Draft Screening Assessment Hydrogen Sulfide (H2S)
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Inventory Size (Ml Or G) 103220 Dimethyl Sulfate 77-78-1 500 Ml
Inventory Bottle Size Number Name CAS# (mL or g) Room # Location 103220 Dimethyl sulfate 77-78-1 500 ml 3222 A-1 Benzonitrile 100-47-0 100ml 3222 A-1 Tin(IV)chloride 1.0 M in DCM 7676-78-8 100ml 3222 A-1 103713 Acetic Anhydride 108-24-7 500ml 3222 A2 103714 Sulfuric acid, fuming 9014-95-7 500g 3222 A2 103723 Phosphorus tribromide 7789-60-8 100g 3222 A2 103724 Trifluoroacetic acid 76-05-1 100g 3222 A2 101342 Succinyl chloride 543-20-4 3222 A2 100069 Chloroacetyl chloride 79-04-9 100ml 3222 A2 10002 Chloroacetyl chloride 79-04-9 100ml 3222 A2 101134 Acetyl chloride 75-36-5 500g 3222 A2 103721 Ethyl chlorooxoacetate 4755-77-5 100g 3222 A2 100423 Titanium(IV) chloride solution 7550-45-0 100ml 3222 A2 103877 Acetic Anhydride 108-24-7 1L 3222 A3 103874 Polyphosphoric acid 8017-16-1 1kg 3222 A3 103695 Chlorosulfonic acid 7790-94-5 100g 3222 A3 103694 Chlorosulfonic acid 7790-94-5 100g 3222 A3 103880 Methanesulfonic acid 75-75-2 500ml 3222 A3 103883 Oxalyl chloride 79-37-8 100ml 3222 A3 103889 Thiodiglycolic acid 123-93-3 500g 3222 A3 103888 Tetrafluoroboric acid 50% 16872-11-0 1L 3222 A3 103886 Tetrafluoroboric acid 50% 16872-11-0 1L 3222 A3 102969 sulfuric acid 7664-93-9 500 mL 2428 A7 102970 hydrochloric acid (37%) 7647-01-0 500 mL 2428 A7 102971 hydrochloric acid (37%) 7647-01-0 500 mL 2428 A7 102973 formic acid (88%) 64-18-6 500 mL 2428 A7 102974 hydrofloric acid (49%) 7664-39-3 500 mL 2428 A7 103320 Ammonium Hydroxide conc. -
Toxicological Profile for Hydrogen Sulfide and Carbonyl Sulfide
HYDROGEN SULFIDE AND CARBONYL SULFIDE 149 6. POTENTIAL FOR HUMAN EXPOSURE 6.1 OVERVIEW Hydrogen sulfide has been found in at least 34 of the 1,832 waste sites that have been proposed for inclusion on the EPA National Priorities List (NPL) and carbonyl sulfide was detected in at least 4 of the 1,832 waste sites (ATSDR 2015). However, the number of sites evaluated for these substances is not known and hydrogen sulfide and carbonyl sulfide are ubiquitous in the atmosphere. The frequency of these sites can be seen in Figures 6-1 and 6-2. Carbonyl sulfide and hydrogen sulfide are principal components in the natural sulfur cycle. Bacteria, fungi, and actinomycetes (a fungus-like bacteria) release hydrogen sulfide during the decomposition of 2- sulfur containing proteins and by the direct reduction of sulfate (SO4 ). Hydrogen sulfide is also emitted from volcanoes, stagnant or polluted waters, and manure or coal pits with low oxygen content (Aneja 1990; Khalil and Ramussen 1984). The majority of carbonyl sulfide that enters the environment is released to air and it is very abundant in the troposphere (Conrad and Meuser 2000; EPA 1994c, 1994d; Meinrat et al. 1992; Simmons et al. 2012; Stimler et al. 2010). It enters the atmosphere from both natural and anthropogenic sources (EPA 1994c, 1994d; Meinrat et al. 1992; Stimler et al. 2010). Carbonyl sulfide is released from wetlands, salt marshes, soil, oceans, deciduous and coniferous trees, and volcanic gases (Blake et al. 2004; EPA 1994c, 1994d; Meinrat et al. 1992; Rasmussen et al. 1982a, 1982b; Stimler et al. -
Sodium Borohydride (Nabh4) Itself Is a Relatively Mild Reducing Agent
1770 Vol. 35 (1987) Chem. Pharm. Bull. _35( 5 )1770-1776(1987). Reactions of Sodium Borohydride. IV.1) Reduction of Aromatic Sulfonyl Chlorides with Sodium Borohydride ATSUKO NOSE and TADAHIRO KUDO* Daiichi College of Pharmaceutical Sciences, 22-1 Tamagawa-cho, Minami-ku, Fukuoka 815, Japan (Received September 12, 1986) Aromatic sulfonyl chlorides were reduced with sodium borohydride in tetrahydrofuran at 0•Ž to the corresponding sulfinic acids in good yields. Further reduction proceeded when the reaction was carried out under reflux in tetrahydrofuran to give disulfide and thiophenol derivatives via sulfinic acid. Furthermore, sulfonamides were reduced with sodium borohydride by heating directly to give sulfide, disulfide and thiophenol derivatives, and diphenyl sulfone was reduced under similar conditions to give thiophenol and biphenyl. Keywords reduction; sodium borohydride; aromatic sulfonyl chloride; sulfonamide; sulfone; aromatic sulfinic acid; disulfide; sulfide; thiophenol Sodium borohydride (NaBH4) itself is a relatively mild reducing agent which is extensively used for the selective reduction of the carbonyl group of ketone, aldehyde and (carboxylic) acid halide derivatives. In the previous papers, we reported that NaBI-14 can reduce some functional groups, such as carboxylic anhydrides,2) carboxylic acids3) and nitro compounds.1) As a continuation of these studies, in the present paper, we wish to report the reduction of aromatic sulfonyl chlorides, sulfinic acids and sulfonamides with NaBH4. Many methods have been reported for the reduction of sulfonyl chlorides to sulfinic acids, such as the use of sodium sulfite,4a-d) zinc,5) electrolytic reduction,6) catalytic reduction,7) magnesium,8) sodium amalgam,9) sodium hydrogen sulfite,10) stannous chlo- TABLE I. -
March 12Th CONTENT
Issue 05, February 27th – March 12th CONTENT Introduction During the first two weeks of March we saw important alliances 1between car manufacturers for the development and supply of Batteries electric vehicles. Daimler AG will cooperate with BYD in China and Vehicles and Mitsubishi Motors will work with PSA Peugeot – Citroen in Europe. These announcements represent an important step BYD and Daimler will develop an for electrifying transportation; however going forward requires Electric Vehicle for the Chinese market many issues that still need to be solved. As a society we have Celgard announced expansion of assumed that it is “possible” to replace (in some way) oil for production capacity in Korea electricity, but the question is if we have figured out where and Misubishi Motors and PSA Peugeot how we could obtain this electricity. Once this issue is solved (at Citroen reached final agreement a “reasonable” price and in an environmental friendly way), Sanyo will supply a lithium ion battery the next step is the efficient distribution of this electricity. We system for traffic signals in Japan have seen some companies that are developing interesting business models, but we are far from a mass implementation. LG Chemical will build Volt battery Summarizing, the question that arises is: are we (as a society) plant in Michigan prepared for electrifying transportation? Regarding lithium, a key raw material for batteries used in electric vehicles, it is important to highlight that most of the projects that have been announced in the last years are in an early stage of development. Anyway, the trend is clear: in less than three years around 20 new Companies have announced more than 40 new lithium projects. -
Sodium Hydrosulfide
SAFETY DATA SHEET 1. Identification Product identifier Sodium Hydrosulfide Solution Other means of identification Product number GENLP-TDC-001-CAN Recommended use Product is a unique alkaline material, playing a vital role in many industrial processes. Recommended restrictions Use in accordance with supplier's recommendations. Manufacturer/Importer/Supplier/Distributor information Importer TDC Energy Canada, LTD. Address 1916 Farmerville Hwy Ruston, LA 71270 Telephone Customer Service (800) 422-6274 Email [email protected] CHEMTREC: 800-424-9300 (Domestic – North America) CHEMTREC: +1-703-527-3887 (International) 2. Hazard identification Physical hazards Corrosive to metals Category 1 Health hazards Acute toxicity, oral Category 3 Skin corrosion/irritation Category 1B Serious eye damage/eye irritation Category 1 Environmental hazards Hazardous to the aquatic environment, acute Category 1 hazard Label elements Signal word Danger Hazard statement May be corrosive to metals. Toxic if swallowed. Causes severe skin burns and eye damage. Very toxic to aquatic life. Precautionary statement Prevention Keep only in original container. Do not breathe mist or vapour. Wash thoroughly after handling. Do not eat, drink or smoke when using this product. Avoid release to the environment. Wear protective gloves/protective clothing/eye protection/face protection. Response If swallowed: Immediately call a poison centre/doctor. Rinse mouth. Do NOT induce vomiting. If on skin (or hair): Take off immediately all contaminated clothing. Rinse skin with water/shower. Wash contaminated clothing before reuse. If inhaled: Remove person to fresh air and keep comfortable for breathing. If in eyes: Rinse cautiously with water for several minutes. Remove contact lenses, if present and easy to do. -
Nahs Technical Guide
TECHNICAL GUIDE FOR SOLUTIONS OF SODIUM HYDROSULFIDE TECHNICAL GUIDE FOR SOLUTIONS OF SODIUM HYDROSULFIDE TABLE OF CONTENTS TOPIC PAGE Overview 1 Health Hazards and First Aid 2 Flammability and Fire Response / Storage 3 Handling (PPE) 4 Equipment Transfers/Recommendations 5 Shipping 13 Releases 14 APPENDIX This Page Intentionally left Blank Appendix A H2S Monitors Appendix B Hydrogen Sulfide Toxicity Chart Appendix C Density, Boiling and Freezing Points of Appendix D Sodium Hydrosulfide Viscosity of Typical 45% Sodium Appendix E Hydrosulfide Solution Sodium Hydrosulfide Site Assessment Appendix F Checklist TECHNICAL GUIDE FOR SOLUTIONS OF SODIUM HYDROSULFIDE Overview Sodium Hydrosulfide, chemical formula NaHS, is a highly alkaline salt solution with a pH of 11.5 to 12.5. The solution is typically yellow to dark green and has a rotten-egg odor due to the Hydrogen Sulfide (H2S) content. The product strength ranges from 20% to 45% by weight and weighs 9 to 11 pounds per gallon (specific gravity from 1.13 to 1.30 g/cm3). Solutions of NaHS are considered stable in normal transportation. The vapor space over NaHS solutions contains highly toxic Hydrogen Sulfide gas. The Hydrogen Sulfide gas is colorless and it is heavier than air. It will remain close to the ground and collect in low lying areas. The amount of Hydrogen Sulfide gas evolved from NaHS solutions is noticeably increased when the pH of the solution is below the pH of 10.2. This happens when the solution comes into contact with acidic materials or other materials that have a pH lower than 10.2. Dilution of the material will also create a minimal amount of Hydrogen Sulfide gas due to the lower pH of water coming in contact with the solution. -
Risto Laitinen/August 4, 2016 International Union of Pure and Applied Chemistry Division VIII Chemical Nomenclature and Structur
Approved Minutes, Busan 2015 Risto Laitinen/August 4, 2016 International Union of Pure and Applied Chemistry Division VIII Chemical Nomenclature and Structure Representation Approved Minutes of Division Committee Meeting in Busan, Korea, 8–9 August, 2015 1. Welcome, introductory remarks and housekeeping announcements Karl-Heinz Hellwich (KHH) welcomed everybody to the meeting, extending a special welcome to those who were attending the Division Committee meeting for the first time. He described house rules and arrangements during the meeting. KHH also regretfully reported that it has come to his attention that since the Bangor meeting in August 2014, Prof. Derek Horton (Member, Division VIII task groups on Carbohydrate and Flavonoids nomenclature; Associate Member, IUBMB-IUPAC Joint Commission on Biochemical Nomenclature) and Dr. Libuse Goebels, Member of the former Commission on Nomenclature of Organic Chemistry) have passed away. The meeting attendees paid a tribute to their memory by a moment of silence. 2. Attendance and apologies Present: Karl-Heinz Hellwich (president, KHH) , Risto Laitinen (acting secretary, RSL), Richard Hartshorn (past-president, RMH), Michael Beckett (MAB), Alan Hutton (ATH), Gerry P. Moss (GPM), Michelle Rogers (MMR), Jiří Vohlídal (JV), Andrey Yerin (AY) Observers: Leah McEwen (part time, chair of proposed project, LME), Elisabeth Mansfield (task group chair, EM), Johan Scheers (young observer, day 1; JS), Prof. Kazuyuki Tatsumi (past- president of the union, part of day 2) Apologies: Ture Damhus (secretary, TD), Vefa Ahsen, Kirill Degtyarenko, Gernot Eller, Mohammed Abul Hashem, Phil Hodge (PH), Todd Lowary, József Nagy, Ebbe Nordlander (EN), Amélia Pilar Rauter (APR), Hinnerk Rey (HR), John Todd, Lidija Varga-Defterdarović. -
Anaerobic Degradation of Methanethiol in a Process for Liquefied Petroleum Gas (LPG) Biodesulfurization
Anaerobic degradation of methanethiol in a process for Liquefied Petroleum Gas (LPG) biodesulfurization Promotoren Prof. dr. ir. A.J.H. Janssen Hoogleraar in de Biologische Gas- en waterreiniging Prof. dr. ir. A.J.M. Stams Persoonlijk hoogleraar bij het laboratorium voor Microbiologie Copromotor Prof. dr. ir. P.N.L. Lens Hoogleraar in de Milieubiotechnologie UNESCO-IHE, Delft Samenstelling promotiecommissie Prof. dr. ir. R.H. Wijffels Wageningen Universiteit, Nederland Dr. ir. G. Muyzer TU Delft, Nederland Dr. H.J.M. op den Camp Radboud Universiteit, Nijmegen, Nederland Prof. dr. ir. H. van Langenhove Universiteit Gent, België Dit onderzoek is uitgevoerd binnen de onderzoeksschool SENSE (Socio-Economic and Natural Sciences of the Environment) Anaerobic degradation of methanethiol in a process for Liquefied Petroleum Gas (LPG) biodesulfurization R.C. van Leerdam Proefschrift ter verkrijging van de graad van doctor op gezag van de rector magnificus van Wageningen Universiteit Prof. dr. M.J. Kropff in het openbaar te verdedigen op maandag 19 november 2007 des namiddags te vier uur in de Aula Van Leerdam, R.C., 2007. Anaerobic degradation of methanethiol in a process for Liquefied Petroleum Gas (LPG) biodesulfurization. PhD-thesis Wageningen University, Wageningen, The Netherlands – with references – with summaries in English and Dutch ISBN: 978-90-8504-787-2 Abstract Due to increasingly stringent environmental legislation car fuels have to be desulfurized to levels below 10 ppm in order to minimize negative effects on the environment as sulfur-containing emissions contribute to acid deposition (‘acid rain’) and to reduce the amount of particulates formed during the burning of the fuel. Moreover, low sulfur specifications are also needed to lengthen the lifetime of car exhaust catalysts. -
Removal of Hydrogen Sulfide from Landfill Gas Using a Solar Regenerable Adsorbent
Removal of Hydrogen Sulfide from Landfill Gas Using a Solar Regenerable Adsorbent by Sreevani Kalapala Submitted in Partial Fulfillment of the Requirements for the Degree of Master of Science in the Chemistry Program YOUNGSTOWN STATE UNIVERSITY May, 2014 Removal of Hydrogen Sulfide from Landfill Gas Using A Solar Regenerable Adsorbent Sreevani Kalapala I hereby release this thesis to the public. I understand that this thesis will be made available from the OhioLINK ETD Center and the Maag Library Circulation Desk for public access. I also authorize the University or other individuals to make copies of this thesis as needed for scholarly research. Signature: Sreevani Kalapala, Student Date Approvals: Dr. Clovis A. Linkous, Thesis Advisor Date Dr. Daryl Mincey, Committee Member Date Dr. Sherri Lovelace-Cameron, Committee Member Date Dr. Salvatore A. Sanders, Associate Dean of Graduate Studies Date ABSTRACT: Landfill gas is a complex mix of gases, containing methane, carbon dioxide, nitrogen and hydrogen sulfide (H2S), created by the action of microorganisms within the landfill. The gas can be collected and flared off or used to produce electricity. However, the H2S content, which may vary from 10’s to 1000’s of ppm, can cause irreversible damage to equipment, and when combusted creates SO2, a precursor of acid rain. It is also a toxic eye and lung irritant, so that prolonged exposure must be kept below a few ppm. Therefore, H2S must be removed before landfill gas can be utilized. Our approach is to scrub H2S into aqueous media and then use an adsorbent to sequester it. The adsorbent is then regenerated in a photocatalytic reaction potentially using sunlight. -
1 Abietic Acid R Abrasive Silica for Polishing DR Acenaphthene M (LC
1 abietic acid R abrasive silica for polishing DR acenaphthene M (LC) acenaphthene quinone R acenaphthylene R acetal (see 1,1-diethoxyethane) acetaldehyde M (FC) acetaldehyde-d (CH3CDO) R acetaldehyde dimethyl acetal CH acetaldoxime R acetamide M (LC) acetamidinium chloride R acetamidoacrylic acid 2- NB acetamidobenzaldehyde p- R acetamidobenzenesulfonyl chloride 4- R acetamidodeoxythioglucopyranose triacetate 2- -2- -1- -β-D- 3,4,6- AB acetamidomethylthiazole 2- -4- PB acetanilide M (LC) acetazolamide R acetdimethylamide see dimethylacetamide, N,N- acethydrazide R acetic acid M (solv) acetic anhydride M (FC) acetmethylamide see methylacetamide, N- acetoacetamide R acetoacetanilide R acetoacetic acid, lithium salt R acetobromoglucose -α-D- NB acetohydroxamic acid R acetoin R acetol (hydroxyacetone) R acetonaphthalide (α)R acetone M (solv) acetone ,A.R. M (solv) acetone-d6 RM acetone cyanohydrin R acetonedicarboxylic acid ,dimethyl ester R acetonedicarboxylic acid -1,3- R acetone dimethyl acetal see dimethoxypropane 2,2- acetonitrile M (solv) acetonitrile-d3 RM acetonylacetone see hexanedione 2,5- acetonylbenzylhydroxycoumarin (3-(α- -4- R acetophenone M (LC) acetophenone oxime R acetophenone trimethylsilyl enol ether see phenyltrimethylsilyl... acetoxyacetone (oxopropyl acetate 2-) R acetoxybenzoic acid 4- DS acetoxynaphthoic acid 6- -2- R 2 acetylacetaldehyde dimethylacetal R acetylacetone (pentanedione -2,4-) M (C) acetylbenzonitrile p- R acetylbiphenyl 4- see phenylacetophenone, p- acetyl bromide M (FC) acetylbromothiophene 2- -5- -
Tourmaline Reference Materials for the in Situ Analysis of Oxygen and Lithium Isotope Ratio Compositions
Vol. 45 — N° 1 03 P.97 – 119 21 Tourmaline Reference Materials for the In Situ Analysis of Oxygen and Lithium Isotope Ratio Compositions Michael Wiedenbeck (1)*, Robert B. Trumbull (1), Martin Rosner (2),AdrianBoyce (3), John H. Fournelle (4),IanA.Franchi (5),RalfHalama (6),ChrisHarris (7),JackH.Lacey (8), Horst Marschall (9) , Anette Meixner (10),AndreasPack (11), Philip A.E. Pogge von Strandmann (9), Michael J. Spicuzza (4),JohnW.Valley (4) and Franziska D.H. Wilke (1) (1) GFZ German Research Centre for Geosciences, Potsdam 14473, Germany (2) Department of Marine Chemistry and Geochemistry, Woods Hole Oceanographic Institution, Woods Hole, MA, 02543, USA (3) Scottish Universities Environmental Research Centre, East Kilbride G75 0QF, UK (4) Department of Geoscience, University of Wisconsin, Madison, WI, 53706, USA (5) School of Physical Sciences, Open University, Milton Keynes MK7 6AA, UK (6) Department of Geology, University of Maryland, College Park, MD, 20742, USA (7) Department of Geological Sciences, University of Cape Town, Rondebosch 7701, South Africa (8) National Environmental Isotope Facility, British Geological Survey, Keyworth NG12 5GG, UK (9) Bristol Isotope Group, School of Earth Sciences, University of Bristol, Bristol BS8 1RJ, UK (10) Faculty of Geosciences & MARUM – Center for Marine Environmental Sciences, University of Bremen, Bremen 28359, Germany (11) Geowissenschaftliches Zentrum, Universitat¨ Gottingen,¨ Gottingen¨ 37077, Germany (12) Present address: IsoAnalysis UG, Berlin 12489, Germany (13) Present address: School of Geography, Geology and Environment, Keele University, Keele ST5 5BG, UK (14) Present address: Institut fur¨ Geowissenschaften, Goethe-Universitat,¨ Frankfurt am Main 60438, Germany (15) Present address: Institute of Earth and Planetary Sciences, University College London and Birkbeck, University of London, London WC1E 6BS, UK * Corresponding author. -
Method 9215: Potentiometric Determination of Sulfide in Aqueous Samples and Distillates with Ion-Selective Electrode, Part of Te
METHOD 9215 POTENTIOMETRIC DETERMINATION OF SULFIDE IN AQUEOUS SAMPLES AND DISTILLATES WITH ION-SELECTIVE ELECTRODE 1.0 SCOPE AND APPLICATION 1.1 This method can be used for measuring total sulfide in a distilled sample. The method is meant to be used as an alternate determinative step following the distillation in either SW- 846 Methods 9030 or 9031. 1.2 This method must not be used for undistilled samples because of possible mercury and silver ion interferences. Also, the ISE only responds to free sulfide dianion and will not detect sulfide in complexes. Therefore, this method would provide low recoveries for undistilled samples. 1.3 The method detection limit is 1.0 mg/L. Sulfide concentrations from 0.1 to 12,000 mg/L may be measured. However, when a linear calibration is used, results less than 1 mg/L may be biased up to approximately 90 percent low. 2.0 SUMMARY OF METHOD 2.1 The distillations in Methods 9030 and/or 9031 are performed, except that the scrubber solution is sulfide anti-oxidant buffer (SAOB), with ascorbic and salicylic acids added as oxygen scavengers. The distillates are then analyzed potentiometrically using a sulfide ion-selective electrode (ISE) in conjunction with a double-junction reference electrode and a pH meter with an expanded millivolt scale or an ISE meter capable of being calibrated directly in terms of sulfide concentration. 2.2 This method is an alternative to the iodometric titration procedure, where a solution of thiosulfate is standardized against the thiosulfate solution, and the sulfide standard is standardized against the iodine solution/thiosulfate solution (which requires daily calibration itself).