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(12) United States Patent (10) Patent No.: US 8,455,647 B2 Delong Et Al
USOO8455647B2 (12) United States Patent (10) Patent No.: US 8,455,647 B2 deLong et al. (45) Date of Patent: *Jun. 4, 2013 (54) 6-AMINOISOQUINOLINE COMPOUNDS 7,671,205 B2 3/2010 deLong et al. 8,034,943 B2 10/2011 delong et al. 2004/0091946 A1 5/2004 Oakley et al. (75) Inventors: Mitchell A. deLong, Chapel Hill, NC 2005/OO32125 A1 2/2005 Oakley et al. (US); Jill Marie Sturdivant, Chapel 2005/0176712 A1 8/2005 Wakabayashi et al. Hill, NC (US); Geoffrey Richard 2005/0282805 A1 12/2005 Hangeland et al. Heintzelman, Durham, NC (US); Susan 2006/027O670 A1 11/2006 Chew et al. M. Royalty, Cary, NC (US) 2007/011 1983 A1 5/2007 Fong 2007/O123561 A1 5/2007 Lee et al. 2007/01294.04 A1 6/2007 Hagihara et al. (73) Assignee: Aerie Pharmaceuticals, Inc., Research 2007/O135499 A1 6/2007 deLong et al. Triangle Park, NC (US) 2007/0142429 A1 6/2007 deLong et al. 2007/O149473 A1 6/2007 Chatterton et al. (*) Notice: Subject to any disclaimer, the term of this 2007/014.9548 A1 6/2007 Hellberg et al. patent is extended or adjusted under 35 2007/0167444 A1 7/2007 Kuramochi et al. 2007/0173530 A1 7/2007 deLong et al. U.S.C. 154(b) by 0 days. 2007/0238741 A1 10/2007 Nagarathnam et al. 2008, 0021026 A1 1/2008 Kahraman et al. This patent is Subject to a terminal dis 2008, 0021217 A1 1/2008 Borchardt et al. claimer. 2008, OO58384 A1 3/2008 Lee et al. -
Ephedrine by Pseudomonas Putida Detection of (—)-Ephedrine: NAD+-Oxidoreductase from Arthrobacter Globiformis
Degradation of (—)-Ephedrine by Pseudomonas putida Detection of (—)-Ephedrine: NAD+-oxidoreductase from Arthrobacter globiformis E. Klamann and F. Lingens Institut für Mikrobiologie, Universität Hohenheim, Garbenstraße 30, D-7000 Stuttgart 70 Z. Naturforsch. 35 c, 80-87 (1980); received October 24, 1979 (—)-Ephedrine, (—)-Ephedrine: NAD+-oxidoreductase, Pseudomonas putida, Arthrobacter globiformis A bacterium utilizing the alkaloid (-)-ephedrine as its sole source of carbon was isolated by an enrichment-culture technique from soil supplemented with 4-benzoyl-l,3-oxazolidinon-(2). The bacterium was identified as Pseudomonas putida by morphological and physiological studies. The following metabolites were isolated from the culture fluid: methylamine, formaldehyde, methyl- benzoylcarbinol (2-hydroxy-1-oxo-l-phenylpropane), benzoid acid, pyrocatechol and cis, cis- muconic acid. A pathway for the degradation of (-)-ephedrine by Pseudomonas putida is proposed and compared with the degradative pathway in Arthrobacter globiformis. The enzyme, which is responsible for the first step in the catabolism of (-)-ephedrine could be demonstrated in extracts from Arthrobacter globiformis. This enzyme catalyses the dehydrogena tion of (—)-ephedrine yielding phenylacetylcarbinol/methylbenzoylcarbinol and methylamine. It requires NAD+ as cofactor and exhibits optimal activity at pH 11 in 0.1 M glycine/NaOH buffer. The K m value for (—)-ephedrine is 0.02 mM and for N A D + 0.11 mM , respectively. No remarkable loss of activity is observed following treatment -
Chlorobenzene
CHLOROBENZENE What is CHLOROBENZENE? Chlorobenzene is a man-made colorless liquid that burns quickly. It has a pleasant smell like the smell of almonds. Some of it will dissolve in water. It also turns into a vapor and goes into the air. Chlorobenzene is not found in nature. Where can chlorobenzene be found and how is it used? Over the past 40 years in the United States, less cholorobenzene is being manufactured. In the past, cholorobenzene was used to make phenol and DDT. Today, it is still used to produce pesticides and chemicals used to prevent or kill unwanted pests. Chlorobenzene may be also be used to grease car parts. Chlorobenzene sent into the air is slowly broken down by other chemicals and sunlight. It can be removed from the air by rain. In water, chlorobenzene will quickly turn into a vapor, or be broken down by bacteria. When it enters soil, most of it is broken down quickly by bacteria and the rest will turn into a vapor or leach into groundwater. How can people be exposed to chlorobenzene? You could be exposed to chlorobenzene through: Breathing the chemical. People who work in places where chlorobenzene is processed or handled are at greatest risk. If you live near a waste site, you could be exposed to vapors in the air. Eating or drinking food or water that has been in contact with chlorobenzene. If you live near a waste site, you could be exposed from water contaminated by chlorobenzene. Touching soil contaminated with chlorobenzene. This happens to people who live near a waste site or a factory. -
Reactions of Aromatic Compounds Just Like an Alkene, Benzene Has Clouds of Electrons Above and Below Its Sigma Bond Framework
Reactions of Aromatic Compounds Just like an alkene, benzene has clouds of electrons above and below its sigma bond framework. Although the electrons are in a stable aromatic system, they are still available for reaction with strong electrophiles. This generates a carbocation which is resonance stabilized (but not aromatic). This cation is called a sigma complex because the electrophile is joined to the benzene ring through a new sigma bond. The sigma complex (also called an arenium ion) is not aromatic since it contains an sp3 carbon (which disrupts the required loop of p orbitals). Ch17 Reactions of Aromatic Compounds (landscape).docx Page1 The loss of aromaticity required to form the sigma complex explains the highly endothermic nature of the first step. (That is why we require strong electrophiles for reaction). The sigma complex wishes to regain its aromaticity, and it may do so by either a reversal of the first step (i.e. regenerate the starting material) or by loss of the proton on the sp3 carbon (leading to a substitution product). When a reaction proceeds this way, it is electrophilic aromatic substitution. There are a wide variety of electrophiles that can be introduced into a benzene ring in this way, and so electrophilic aromatic substitution is a very important method for the synthesis of substituted aromatic compounds. Ch17 Reactions of Aromatic Compounds (landscape).docx Page2 Bromination of Benzene Bromination follows the same general mechanism for the electrophilic aromatic substitution (EAS). Bromine itself is not electrophilic enough to react with benzene. But the addition of a strong Lewis acid (electron pair acceptor), such as FeBr3, catalyses the reaction, and leads to the substitution product. -
Ligand-Based Pharmacophore Studies in the Dopaminergic System Amar P
University of Wollongong Research Online University of Wollongong Thesis Collection University of Wollongong Thesis Collections 2011 Ligand-based pharmacophore studies in the dopaminergic system Amar P. Inamdar University of Wollongong Recommended Citation Inamdar, Amar P., Ligand-based pharmacophore studies in the dopaminergic system, Doctor of Philosophy thesis, School of Chemistry, University of Wollongong, 2011. http://ro.uow.edu.au/theses/3535 Research Online is the open access institutional repository for the University of Wollongong. For further information contact Manager Repository Services: [email protected]. LIGAND-BASED PHARMACOPHORE STUDIES IN THE DOPAMINERGIC SYSTEM A thesis submitted in partial fulfilment of the requirements for the award of the degree DOCTOR OF PHILOSOPHY From UNIVERSITY OF WOLLONGONG By AMAR P. INAMDAR, B.PHARM., M.PHARM. SCHOOL OF CHEMISTRY November 2011 THESIS CERTIFICATION I, Amar P. Inamdar, declare that this thesis, submitted in partial fulfilment of the requirements for the award of Doctor of Philosophy, in the School of Chemistry, University of Wollongong, is wholly my own work unless otherwise referenced or acknowledged. The document has not been submitted for qualifications at any other academic institution. Amar P. Inamdar November 2011 i ACKNOWLEDGEMENTS I am truly grateful to my supervisor, Prof. John B. Bremner, whose support, encouragement and guidance has helped me immensely in the completion of this project. Most importantly, I am thankful for his patience over all these years and believing in me in spite of various difficult periods in this journey. I know he has sacrificed a significant amount of his personal time to make this happen. I also owe my deepest gratitude to Associate Prof. -
Toxicological Profile for Chlorobenzene
TOXICOLOGICAL PROFILE FOR CHLOROBENZENE Agency for Toxic Substances and Disease Registry U.S. Public Health Service December 1990 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. 1 1. PUBLIC HEALTH STATEMENT This Statement was prepared to give you information about chlorobenzene and to emphasize the human health effects that may result from exposure to it. The Environmental Protection Agency (EPA) has identified 1,177 sites on its National Priorities List (NPL). Chlorobenzene has been found at 97 of these sites. However, we do not know how many of the 1,177 NPL sites have been evaluated for chlorobenzene. As EPA evaluates more sites, the number of sites at which chlorobenzene is found may change. The information is important for you because chlorobenzene may cause harmful health effects and because these sites are potential or actual sources of human exposure to chlorobenzene. When a chemical is released from a large area, such as an industrial plant, or from a container, such as a drum or bottle, it enters the environment as a chemical emission. This emission, which is also called a release, does not always lead to exposure. You can be exposed to a chemical only when you come into contact with the chemical. You may be exposed to it in the environment by breathing, eating, or drinking substances containing the chemical or from skin contact with it. If you are exposed to a hazardous substance such as chlorobenzene, several factors will determine whether harmful health effects will occur and what the type and severity of those health effects will be. -
Kinetic Investigation of Nitroarylation of Pyrrole with 1-Chloro-4
ienc Sc es al J c o i u m r e n a h l C Selvaraj et al., Chem Sci J 2015, 6:3 Chemical Sciences Journal DOI: 10.4172/2150-3494.1000104 ISSN: 2150-3494 Research Article Article OpenOpen Access Access Kinetic Investigation of Nitroarylation of Pyrrole with 1-Chloro-4- Nitrobenzene Using a New Multi-Site Phase-Transfer Catalyst under Ultrasonic Condition Selvaraj V1*, Harikumar K2, Sathiyaraj M3 and Rajendran V3 1PG Department of Chemistry, Sri Akilandeswari Women’s College, Wandiwash, Tamil Nadu, India 2Sri Chandrashekarendra Saraswathi Viswa Maha Vidyalaya University, Kanchipuram, Enathur, Tamil Nadu, India 3Department of Chemistry, Pachaiyappa’s College for Men, Kanchipuram, Tamil Nadu, India Abstract In the present research work, the solid-liquid reaction was successfully carried out in the new synthesized multi- site phase-transfer catalyst, namely i.e., 1,3,5-tribenzyl-1,3,5-triethyl-1,3,5-triazinane-1,3,5-triium trichloride(MPTC), and sonication (40 kHz, 300 W) to produce the desired product namely 1-(4-nitropheny) pyrrole from pyrrole and 4-nitrochlorobenzene. The selectivity of N-arylation product was obtained under sonication and MPTC. The combination of ultrasound and MPTC resulted in better efficacy as compared to the individual operations. The apparent reaction rate is greatly enhanced and observed to obey the pseudo-first order kinetics. The appk value increases with increasing kinetic parameters that is the amount of [MPTC], [substrate], ultrasonication, stirring speed, temperature, etc. Keywords: Sonochemistry; Pyrrole; Interfacial reaction; Kinetics; The effect of ultrasonic energies in organic syntheses (homogeneous MPTC; 1-Chloro-4-Nitrobenzene and heterogeneous reactions) has been boosted in recent years [21-27]. -
Chlorobenzenes (PDF)
EPA-454/R-93-044 LOCATING AND ESTIMATING AIR EMISSIONS FROM SOURCES OF CHLOROBENZENES (REVISED) Office of Air Quality Planning and Standards U.S. Environmental Protection Agency Research Triangle Park, North Carolina 27711 March 1994 This report has been reviewed by the Office of Air Quality Planning and Standards, U.S. Environmental Protection Agency, and has been approved for publication. Any mention of trade names or commercial products is not intended to constitute endorsement or recommendation for use. ii CONTENTS Section Page DISCLAIMER ..................................................... ii LIST OF FIGURES .................................................. vi LIST OF TABLES .................................................. vii 1.0 PURPOSE OF DOCUMENT ..................................... 1-1 1.1 Reference for Section 1.0 ................................... 1-5 2.0 OVERVIEW OF DOCUMENT CONTENTS .......................... 2-1 2.1 References for Section 2.0 .................................. 2-5 3.0 BACKGROUND .............................................. 3-1 3.1 Nature of Pollutant ....................................... 3-1 3.1.1 Properties of Chlorobenzenes ........................... 3-5 3.1.2 Properties of Monochlorobenzene ........................ 3-6 3.1.3 Properties of Dichlorobenzenes .......................... 3-6 3.1.4 Properties of Trichlorobenzenes ......................... 3-7 3.1.5 Properties of Hexachlorobenzene ........................ 3-7 3.2 Overview of Production and Use .............................. 3-8 3.3 -
Paper 1 CIE Chemistry A-Level
PMT Cambridge International Examinations Cambridge International Advanced Subsidiary and Advanced Level CHEMISTRY 9701/12 Paper 1 Multiple Choice February/March 2017 1 hour Additional Materials: Multiple Choice Answer Sheet *7298237059* Soft clean eraser Soft pencil (type B or HB is recommended) Data Booklet READ THESE INSTRUCTIONS FIRST Write in soft pencil. Do not use staples, paper clips, glue or correction fluid. Write your name, Centre number and candidate number on the Answer Sheet in the spaces provided unless this has been done for you. DO NOT WRITE IN ANY BARCODES. There are forty questions on this paper. Answer all questions. For each question there are four possible answers A, B, C and D. Choose the one you consider correct and record your choice in soft pencil on the separate Answer Sheet. Read the instructions on the Answer Sheet very carefully. Each correct answer will score one mark. A mark will not be deducted for a wrong answer. Any rough working should be done in this booklet. Electronic calculators may be used. This document consists of 14 printed pages and 2 blank pages. IB17 03_9701_12/4RP © UCLES 2017 [Turn over PMT 2 Section A For each question there are four possible answers, A, B, C and D. Choose the one you consider to be correct. Use of the Data Booklet may be appropriate for some questions. – 1 Which ion has the same electronic configuration as Cl ? A F– B P+ C Sc3+ D Si4+ 2 Compounds J and K each contain 40% carbon by mass. What could J and K be? J K A a hexose, C6H12O6 starch, (C6H10O5)n B a pentose, C5H10O5 a hexose, C6H12O6 C a pentose, C5H10O5 sucrose, C12H22O11 D starch, (C6H10O5)n sucrose, C12H22O11 3 Two moles of compound P were placed in a sealed container. -
Pesticides and Intermediates, Supp. A
PROCESS ECONOMICS PROGRAM SRI INTERNATIONAL Menlo Park, California ABSTRACT 94025 l Process Economics Program Report No. 171A (August 1985) -0 This report describes and evaluates the processes for making carbo- furan and mancozeb, as well as the intermediates for these two pesti- cides. Carbofuran is made from either catechol or o-nitrochlorobenzene. The economics of each route, including the manufacture of the inter- mediates methyl isocyanate and methallyl chloride, are evaluated. The catechol route is found to be economically superior. For methyl iso- cyanate, which is common to both routes, two nonphosgenation processes are evaluated and compared with two phosgenation processes. The non- phosgenation route is not only competitive with the phosgenation route, but also avoids the transport of both methyl isocyanate and Phosgene when integrated with carbofuran production. Mancoxeb is evaluated in detail, with a brief evaluation of two similar pesticides, maneb, and zineb. The intermediates are carbon disulfide and ethylenediamine. The process for making carbon disulfide from methane and sulfur is evaluated, with a discussion of the use of alternative carbon sources. For ethylenediamine, two processes start- ing from ethylene dichloride, one process from monoethanolamine, and 0 another from ethylene oxide are evaluated and compared. PEP'84 YCY, DJL, CSL - Report No.171A 0 PESTICIDES AND INTERMEDIATES SUPPLEMENT A by YEN-CHEN YEN with contributions by DIN-JIN LIN 0 and CHUN-SAN LIU August 1985 A private report by the PROCESS ECONOMICS PROGRAM Menlo Park, California 94025 For detailed marketing data and information, the reader is referred to one of the SRI programs specializing in marketing research. -
A Sustainable Route from Biogenic Levulinic Acid to 1,5-Dimethyl-2-Pyrrolidone
Electronic Supplementary Material (ESI) for Green Chemistry. This journal is © The Royal Society of Chemistry 2021 Supplementary Information Reviving electrocatalytic reductive amination: A sustainable route from biogenic levulinic acid to 1,5-dimethyl-2-pyrrolidone Sonja D. Mürtza, Nils Kuriga, F. Joschka Holzhäusera, Regina Palkovits∗a a Institute of Technical and Macromolecular Chemistry, RWTH Aachen University, Worringerweg 2, 52074 Aachen, Germany. ∗ author of correspondence: [email protected] Contents Contents 1 Additional results2 1.1 Influence of the amine structure . .2 2 Experimental4 2.1 Electrolysis batch experiments . .4 2.2 Microwave experiments . .5 2.3 Purification of the product solution . .6 2.4 Nuclear magnetic resonance spectroscopy . .6 2.5 Chemicals: Origin and purity . .7 3 NMR spectroscopy8 3.1 Basic equation for calculations . .8 3.2 N-Methylisopropylamine . .9 3.3 N-Methylbutan-2-amine . 10 3.4 N-Methylpentan-2-amine . 11 3.5 N-Methylpentan-3-amine . 12 3.6 N-Methylcyclopentanamine . 13 3.7 4-(Methylamino)-pentanoic acid . 14 3.8 1,5-Dimethyl-2-pyrrolidone . 15 1 1 Additional results 1 Additional results 1.1 Influence of the amine structure Due to the differing results for sterically different ketonic substrates, an impact of the steric hindrance of the amine was expected as well. The reductive amination of acetone with methylamine and ethylamine was already investigated by Smirnov et al.[1] In this work, very similar results were obtained (Figure S1). 1.0 0.8 Conversion Y (Amine) 0.6 Y (Amine)[47] 0.4 Y (Alcohol) Y (Alcohol)[47] 0.2 Conversion, Yield (-) 0.0 Ammonia Methylamine Ethylamine Ethanolamine Figure S1: Conversion and yields Y of the electrocatalytic reductive amination of acetone with different amines compared to the results of Smirnov et al.[1] Conditions: Pb elec- −2 −1 trodes, 0.04 A cm , 2.4 mol L ketone in 0.5 M KH2PO4, acetone to amine ratio: 1:1.2, pH = 12, one faraday equivalent, 283 K. -
Agency for Toxic Substances and Disease Registry U.S. Public Health Service
TOXICOLOGICAL PROFILE FOR CHLOROBENZENE Agency for Toxic Substances and Disease Registry U.S. Public Health Service December 1990 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. iii FOREWORD The Superfund Amendments and Reauthorization Act (SARA) of 1986 (Public Law 99-499) extended and amended the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA or Superfund). This public law directed the Agency for Toxic Substances and Disease Registry (ATSDR) to prepare toxicological profiles for hazardous substances which are most commonly found at facilities on the CERCLA National Priorities List and which pose the most significant potential threat to human health, as determined by ATSDR and the Environmental Protection Agency (EPA). The lists of the 250 most significant hazardous substances were published in the Federal Register on April 17, 1987, on October 20, 1988, on October 26, 1989, and on October 17, 1990. Section 104(i)(3) of CERCLA, as amended, directs the Administrator of ATSDR to prepare a toxicological profile for each substance on the list. Each profile must include the following content: (A) An examination, summary, and interpretation of available toxicological information and epidemiological evaluations on the hazardous substance in order to ascertain the levels of significant human exposure for the substance and the associated acute, subacute, and chronic health effects, (B) A determination of whether adequate information on the health effects of each substance is available or in the process of development to determine levels of exposure which present a significant risk to human health of acute, subacute, and chronic health effects, and (C) Where appropriate, an identification of toxicological testing needed to identify the types or levels of exposure that may present significant risk of adverse health effects in humans.