency (EPA). The original guidelines were published in the Federal Register on April 17, 1987. Each profile will be revised and republished as necessary. The ATSDR toxicological profile succinctly characterizes the toxicologic and adverse health effects information for the hazardous substance described therein. Each peer-reviewed profile identifies and reviews the key literature that describes a hazardous substance's toxicologic properties. Other pertinent literature is also presented, but is described in less detail than the key studies. -
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.