Sulfur Dioxide and “Sulfurous Acid” Solutions. S + O 2 → SO2 (G
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1 the Volumetric Determination of Hydroxylamine
VOLUMETRIC DETERMINATION OF HYDROXYLAMINE. I363 [CONTRIBUTION FROM THE CHEMICAL LABORATORYOF THE UNIVERSITY OF CALIFORNIA.1 THE VOLUMETRIC DETERMINATION OF HYDROXYLAMINE. BY WILLIAMC. BRAY,MIBUM E. SIMPSONAND ANNA A. MACKENZIE. Received July 17, 1919 In the present investigation 3 volumetric methods of determining hydroxylamine in aqueous solution have been studied : The titanous salt method,' in which the hydroxylamine is reduced by excess titanous salt in acid solution with exclusion of air, and the excess titrated with permanganate. 2NH20H + Ti2(S04)3 = (NH4)2S04 + 4TiOS04 + HzS04. (I) The ferric salt method,2 in which the hydroxylamine is oxidized in an acid solution by excess of a ferric salt, the mixture is boiled and the fer- rous salt formed titrated with permanganate. 2NH20H + 2Fe@04)3 = N2O + 4FeS04 + 2H2S04 + H20. (2) The iodine method,3 in which the hydroxylamine is oxidized by iodine in a neutral solution, e. g., in the presence of disodium phosphate. 2NH20H + 212 = N2O + 4HI + H2O (3) or 2NH20H + 213- = N20 + 61- + 4H+ + HzO. Our first experiments, with the iodine method, yielded irregular results which could not be interpreted until the concentration of the hydroxyl- amine solution was accurately determined. An examination of the literature showed a rather unsatisfactory state of affairs. The advocates of the ferric sulfate method furnish evidence that it is perfectly reliable, but Leuba4 gives detailed experimental data to prove the contrary, and Adams5 states that he could not obtain reproducible results with it. The investigators who have used the iodine method consider it to be fairly satisfactory, but some of them state that it is not very accurate, and Rupp and Maeder6 have recently concluded that correct results are obtained only by a compensation of errors. -
A Fundamental Evaluation of the Atmospheric Pre-Leaching Section of the Nickel-Copper Matte Treatment Process
A FUNDAMENTAL EVALUATION OF THE ATMOSPHERIC PRE-LEACHING SECTION OF THE NICKEL-COPPER MATTE TREATMENT PROCESS by RODRICK MULENGA LAMYA Dissertation presented for the Degree of DOCTOR OF PHILOSOPHY (Extractive Metallurgical Engineering) in the Department of Process Engineering at the University of Stellenbosch, South Africa Promoter Prof. L. Lorenzen STELLENBOSCH March 2007 DECLARATION I the undersigned, hereby declare that the work contained in this dissertation is my own original work and that I have not previously in its entirety or in part submitted it at any university for a degree. Signature: ............................................... Date: ....................................................... Copyright © 2007 Stellenbosch University All rights reserved i SYNOPSIS Nickel-Copper sulphide ores are the most important Platinum Group Metal bearing ores. The South African deposits are exceptionally rich in the platinum group metals (PGMs) and production of the PGMs is the primary purpose of treating these ores. The methods used in the recovery of the PGMs from the nickel-copper ores generally consists of ore concentration by physical techniques, pyrometallurgical concentration and hydrometallurgical extraction of the base metals followed by the PGMs. Pyrometallurgical concentration produces Ni-Cu matte, which is treated by hydrometallurgical processes to recover the nickel, copper, cobalt and the precious metals. In this study, the leaching behaviour of a Ni–Cu matte in CuSO4–H2SO4 solution during the repulping (pre-leach) stage at Impala Platinum Refineries was studied. The repulping stage is basically a non–oxidative atmospheric leach stage, in which nickel, iron and cobalt are partially dissolved, while the copper is precipitated. To understand the nature of the leaching process during this stage of the base metal refining operation, the effects of variations in the key process variables such as temperature, stirring rate, particle size, pulp density, residence time, initial copper and acid concentrations were investigated. -
APPENDIX G Acid Dissociation Constants
harxxxxx_App-G.qxd 3/8/10 1:34 PM Page AP11 APPENDIX G Acid Dissociation Constants § ϭ 0.1 M 0 ؍ (Ionic strength ( † ‡ † Name Structure* pKa Ka pKa ϫ Ϫ5 Acetic acid CH3CO2H 4.756 1.75 10 4.56 (ethanoic acid) N ϩ H3 ϫ Ϫ3 Alanine CHCH3 2.344 (CO2H) 4.53 10 2.33 ϫ Ϫ10 9.868 (NH3) 1.36 10 9.71 CO2H ϩ Ϫ5 Aminobenzene NH3 4.601 2.51 ϫ 10 4.64 (aniline) ϪO SNϩ Ϫ4 4-Aminobenzenesulfonic acid 3 H3 3.232 5.86 ϫ 10 3.01 (sulfanilic acid) ϩ NH3 ϫ Ϫ3 2-Aminobenzoic acid 2.08 (CO2H) 8.3 10 2.01 ϫ Ϫ5 (anthranilic acid) 4.96 (NH3) 1.10 10 4.78 CO2H ϩ 2-Aminoethanethiol HSCH2CH2NH3 —— 8.21 (SH) (2-mercaptoethylamine) —— 10.73 (NH3) ϩ ϫ Ϫ10 2-Aminoethanol HOCH2CH2NH3 9.498 3.18 10 9.52 (ethanolamine) O H ϫ Ϫ5 4.70 (NH3) (20°) 2.0 10 4.74 2-Aminophenol Ϫ 9.97 (OH) (20°) 1.05 ϫ 10 10 9.87 ϩ NH3 ϩ ϫ Ϫ10 Ammonia NH4 9.245 5.69 10 9.26 N ϩ H3 N ϩ H2 ϫ Ϫ2 1.823 (CO2H) 1.50 10 2.03 CHCH CH CH NHC ϫ Ϫ9 Arginine 2 2 2 8.991 (NH3) 1.02 10 9.00 NH —— (NH2) —— (12.1) CO2H 2 O Ϫ 2.24 5.8 ϫ 10 3 2.15 Ϫ Arsenic acid HO As OH 6.96 1.10 ϫ 10 7 6.65 Ϫ (hydrogen arsenate) (11.50) 3.2 ϫ 10 12 (11.18) OH ϫ Ϫ10 Arsenious acid As(OH)3 9.29 5.1 10 9.14 (hydrogen arsenite) N ϩ O H3 Asparagine CHCH2CNH2 —— —— 2.16 (CO2H) —— —— 8.73 (NH3) CO2H *Each acid is written in its protonated form. -
The Synthesis and Characterization of Novel Pentafluorosulfanyl-Containing Heterocycles and Pentafluorosulfanyldifluoromethane
Clemson University TigerPrints All Dissertations Dissertations May 2019 The yS nthesis and Characterization of Novel Pentafluorosulfanyl-Containing Heterocycles and Pentafluorosulfanyldifluoromethane Steven Paul Belina Clemson University, [email protected] Follow this and additional works at: https://tigerprints.clemson.edu/all_dissertations Recommended Citation Belina, Steven Paul, "The yS nthesis and Characterization of Novel Pentafluorosulfanyl-Containing Heterocycles and Pentafluorosulfanyldifluoromethane" (2019). All Dissertations. 2373. https://tigerprints.clemson.edu/all_dissertations/2373 This Dissertation is brought to you for free and open access by the Dissertations at TigerPrints. It has been accepted for inclusion in All Dissertations by an authorized administrator of TigerPrints. For more information, please contact [email protected]. THE SYNTHESIS AND CHARACTERIZATION OF NOVEL PENTAFLUOROSULFANYL-CONTAINING HETEROCYCLES AND PENTAFLUOROSULFANYLDIFLUOROMETHANE A Dissertation Presented to the Graduate School of Clemson University In Partial Fulfillment of the Requirements for the Degree Doctor of Philosophy Chemistry by Steven Paul Belina May 2019 Accepted by Joseph S. Thrasher, Ph.D., Committee Chair Julia L. Brumaghim, Ph.D. R. Karl Dieter, Ph.D. Joseph W. Kolis, Ph.D. Title Page ABSTRACT Beginning in the early 1960s, scientists began to experiment with the pentafluorosulfanyl moiety. The unique properties of the functional group has attracted interest among fluorine chemists and more recently even organic chemists. These properties include high group electronegativity, high steric bulk, high lipophilicity, a highly electron withdrawing nature, and a square pyramidal geometry. However, the development and deployment of the pentafluorosulfanyl functional group has been significantly slowed. The main cause for the slow development is a lack of easily available reagents to synthesize pentafluorosulfanyl-containing compounds. Historically, the primary reagents used for synthesizing pentafluorosulfanyl-containing compounds were SF5Cl and SF5Br. -
Why Nature Chose Selenium Hans J
Reviews pubs.acs.org/acschemicalbiology Why Nature Chose Selenium Hans J. Reich*, ‡ and Robert J. Hondal*,† † University of Vermont, Department of Biochemistry, 89 Beaumont Ave, Given Laboratory, Room B413, Burlington, Vermont 05405, United States ‡ University of WisconsinMadison, Department of Chemistry, 1101 University Avenue, Madison, Wisconsin 53706, United States ABSTRACT: The authors were asked by the Editors of ACS Chemical Biology to write an article titled “Why Nature Chose Selenium” for the occasion of the upcoming bicentennial of the discovery of selenium by the Swedish chemist Jöns Jacob Berzelius in 1817 and styled after the famous work of Frank Westheimer on the biological chemistry of phosphate [Westheimer, F. H. (1987) Why Nature Chose Phosphates, Science 235, 1173−1178]. This work gives a history of the important discoveries of the biological processes that selenium participates in, and a point-by-point comparison of the chemistry of selenium with the atom it replaces in biology, sulfur. This analysis shows that redox chemistry is the largest chemical difference between the two chalcogens. This difference is very large for both one-electron and two-electron redox reactions. Much of this difference is due to the inability of selenium to form π bonds of all types. The outer valence electrons of selenium are also more loosely held than those of sulfur. As a result, selenium is a better nucleophile and will react with reactive oxygen species faster than sulfur, but the resulting lack of π-bond character in the Se−O bond means that the Se-oxide can be much more readily reduced in comparison to S-oxides. -
United States Patent As Fice Patiented Sept
s 2,904,403 United States Patent As fice Patiented Sept. 15, 1959 1 2 are agitated during this period by any suitable means. The vessel is then cooled, opened and iodine penta 2,904,403 fluoride collected and purified by conventional procedures such as distillation. When alkali or alkaline earth metal PREPARATION OF BF iodates are used in the process, the iodine pentafluoride William Channing Smith, Wilmington, Del, assignor to may be isolated in the form of a solid complex compound E. H. du Pont de Nemours and Company, Wilmington, with alkali or alkaline earth metal fluorides. Dei, a corporation of Delaware in a continuous process gaseous sulfur tetrafluoride is No Drawing. Application June 7, 1957 passed through a tube containing the iodine compound, Serial No. 664,162 0 preferably heated to a temperature high enough to vola tilize the iodine pentafluoride as it is formed. The 5 Claims. (C. 23-205) iodine pentafluoride is separated from the gas effluent by cooling in traps and the unreacted sulfur tetrafluoride is recycled through the reaction tube. This invention relates to iodine fluorides and has as 5 The following examples illustrate the process of the its primary object provision of a novel method of prepar invention. ing such fluorides, iodine pentafluoride in particular. Iodine pentafluoride is a versatile and well-known Example 1 fluorinating agent which can be used to prepare fluorine (A) A bomb, lined with stainless steel and of 145 mi. bearing compounds that are not readily accessible by 20 capacity, was charged with 33.4 g. (0.10 mode) of iodine other routes. -
United States Patent Office Patented Mar
3,373,000 United States Patent Office Patented Mar. 2, 1968 2 3,373,000 monofluoride is also an economical reactant, since it is PROCESS FOR PREPARING TETRAFLUORDES conveniently prepared by the disproportionation of ele AND HEXAFLUOR DES mental chlorine in liquid hydrogen fluoride, thereby avoid James J. Pitts, West Haven, and Albert W. Jache, North ing the use of expensive elemental fluorine. The selective Haven, Conn., assignors to Olin Mathieson Chemical fluorination process of this invention is particularly Sur Corporation, a corporation of Virginia prising and unexpected in view of the prior art which No Drawing. Filed Nov. 1, 1966, Ser. No. 591,079 teaches that chlorine monofluoride adds to a wide variety 9 Claims. (Cl. 23-352) of compounds, thereby acting as a chloro-fluorinating agent. For instance, U.S. Patent 3,035,893 discloses the 10 preparation of sulfur chloride pentafluoride from Sulfur ABSTRACT OF THE DISCLOSURE tetrafluoride and chlorine monofluoride. The tetrafluorides and hexafluorides of sulfur, selenium According to the process of this invention, the tetra and tellurium are provided by reacting chlorine mono fluorides and hexafluorides of sulfur, selenium and tel fluoride with sulfur, selenium, tellurium, metal sulfides, lurium are provided by reacting chlorine monofluoride metal selenides or metal tellurides. The hexafluorides of 15 with a material selected from the group consisting of Sul tungsten, molybdenum and uranium are provided by the fur, selenium, tellurium, metal sulfides, metal selenides reaction of chlorine monofluoride with the metals, their and metal tellurides. The hexafluorides of tungsten, oxides, sulfides and salts containing the metallate anion. molybdenum and uranium are provided by reacting These tetrafluorides and hexafluorides are well-known chlorine monofluoride with a material selected from the compounds, useful as fluorinating agents, gaseous di 20 group consisting of tungsten; molybdenum, uranium; the electrics, sources of high purity metallic powders, etc. -
Chemical Names and CAS Numbers Final
Chemical Abstract Chemical Formula Chemical Name Service (CAS) Number C3H8O 1‐propanol C4H7BrO2 2‐bromobutyric acid 80‐58‐0 GeH3COOH 2‐germaacetic acid C4H10 2‐methylpropane 75‐28‐5 C3H8O 2‐propanol 67‐63‐0 C6H10O3 4‐acetylbutyric acid 448671 C4H7BrO2 4‐bromobutyric acid 2623‐87‐2 CH3CHO acetaldehyde CH3CONH2 acetamide C8H9NO2 acetaminophen 103‐90‐2 − C2H3O2 acetate ion − CH3COO acetate ion C2H4O2 acetic acid 64‐19‐7 CH3COOH acetic acid (CH3)2CO acetone CH3COCl acetyl chloride C2H2 acetylene 74‐86‐2 HCCH acetylene C9H8O4 acetylsalicylic acid 50‐78‐2 H2C(CH)CN acrylonitrile C3H7NO2 Ala C3H7NO2 alanine 56‐41‐7 NaAlSi3O3 albite AlSb aluminium antimonide 25152‐52‐7 AlAs aluminium arsenide 22831‐42‐1 AlBO2 aluminium borate 61279‐70‐7 AlBO aluminium boron oxide 12041‐48‐4 AlBr3 aluminium bromide 7727‐15‐3 AlBr3•6H2O aluminium bromide hexahydrate 2149397 AlCl4Cs aluminium caesium tetrachloride 17992‐03‐9 AlCl3 aluminium chloride (anhydrous) 7446‐70‐0 AlCl3•6H2O aluminium chloride hexahydrate 7784‐13‐6 AlClO aluminium chloride oxide 13596‐11‐7 AlB2 aluminium diboride 12041‐50‐8 AlF2 aluminium difluoride 13569‐23‐8 AlF2O aluminium difluoride oxide 38344‐66‐0 AlB12 aluminium dodecaboride 12041‐54‐2 Al2F6 aluminium fluoride 17949‐86‐9 AlF3 aluminium fluoride 7784‐18‐1 Al(CHO2)3 aluminium formate 7360‐53‐4 1 of 75 Chemical Abstract Chemical Formula Chemical Name Service (CAS) Number Al(OH)3 aluminium hydroxide 21645‐51‐2 Al2I6 aluminium iodide 18898‐35‐6 AlI3 aluminium iodide 7784‐23‐8 AlBr aluminium monobromide 22359‐97‐3 AlCl aluminium monochloride -
Risk-Based Closure Guide Draft
Risk-based Closure Guide July 1, 2021 Office of Land Quality Indiana Department of Environmental Management Disclaimer This Nonrule Policy Document (NPD) is being established by the Indiana Department of Environmental Management (IDEM) consistent with its authority under IC 13-14-1-11.5. It is intended solely as guidance and shall be used in conjunction with applicable rules or laws. It does not replace applicable rules or laws, and if it conflicts with these rules or laws, the rules or laws shall control. Pursuant to IC 13-14-1-11.5, this NPD will be available for public inspection for at least forty-five (45) days prior to presentation to the appropriate State Environmental Board, and may be put into effect by IDEM thirty (30) days afterward. If the NPD is presented to more than one board, it will be effective thirty (30) days after presentation to the last State Environmental Board. IDEM also will submit the NPD to the Indiana Register for publication. 2 Table of Contents 1 Introduction ..................................................................................................................................... 7 1.1 Applicability .............................................................................................................................. 8 1.2 Types of Closure ...................................................................................................................... 9 1.3 Process Overview ................................................................................................................... -
AP Environmental Science Air Pollution Formulas
AP Environmental Science Air Pollution Formulas 4FeS2 11 O 2 2 Fe 2 O 3 8 SO 2 Impurities such as pyrite or iron pyrite are found in coal, when we burn coal it interacts with atmospheric oxygen to form iron oxide and sulfur dioxide (a primary air pollutant). 22SO2 O 2 SO 3 The primary air pollutant, sulfur dioxide, is oxidized, once in the atmosphere, to sulfur trioxide. SO3 H 2 O H 2 SO 4 Sulfur trioxide dissolves it atmospheric water droplets to form sulfuric acid. Sulfuric acid is a major component of acid rain. Sulfuric acid is considered a secondary air pollutant SOx The generalized representation of sulfur oxides, whether it be sulfur dioxide or sulfur trioxide. The Sulfur oxides are considered primary air pollutants. N22 O2 NO Molecules of nitrogen and atmospheric oxygen combine AT VERY HIGH TEMPERATURES to form nitric oxide, a colorless gas. The high temperatures of natural processes like lightening or those of the combustion chambers of an engine are effective in causing this conversion. Nitric oxide is a primary air pollutant 22NO O22 NO Once in the atmosphere, nitric acid reacts with additional oxygen to form nitrogen dioxide, a red- brown toxic gas that causes irritation to the eyes and respiratory system NO2 H 2 O HNO 3 Further reaction of nitrogen dioxide with water can produce nitric acid, another component of acid rain Photochemical Smog N22 O Energy 2 NO Nitrogen oxide is an essential ingredient of photochemical smog that is produced during the high temperatures associated with combustion of vehicle’s engines. -
Atmospheric Chemistry Lecture 2
AtmosphericAtmospheric ChemistryChemistry LectureLecture 2:2: TroposphericTropospheric ChemistryChemistry andand AerosolsAerosols Jim Smith Atmospheric Chemistry Division / NCAR [email protected] Outline for Second Lecture Tropospheric Chemistry and Aerosols Primary and secondary pollutants Sulfur chemistry Nitrogen chemistry Acid rain Chemistry of the background troposphere: • CO • Methane • Formaldehyde Urban Air Pollution • Hydrocarbon oxidation • Ozone Isopleth plots • Smog meteorology Tropospheric Chemistry Primary and Secondary Pollutants and their impacts Primary pollutants are those emitted directly from sources • CO: affects oxygen-carrying capacity of blood (but not at urban concentrations) • NO: secondary reactions • NO 2: 5% in urban, much higher for biomass burning • SO 2: respiratory constriction (asthma, bronchitis) • NH 3: aerosol formation • soot: visibility reduction, PAH is carcinogen • isoprene: emitted from plants, leads to ozone and makes a certain President think the ozone problem is caused by trees. • vanillan: yummy smell from Ponderosa Pine Secondary pollutants are those formed in the atmosphere by chemical interactions among primary pollutants and normal atmospheric constituents. • NO 2 (95%): lung damage •H2SO 4: Aerosol formation, visibility reduction and acid rain • PAN: hurts your eyes, damage to plants •O3: damage to plants & plastics, lung damage (only short-term?) Tropospheric Chemistry Sulfur Cycle Image courtesy of Hugh Powell, Univ. of Durham, UK Tropospheric Chemistry Sulfur Cycle SO 2 can -
ABSTRACT RUDD, HAYDEN. Assessing the Vulnerability Of
ABSTRACT RUDD, HAYDEN. Assessing the Vulnerability of Coastal Plain Groundwater to Flood Water Intrusion using High Resolution Mass Spectrometry. (Under the direction of Dr. Elizabeth Guthrie Nichols). Communities in the North Carolina Coastal Plain (NCCP) depend on safe and reliable groundwater for private well use, agriculture, industry, and livelihoods. Although storm intensity and frequency are predicted to increase in coastal areas, the risk of surficial and confined aquifer contamination from extreme storms is not understood. In September 2018, Hurricane Florence caused extensive flooding across the NCCP for several weeks. The North Carolina Department of Environmental Quality (NCDEQ) Groundwater Management Branch had just completed sampling of some wells in their monitoring network when Hurricane Florence made landfall. NCDEQ returned to these wells, particularly those flooded by Hurricane Florence, for post-flood sampling. These groundwater samples were analyzed by NCDEQ for regulated semi-volatile organics with few to any detections of regulated organic contaminants. NCDEQ provided NC State the same sample extracts for analysis by high resolution mass spectrometry (HRMS). This research reports on the non-targeted and suspect-screening HRMS analyses of groundwater from nested monitoring wells. Some monitoring well sites experienced flooding during the study period, and some did not. The goal of this research was to advance our understanding of coastal aquifer susceptibility to flooding by producing the first comprehensive organic chemical profiles of coastal aquifers and by determining if aquifers have distinct organic chemical profiles that change after flooding events. This study used HRMS analyses to produce the first comprehensive organic chemical profiles of 11 aquifers in the coastal plain.