Consolidated List of Chemicals Subject to EPCRA + Section 112(R)
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Mechanistic Insights Into the Hydrocyanation Reaction
Mechanistic insights into the hydrocyanation reaction Citation for published version (APA): Bini, L. (2009). Mechanistic insights into the hydrocyanation reaction. Technische Universiteit Eindhoven. https://doi.org/10.6100/IR644067 DOI: 10.6100/IR644067 Document status and date: Published: 01/01/2009 Document Version: Publisher’s PDF, also known as Version of Record (includes final page, issue and volume numbers) Please check the document version of this publication: • A submitted manuscript is the version of the article upon submission and before peer-review. There can be important differences between the submitted version and the official published version of record. People interested in the research are advised to contact the author for the final version of the publication, or visit the DOI to the publisher's website. • The final author version and the galley proof are versions of the publication after peer review. • The final published version features the final layout of the paper including the volume, issue and page numbers. Link to publication General rights Copyright and moral rights for the publications made accessible in the public portal are retained by the authors and/or other copyright owners and it is a condition of accessing publications that users recognise and abide by the legal requirements associated with these rights. • Users may download and print one copy of any publication from the public portal for the purpose of private study or research. • You may not further distribute the material or use it for any profit-making activity or commercial gain • You may freely distribute the URL identifying the publication in the public portal. -
Numerical Simulation of a Two-Phase Flow for the Acrylonitrile Electrolytic Adiponitrile Process in a Vertical/Horizontal Electrolysis Cell
energies Article Numerical Simulation of a Two-Phase Flow for the Acrylonitrile Electrolytic Adiponitrile Process in a Vertical/Horizontal Electrolysis Cell Jiin-Yuh Jang * and Yu-Feng Gan Department of Mechanical Engineering, National Cheng-Kung University, Tainan 70101, Taiwan; [email protected] * Correspondence: [email protected]; Tel.: +886-6-2088573 Received: 7 September 2018; Accepted: 6 October 2018; Published: 12 October 2018 Abstract: This paper investigated the effect of oxygen holdup on the current density distribution over the electrode of a vertical/horizontal electrolysis cell with a two-dimensional Eulerian–Eulerian two-phase flow model in the acrylonitrile (AN) electrolytic adiponitrile (ADN) process. The physical models consisted of a vertical/horizontal electrolysis cell 10 mm wide and 600 mm long. The electrical potential difference between the anode and cathode was fixed at 5 V, which corresponded to a uniform current density j = 0.4 A/cm2 without any bubbles released from the electrodes. The effects of different inlet electrolyte velocities (vin = 0.4, 0.6, 1.0 and 1.5 m/s) on the void fraction and the current density distributions were discussed in detail. It is shown that, for a given applied voltage, as the electrolyte velocity is increased, the gas diffusion layer thickness decreased and this resulted in the decrease of the gas void fraction and increase of the corresponding current density; for a given velocity, the current density for a vertical cell was higher than that for a horizontal cell. Furthermore, assuming the release of uniform mass flux for the oxygen results in overestimation of the total gas accumulation mass flow rate by 2.8% and 5.8% and it will also result in underestimation of the current density by 0.3% and 2.4% for a vertical cell and a horizontal cell, respectively. -
Relative Tolerance of Peanuts to Alachlor and Metolachlor' Materials
Relative Tolerance of Peanuts to Alachlor and Metolachlor' Glenn Wehtje*, John W. Wilcut, T. Vint Hicks2. and John McGuire3 ABSTRACT vealed that peas were most sensitive across all the sub- Field studies were conducted during 1984, 1985, and 1987 to evaluate weed control and the relative tolerance of peanuts stituted amide herbicides when the application was (Arachis hypogaea) to alachlor and metolachlor when applied at made 2 days after planting. This time of application cor- rates from 2.2 to 13.4 kg adha. Both single and split responded to shoot emergence, which is considered to preemergence, and postemergence applications were in- be the most sensitive portion of the seedling, through cluded. In 1984 and 1985, neither herbicide adversely affected the surface of the treated soil. Later applications re- yields compared to a hand-weeded control. In 1987, metolachlor at a rate of 9.0 kgha and alachlor at 13.4 k&a re- sulted in progressively less injury, indicating that the duced yields. Across all years, at least a two-fold safety factor foliar portion of the developing pea was relatively toler- existed between the maximum registered rate and the rate ant once emerged. Field studies indicated injury was necessary for peanut injury. Occurrence of injury appears to be markedly influenced by rainfall soon after planting. related to rainfall. Metolachlor was slightly more mobile than alachlor in soil chromatography trials, which may be a factor in Putnam and Rice (7) evaluated the factors associated its slightly greater propensity to be injurious under certain with alachlor injury on snap beans (Phaseolus vulgaris conditions of extensive leaching and/or slow peanut L.). -
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 -
2,4-Dichlorophenoxyacetic Acid
2,4-Dichlorophenoxyacetic acid 2,4-Dichlorophenoxyacetic acid IUPAC (2,4-dichlorophenoxy)acetic acid name 2,4-D Other hedonal names trinoxol Identifiers CAS [94-75-7] number SMILES OC(COC1=CC=C(Cl)C=C1Cl)=O ChemSpider 1441 ID Properties Molecular C H Cl O formula 8 6 2 3 Molar mass 221.04 g mol−1 Appearance white to yellow powder Melting point 140.5 °C (413.5 K) Boiling 160 °C (0.4 mm Hg) point Solubility in 900 mg/L (25 °C) water Related compounds Related 2,4,5-T, Dichlorprop compounds Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa) 2,4-Dichlorophenoxyacetic acid (2,4-D) is a common systemic herbicide used in the control of broadleaf weeds. It is the most widely used herbicide in the world, and the third most commonly used in North America.[1] 2,4-D is also an important synthetic auxin, often used in laboratories for plant research and as a supplement in plant cell culture media such as MS medium. History 2,4-D was developed during World War II by a British team at Rothamsted Experimental Station, under the leadership of Judah Hirsch Quastel, aiming to increase crop yields for a nation at war.[citation needed] When it was commercially released in 1946, it became the first successful selective herbicide and allowed for greatly enhanced weed control in wheat, maize (corn), rice, and similar cereal grass crop, because it only kills dicots, leaving behind monocots. Mechanism of herbicide action 2,4-D is a synthetic auxin, which is a class of plant growth regulators. -
Conversion of Carbon Dioxide to Acetylene on a Micro Scale
810 NATURE June 14, 1947 Vol. 159 orbitale of the ethmoid is reduced". In the orang Stainless steel was found to be the most satis and the gibbon a large planum orbitale articulates factory furnace material tried. From mild steel in front with the lacrimal, as in man. The figure relatively large amounts of acetylene were produced we give of the orbital wall in Pleaianthropus shows in blank experiments, and a fused silica envelope a condition almost exactly as in man. fitted with a nickel thimble was found, after it had We are here not at present concerned with the been used with calcium and barium metals, to absorb question of whether man and the Australopithecinre carbon dioxide when hot even when no calcium or have arisen from an early anthropoid, or a pre barium was present. In carrying out the absorption anthropoid, or an Old World monkey or a tarsioid ; of carbon dioxide by barium metal in the stainless but we think the evidence afforded by this new skull steel furnace it was found that when the pressure of Plesianthropus shows that the Australopithecinre at which the gas was admitted was less than about and man are very closely allied, and that these small 10·1 mm. of mercury, the yield of acetylene was brained man-like beings were very nearly human. variable and only about 45 per cent. Good yields R. BROOM were obtained when the carbon dioxide at its full J. T. RoBINSON pressure was admitted to the furnace before raising Transvaal Museum, Pretoria. the temperature above 400° C. -
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) -
Transport of Dangerous Goods
ST/SG/AC.10/1/Rev.16 (Vol.I) Recommendations on the TRANSPORT OF DANGEROUS GOODS Model Regulations Volume I Sixteenth revised edition UNITED NATIONS New York and Geneva, 2009 NOTE The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. ST/SG/AC.10/1/Rev.16 (Vol.I) Copyright © United Nations, 2009 All rights reserved. No part of this publication may, for sales purposes, be reproduced, stored in a retrieval system or transmitted in any form or by any means, electronic, electrostatic, magnetic tape, mechanical, photocopying or otherwise, without prior permission in writing from the United Nations. UNITED NATIONS Sales No. E.09.VIII.2 ISBN 978-92-1-139136-7 (complete set of two volumes) ISSN 1014-5753 Volumes I and II not to be sold separately FOREWORD The Recommendations on the Transport of Dangerous Goods are addressed to governments and to the international organizations concerned with safety in the transport of dangerous goods. The first version, prepared by the United Nations Economic and Social Council's Committee of Experts on the Transport of Dangerous Goods, was published in 1956 (ST/ECA/43-E/CN.2/170). In response to developments in technology and the changing needs of users, they have been regularly amended and updated at succeeding sessions of the Committee of Experts pursuant to Resolution 645 G (XXIII) of 26 April 1957 of the Economic and Social Council and subsequent resolutions. -
Problématiques Environnementales Et Du Développement Durable
Université Paris EST Ecole Doctorale Sciences, Ingénierie et Environnement THESE DE DOCTORAT Présentée par: SEYDINA IBRAHIMA KEBE Pour obtenir le grade de Docteur de l’Université Paris EST Spécialité : Chimie et Sciences des Matériaux Sujet de Thèse : Synthèse de matériaux monolithiques pour la séparation et la catalyse en phase liquide: Problématiques environnementales et du développement durable Soutenance le 9 décembre 2016 Devant la commission d’examen formée de : K. Faure : Chargée de recherche, CNRS Rapporteur T. Tran-Maignan : Maître de conférences Rapporteur F. Le Derf : Professeur Examinateur A. Elaissari : Directeur de recherche, CNRS Examinateur A. Bressy : Chargée de recherche, CNRS Membre invité M. Guerrouache : Ingénieur de recherche Membre invité B. Carbonnier : Professeur Directeur de thèse Thèse réalisée au sein de l’équipe Systèmes Polymères Complexes, ICMPE, CNRS, Thiais France Remerciements Je tiens à profiter de ce rapport pour exprimer mes plus grands et chaleureux remerciements envers tous ceux qui ont, en leur manière, contribué à la réussite de cette thèse Cette thèse a pu être réalisée grâce à l'accueil Madame Valérie LANGLOIS adjointe directrice de l’ICMPE, directrice du SPC professeur et chercheuse à l’Université Paris Est Créteil (UPEC). Je lui témoigne ma reconnaissance. Je n’aurais jamais commencé sans exprimer tout particulièrement mes plus grands remerciements et à témoigner toute ma reconnaissance à Benjamin CARBONNIER mon directeur de thèse, professeur des universités à l’UPEC pour l’expérience enrichissante qu’il m’a fait vivre. De simples mots, ne sauraient décrire ma satisfaction à son égard. Je tiens à remercier Mohamed GUERROUACHE, ingénieur, pour son temps consacré à me donner des explications et à me guider. -
CAUTION Or Streams with the Product Or Used Containers
PROTECTION OF WILDLIFE, FISH, CRUSTACEANS AND THE ENVIRONMENT Abamectin is extremely toxic to aquatic species. DO NOT contaminate dams, rivers CAUTION or streams with the product or used containers. KEEP OUT OF REACH OF CHILDREN FIRST AID READ SAFETY DIRECTIONS BEFORE OPENING OR USING If poisoning occurs contact a doctor or the Poisons Info Centre. Phone Australia FOR ANIMAL TREATMENT ONLY 13 11 26; New Zealand 0800 764 766. If skin contact occurs, remove contaminated clothing and wash skin thoroughly. ® SAFETY DIRECTIONS EQUITAK EXCEL ORAL PASTE HARMFUL IF SWALLOWED. May irritate the eyes and skin; avoid contact with eyes 3 in 1 Wormer for Horses and skin. Repeated exposure may cause allergic disorders. When opening the container and using the product, wear rubber gloves. Wash hands after use. DESCRIPTION EMERGENCY RESPONSE A pale cream to tan coloured, apple flavoured, palatable paste with a characteristic In case of spillage wear appropriate protective clothing and prevent material from odour and taste. Each gram contains Oxfendazole 200mg, Praziquantel 50mg and entering waterways. Absorb spills with inert material and place in waste containers. Abamectin 4mg. Wash the area with water and absorb with further inert material. Dispose of waste safely. MODE OF ACTION Abamectin stimulates the release of the neurotransmitter GABA in roundworms, MEAT WITHHOLDING PERIOD (HORSES): DO NOT USE less than 28 days which increases the membrane permeability of neurons to chloride ions. Normal before slaughter for human consumption. neural transmission is thus inhibited causing paralysis and death of the parasite. STORAGE Praziquantel affects the attachment of tapeworms to the host tissues by causing Store below 30°C (room temperature), tightly closed, in the original syringe and in spastic paralysis. -
Ammonia As a Refrigerant
1791 Tullie Circle, NE. Atlanta, Georgia 30329-2305, USA www.ashrae.org ASHRAE Position Document on Ammonia as a Refrigerant Approved by ASHRAE Board of Directors February 1, 2017 Expires February 1, 2020 ASHRAE S H A P I N G T O M O R R O W ’ S B U I L T E N V I R O N M E N T T O D A Y © 2017 ASHRAE (www.ashrae.org). For personal use only. Additional reproduction, distribution, or transmission in either print or digital form is not permitted without ASHRAE’s prior written permission. COMMITTEE ROSTER The ASHRAE Position Document on “Ammonia as a Refrigerant” was developed by the Society’s Refrigeration Committee. Position Document Committee formed on January 8, 2016 with Dave Rule as its chair. Dave Rule, Chair Georgi Kazachki IIAR Dayton Phoenix Group Alexandria, VA, USA Dayton, OH, USA Ray Cole Richard Royal Axiom Engineers, Inc. Walmart Monterey, CA, USA Bentonville, Arkansas, USA Dan Dettmers Greg Scrivener IRC, University of Wisconsin Cold Dynamics Madison, WI, USA Meadow Lake, SK, Canada Derek Hamilton Azane Inc. San Francisco, CA, USA Other contributors: M. Kent Anderson Caleb Nelson Consultant Azane, Inc. Bethesda, MD, USA Missoula, MT, USA Cognizant Committees The chairperson of Refrigerant Committee also served as ex-officio members: Karim Amrane REF Committee AHRI Bethesda, MD, USA i © 2017 ASHRAE (www.ashrae.org). For personal use only. Additional reproduction, distribution, or transmission in either print or digital form is not permitted without ASHRAE’s prior written permission. HISTORY of REVISION / REAFFIRMATION / WITHDRAWAL -
Acifluorfen Sorption, Degradation, and Mobility in a Mississippi Delta Soil
Acifluorfen Sorption, Degradation, and Mobility in a Mississippi Delta Soil L. A. Gaston* and M. A. Locke ABSTRACT repulsion effects, acifluorfen is sorbed by soil or soil Potential surface water and groundwater contaminants include her- constituents (Pusino et al., 1991; Ruggiero et al., 1992; bicides that are applied postemergence. Although applied to the plant Pusino et al., 1993; Gennari et al., 1994b; NeÁgre et al., canopy, a portion of any application reaches the soil either directly 1995; Locke et al., 1997). Although the extent of sorp- or via subsequent foliar washoff. This study examined sorption, degra- tion in soil is generally proportional to OC content dation, and mobility of the postemergence herbicide acifluorfen (5-[2- (Gennari et al., 1994b; NeÁgre et al., 1995; Locke et al., chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid) in Dundee 1997), sorption likely involves processes other than par- silty clay loam (fine-silty, mixed, thermic, Aeric Ochraqualf) taken titioning between aqueous and organic matter phases. from conventional till (CT) and no-till (NT) field plots. Homogeneous In particular, acifluorfen forms complexes with divalent surface and subsurface samples were used in the sorption and degrada- tion studies; intact soil columns (30 cm long and 10 cm diam.) were and trivalent cations (Pusino et al., 1991; Pusino et al., used in the mobility study. Batch sorption isotherms were nonlinear 1993) that may be sorbed or precipitated. Complex for- (Freundlich model) and sorption paralleled organic C (OC) content. mation and subsequent sorption may partially account All tillage by depth combinations of soil exhibited a time-dependent for increased acifluorfen sorption with decreasing soil approach to sorption equilibrium that was well described by a two- pH or increasing cation exchange capacity (Pusino et site equilibrium±kinetic model.