Thermodynamic Properties of Solid and Liquid Ethylbenzene from 0 to 300 Degrees K
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Toxicological Profile for Ethylbenzene
ETHYLBENZENE 221 9. REFERENCES Abraham MH, Ibrahim A, Acree WE. 2005. Air to blood distribution of volatile organic compounds: A linear free energy analysis. Chem Res Toxicol 18(5):904-911. ACGIH. 1992. 1992-1993 Threshold limit values for chemical substances and physical agents and biological exposure indices. Cincinnati, OH: American Conference of Governmental Industrial Hygienists, 21. ACGIH. 2002. Ethylbenzene. Documentation of the threshold limit values for chemical substances and physical agents and biological exposure indices. 7th ed. Cincinnati, OH: American Conference of Governmental Industrial Hygienists. ACGIH. 2006. Ethylbenzene. Threshold limit values for chemical substances and physical agents and biological exposure indices. Cincinnati, OH: American Conference of Governmental Industrial Hygienists, 29, 104. Acton DW, Barker JF. 1992. In situ biodegradation potential of aromatic hydrocarbons in anaerobic groundwaters. J Contam Hydrol 9:325-352. Adinolfi M. 1985. The development of the human blood-CSF-brain barrier. Dev Med Child Neurol 27(4):532-537. Adlercreutz H. 1995. Phytoestrogens: Epidemiology and a possible role in cancer protection. Environ Health Perspect Suppl 103(7):103-112. Agency for Toxic Substances and Disease Registry. 1989. Decision guide for identifying substance- specific data needs related to toxicological profiles; Notice. Agency for Toxic Substances and Disease Registry, Division of Toxicology. Fed Regist 54(174):37618-37634. Agency for Toxic Substances and Disease Registry. 1990. Biomarkers of organ damage or dysfunction for the renal, hepatobiliary and immune systems. Subcommittee on Biomarkers of Organ Damage and Dysfunction. Atlanta, GA: Agency for Toxic Substances and Disease Registry. Agency for Toxic Substances and Disease Registry. 1992. Toxicological profile for styrene. -
Feas: Heat Capacity, Enthalpy Increments, Other Thermodynamic Properties from 5 to 1350 K, and Magnetic Transition A
M-2341 J. Chem. Thermodynumics 1989,21, 363-373 FeAs: Heat capacity, enthalpy increments, other thermodynamic properties from 5 to 1350 K, and magnetic transition a DOMINGO GONZALEZ-ALVAREZ, Fact&ad de Ciencias de la Universidad de Zaragoza, Departamento de Fisica Fundamental, 5009 Zaragoza, Spain FREDRIK GR0NVOLD, Chemical Institute, University of Oslo, Blindern, Oslo 3, Norway BENGT FALK,b EDGAR F. WESTRUM, JR., Department of Chemistry, University of Michigan, Ann Arbor, MI 48109, U.S.A. R. BLACHNIK,’ and G. KUDERMANNd Technical University, Siegen, Federal Republic of Germany (Received 2 January 1989) The heat capacity of iron monoarsenide has been determined by adiabatic calorimetry from 5 to 1030 K and bv drou calorimetrv relative to 298.15 K over the range 875 to 1350 K. A small h-type transition is observed at ?;, = (70.95 kO.02) K. It is related & the disappearance of a doubly helically ordered magnetic-spin structure on heating. The obviously cooperative entropy increment of transition is only A&JR = 0.021. The higher-temperature heat capacity rises considerably above lattice expectations. Part of the rise is ascribed to low-spin electron redistribution in iron, while the further excess above 800 K presumably arises from a beginning low- to high-spin transition, possibly connected with interstitial defect formation in the MnP- type structure. FeAs melts at about 1325 K with A,,,Hk=6180R.K. Thermodynamic functions have been evaluated and the values of C,,,(T), S:(T), H:(T), and @i(T), are 6.057R, 7.513R,1177R.K, and 3.567Rat 298.15 K, and 8.75R,16.03R, 6287R.K, and 9.74512at 1000 K. -
High Temperature Enthalpies of the Lead Halides
HIGH TEMPERATURE ENTHALPIES OF THE LEAD HALIDES: ENTHALPIES AND ENTROPIES OF FUSION APPROVED: Graduate Committee: Major Professor Committee Member Min fessor Committee Member X Committee Member UJ. Committee Member Committee Member Chairman of the Department of Chemistry Dean or the Graduate School HIGH TEMPERATURE ENTHALPIES OF THE LEAD HALIDES: ENTHALPIES AND ENTROPIES OF FUSION DISSERTATION Presented to the Graduate Council of the North Texas State University in Partial Fulfillment of the Requirements For the Degree of DOCTOR OF PHILOSOPHY By Clarence W, Linsey, B. S., M. S, Denton, Texas June, 1970 ACKNOWLEDGEMENT This dissertation is based on research conducted at the Oak Ridge National Laboratory, Oak Ridge, Tennessee, which is operated by the Uniofl Carbide Corporation for the U. S. Atomic Energy Commission. The author is also indebted to the Oak Ridge Associated Universities for the Oak Ridge Graduate Fellowship which he held during the laboratory phase. 11 TABLE OF CONTENTS Page LIST OF TABLES iv LIST OF ILLUSTRATIONS v Chapter I. INTRODUCTION . 1 Lead Fluoride Lead Chloride Lead Bromide Lead Iodide II. EXPERIMENTAL 11 Reagents Fusion-Filtration Method Encapsulation of Samples Equipment and Procedure Bunsen Ice Calorimeter Computer Programs Shomate Method Treatment of Data Near the Melting Point Solution Calorimeter Heat of Solution Calculations III. RESULTS AND DISCUSSION 41 Lead Fluoride Variation in Heat Contents of the Nichrome V Capsules Lead Chloride Lead Bromide Lead Iodide Summary BIBLIOGRAPHY ...... 98 in LIST OF TABLES Table Pa8e I. High-Temperature Enthalpy Data for Cubic PbE2 Encapsulated in Gold 42 II. High-Temperature Enthalpy Data for Cubic PbF2 Encapsulated in Molybdenum 48 III. -
Ethylbenzene- Toxfaqs™ CAS # 100-41-4
Ethylbenzene- ToxFAQs™ CAS # 100-41-4 This fact sheet answers the most frequently asked health questions (FAQs) about ethylbenzene. For more information, call the CDC Information Center at 1-800-232-4636. This fact sheet is one in a series of summaries about hazardous substances and their health effects. It is important you understand this information because this substance may harm you. The effects of exposure to any hazardous substance depend on the dose, the duration, how you are exposed, personal traits and habits, and whether other chemicals are present. HIGHLIGHTS: Ethylbenzene is a colorless liquid found in a number of products including gasoline and paints. Breathing very high levels can cause dizziness and throat and eye irritation. Breathing lower levels has resulted in hearing effects and kidney damage in animals. Ethylbenzene has been found in at least 829 of 1,699 National Priorities List (NPL) sites identified by the Environmental Protection Agency (EPA). What is ethylbenzene? • Releases of ethylbenzene into the air occur from burning oil, gas, and coal and from industries Ethylbenzene is a colorless, flammable liquid that smells using ethylbenzene. like gasoline. • Ethylbenzene is not often found in drinking water. It is naturally found in coal tar and petroleum and is also Higher levels may be found in residential drinking found in manufactured products such as inks, pesticides, water wells near landfills, waste sites, or leaking and paints. underground fuel storage tanks. Ethylbenzene is used primarily to make another chemical, • Exposure can occur if you work in an industry where styrene. Other uses include as a solvent, in fuels, and to ethylbenzene is used or made. -
THERMODYNAMIC EVALUATION of the Cu-Ti SYSTEM in VIEW of SOLID STATE AMORPHIZATION REACTIONS L
THERMODYNAMIC EVALUATION OF THE Cu-Ti SYSTEM IN VIEW OF SOLID STATE AMORPHIZATION REACTIONS L. Battezzati, M. Baricco, G. Riontino, I. Soletta To cite this version: L. Battezzati, M. Baricco, G. Riontino, I. Soletta. THERMODYNAMIC EVALUATION OF THE Cu- Ti SYSTEM IN VIEW OF SOLID STATE AMORPHIZATION REACTIONS. Journal de Physique Colloques, 1990, 51 (C4), pp.C4-79-C4-85. 10.1051/jphyscol:1990409. jpa-00230769 HAL Id: jpa-00230769 https://hal.archives-ouvertes.fr/jpa-00230769 Submitted on 1 Jan 1990 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. ~OLLOQUEDE PHYSIQUE Colloque C4, suppl6ment au 11'14, Tome 51, 15 juillet 1990 THERMODYNAMIC EVALUATION OF THE Cu-Ti SYSTEM IN VIEW OF SOLID STATE AMORPHIZATION REACTIONS L. BATTEZZATI* , M. BARICCO*~ *""" , G. RIONTINO" *"* and I. SOLETTA** * '~ipartimento di Chimica Inorganics, Chimica Fisica e Chimica dei Materiali, Universitd di Torino, Italy ""~stitutoElettrotecnico Nazionale Galileo Perraris, Torino, Italy *.* Dipartimento di Chimica, Universitd di Sassari, Italy *et* INPM, Unita' di Ricerca di Torino, Italy Resumk -La description thermodynamique du sist6me Cu-Ti est reconsideree, car les calculs he la littgrature, bien que donnant une bonne representation du diagramme de phase, ne prevoient pas la possibilit6 de l'amorphisation. -
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. -
Ethylbenzene Environmental Hazard Summary
ENVIRONMENTAL CONTAMINANTS ENCYCLOPEDIA ETHYLBENZENE 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 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 and hardware (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 most large databases (such as EPA's national STORET water quality database), this document contains information of variable quality from very diverse sources. -
A New Perspective on Catalytic Dehydrogenation of Ethylbenzene: the Influence of Side-Reactions on Catalytic Performance
Catalysis Science & Technology A new perspective on catalytic dehydrogenation of ethylbenzene: the influence of side-reactions on catalytic performance Journal: Catalysis Science & Technology Manuscript ID: CY-ART-03-2015-000457.R1 Article Type: Paper Date Submitted by the Author: 18-May-2015 Complete List of Authors: Gomez Sanz, Sara; University of Cambridge, Department of Chemical Engineering and Biotechnology McMillan, Liam; University of Cambridge, Department of Chemical Engineering and Biotechnology McGregor, James; University of Sheffield, Department of Chemical and Biological Engineering Zeitler, J.; University of Cambridge, Department of Chemical Engineering; Al-Yassir, Nabil; King Fahd University of Petroleum & Minerals, Center of Research Excellence in Petroleum Refining and Petrochemical Khattaf, Sulaiman; King Fahd University of Petroleum and Minerals, Center of Research Excellence in Petroleum Refining and Petrochemical Gladden, Lynn; University of Cambridge, Department of Chemical Engineering and Biotechnology, Page 1 of 44 Catalysis Science & Technology The direct dehydrogenation of ethylbenzene to styrene over CrO x/Al 2O3 proceeds via a partially oxidative mechanism due to the formation of CO 2 in situ during reaction. Other side reactions, including coke formation, also play a key role in dictating catalytic performance. Catalysis Science & Technology Page 2 of 44 A new perspective on catalytic dehydrogenation of ethylbenzene: the influence of side-reactions on catalytic performance Sara Gomez a, Liam McMillan a, James -
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'() -
Efficient Approach to Compute Melting Properties Fully from Ab Initio With
PHYSICAL REVIEW B 96, 224202 (2017) Efficient approach to compute melting properties fully from ab initio with application to Cu Li-Fang Zhu,* Blazej Grabowski, and Jörg Neugebauer Max-Planck-Institut für Eisenforschung GmbH, D-40237 Düsseldorf, Germany (Received 3 August 2017; revised manuscript received 16 October 2017; published 13 December 2017) Applying thermodynamic integration within an ab initio-based free-energy approach is a state-of-the-art method to calculate melting points of materials. However, the high computational cost and the reliance on a good reference system for calculating the liquid free energy have so far hindered a general application. To overcome these challenges, we propose the two-optimized references thermodynamic integration using Langevin dynamics (TOR-TILD) method in this work by extending the two-stage upsampled thermodynamic integration using Langevin dynamics (TU-TILD) method, which has been originally developed to obtain anharmonic free energies of solids, to the calculation of liquid free energies. The core idea of TOR-TILD is to fit two empirical potentials to the energies from density functional theory based molecular dynamics runs for the solid and the liquid phase and to use these potentials as reference systems for thermodynamic integration. Because the empirical potentials closely reproduce the ab initio system in the relevant part of the phase space the convergence of the thermodynamic integration is very rapid. Therefore, the proposed approach improves significantly the computational efficiency while preserving the required accuracy. As a test case, we apply TOR-TILD to fcc Cu computing not only the melting point but various other melting properties, such as the entropy and enthalpy of fusion and the volume change upon melting. -
Recommendations for Exposure-Based Assessmentpdf Icon
60 3. Recommendation for Exposure-Based Assessment of Joint Toxic Action of the Mixture Benzene, toluene, ethylbenzene, and xylenes frequently occur together at hazardous waste sites. The four chemicals are volatile and have good solvent properties. Toxicokinetic studies in humans and animals indicate that these chemicals are well absorbed, distribute to lipid-rich and highly vascular tissues such as the brain, bone marrow, and body fat due to their lipophilicity, and are rapidly eliminated from the body (Appendices A, B, C, and D). Metabolism of the four chemicals is dose-dependent and generally extensive at dose levels that do not saturate the first metabolic step of each compound, which involves cytochrome P-450-dependent mixed function oxidases. The predominant cytochrome P-450 isozyme involved in the metabolism of each chemical is CYP2E1. As discussed in Chapter 2 and the Appendices, all four chemicals can produce neurological impairment via parent compound-induced physical and chemical changes in nervous system membranes. Exposure to benzene can additionally cause hematological effects including aplastic anemia, with subsequent manifestation of acute myelogenous leukemia, via the action of reactive metabolites. No data are available on toxic or carcinogenic responses to whole mixtures of BTEX. To conduct exposure-based assessments of possible health hazards from BTEX in the absence of these data, a component-based approach that considers both the shared (neurologic) and unique (hematologic/ immunologic/carcinogenic) critical effects of the chemicals is recommended. In particular, as explained below, it is advised that (1) the Hazard Index approach be used to assess the joint neurotoxic hazard of the four mixture components, and (2) the hematological and carcinogenic hazards be assessed on a benzene- specific basis. -
Ethylbenzene
Ethylbenzene 100-41-4 Hazard Summary Ethylbenzene is mainly used in the manufacture of styrene. Acute (short-term) exposure to ethylbenzene in humans results in respiratory effects, such as throat irritation and chest constriction, irritation of the eyes, and neurological effects such as dizziness. Chronic (long-term) exposure to ethylbenzene by inhalation in humans has shown conflicting results regarding its effects on the blood. Animal studies have reported effects on the blood, liver, and kidneys from chronic inhalation exposure to ethylbenzene. Limited information is available on the carcinogenic effects of ethylbenzene in humans. In a study by the National Toxicology Program (NTP), exposure to ethylbenzene by inhalation resulted in an increased incidence of kidney and testicular tumors in rats, and lung and liver tumors in mice. EPA has classified ethylbenzene as a Group D, not classifiable as to human carcinogenicity. Please Note: The main sources of information for this fact sheet are EPA's Integrated Risk Information System (IRIS) (5), which contains information on inhalation and oral chronic toxicity of ethylbenzene and the RfC, and oral chronic toxicity and the RfD, and the Agency for Toxic Substances and Disease Registry's (ATSDR's) Toxicological Profile for Ethylbenzene. (1) Uses Ethylbenzene is used primarily in the production of styrene. It is also used as a solvent, as a constituent of asphalt and naphtha, and in fuels. (1) Sources and Potential Exposure In one study, ethylbenzene was detected in urban air at a median concentration of 0.62 parts per billion (ppb). The median level in suburban air was about 0.62 ppb, while the mean level measured in air in rural locations was about 0.13 ppb.