Analysis of Trace Hydrocarbon Impurities in 1,3-Butadiene Using Optimized Rt®-Alumina BOND/MAPD PLOT Columns by Rick Morehead, Jan Pijpelink, Jaap De Zeeuw, Tom Vezza
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Next Generation PLOT Alumina Technology for Accurate Measurement of Trace Polar Hydrocarbons in Hydrocarbon Streams
Next generation PLOT alumina technology for accurate measurement of trace polar hydrocarbons in hydrocarbon streams Jaap de Zeeuw, Tom Vezza, Bill Bromps, Rick Morehead and Gary Stidsen Restek Corporation, Bellefonte, USA 1 Next generation PLOT alumina technology for accurate measurement of trace polar hydrocarbons in hydrocarbon streams Jaap de Zeeuw, Tom Vezza, Bill Bromps, Rick More head and Gary Stidsen Restek Corporation Summary In light hydrocarbon analysis, the separation and detection of traces of polar hydrocarbons like acetylene, propadiene and methyl acetylene is very important. Using commercial alumina columns with KCl or Na2SO4 deactivation, often results in low response of polar hydrocarbons. Additionally, challenges are observed in response-in time stability. Solutions have been proposed to maximize response for components like methyl acetylene and propadiene, using alumina columns that were specially deactivated. Operating such columns showed still several challenges: Due to different deactivations, the retention and loadability of such alumina columns has been drastically reduced. A new Alumina deactivation technology was developed that combined the high response for polar hydrocarbon with maintaining the loadability. This allows the high response for components like methyl acetylene, acetylene and propadiene, also to be used for impurity analysis as well as TCD type applications. Such columns also showed excellent stability of response in time, which was superior then existing solutions. Additionally, it was observed that such alumina columns could be used up to 250 C, extending the Tmax by 50C. This allows higher hydrocarbon elution, faster stabilization and also widens application scope of any GC where multiple columns are used. In this poster the data is presented showing the improvements made in this important application field. -
(C4-Naphthalene) Environmental Hazard Summary
ENVIRONMENTAL CONTAMINANTS ENCYCLOPEDIA C4-NAPHTHALENE ENTRY Note: This entry is for C4 Naphthalenes only. For naphthalene(s) in general, see Naphthalene entry. July 1, 1997 COMPILERS/EDITORS: ROY J. IRWIN, NATIONAL PARK SERVICE WITH ASSISTANCE FROM COLORADO STATE UNIVERSITY STUDENT ASSISTANT CONTAMINANTS SPECIALISTS: MARK VAN MOUWERIK LYNETTE STEVENS MARION DUBLER SEESE WENDY BASHAM NATIONAL PARK SERVICE WATER RESOURCES DIVISIONS, WATER OPERATIONS BRANCH 1201 Oakridge Drive, Suite 250 FORT COLLINS, COLORADO 80525 WARNING/DISCLAIMERS: Where specific products, books, or laboratories are mentioned, no official U.S. government endorsement is intended or implied. Digital format users: No software was independently developed for this project. Technical questions related to software should be directed to the manufacturer of whatever software is being used to read the files. Adobe Acrobat PDF files are supplied to allow use of this product with a wide variety of software, hardware, and operating systems (DOS, Windows, MAC, and UNIX). This document was put together by human beings, mostly by compiling or summarizing what other human beings have written. Therefore, it most likely contains some mistakes and/or potential misinterpretations and should be used primarily as a way to search quickly for basic information and information sources. It should not be viewed as an exhaustive, "last-word" source for critical applications (such as those requiring legally defensible information). For critical applications (such as litigation applications), it is best to use this document to find sources, and then to obtain the original documents and/or talk to the authors before depending too heavily on a particular piece of information. Like a library or many large databases (such as EPA's national STORET water quality database), this document contains information of variable quality from very diverse sources. -
BENZENE Disclaimer
United States Office of Air Quality EPA-454/R-98-011 Environmental Protection Planning And Standards June 1998 Agency Research Triangle Park, NC 27711 AIR EPA LOCATING AND ESTIMATING AIR EMISSIONS FROM SOURCES OF BENZENE Disclaimer This report has been reviewed by the Office of Air Quality Planning and Standards, U.S. Environmental Protection Agency, and has been approved for publication. Mention of trade names and commercial products does not constitute endorsement or recommendation of use. EPA-454/R-98-011 ii TABLE OF CONTENTS Section Page LIST OF TABLES.....................................................x LIST OF FIGURES.................................................. xvi EXECUTIVE SUMMARY.............................................xx 1.0 PURPOSE OF DOCUMENT .......................................... 1-1 2.0 OVERVIEW OF DOCUMENT CONTENTS.............................. 2-1 3.0 BACKGROUND INFORMATION ...................................... 3-1 3.1 NATURE OF POLLUTANT..................................... 3-1 3.2 OVERVIEW OF PRODUCTION AND USE ......................... 3-4 3.3 OVERVIEW OF EMISSIONS.................................... 3-8 4.0 EMISSIONS FROM BENZENE PRODUCTION ........................... 4-1 4.1 CATALYTIC REFORMING/SEPARATION PROCESS................ 4-7 4.1.1 Process Description for Catalytic Reforming/Separation........... 4-7 4.1.2 Benzene Emissions from Catalytic Reforming/Separation .......... 4-9 4.2 TOLUENE DEALKYLATION AND TOLUENE DISPROPORTIONATION PROCESS ............................ 4-11 4.2.1 Toluene Dealkylation -
BUTADIENE AS a CHEMICAL RAW MATERIAL (September 1998)
Abstract Process Economics Program Report 35D BUTADIENE AS A CHEMICAL RAW MATERIAL (September 1998) The dominant technology for producing butadiene (BD) is the cracking of naphtha to pro- duce ethylene. BD is obtained as a coproduct. As the growth of ethylene production outpaced the growth of BD demand, an oversupply of BD has been created. This situation provides the incen- tive for developing technologies with BD as the starting material. The objective of this report is to evaluate the economics of BD-based routes and to compare the economics with those of cur- rently commercial technologies. In addition, this report addresses commercial aspects of the butadiene industry such as supply/demand, BD surplus, price projections, pricing history, and BD value in nonchemical applications. We present process economics for two technologies: • Cyclodimerization of BD leading to ethylbenzene (DSM-Chiyoda) • Hydrocyanation of BD leading to caprolactam (BASF). Furthermore, we present updated economics for technologies evaluated earlier by PEP: • Cyclodimerization of BD leading to styrene (Dow) • Carboalkoxylation of BD leading to caprolactam and to adipic acid • Hydrocyanation of BD leading to hexamethylenediamine. We also present a comparison of the DSM-Chiyoda and Dow technologies for producing sty- rene. The Dow technology produces styrene directly and is limited in terms of capacity by the BD available from a world-scale naphtha cracker. The 250 million lb/yr (113,000 t/yr) capacity se- lected for the Dow technology requires the BD output of two world-scale naphtha crackers. The DSM-Chiyoda technology produces ethylbenzene. In our evaluations, we assumed a scheme whereby ethylbenzene from a 266 million lb/yr (121,000 t/yr) DSM-Chiyoda unit is combined with 798 million lb/yr (362,000 t/yr) of ethylbenzene produced by conventional alkylation of benzene with ethylene. -
Supplement of Compilation and Evaluation of Gas Phase Diffusion Coefficients of Reactive Trace Gases in the Atmosphere
Supplement of Atmos. Chem. Phys., 15, 5585–5598, 2015 http://www.atmos-chem-phys.net/15/5585/2015/ doi:10.5194/acp-15-5585-2015-supplement © Author(s) 2015. CC Attribution 3.0 License. Supplement of Compilation and evaluation of gas phase diffusion coefficients of reactive trace gases in the atmosphere: Volume 2. Diffusivities of organic compounds, pressure-normalised mean free paths, and average Knudsen numbers for gas uptake calculations M. J. Tang et al. Correspondence to: M. J. Tang ([email protected]) and M. Kalberer ([email protected]) The copyright of individual parts of the supplement might differ from the CC-BY 3.0 licence. Table of Contents 1 Alkanes and cycloalkanes ............................................................................................ 1 1.1 CH 4 (methane), C 2H6 (ethane), and C 3H8 (propane) ............................................. 1 1.2 C 4H10 (butane, methyl propane) ............................................................................ 3 1.3 C 5H12 (n-pentane, methyl butane, dimethyl butane) ............................................. 5 1.4 C 6H14 (n-hexane, 2,3-dimethyl butane) ................................................................ 7 1.5 C 7H16 (n-heptane, 2,4-dimethyl pentane).............................................................. 9 1.6 C 8H18 (n-octane, 2,2,4-trimethyl pentane) .......................................................... 11 1.7 C 9H20 (n-nonane), C 10 H22 (n-decane, 2,3,3-trimethyl heptane) and C 12 H26 (n- dodecane) ................................................................................................................. -
ETHYLENE PLANT ENHANCEMENT (April 2001)
Abstract Process Economics Program Report 29G ETHYLENE PLANT ENHANCEMENT (April 2001) The prospects for ethylene demand remain strong but much of the future increase in production capacity may come from incremental enhancement of existing plants, rather than from new “grass-roots” production facilities. Steam cracking for ethylene originated as early as the 1920s and was commercialized in the 1950s. The importance of ethylene continues to drive research and development of this technology along with the exploration of nonconventional technologies in order to achieve higher yields of olefins and lower capital and operating costs. However, as recently discussed in PEP Report 29F, Ethylene by Nonconventional Processes (August 1998), it is unlikely nonconventional processes will replace steam cracking for ethylene production in the foreseeable future. This study examines potential improvements in conventional steam cracker operations with emphasis on improving the competitive edge of existing plants. Ethane, LPG and naphtha are the dominant steam cracker feedstocks. Natural gas condensate is abundant in North America and the Middle East while naphtha is commonly used in Asia and Europe. Since the 1970s many new ethylene plants have been built with feedstock flexibility. In PEP Report 220, Ethylene Feedstock Outlook (May 1999), SRIC currently projects that generally ethylene feedstocks supply will be adequate over the next decade even considering that the demand for ethylene is increasing twice as fast as petroleum refining (4- 5%/year versus 2%/year). Significant technological developments exist for all sections of the ethylene steam cracker that could be implemented in plant revamps. Examples include new large capacity yet compact and efficient furnaces; coke inhibition technology; larger, more efficient compressors; fractionation schemes; mixed refrigerants; and advance control and optimization systems. -
Butadiene Bdi
BUTADIENE BDI CAUTIONARY RESPONSE INFORMATION 4. FIRE HAZARDS 7. SHIPPING INFORMATION 4.1 Flash Point: 7.1 Grades of Purity: Research grade: 99.86 Common Synonyms Liquefied compressed Colorless Gasoline-like odor 105°F (est.) mole% Special purity: 99.5 mole% Rubber Biethylene gas 4.2 Flammable Limits in Air: 2.0%-11.5% grade: 99.0mole% Commercial: 98% Bivinyl 4.3 Fire Extinguishing Agents: Stop flow of 7.2 Storage Temperature: Ambient 1,3-Butadiene Divinyl Floats and boils on water. Flammable visible vapor cloud is produced. gas 7.3 Inert Atmosphere: No requirement Vinyl ethylene 4.4 Fire Extinguishing Agents Not to Be 7.4 Venting: Safety relief Used: Not pertinent 7.5 IMO Pollution Category: Currently not available 4.5 Special Hazards of Combustion Restrict access. 7.6 Ship Type: 2 Avoid contact with liquid and gas. Products: Not pertinent Wear goggles, self-contained breathing apparatus, and rubber overclothing (including gloves). 4.6 Behavior in Fire: Vapors heavier than air 7.7 Barge Hull Type: 2 Shut off ignition sources and call fire department. and may travel a considerable distance Evacuate area in case of large discharge. to a source of ignition and flashback. 8. HAZARD CLASSIFICATIONS Stay upwind and use water spray to ``knock down'' vapor. Containers may explode in a fire due to Notify local health and pollution control agencies. polymerization. 8.1 49 CFR Category: Flammable gas Protect water intakes. 4.7 Auto Ignition Temperature: 788°F 8.2 49 CFR Class: 2.1 4.8 Electrical Hazards: Class 1, Group B 8.3 49 CFR Package Group: Not listed. -
Supporting Information for Modeling the Formation and Composition Of
Supporting Information for Modeling the Formation and Composition of Secondary Organic Aerosol from Diesel Exhaust Using Parameterized and Semi-explicit Chemistry and Thermodynamic Models Sailaja Eluri1, Christopher D. Cappa2, Beth Friedman3, Delphine K. Farmer3, and Shantanu H. Jathar1 1 Department of Mechanical Engineering, Colorado State University, Fort Collins, CO, USA, 80523 2 Department of Civil and Environmental Engineering, University of California Davis, Davis, CA, USA, 95616 3 Department of Chemistry, Colorado State University, Fort Collins, CO, USA, 80523 Correspondence to: Shantanu H. Jathar ([email protected]) Table S1: Mass speciation and kOH for VOC emissions profile #3161 3 -1 - Species Name kOH (cm molecules s Mass Percent (%) 1) (1-methylpropyl) benzene 8.50×10'() 0.023 (2-methylpropyl) benzene 8.71×10'() 0.060 1,2,3-trimethylbenzene 3.27×10'(( 0.056 1,2,4-trimethylbenzene 3.25×10'(( 0.246 1,2-diethylbenzene 8.11×10'() 0.042 1,2-propadiene 9.82×10'() 0.218 1,3,5-trimethylbenzene 5.67×10'(( 0.088 1,3-butadiene 6.66×10'(( 0.088 1-butene 3.14×10'(( 0.311 1-methyl-2-ethylbenzene 7.44×10'() 0.065 1-methyl-3-ethylbenzene 1.39×10'(( 0.116 1-pentene 3.14×10'(( 0.148 2,2,4-trimethylpentane 3.34×10'() 0.139 2,2-dimethylbutane 2.23×10'() 0.028 2,3,4-trimethylpentane 6.60×10'() 0.009 2,3-dimethyl-1-butene 5.38×10'(( 0.014 2,3-dimethylhexane 8.55×10'() 0.005 2,3-dimethylpentane 7.14×10'() 0.032 2,4-dimethylhexane 8.55×10'() 0.019 2,4-dimethylpentane 4.77×10'() 0.009 2-methylheptane 8.28×10'() 0.028 2-methylhexane 6.86×10'() -
Fullerene Derivatives and Fullerene Superconductors H
Digital Commons @ George Fox University Faculty Publications - Department of Biology and Department of Biology and Chemistry Chemistry 1993 Fullerene Derivatives and Fullerene Superconductors H. H. Wang J. A. Schlueter A. C. Cooper J. L. Smart [email protected] M. E. Whitten See next page for additional authors Follow this and additional works at: http://digitalcommons.georgefox.edu/bio_fac Part of the Chemistry Commons, and the Physics Commons Recommended Citation Previously published in Journal of Physics and Chemistry of Solids, 1993, 54(12), 1655-1666. This Article is brought to you for free and open access by the Department of Biology and Chemistry at Digital Commons @ George Fox University. It has been accepted for inclusion in Faculty Publications - Department of Biology and Chemistry by an authorized administrator of Digital Commons @ George Fox University. For more information, please contact [email protected]. Authors H. H. Wang, J. A. Schlueter, A. C. Cooper, J. L. Smart, M. E. Whitten, U. Geiser, K. D. Carlson, J. M. Williams, U. Welp, J. D. Dudek, and M. A. Caleca This article is available at Digital Commons @ George Fox University: http://digitalcommons.georgefox.edu/bio_fac/91 Fullerene Derivatives and Fullerene Superconductors H. H. Wang, J. A. Schlueter, A. C. Cooper, J. L. Smart, M. E. Whitten, U. Geiser, K. D. Carlson, J. M. Williams, U. Welp, J. D. Dudek and M. A. Caleca Chemistry and Materials Science Divisions Argonne National Laboratory 9700 South Cass Avenue Argonne, IL 60439 DISCLAIMER This report was prepared as an account of work sponsored by an agency of the United States Government. -
Community-Scale Air Toxics Ambient Monitoring Projects (CSATAM) Summary Report
Community-Scale Air Toxics Ambient Monitoring Projects (CSATAM) Summary Report U.S. Environmental Protection Agency Office of Air Quality, Planning and Standards Air Quality Analysis Division 109 TW Alexander Drive Research Triangle Park, NC 27711 July 2009 DISCLAIMER The information presented in this document is intended as a technical resource to those conducting community-scale monitoring projects. The mention of commercial products, their source, or their use in connection with material reported herein is not to be construed as actual or implied endorsement of such products. This is document and will be updated periodically as additional final reports are delivered. The Environmental Protection Agency welcomes public input on this document at any time. Comments should be sent to Barbara Driscoll ([email protected]). FORWARD In June 2009, Eastern Research Group (ERG) under subcontract to RTI International prepared a final technical report under Contract No. EP-D-08-047, Work Assignment 1-03. The report was prepared for Barbara Driscoll of the Air Quality Assessment Division (AQAD) within the Office of Air Quality Planning and Standards (OAQPS) in Research Triangle Park, North Carolina. The report was written by Regi Ooman and was incorporated into this final report. ii TABLE OF CONTENTS Page List of Figures ................................................................................................................................... v List of Tables.................................................................................................................................... -
Identification of Gas-Phase Pyrolysis Products in A
Atmos. Meas. Tech., 12, 763–776, 2019 https://doi.org/10.5194/amt-12-763-2019 © Author(s) 2019. This work is distributed under the Creative Commons Attribution 4.0 License. Identification of gas-phase pyrolysis products in a prescribed fire: first detections using infrared spectroscopy for naphthalene, methyl nitrite, allene, acrolein and acetaldehyde Nicole K. Scharko1, Ashley M. Oeck1, Russell G. Tonkyn1, Stephen P. Baker2, Emily N. Lincoln2, Joey Chong3, Bonni M. Corcoran3, Gloria M. Burke3, David R. Weise3, Tanya L. Myers1, Catherine A. Banach1, David W. T. Griffith4, and Timothy J. Johnson1 1Pacific Northwest National Laboratories, Richland, WA, USA 2Rocky Mountain Research Station, USDA Forest Service, Missoula, MT, USA 3Pacific Southwest Research Station, USDA Forest Service, Riverside, CA, USA 4Centre for Atmospheric Chemistry, University of Wollongong, Wollongong NSW 2522, Australia Correspondence: Timothy J. Johnson ([email protected]) Received: 1 October 2018 – Discussion started: 13 November 2018 Revised: 16 January 2019 – Accepted: 16 January 2019 – Published: 1 February 2019 Abstract. Volatile organic compounds (VOCs) are emitted ventive tool to reduce hazardous fuel buildups in an effort to from many sources, including wildland fire. VOCs have re- reduce or eliminate the risk of such wildfires (Fernandes and ceived heightened emphasis due to such gases’ influential Botelho, 2003). Understanding the products associated with role in the atmosphere, as well as possible health effects. the burning of biomass has received considerable attention We have used extractive infrared (IR) spectroscopy on re- since the emissions can markedly impact the atmosphere. cent prescribed burns in longleaf pine stands and herein re- Fourier-transform infrared (FTIR) spectroscopy is one tech- port the first detection of five compounds using this tech- nique that has been extensively used to identify and quantify nique. -
Steam Cracking: Chemical Engineering
Steam Cracking: Kinetics and Feed Characterisation João Pedro Vilhena de Freitas Moreira Thesis to obtain the Master of Science Degree in Chemical Engineering Supervisors: Professor Doctor Henrique Aníbal Santos de Matos Doctor Štepánˇ Špatenka Examination Committee Chairperson: Professor Doctor Carlos Manuel Faria de Barros Henriques Supervisor: Professor Doctor Henrique Aníbal Santos de Matos Member of the Committee: Specialist Engineer André Alexandre Bravo Ferreira Vilelas November 2015 ii The roots of education are bitter, but the fruit is sweet. – Aristotle All I am I owe to my mother. – George Washington iii iv Acknowledgments To begin with, my deepest thanks to Professor Carla Pinheiro, Professor Henrique Matos and Pro- fessor Costas Pantelides for allowing me to take this internship at Process Systems Enterprise Ltd., London, a seven-month truly worthy experience for both my professional and personal life which I will certainly never forget. I would also like to thank my PSE and IST supervisors, who help me to go through this final journey as a Chemical Engineering student. To Stˇ epˇ an´ and Sreekumar from PSE, thank you so much for your patience, for helping and encouraging me to always keep a positive attitude, even when harder problems arose. To Prof. Henrique who always showed availability to answer my questions and to meet in person whenever possible. Gostaria tambem´ de agradecer aos meus colegas de casa e de curso Andre,´ Frederico, Joana e Miguel, com quem partilhei casa. Foi uma experienciaˆ inesquec´ıvel que atravessamos´ juntos e cer- tamente que a vossa presenc¸a diaria´ apos´ cada dia de trabalho ajudou imenso a aliviar as saudades de casa.