The Process of Acetonitrile Synthesis Over Γ-Al2o3 Promoted By
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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. -
Overview of VOC Emissions and Chemistry from PTR
Open Access Atmos. Chem. Phys. Discuss., 15, C7547–C7558, 2015 Atmospheric www.atmos-chem-phys-discuss.net/15/C7547/2015/ Chemistry © Author(s) 2015. This work is distributed under the Creative Commons Attribute 3.0 License. and Physics Discussions Interactive comment on “Overview of VOC emissions and chemistry from PTR-TOF-MS measurements during the SusKat-ABC campaign: high acetaldehyde, isoprene and isocyanic acid in wintertime air of the Kathmandu Valley” by C. Sarkar et al. Anonymous Referee #1 Received and published: 3 October 2015 The study produced a lot of important, unique content of great interest to ACP read- ers. However, the presentation is not quite there. For example, the references have unwanted numbers appended throughout. More importantly, the length should be cut in half while both clarifying and focusing on the main points that are most strongly sup- ported as discussed below. Some other summary thoughts about authors presumed key points in conclusions and abstract: C7547 1. First deployment of PTR-TOF-MS in South Asia, This is very significant as are the high levels measured of certain species noted below. 2. 71 ion peaks detected, of which 37 had campaign average concentrations greater than 200 ppt, which highlights chemical complexity of the Kathmandu Valley‘s air. Great, but briefly, why the 200 ppt cut-off? 3. Acetaldehyde, acetonitrile, isoprene concentrations were among the highest recorded in the world. They are among the highest reported for urban ambi- ent air. Urban area isoprene could be overestimated due to isomers from other sources. For instance, in smoke the “isoprene peak” is 20 % penetenes. -
Use of Solvents for Pahs Extraction and Enhancement of the Pahs Bioremediation in Coal- Tar-Contaminated Soils Pak-Hing Lee Iowa State University
Iowa State University Capstones, Theses and Retrospective Theses and Dissertations Dissertations 2000 Use of solvents for PAHs extraction and enhancement of the PAHs bioremediation in coal- tar-contaminated soils Pak-Hing Lee Iowa State University Follow this and additional works at: https://lib.dr.iastate.edu/rtd Part of the Environmental Engineering Commons Recommended Citation Lee, Pak-Hing, "Use of solvents for PAHs extraction and enhancement of the PAHs bioremediation in coal-tar-contaminated soils " (2000). Retrospective Theses and Dissertations. 13912. https://lib.dr.iastate.edu/rtd/13912 This Dissertation is brought to you for free and open access by the Iowa State University Capstones, Theses and Dissertations at Iowa State University Digital Repository. It has been accepted for inclusion in Retrospective Theses and Dissertations by an authorized administrator of Iowa State University Digital Repository. For more information, please contact [email protected]. INFORMATION TO USERS This manuscript has been reproduced from the microfilm master. UMI films the text directly from the original or copy submitted. Thus, some thesis and dissertation copies are in typewriter fece, while others may be from any type of computer printer. The quality of this reproduction is dependent upon the quaiity of the copy submitted. Broken or indistinct print colored or poor quality illustrations and photographs, print bleedthrough, substeindard margins, and improper alignment can adversely affect reproduction. In the unlilcely event that the author did not send UMI a complete manuscript and there are missing pages, these will be noted. Also, if unauthorized copyright material had to be removed, a note will indicate the deletion. -
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. -
EPA Method 8315A (SW-846): Determination of Carbonyl Compounds by High Performance Liquid Chromatography (HPLC)
METHOD 8315A DETERMINATION OF CARBONYL COMPOUNDS BY HIGH PERFORMANCE LIQUID CHROMATOGRAPHY (HPLC) 1.0 SCOPE AND APPLICATION 1.1 This method provides procedures for the determination of free carbonyl compounds in various matrices by derivatization with 2,4-dinitrophenylhydrazine (DNPH). The method utilizes high performance liquid chromatography (HPLC) with ultraviolet/visible (UV/vis) detection to identify and quantitate the target analytes. This method includes two procedures encompassing all aspects of the analysis (extraction to determination of concentration). Procedure 1 is appropriate for the analysis of aqueous, soil and waste samples and stack samples collected by Method 0011. Procedure 2 is appropriate for the analysis of indoor air samples collected by Method 0100. The list of target analytes differs by procedure. The appropriate procedure for each target analyte is listed in the table below. Compound CAS No. a Proc. 1b Proc. 2 b Acetaldehyde 75-07-0 X X Acetone 67-64-1 X Acrolein 107-02-8 X Benzaldehyde 100-52-7 X Butanal (Butyraldehyde) 123-72-8 X X Crotonaldehyde 123-73-9 X X Cyclohexanone 108-94-1 X Decanal 112-31-2 X 2,5-Dimethylbenzaldehyde 5779-94-2 X Formaldehyde 50-00-0 X X Heptanal 111-71-7 X Hexanal (Hexaldehyde) 66-25-1 X X Isovaleraldehyde 590-86-3 X Nonanal 124-19-6 X Octanal 124-13-0 X Pentanal (Valeraldehyde) 110-62-3 X X Propanal (Propionaldehyde) 123-38-6 X X m-Tolualdehyde 620-23-5 X X o-Tolualdehyde 529-20-4 X p-Tolualdehyde 104-87-0 X a Chemical Abstract Service Registry Number. -
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 Processing
Peracetic Acid Processing Identification Chemical Name(s): CAS Number: peroxyacetic acid, ethaneperoxic acid 79-21-0 Other Names: Other Codes: per acid, periacetic acid, PAA NIOSH Registry Number: SD8750000 TRI Chemical ID: 000079210 UN/ID Number: UN3105 Summary Recommendation Synthetic / Allowed or Suggested Non-Synthetic: Prohibited: Annotation: Synthetic Allowed (consensus) Allowed only for direct food contact for use in wash water. Allowed as a (consensus) sanitizer on surfaces in contact with organic food. (consensus) From hydrogen peroxide and fermented acetic acid sources only. (Not discussed by processing reviewers--see discussion of source under Crops PAA TAP review.) Characterization Composition: C2H4O3. Peracetic acid is a mixture of acetic acid (CH3COOH) and hydrogen peroxide (H2O2) in an aqueous solution. Acetic acid is the principle component of vinegar. Hydrogen peroxide has been previously recommended by the NOSB for the National List in processing (synthetic, allowed at Austin, 1995). Properties: It is a very strong oxidizing agent and has stronger oxidation potential than chlorine or chlorine dioxide. Liquid, clear, and colorless with no foaming capability. It has a strong pungent acetic acid odor, and the pH is acid (2.8). Specific gravity is 1.114 and weighs 9.28 pounds per gallon. Stable upon transport. How Made: Peracetic acid (PAA) is produced by reacting acetic acid and hydrogen peroxide. The reaction is allowed to continue for up to ten days in order to achieve high yields of product according to the following equation. O O || || CH3-C-OH + H2O2 CH3C-O-OH + H2O acetic acid hydrogen peroxyacetic peroxide acid Due to reaction limitations, PAA generation can be up to 15% with residual levels of hydrogen peroxide (up to 25%) and acetic acid (up to 35%) with water up to 25%. -
Acetonitrile
Fact Sheet Acetonitrile What is Acetonitrile Acetonitrile is a toxic, colorless liquid with an ether-like odor and a sweet, burnt taste. It is an extremely dangerous substance and must be handled with caution as it can cause severe health effects and/or death. It is also known as cyanomethane, ethyl nitrile, ethanenitrile, methanecarbonitrile, acetronitrile cluster and methyl cyanide. Acetonitrile is easily ignited by heat, sparks or flames and gives off highly toxic hydrogen cyanide fumes when heated. It dissolves easily in water. It can react with water, steam or acids to produce flammable vapors that can from explosive mixtures when exposed to air. The vapors are heavier than air and can travel to low or confined areas. Containers of the liquid can explode when heated. Acetonitrile is used to make pharmaceuticals, perfumes, rubber products, pesticides, acrylic nail removers and batteries. It is also used to extract fatty acids from animal and vegetable oils. Before working with acetonitrile, employee training must be provided on safe handling and storage procedures. Pregnant women should avoid contact with acetonitrile. Exposure Exposure usually occurs in the industries where acetonitrile is produced or used. Though unlikely, the general population may be exposed by due to chemical spills, accidents or releases. It is also found in cigarette smoke and automobile exhaust. Acetonitrile changes to cyanide with the body. Route of exposure can occur by: . Breathing ─Inhalation of acetonitrile vapors can cause adverse health effects. Eating/Drinking ─Ingestion of acetonitrile is not a likely route of exposure due to its irritating effects. Skin/Eye Contact ─Acetonitrile vapors and liquids can be absorbed through the skin or eyes. -
An Extractive Distillation System for Benzene-Acetonitrile Separation Using Dimethyl Sulfoxide As an Entrainer Bloch Sohil Y
An Extractive Distillation System for Benzene-Acetonitrile Separation Using Dimethyl Sulfoxide as an Entrainer Bloch Sohil Y. & Mehulkumar Sutariya Sardar Vallabhbhai National Institute of Technology, Surat Email: [email protected] Unit System: Pressure-Kpa; Molar Flow-kg/hr; Other-SI Background Hydrocarbons like Acetonitrile and Benzene are important raw materials in the manufacturing of polymeric products and as a solvent. They often require high-purity Acetonitrile and Benzene. Acetonitrile is widely used mainly as a solvent in the purification of butadiene in refineries it is widely used in battery applications because of its relatively high dielectric constant and ability to dissolve electrolytes. For similar reasons it is a popular solvent in cyclic voltammetry. Acetonitrile plays a significant role as the dominant solvent used in the manufacture of DNA oligonucleotides from monomers.Industrially, it is used as a solvent for the manufacture of pharmaceuticals and photographic film.The mixer of Acetonitrile and Benzene can not be seperated out by the simple distillation column because of the less difference between their boiling point (near 1.5 K) and same boiling point behaviour of azeotrope. Extractive Distillation of Close Boiling Compounds Extractive distillation is the method of separating close boiling compounds from each other by carrying out the distillation in a multiple columns in the presence of an added liquid or liquid mixture.1 This Liquid or Liquid mixture is known as extractive agent or entrainer. The presence of the entrainer alter the volatility of compounds and thus the degree of separation is increase with the same numbers of plate. This entrainer must have high boiling point than the compounds which are going to separated. -
NMR Chemical Shifts of Common Laboratory Solvents As Trace Impurities
7512 J. Org. Chem. 1997, 62, 7512-7515 NMR Chemical Shifts of Common Laboratory Solvents as Trace Impurities Hugo E. Gottlieb,* Vadim Kotlyar, and Abraham Nudelman* Department of Chemistry, Bar-Ilan University, Ramat-Gan 52900, Israel Received June 27, 1997 In the course of the routine use of NMR as an aid for organic chemistry, a day-to-day problem is the identifica- tion of signals deriving from common contaminants (water, solvents, stabilizers, oils) in less-than-analyti- cally-pure samples. This data may be available in the literature, but the time involved in searching for it may be considerable. Another issue is the concentration dependence of chemical shifts (especially 1H); results obtained two or three decades ago usually refer to much Figure 1. Chemical shift of HDO as a function of tempera- more concentrated samples, and run at lower magnetic ture. fields, than today’s practice. 1 13 We therefore decided to collect H and C chemical dependent (vide infra). Also, any potential hydrogen- shifts of what are, in our experience, the most popular bond acceptor will tend to shift the water signal down- “extra peaks” in a variety of commonly used NMR field; this is particularly true for nonpolar solvents. In solvents, in the hope that this will be of assistance to contrast, in e.g. DMSO the water is already strongly the practicing chemist. hydrogen-bonded to the solvent, and solutes have only a negligible effect on its chemical shift. This is also true Experimental Section for D2O; the chemical shift of the residual HDO is very NMR spectra were taken in a Bruker DPX-300 instrument temperature-dependent (vide infra) but, maybe counter- (300.1 and 75.5 MHz for 1H and 13C, respectively).