Peracetic Acid Processing
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Allyson M. Buytendyk
DISCOVERING THE ELECTRONIC PROPERTIES OF METAL HYDRIDES, METAL OXIDES AND ORGANIC MOLECULES USING ANION PHOTOELECTRON SPECTROSCOPY by Allyson M. Buytendyk A dissertation submitted to Johns Hopkins University in conformity with the requirements for the degree of Doctor of Philosophy Baltimore, Maryland September, 2015 © 2015 Allyson M. Buytendyk All Rights Reserved ABSTRACT Negatively charged molecular ions were studied in the gas phase using anion photoelectron spectroscopy. By coupling theory with the experimentally measured electronic structure, the geometries of the neutral and anion complexes could be predicted. The experiments were conducted using a one-of-a-kind time- of-flight mass spectrometer coupled with a pulsed negative ion photoelectron spectrometer. The molecules studied include metal oxides, metal hydrides, aromatic heterocylic organic compounds, and proton-coupled organic acids. Metal oxides serve as catalysts in reactions from many scientific fields and understanding the catalysis process at the molecular level could help improve reaction efficiencies - - (Chapter 1). The experimental investigation of the super-alkali anions, Li3O and Na3O , revealed both photodetachment and photoionization occur due to the low ionization potential of both neutral molecules. Additionally, HfO- and ZrO- were studied, and although both Hf and Zr have very similar atomic properties, their oxides differ greatly where ZrO- has a much lower electron affinity than HfO-. In the pursuit of using hydrogen as an environmentally friendly fuel alternative, a practical method for storing hydrogen is necessary and metal hydrides are thought to be the answer (Chapter 2). Studies yielding structural and electronic information about the hydrogen - - bonding/interacting in the complex, such as in MgH and AlH4 , are vital to constructing a practical hydrogen storage device. -
Selective Conversion of Acetone to Isobutene and Acetic Acid On
Journal of Catalysis 360 (2018) 66–80 Contents lists available at ScienceDirect Journal of Catalysis journal homepage: www.elsevier.com/locate/jcat Selective conversion of acetone to isobutene and acetic acid on aluminosilicates: Kinetic coupling between acid-catalyzed and radical- mediated pathways ⇑ Stanley Herrmann, Enrique Iglesia Department of Chemical and Biomolecular Engineering, University of California, Berkeley, United States article info abstract Article history: Solid Brønsted acids catalyze aldol condensations that form CAC bonds and remove O-atoms from oxy- Received 1 December 2017 genate reactants, but sequential b-scission reactions also cleave CAC bonds, leading to isobutene and Revised 25 January 2018 acetic acid products for acetone reactants. The elementary steps and site requirements that cause these Accepted 29 January 2018 selectivities to depend sensitively on Al content and framework type in aluminosilicate solid acids remain speculative. Acetone reactions on microporous and mesoporous aluminosilicates (FER, TON, MFI, BEA, MCM-41) showed highest b-scission selectivities on MFI and BEA; they increased as the Al content and Keywords: the intracrystalline density of active protons decreased. The effects of acetone and H O pressure on turn- Solid Brønsted acids 2 over rates and selectivities indicate that an equilibrated pool of reactive C ketols and alkenones are pre- Aldol condensation 6 b-Scission in oxygenates sent at pseudo-steady-state concentrations during catalysis and that they act as intermediates in b- Radical chain cycles scission routes. Two distinct C6 b-scission pathways contribute to the formation of isobutene and acetic Confinement effects acid: (i) a minor H2O-mediated route involving b-scission of C6 ketols on protons and (ii) the predominant anhydrous path, in which H-transfer forms unsaturated C6 enols at protons and these enols propagate radical chains mediated by transition states stabilized by van der Waals contacts within vicinal microp- orous voids. -
Method 323—Measurement of Formaldehyde Emissions from Natural Gas-Fired Stationary Sources—Acetyl Acetone Derivitization Method
While we have taken steps to ensure the accuracy of this Internet version of the document, it is not the official version. Please refer to the official version in the FR publication, which appears on the Government Printing Office's FDSys website (http://www.gpo.gov/fdsys/browse/collectionCfr.action?). Method 323—Measurement of Formaldehyde Emissions From Natural Gas-Fired Stationary Sources—Acetyl Acetone Derivitization Method 1.0 Introduction. This method describes the sampling and analysis procedures of the acetyl acetone colorimetric method for measuring formaldehyde emissions in the exhaust of natural gas-fired, stationary combustion sources. This method, which was prepared by the Gas Research Institute (GRI), is based on the Chilled Impinger Train Method for Methanol, Acetone, Acetaldehyde, Methyl Ethyl Ketone, and Formaldehyde (Technical Bulletin No. 684) developed and published by the National Council of the Paper Industry for Air and Stream Improvement, Inc. (NCASI). However, this method has been prepared specifically for formaldehyde and does not include specifications (e.g., equipment and supplies) and procedures (e.g., sampling and analytical) for methanol, acetone, acetaldehyde, and methyl ethyl ketone. To obtain reliable results, persons using this method should have a thorough knowledge of at least Methods 1 and 2 of 40 CFR part 60, appendix A–1; Method 3 of 40 CFR part 60, appendix A–2; and Method 4 of 40 CFR part 60, appendix A–3. 1.1 Scope and Application 1.1.1 Analytes. The only analyte measured by this method is formaldehyde (CAS Number 50–00–0). 1.1.2 Applicability. This method is for analyzing formaldehyde emissions from uncontrolled and controlled natural gas-fired, stationary combustion sources. -
UNIVERSITY of CALIFORNIA Los Angeles Co-Production of Acetic
UNIVERSITY OF CALIFORNIA Los Angeles Co-production of Acetic Acid and Hydrogen/Power from Natural Gas with Zero Carbon Dioxide Emissions A thesis submitted in partial satisfaction of the requirements for the degree Master of Science in Chemical Engineering by Ibubeleye Somiari 2017 © Copyright by Ibubeleye Somiari 2017 ABSTRACT OF THE THESIS Co-production of Acetic Acid and Hydrogen/Power from Natural Gas with Zero Carbon Dioxide Emissions by Ibubeleye Somiari Master of Science in Chemical Engineering University of California, Los Angeles, 2017 Professor Vasilios Manousiouthakis, Chair In this work, a process plant flow sheet that co-produces acetic acid and hydrogen/power from natural gas with zero carbon dioxide emissions is developed. Two cases are explored: the production of acetic acid and hydrogen (case 1) and the production of acetic acid and power (case 2). This is realized by the selection of an appropriate reaction cluster whose sum results in the overall reaction that co-produces acetic acid and hydrogen/power. The concept of energetic self- sufficiency is introduced and it imposes constraints on the system defined in terms of the ratio of oxygen feed to acetic acid produced. Heat and power integration of the converged flowsheet reveals an operating range for each case that guarantees energetic self-sufficiency. Operating points are chosen to conduct a preliminary economic analysis and a carbon dioxide cost and performance metric calculation to quantify profitability and carbon capture potential of the overall process. ii The thesis of Ibubeleye Somiari is approved. Yvonne Chen Tatiana Segura Vasilios Manousiouthakis, Committee Chair University of California, Los Angeles 2017 iii TABLE OF CONTENTS 1. -
The Decomposition Kinetics of Peracetic Acid and Hydrogen Peroxide in Municipal Wastewaters
Disinfection Forum No 10, October 2015 The Decomposition Kinetics of Peracetic Acid and Hydrogen Peroxide in Municipal Wastewaters INTRODUCTION Efficient control of microbial populations in municipal wastewater using peracetic acid (PAA) requires an understanding of the PAA decomposition kinetics. This knowledge is critical to ensure the proper dosing of PAA needed to achieve an adequate concentration within the contact time of the disinfection chamber. In addition, the impact of PAA on the environment, post-discharge into the receiving water body, also is dependent upon the longevity of the PAA in the environment, before decomposing to acetic acid, oxygen and water. As a result, the decomposition kinetics of PAA may have a significant impact on aquatic and environmental toxicity. PAA is not manufactured as a pure compound. The solution exists as an equilibrium mixture of PAA, hydrogen peroxide, acetic acid, and water: ↔ + + Acetic Acid Hydrogen Peroxide Peracetic Acid Water PeroxyChem’s VigorOx® WWT II Wastewater Disinfection Technology contains 15% peracetic acid by weight and 23% hydrogen peroxide as delivered. Although hydrogen peroxide is present in the formulation, peracetic acid is considered to be the active component for disinfection1 in wastewater. There have been several published studies investigating the decomposition kinetics of PAA in different water matrices, including municipal wastewater2-7. Yuan7 states that PAA may be consumed in the following three competitive reactions: 1. Spontaneous decomposition 2 CH3CO3H à 2 CH3CO2H + O2 Eq (1) 2. Hydrolysis CH3CO3H + H2O à CH3CO2H + H2O2 Eq (2) 3. Transition metal catalyzed decomposition + CH3CO3H + M à CH3CO2H + O2 + other products Eq (3) At neutral pH’s, both peracetic acid and hydrogen peroxide can be rapidly consumed by these reactions7 (hydrogen peroxide will decompose to water and oxygen via 2H2O2 à 2H2O + O2). -
Peracetic Acid
Regulation (EU) No 528/2012 concerning the making available on the market and use of biocidal products Evaluation of active substances Assessment Report Peracetic acid Product-types 11 and 12 (Preservatives for liquid cooling and processing systems) (Slimicides) August 2016 Finland Peracetic acid Product-types 11 and 12 August 2016 CONTENTS 1. STATEMENT OF SUBJECT MATTER AND PURPOSE ........................................................ 2 1.1. Procedure followed ............................................................................................. 2 1.2. Purpose of the assessment report ....................................................................... 2 2. OVERALL SUMMARY AND CONCLUSIONS ..................................................................... 4 2.1. Presentation of the Active Substance .................................................................. 4 2.1.1. Identity, Physico-Chemical Properties & Methods of Analysis ................. 4 2.1.2. Intended Uses and Efficacy ..................................................................... 7 2.1.3. Classification and Labelling ..................................................................... 8 2.2. Summary of the Risk Assessment ....................................................................... 9 2.2.1. Human Health Risk Assessment .............................................................. 9 2.2.1.1. Hazard identification ................................................................................... 9 2.2.1.2. Effects assessment ................................................................................... -
Particularly Hazardous Substances
Particularly Hazardous Substances In its Laboratory Standard, OSHA requires the establishment of additional protections for persons working with "Particularly Hazardous Substances" (PHS). OSHA defines these materials as "select" carcinogens, reproductive toxins and acutely toxic materials. Should you wish to add: explosive, violently reactive, pyrophoric and water-reactve materials to this category, the information is included. Carbon nanotubes have also been added due to their suspected carcinogenic properties. This table is designed to assist the laboratory in the identification of PHS, although it is not definitively conclusive or entirely comprehensive. *Notes on the proper use of this table appear on page 12. 1 6 5 2 3 4 Substance CAS National Toxicity National Program Carcinogen Toxin Acute Regulated OSHA Carcinogen Group IARC Carcinogen Toxin Reproductive Violently Reactive/ Explosive/Peroxide Forming/Pyrophoric A-a-C(2-Amino-9H-pyrido[2,3,b]indole) 2648-68-5 2B Acetal 105-57-7 yes Acetaldehyde 75-07-0 NTP AT 2B Acrolein (2-Propenal) 107-02-8 AT Acetamide 126850-14-4 2B 2-Acetylaminofluorene 53-96-3 NTP ORC Acrylamide 79-06-6 NTP 2B Acrylyl Chloride 814-68-6 AT Acrylonitrile 107-13-1 NTP ORC 2B Adriamycin 23214-92-8 NTP 2A Aflatoxins 1402-68-2 NTP 1 Allylamine 107-11-9 AT Alkylaluminums varies AT Allyl Chloride 107-05-1 AT ortho-Aminoazotoluene 97-56-3 NTP 2B para-aminoazobenzene 60-09-3 2B 4-Aminobiphenyl 92-67-1 NTP ORC 1 1-Amino-2-Methylanthraquinone 82-28-0 NTP (2-Amino-6-methyldipyrido[1,2-a:3’,2’-d]imidazole) 67730-11-4 2B -
Measurement of Formic and Acetic Acid in Air by Chemical Ionization Mass Spectroscopy: Airborne Method Development
University of Rhode Island DigitalCommons@URI Open Access Master's Theses 2015 Measurement of Formic and Acetic Acid in Air by Chemical Ionization Mass Spectroscopy: Airborne Method Development Victoria Treadaway University of Rhode Island, [email protected] Follow this and additional works at: https://digitalcommons.uri.edu/theses Recommended Citation Treadaway, Victoria, "Measurement of Formic and Acetic Acid in Air by Chemical Ionization Mass Spectroscopy: Airborne Method Development" (2015). Open Access Master's Theses. Paper 603. https://digitalcommons.uri.edu/theses/603 This Thesis is brought to you for free and open access by DigitalCommons@URI. It has been accepted for inclusion in Open Access Master's Theses by an authorized administrator of DigitalCommons@URI. For more information, please contact [email protected]. MEASUREMENT OF FORMIC AND ACETIC ACID IN AIR BY CHEMICAL IONIZATION MASS SPECTROSCOPY: AIRBORNE METHOD DEVELOPMENT BY VICTORIA TREADAWAY A THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF MASTER OF SCIENCE IN OCEANOGRAPHY UNIVERSITY OF RHODE ISLAND 2015 MASTER OF SCIENCE THESIS OF VICTORIA TREADAWAY APPROVED: Thesis Committee: Major Professor Brian Heikes John Merrill James Smith Nasser H. Zawia DEAN OF THE GRADUATE SCHOOL UNIVERSITY OF RHODE ISLAND 2015 ABSTRACT The goals of this study were to determine whether formic and acetic acid could be quantified from the Deep Convective Clouds and Chemistry Experiment (DC3) through post-mission calibration and analysis and to optimize a reagent gas mix with CH3I, CO2, and O2 that allows quantitative cluster ion formation with hydroperoxides and organic acids suitable for use in future field measurements. -
Peracetic Acid Bleaching CH CO H
Peracetic Acid Bleaching CH3CO3H Introduction of Bleaching Bleaching is a chemical decoloration and delignification process carried out on various types of pulp. DliDelignifi cati on Removal of the chromophores At in dus tr ia l scal e, bl eachi ng i s perf ormed b y chl ori ne, chl ori ne dioxide, oxygen, hydrogen peroxide, ozone and peracetic acid. Effic iency: ClO2 = Cl2 = O3 >CH3COOOH > H2O2 >O> O2 Often bleaching chemicals are wasted in secondary reactions. D. Lachenal and C. Chirat, Cellulose Chem. Technol., 39, 5-6, 511-156 (2005) 2 Electron Exchange Theory Ring opening of the aromatic units necessitates the exchange of 4 e - # of e- can be exchanged per bleaching molecule - + O3 + 6 e + 6 H → 3 H2O - + - CCOlO2 + 55e e + 4 H → Cl + 2 H2O2 - + O2 + 4 e + 4 H → 2 H2O - + H2O2 + 2 e + 2 H → 2 H2O - + CH3COOOH + 2 e + 2 H → CH3COOH + H2O # of e- exchanged per molecule decreases in the following order: O3 > ClO2 > O2 > H2O2 = CH3COOOH D. Lachenal and C. Chirat, Cellulose Chem. Technol., 39, 5-6, 511-156 (2005) 3 Actual Electron Exchange - ClO2 and O3 100 g un bleac he d SW k raf t pul p, k appa # f rom 30 to ~ 4 -5 - 2.3% ClO2 (0.034 mole) on pulp: 0.034 x 5 = 0.17 e is exchanged - 14%1.4% O3 (0.03 mole)on pulp: 0 .03 x 6 = 018e0.18 e is exchanged Chemicals % consumed1 Kappa number * ClO2 2.3 4.5 O3 1.5 3.5 O3 1.4 5.0 O3 1.3 6.5 1Chemicals consumed are shown as % on pulp. -
List of Extremely Hazardous Substances
Emergency Planning and Community Right-to-Know Facility Reporting Compliance Manual List of Extremely Hazardous Substances Threshold Threshold Quantity (TQ) Reportable Planning (pounds) Quantity Quantity (Industry Use (pounds) (pounds) CAS # Chemical Name Only) (Spill/Release) (LEPC Use Only) 75-86-5 Acetone Cyanohydrin 500 10 1,000 1752-30-3 Acetone Thiosemicarbazide 500/500 1,000 1,000/10,000 107-02-8 Acrolein 500 1 500 79-06-1 Acrylamide 500/500 5,000 1,000/10,000 107-13-1 Acrylonitrile 500 100 10,000 814-68-6 Acrylyl Chloride 100 100 100 111-69-3 Adiponitrile 500 1,000 1,000 116-06-3 Aldicarb 100/500 1 100/10,000 309-00-2 Aldrin 500/500 1 500/10,000 107-18-6 Allyl Alcohol 500 100 1,000 107-11-9 Allylamine 500 500 500 20859-73-8 Aluminum Phosphide 500 100 500 54-62-6 Aminopterin 500/500 500 500/10,000 78-53-5 Amiton 500 500 500 3734-97-2 Amiton Oxalate 100/500 100 100/10,000 7664-41-7 Ammonia 500 100 500 300-62-9 Amphetamine 500 1,000 1,000 62-53-3 Aniline 500 5,000 1,000 88-05-1 Aniline, 2,4,6-trimethyl- 500 500 500 7783-70-2 Antimony pentafluoride 500 500 500 1397-94-0 Antimycin A 500/500 1,000 1,000/10,000 86-88-4 ANTU 500/500 100 500/10,000 1303-28-2 Arsenic pentoxide 100/500 1 100/10,000 1327-53-3 Arsenous oxide 100/500 1 100/10,000 7784-34-1 Arsenous trichloride 500 1 500 7784-42-1 Arsine 100 100 100 2642-71-9 Azinphos-Ethyl 100/500 100 100/10,000 86-50-0 Azinphos-Methyl 10/500 1 10/10,000 98-87-3 Benzal Chloride 500 5,000 500 98-16-8 Benzenamine, 3-(trifluoromethyl)- 500 500 500 100-14-1 Benzene, 1-(chloromethyl)-4-nitro- 500/500 -
Ammonium Acetate
Right to Know Hazardous Substance Fact Sheet Common Name: AMMONIUM ACETATE Synonyms: None CAS Number: 631-61-8 Chemical Name: Acetic Acid, Ammonium Salt RTK Substance Number: 0085 Date: April 2002 Revision: March 2011 DOT Number: UN 9079 Description and Use EMERGENCY RESPONDERS >>>> SEE LAST PAGE Ammonium Acetate is a white, crystalline (sand-like) solid Hazard Summary with a slight vinegar-like odor. It is used in chemical analysis, Hazard Rating NJDOH NFPA textile dyeing, and preserving meats. HEALTH 2 - FLAMMABILITY 1 - REACTIVITY 0 - POISONOUS GASES ARE PRODUCED IN FIRE Reasons for Citation f Ammonium Acetate is on the Right to Know Hazardous Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; 4=severe Substance List because it is cited by DOT and IRIS. f Ammonium Acetate can affect you when inhaled. f Contact can irritate and burn the skin and eyes. f Inhaling Ammonium Acetate can irritate the nose, throat and lungs causing coughing, wheezing and/or shortness of breath. SEE GLOSSARY ON PAGE 5. FIRST AID Eye Contact Workplace Exposure Limits f Immediately flush with large amounts of water for at least 30 No occupational exposure limits have been established for minutes, lifting upper and lower lids. Remove contact Ammonium Acetate. However, it may pose a health risk. lenses, if worn, while flushing. Seek medical attention. Always follow safe work practices. Skin Contact f Quickly remove contaminated clothing. Immediately wash contaminated skin with large amounts of water. Inhalation f Remove the person from exposure. f Begin rescue breathing (using universal precautions) if breathing has stopped and CPR if heart action has stopped. -
(12) Patent Application Publication (10) Pub. No.: US 2016/0372276 A1 HAN Et Al
US 20160372276A1 (19) United States (12) Patent Application Publication (10) Pub. No.: US 2016/0372276 A1 HAN et al. (43) Pub. Date: Dec. 22, 2016 (54) A PRECIOUS METAL SWITCH CONTACT C2.5D 5/48 (2006.01) COMPONENT AND ITS PREPARATION C2.5D 3/48 (2006.01) METHOD C2.5D 3/46 (2006.01) C2.5D 5/02 (2006.01) (71) Applicant: NANTONG MEMTECH HIH II/04 (2006.01) TECHNOLOGIES CO., LTD, C23C 8/42 (2006.01) Nantong (CN) (52) U.S. Cl. CPC ................ H01H I/02 (2013.01); H0IH II/04 (72) Inventors: Huisheng HAN, Nantong (CN); (2013.01); C23C 18/1605 (2013.01); C23C HONGMEI ZHANG, NANTONG 18/1689 (2013.01); C23C 18/42 (2013.01); (CN); YANG DING, NANTONG (CN); C25D 3/48 (2013.01); C25D 3/46 (2013.01); ZHIHONG DONG, NANTONG (CN); C25D 5/022 (2013.01); C25D 5/48 (2013.01) CHENG HUANG, NANTONG (CN) (57) ABSTRACT (21) Appl. No.: 14/896,403 This invention discloses a preparation method for precious metal Switching contact components by means of plating (22) PCT Filed: Sep. 15, 2014 masking, plating and etching processes. The plating masking PCT/CN2014/090913 process is performed by using a plating mask ink with or (86). PCT No.: without a photo exposure machine. Plating of precious S 371 (c)(1), metals is performed by electroless plating or electro plating (2) Date: Dec. 7, 2015 methods. Etching is carried out with etching solutions con taining weak organic acids, weak inorganic acids or acidic (30) Foreign Application Priority Data buffering agents. Improvement of the etched Surface gloss and prevention of the side etching are realized with the Sep.