Oxidizer Safety
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Working with Hazardous Chemicals
A Publication of Reliable Methods for the Preparation of Organic Compounds Working with Hazardous Chemicals The procedures in Organic Syntheses are intended for use only by persons with proper training in experimental organic chemistry. All hazardous materials should be handled using the standard procedures for work with chemicals described in references such as "Prudent Practices in the Laboratory" (The National Academies Press, Washington, D.C., 2011; the full text can be accessed free of charge at http://www.nap.edu/catalog.php?record_id=12654). All chemical waste should be disposed of in accordance with local regulations. For general guidelines for the management of chemical waste, see Chapter 8 of Prudent Practices. In some articles in Organic Syntheses, chemical-specific hazards are highlighted in red “Caution Notes” within a procedure. It is important to recognize that the absence of a caution note does not imply that no significant hazards are associated with the chemicals involved in that procedure. Prior to performing a reaction, a thorough risk assessment should be carried out that includes a review of the potential hazards associated with each chemical and experimental operation on the scale that is planned for the procedure. Guidelines for carrying out a risk assessment and for analyzing the hazards associated with chemicals can be found in Chapter 4 of Prudent Practices. The procedures described in Organic Syntheses are provided as published and are conducted at one's own risk. Organic Syntheses, Inc., its Editors, and its Board of Directors do not warrant or guarantee the safety of individuals using these procedures and hereby disclaim any liability for any injuries or damages claimed to have resulted from or related in any way to the procedures herein. -
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. -
Coast Guard, DHS Pt. 150, App. I
Coast Guard, DHS Pt. 150, App. I APPENDIX I TO PART 150—EXCEPTIONS Member of reactive group Compatible with TO THE CHART Propylene glycol (20) (a) The binary combinations listed below Oleum (0) ............................... Hexane (31) have been tested as prescribed in Appendix Dichloromethane (36) III and found not to be dangerously reactive. Perchloroethylene (36) These combinations are exceptions to the 1,2-Propylene glycol (20) ...... Diethylenetriamine (7) Compatibility Chart (Figure 1) and may be Polyethylene polyamines (7) Triethylenetetramine (7) stowed in adjacent tanks. Sodium dichromate, 70% (0) Methyl alcohol (20) Member of reactive group Compatible with Sodium hydrosulfide solution Methyl alcohol (20) (5). Acetone (18) .......................... Diethylenetriamine (7) Iso-Propyl alcohol (20) Acetone cyanohydrin (0) ....... Acetic acid (4) Sulfuric acid (2) ..................... Coconut oil (34) Acrylonitrile (15) ..................... Triethanolamine (8) Coconut oil acid (34) Palm oil (34) 1,3-Butylene glycol (20) ......... Morpholine (7) Tallow (34) 1,4-Butylene glycol (20) ......... Ethylamine (7) Sulfuric acid, 98% or less (2) Choice white grease tallow Triethanolamine (8) (34) gamma-Butyrolactone (0) ...... N-Methyl-2-pyrrolidone (9) Caustic potash, 50% or less Isobutyl alcohol (20) (b) The binary combinations listed below (5). Ethyl alcohol (20) have been determined to be dangerously re- Ethylene glycol (20) active, based on either data obtained in the Isopropyl alcohol (20) Methyl alcohol (20) literature or on laboratory testing which has iso-Octyl alcohol (20) been carried out in accordance with proce- Caustic soda, 50% or less (5) Butyl alcohol (20) dures prescribed in Appendix III. These com- tert-Butyl alcohol, Methanol binations are exceptions to the Compat- mixtures ibility Chart (Figure 1) and may not be Decyl alcohol (20) stowed in adjacent tanks. -
1,45%,562 UNITED SATES P All.‘ Bl If" Til?
Patented May 1, 1923. 1,45%,562 UNITED SATES P All.‘ bl if" til? . ROBERT E. WILSON, LEON ‘JV. PARSONS, AND STANLEY 1E. OHXSHOLIYI, OF WASHINGTON, DISTRICT OF COLUMBIA. PROCESS THE PRODUCTION OE‘ All‘HALLEAETELMLETAL PERTJIANGANATES. N0 Drawing". Application ?led September 27, 1918. Serial No. 255,975. To (all to]: am it may concern. .' manganate by oxidation or acidification, Be it known that we, Romain‘ E. lllinsou, metatheses into calcium pern'iangamite by LEON “7. Parsons, and STANLEY L. Unis treatment With calcium sulphate or milk at HoLM, citizens of the United States. and sta lime. tioned at ViTashington, District of Columbia, O'li' these four possible methods, (1.) is not 60 in the o?icc of the Director the Chemical a possible large scale method. on account l/Varfare Service, Research Division, have in of its use ot silver; (2) and are elec vented a Process for the ll’roduction oif Al trolytic methods Without a. great deal out kali-Earth-l\letal Permanpjanates, of which promise, and are to be considered elsewhere; ll) the ‘following is a speci?cation. (ll) the principal subject of this applica G3 in The present invention relates to the pro tion. duction oi? alkah» earth metal permangam Three distinct methods for preparing: ba~ nates and especially the permanganates of rium (or strontium) manganate have been calcium and magnesium as these have beenv here investigated. The ?rst of? these meth found to be very ellicient oxidizing agents ods involves heating together barium perox 70 for certain purposes, more e?icient even. than ide, hydroxide, or a salt, such as the nitrate the permanganates of the allmliearth metals. -
Decolorization of Reactive Orange 16 Via Ferrate(VI) Oxidation Assisted by Sonication
Turkish Journal of Chemistry Turk J Chem (2017) 41: 577 { 586 http://journals.tubitak.gov.tr/chem/ ⃝c TUB¨ ITAK_ Research Article doi:10.3906/kim-1701-8 Decolorization of reactive orange 16 via ferrate(VI) oxidation assisted by sonication Serkan S¸AHINKAYA_ ∗ Department of Environmental Engineering, Faculty of Engineering and Architecture, Nev¸sehirHacı Bekta¸sVeli University, Nev¸sehir,Turkey Received: 02.01.2017 • Accepted/Published Online: 24.03.2017 • Final Version: 05.09.2017 Abstract: The decolorization of azo dye C.I. reactive orange 16 (RO 16) via ferrate(VI) and sono-ferrate(VI) methods, which is the combination of the ferrate(VI) oxidation method with sonication, has been achieved in the present study. The influences of some important operating parameters, which are the initial pH, the concentration of potassium ferrate(VI) (K 2 FeO 4) and the RO 16 dye, and ultrasonic density (for only the sono-ferrate(VI) method), on the color removal have −1 been investigated. The optimum conditions have been determined as pH = 7 and [K 2 FeO 4 ] = 50 mg L for the −1 −1 individual ferrate(VI) oxidation method and pH = 7 and [K 2 FeO 4 ] = 50 mg L by direct sonication at 0.50 W mL ultrasonic density and 20 kHz fixed frequency for the sono-ferrate(VI) method. The color removal efficiencies were 85% by ferrate(VI) method and 91% by sono-ferrate(VI) method. Kinetic studies were also performed for the decolorization of RO 16 under the optimized conditions at room temperature. It was seen that the oxidative decolorization of RO 16 via the sono-ferrate(VI) method happened more rapidly because of the production of OH • radical through sonication compared to the individual ferrate(VI) method. -
Kinetic Studies on Permanganate Oxidation of Acetophenones Under
Indi an Journal of Chemistry Vol. 40A, June 2001, pp. 610-612 Kinetic studies on permanganate oxidation of The ketones were further purified by vacuum acetophenones under phase transfer catalysis distillation. The solvents employed were purified by standard methods and doubly distilled water was P S Sheeba & T D Radhakrishnan Nair* always used. The catalysts used were tricapryl Department of Chemistry, Calicut University methylammonium chloride (TCMAC) and tetrabutyl Calicut University P.O., Kerala 673 635. India ammonium bromide (TBAB). The former has Received 18 October 2000; revised 8 March 2001 relatively larger organic structure (C 10H21 )JN+CH 3Cr compared to the latter (C4 H9) 4N+B(. Kinetic studies on the permanganate oxidation of The solutions containing the permanganate ions in acetopheno_ne and some of its substituents in organic media using the organic solvents were prepared by shaking the techn1que of phase transfer catalysis are reported. aqueous potassium permanganate solution with the Tncaprylmethylammonium chloride and tetrabutylammonium bromide have been used as the phase transfer catalysts. The organic solvents contammg the phase transfer 4 reaction shows first order dependence each on [ketones] and the catalysts as reported elsewhere . The solutions of the [permanganate ions] respectively . The rate coefficients fit well oxidant thus prepared in the organic solvent and the with the Hammett equation and the p-value calculated aorees well substrate in the organic solvent were thermally with the reaction requirements. "' equilibrated (± 0.05°C) at the desired temperature for Potassium permanganate is a powerful oxidizing about half an hour before mixing. Kinetic runs were carried out under pseudo-first order conditions. -
Manufacturing of Potassium Permanganate Kmno4 This Is the Most Important and Well Known Salt of Permanganic Acid
Manufacturing of Potassium Permanganate KMnO4 This is the most important and well known salt of permanganic acid. It is prepared from the pyrolusite ore. It is prepared by fusing pyrolusite ore either with KOH or K2CO3 in presence of atmospheric oxygen or any other oxidising agent such as KNO3. The mass turns green with the formation of potassium manganate, K2MnO4. 2MnO2 + 4KOH + O2 →2K2MnO4 + 2H2O 2MnO2 + 2K2CO3 + O2 →2K2MnO4 + 2CO2 The fused mass is extracted with water. The solution is now treated with a current of chlorine or ozone or carbon dioxide to convert manganate into permanganate. 2K2MnO4 + Cl2 → 2KMnO4 + 2KCl 2K2MnO4 + H2O + O3 → 2KMnO4 + 2KOH + O2 3K2MnO4 + 2CO2 → 2KMnO4 + MnO2 + 2K2CO3 Now-a-days, the conversion is done electrolytically. It is electrolysed between iron cathode and nickel anode. Dilute alkali solution is taken in the cathodic compartment and potassium manganate solution is taken in the anodic compartment. Both the compartments are separated by a diaphragm. On passing current, the oxygen evolved at anode oxidises manganate into permanganate. At anode: 2K2MnO4 + H2O + O → 2KMnO4 + 2KOH 2- - - MnO4 → MnO4 + e + - At cathode: 2H + 2e → H2 Properties: It is purple coloured crystalline compound. It is fairly soluble in water. When heated alone or with an alkali, it decomposes evolving oxygen. 2KMnO4 → K2MnO4 + MnO2 + O2 4KMnO4 + 4KOH → 4K2MnO4 + 2H2O + O2 On treatment with conc. H2SO4, it forms manganese heptoxide via permanganyl sulphate which decomposes explosively on heating. 2KMnO4+3H2SO4 → 2KHSO4 + (MnO3)2SO4 + 2H2O (MnO3)2SO4 + H2O → Mn2O7 + H2SO4 Mn2O7 → 2MnO2 + 3/2O2 Potassium permanganate is a powerful oxidising agent. A mixture of sulphur, charcoal and KMnO4 forms an explosive powder. -
Hazardous Material Inventory Statement
City of Brooklyn Park FIRE DEPARTMENT 5200 - 85th Avenue North Brooklyn Park MN 55443 Phone: (763)493-8020 Fax: (763) 493-8391 Hazardous Materials Inventory Statement Users Guide A separate inventory statement shall be provided for each building. An amended inventory statement shall be provided within 30 days of the storage of any hazardous materials or plastics that changes or adds a hazard class or which is sufficient in quantity to cause an increase in the quantity which exceeds 5 percent for any hazard class. The hazardous materials inventory statement shall list by hazard class categories. Each grouping shall provide the following information for each hazardous material listed for that group including a total quantity for each group of hazard class. 1. Hazard class. (See attached Hazardous Materials Categories Listing) 2. Common or trade name. 3. Chemical Abstract Service Number (CAS number) found in 29 Code of Federal Regulations (C.F.R.). 4. Whether the material is pure or a mixture, and whether the material is a solid, liquid or gas 5. Maximum aggregate quantity stored at any one time. 6. Maximum aggregate quantity In-Use (Open to atmosphere) at any one time. 7. Maximum aggregate quantity In-Use (Closed to atmosphere) at any one time. 8. Storage conditions related to the storage type, high-pile, encapsulated, non-encapsulated. Attached is a listing of categories that all materials need to be organized to. Definitions of these categories are also attached for your use. At the end of this packet are blank forms for completing this project. For questions regarding Hazardous Materials Inventory Statement contact the Fire Department at 763-493-8020. -
Towards Better Understanding of C60 Organosols†
PCCP View Article Online PAPER View Journal | View Issue Towards better understanding of C60 organosols† a a a Cite this: Phys. Chem. Chem. Phys., Nikolay O. Mchedlov-Petrossyan,* Nika N. Kamneva, Younis T. M. Al-Shuuchi, b c d e 2016, 18,2517 Andriy I. Marynin, Olexii S. Zozulia, Alexander P. Kryshtal, Vladimir K. Klochkov and Sergey V. Shekhovtsova It is of common knowledge that fullerenes form colloids in polar solvents. However, the coagulation via electrolytes and the origin of the negative charge of species are still unexplored. Using a ‘radical À scavenger’ and electrospray ionization spectroscopy (ESI), we proved the formation of ion-radical C60 2À 2À and its (probable) transformation into C60 or (C60)2 . The coagulation of C60 organosols by NaClO4 and other perchlorates and nitrates in acetonitrile and its mixture with benzene obeys the Schulze– Hardy rule. At higher Ca(ClO4)2 and La(ClO4)3 concentrations, instead of coagulation, stable re-charged Received 7th November 2015, colloidal particles appeared, up to a zeta-potential of +(20–42) mV, as compared with À(33–35) mV of Accepted 7th December 2015 the initial organosols. The influence of both HClO4 and CF3SO3H was similar. This phenomenon is attrib- DOI: 10.1039/c5cp06806a uted to poor solvation of inorganic cations in cationo- and protophobic acetonitrile, which was proven using [2.2.2] cryptand. Further increasing the concentration of Ca(ClO4)2 led again to coagulation, thus www.rsc.org/pccp demonstrating a novel type of ‘coagulation zones’. 1. Introduction believe that -
Prohibited and Restricted Chemical List
School Emergency Response Plan and Management Guide Prohibited and Restricted Chemical List PROHIBITED AND RESTRICTED CHEMICAL LIST Introduction After incidents of laboratory chemical contamination at several schools, DCPS, The American Association for the Advancement of Science (AAAS) and DC Fire and Emergency Management Services developed an aggressive program for chemical control to eliminate student and staff exposure to potential hazardous chemicals. Based upon this program, all principals are required to conduct a complete yearly inventory of all chemicals located at each school building to identify for the removal and disposal of any prohibited/banned chemicals. Prohibited chemicals are those that pose an inherent, immediate, and potentially life- threatening risk, injury, or impairment due to toxicity or other chemical properties to students, staff, or other occupants of the school. These chemicals are prohibited from use and/or storage at the school, and the school is prohibited from purchasing or accepting donations of such chemicals. Restricted chemicals are chemicals that are restricted by use and/or quantities. If restricted chemicals are present at the school, each storage location must be addressed in the school's written emergency plan. Also, plan maps must clearly denote the storage locations of these chemicals. Restricted chemicals—demonstration use only are a subclass in the Restricted chemicals list that are limited to instructor demonstration. Students may not participate in handling or preparation of restricted chemicals as part of a demonstration. If Restricted chemicals—demonstration use only are present at the school, each storage location must be addressed in the school's written emergency plan. Section 7: Appendices – October 2009 37 School Emergency Response Plan and Management Guide Prohibited and Restricted Chemical List Following is a table of chemicals that are Prohibited—banned, Restricted—academic curriculum use, and Restricted—demonstration use only. -
Experiment: Determination of Manganese in Steel
p.1 of 4 Chemistry 201 – Winter 2007 Experiment: Determination of Manganese in Steel Manganese (Mn) in steel may be determined upon dissolution as manganese (VII) after oxidation from the manganese oxidation state (II). This procedure calls for three oxidizing agents. Manganese (VII) may be determined spectrophotometrically. During dissolution of the sample with dilute nitric acid to form iron (II) and manganese (II), nitrogen oxide gases are formed. These must be removed, partially by boiling, and the rest with ammonium peroxydisulfate which also removes carbon or other organic matter present. The nitrogen oxides may react with periodic acid which is used to convert manganese to the (VII) oxidation state. Excess peroxydisulfate is decomposed by boiling. The equations are: - + 2+ 3 Mn + 2 NO3 + 8H ---> 3 Mn + 2 NO (g) + 4H2O 2- - 2- + 2 NO2 (g) + S2O8 + 2 H2O ---> 2 NO3 + 2 SO4 + 4 H 2- 2- + 2 S2O8 + 2 H2O + heat ---> 4 SO4 + O2 + 4 H 2+ - - + - 2 Mn + 5 IO4 + 3 H2O ---> 2 MnO4 + 6 H + 5 IO3 NO(colorless gas) + 1/2 O2 (g) <---> NO2 (brown gas) Note: Peroxydisulfate has the required oxidizing potential to change the oxidation state of manganese from (II) to (IV), but the reaction is too slow. Silver could be employed catalytically but the results are too erratic. Periodate oxidizes the manganese to the (VII) state quantitatively and rapidly at the boiling point, and it is advisable to add the sparingly soluble periodate salt in several portions to maintain an excess and to allow for some decomposition of the latter salt at the elevated temperatures. -
Layered Iron Vanadate As a High-Capacity Cathode Material for Nonaqueous Calcium-Ion Batteries
batteries Article Layered Iron Vanadate as a High-Capacity Cathode Material for Nonaqueous Calcium-Ion Batteries Munseok S. Chae 1 , Dedy Setiawan 1, Hyojeong J. Kim 1 and Seung-Tae Hong 1,2,* 1 Department of Energy Science and Engineering, DGIST (Daegu Gyeongbuk Institute of Science and Technology), Daegu 42988, Korea; [email protected] (M.S.C.); [email protected] (D.S.); [email protected] (H.J.K.) 2 Energy Science and Engineering Research Center, DGIST (Daegu Gyeongbuk Institute of Science and Technology), Daegu 42988, Korea * Correspondence: [email protected]; Tel.: +82-53-785-6415 Abstract: Calcium-ion batteries represent a promising alternative to the current lithium-ion batteries. Nevertheless, calcium-ion intercalating materials in nonaqueous electrolytes are scarce, probably due to the difficulties in finding suitable host materials. Considering that research into calcium-ion batteries is in its infancy, discovering and characterizing new host materials would be critical to further development. Here, we demonstrate FeV3O9·1.2H2O as a high-performance calcium-ion battery cathode material that delivers a reversible discharge capacity of 303 mAh g−1 with a good cycling stability and an average discharge voltage of ~2.6 V (vs. Ca/Ca2+). The material was synthesized via a facile co-precipitation method. Its reversible capacity is the highest among calcium- ion battery materials, and it is the first example of a material with a capacity much larger than that of conventional lithium-ion battery cathode materials. Bulk intercalation of calcium into the host lattice contributed predominantly to the total capacity at a lower rate, but became comparable to that due to Citation: Chae, M.S.; Setiawan, D.; surface adsorption at a higher rate.