Predicting Physical Properties of Alkanes with Neural Networks
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Effective Removal of Alkanes and Polycyclic Aromatic Hydrocarbons by Bacteria from Soil Chronically Exposed to Crude Petroleum Oil
Effective Removal of Alkanes and Polycyclic Aromatic Hydrocarbons by Bacteria from Soil Chronically Exposed to Crude Petroleum Oil Eman Afkar ( [email protected] ) Dept. of Basic Sciences, Preparatory Year Deanship (PYD), King Faisal University, Al-Ahsa, 31982, Saudi Arabia. https://orcid.org/0000-0002-7442-4880 Aly M. Hafez Dept. of Chemistry, College of Science, King Faisal University, Al-Ahsa, 31982, Saudi Arabia. Rashid I.H. Ibrahim Dept. of Biological Sciences, College of Science, King Faisal University, Al-Ahsa, 31982, Saudi Arabia. Dept. of Botany, Faculty of Science, University of Khartoum, PO Box 321, PC 11115, Sudan Munirah Aldayel Dept. of Biological Sciences, College of Science, King Faisal University, Al-Ahsa, 31982, Saudi Arabia. Research Keywords: n-alkanes, GC-MS, crude oil degradation, bacteria, contaminants, hydrocarbons Posted Date: February 16th, 2021 DOI: https://doi.org/10.21203/rs.3.rs-207407/v1 License: This work is licensed under a Creative Commons Attribution 4.0 International License. Read Full License Page 1/18 Abstract In this study, two bacterial strains isolated from an oil-contaminated soil, designated as AramcoS2 and AramcoS4 were able to degrade crude oil, long-chain n-alkanes of C10 to C20; (n-decane, n-undecane, n- dodecane, n-tridecane, n-tetradecane, n-pentadecane, n-hexadecane, n-heptadecane, n-octadecane n- nonadecane, and n-eicosane) and polycyclic aromatic hydrocarbons (PAHs) including biphenyl, naphthalene, and anthracene. Gas chromatography-mass spectrometry (GC-MS) technique was conducted to analyze and identify the crude oil residues after biodegradation. AramcoS2 and AramcoS4 were able to reduce the concentration of long-chain n-alkanes of C10-C20 eciently on average by 77% of the original concentration. -
A Confinement Strategy to Prepare N-Doped Reduced Graphene Oxide
Electronic Supplementary Material (ESI) for Nanoscale. This journal is © The Royal Society of Chemistry 2019 Supporting Information A confinement strategy to prepare N-doped reduced graphene oxide foams with desired monolithic structures for supercapacitors Daoqing Liu,a,b,# Qianwei Li, *c,# Si Li, a,b Jinbao Hou,d Huazhang Zhao *a,b a Department of Environmental Engineering, Peking University, Beijing 100871, China b The Key Laboratory of Water and Sediment Sciences, Ministry of Education, Beijing 100871, China c State Key Laboratory of Heavy Oil Processing, Beijing Key Laboratory of Oil and Gas Pollution Control, China University of Petroleum, 18 Fuxue Road, Changping District, Beijing 102249, China d College of Chemical Engineering, Beijing University of Chemical Technology, Beijing 100029, China # Co-first author. * Corresponding author. Tel/fax: +86-10-62758748; email address: [email protected] (H.Z. Zhao). S1 Experimental Methods 1. Preparation of graphite oxide (GO) Graphite oxide was prepared from natural graphite (Jinglong Co., Beijing, China) according to 1 a modified Hummers method : 120 mL 98 wt% H2SO4 was poured into a beaker containing a mixture of 5 g natural graphite and 2.5 g NaNO3, and then the mixture was stirred in an ice bath for 30 min. 15 g KMnO4 was added slowly into the mixture, which was allowed to react for 2 h at a temperature no more than 20°C. Then, the temperature was risen to 35°C, and the reaction was performed for another 2 h. After that, the reactant mixture was poured slowly into 360 mL distilled water under violent stirring condition so as to control the temperature no more than 90°C, followed by further reaction at 75°C for 1 h. -
Sections-A, B and C
Science IX Sample Paper 7 Solved www.rava.org.in CLASS IX (2019-20) SCIENCE (CODE 086) SAMPLE PAPER-7 Time : 3 Hours Maximum Marks : 80 General Instructions : (i) The question paper comprises of three sections-A, B and C. Attempt all the sections. (ii) All questions are compulsory. (iii) Internal choice is given in each sections. (iv) All questions in Section A are one-mark questions comprising MCQ, VSA type and assertion-reason type questions. They are to be answered in one word or in one sentence. (v) All questions in Section B are three-mark, short-answer type questions. These are to be answered in about 50-60 words each. (vi) All questions in Section C are five-mark, long-answer type questions. These are to be answered in about 80-90 words each. (vii) This question paper consists of a total of 30 questions. 6. Who proposed the fluid mosaic model of protoplasm? [1] Section - A (a) Singer and Nicolson (b) Watson and Crick (c) Robert Hook (d) Robert Brown 1. Which of the following actions a force can do? [1] (a) Can move a stationary object. Ans : (a) Singer and Nicolson. (b) Can stop a moving object. or (c) Can change the speed of a moving object. Which of the following are complex tissues? (d) All of the above. (a) Xylem and Phloem Ans : (d) All of the above (b) Collenchyma and Sclerenchyma (c) Parenchyma and Collenchyma 2. Ozone layer protects us from which one of the (d) Xylem and Parenchyma following? [1] (a) X- rays. -
Catalytic Pyrolysis of Plastic Wastes for the Production of Liquid Fuels for Engines
Electronic Supplementary Material (ESI) for RSC Advances. This journal is © The Royal Society of Chemistry 2019 Supporting information for: Catalytic pyrolysis of plastic wastes for the production of liquid fuels for engines Supattra Budsaereechaia, Andrew J. Huntb and Yuvarat Ngernyen*a aDepartment of Chemical Engineering, Faculty of Engineering, Khon Kaen University, Khon Kaen, 40002, Thailand. E-mail:[email protected] bMaterials Chemistry Research Center, Department of Chemistry and Center of Excellence for Innovation in Chemistry, Faculty of Science, Khon Kaen University, Khon Kaen, 40002, Thailand Fig. S1 The process for pelletization of catalyst PS PS+bentonite PP ) t e PP+bentonite s f f o % ( LDPE e c n a t t LDPE+bentonite s i m s n HDPE a r T HDPE+bentonite Gasohol 91 Diesel 4000 3500 3000 2500 2000 1500 1000 500 Wavenumber (cm-1) Fig. S2 FTIR spectra of oil from pyrolysis of plastic waste type. Table S1 Compounds in oils (%Area) from the pyrolysis of plastic wastes as detected by GCMS analysis PS PP LDPE HDPE Gasohol 91 Diesel Compound NC C Compound NC C Compound NC C Compound NC C 1- 0 0.15 Pentane 1.13 1.29 n-Hexane 0.71 0.73 n-Hexane 0.65 0.64 Butane, 2- Octane : 0.32 Tetradecene methyl- : 2.60 Toluene 7.93 7.56 Cyclohexane 2.28 2.51 1-Hexene 1.05 1.10 1-Hexene 1.15 1.16 Pentane : 1.95 Nonane : 0.83 Ethylbenzen 15.07 11.29 Heptane, 4- 1.81 1.68 Heptane 1.26 1.35 Heptane 1.22 1.23 Butane, 2,2- Decane : 1.34 e methyl- dimethyl- : 0.47 1-Tridecene 0 0.14 2,2-Dimethyl- 0.63 0 1-Heptene 1.37 1.46 1-Heptene 1.32 1.35 Pentane, -
Molecular Dynamics Simulation Studies of Physico of Liquid
MD Simulation of Liquid Pentane Isomers Bull. Korean Chem. Soc. 1999, Vol. 20, No. 8 897 Molecular Dynamics Simulation Studies of Physico Chemical Properties of Liquid Pentane Isomers Seng Kue Lee and Song Hi Lee* Department of Chemistry, Kyungsung University, Pusan 608-736, Korea Received January 15, 1999 We have presented the thermodynamic, structural and dynamic properties of liquid pentane isomers - normal pentane, isopentane, and neopentane - using an expanded collapsed atomic model. The thermodynamic prop erties show that the intermolecular interactions become weaker as the molecular shape becomes more nearly spherical and the surface area decreases with branching. The structural properties are well predicted from the site-site radial, the average end-to-end distance, and the root-mean-squared radius of gyration distribution func tions. The dynamic properties are obtained from the time correlation functions - the mean square displacement (MSD), the velocity auto-correlation (VAC), the cosine (CAC), the stress (SAC), the pressure (PAC), and the heat flux auto-correlation (HFAC) functions - of liquid pentane isomers. Two self-diffusion coefficients of liq uid pentane isomers calculated from the MSD's via the Einstein equation and the VAC's via the Green-Kubo relation show the same trend but do not coincide with the branching effect on self-diffusion. The rotational re laxation time of liquid pentane isomers obtained from the CAC's decreases monotonously as branching increas es. Two kinds of viscosities of liquid pentane isomers calculated from the SAC and PAC functions via the Green-Kubo relation have the same trend compared with the experimental results. The thermal conductivity calculated from the HFAC increases as branching increases. -
Synthetic Turf Scientific Advisory Panel Meeting Materials
California Environmental Protection Agency Office of Environmental Health Hazard Assessment Synthetic Turf Study Synthetic Turf Scientific Advisory Panel Meeting May 31, 2019 MEETING MATERIALS THIS PAGE LEFT BLANK INTENTIONALLY Office of Environmental Health Hazard Assessment California Environmental Protection Agency Agenda Synthetic Turf Scientific Advisory Panel Meeting May 31, 2019, 9:30 a.m. – 4:00 p.m. 1001 I Street, CalEPA Headquarters Building, Sacramento Byron Sher Auditorium The agenda for this meeting is given below. The order of items on the agenda is provided for general reference only. The order in which items are taken up by the Panel is subject to change. 1. Welcome and Opening Remarks 2. Synthetic Turf and Playground Studies Overview 4. Synthetic Turf Field Exposure Model Exposure Equations Exposure Parameters 3. Non-Targeted Chemical Analysis Volatile Organics on Synthetic Turf Fields Non-Polar Organics Constituents in Crumb Rubber Polar Organic Constituents in Crumb Rubber 5. Public Comments: For members of the public attending in-person: Comments will be limited to three minutes per commenter. For members of the public attending via the internet: Comments may be sent via email to [email protected]. Email comments will be read aloud, up to three minutes each, by staff of OEHHA during the public comment period, as time allows. 6. Further Panel Discussion and Closing Remarks 7. Wrap Up and Adjournment Agenda Synthetic Turf Advisory Panel Meeting May 31, 2019 THIS PAGE LEFT BLANK INTENTIONALLY Office of Environmental Health Hazard Assessment California Environmental Protection Agency DRAFT for Discussion at May 2019 SAP Meeting. Table of Contents Synthetic Turf and Playground Studies Overview May 2019 Update ..... -
Quantitation of Hydrocarbons in Vehicle Exhaust and Ambient Air
QUANTITATION OF HYDROCARBONS IN VEHICLE EXHAUST AND AMBIENT AIR by Randall Bramston-Cook Lotus Consulting 5781 Campo Walk, Long Beach, California 90803 Presented at EPA Measurement of Toxic and Related Air Pollutants Conference, Cary, North Caolina, September 1, 1998 Copyright 1998 Lotus Flower, Inc. QUANTITATION OF HYDROCARBONS IN VEHICLE EXHAUST AND AMBIENT AIR Randall Bramston-Cook Lotus Consulting 5781 Campo Walk, Long Beach, California 90803 ABSTRACT Ironically, one of the most complex analyses in gas chromatography involves the simplest computation to generate concentrations. The difficult determination of hydrocarbons in vehicle exhaust and ambient air involves separation of over 200 compounds, requires cryogenic concentration to bring expected concentrations into a detectable range, and mandates usage of multiple columns and intricate valving. Yet, quantitation of these hydrocarbons can be calibrated with only one or two component standards and a simple mathematical operation. Requirements for meeting this goal include: (1) even detector responses for all hydrocarbons from ethane to n-tridecane (including olefins and aromatics), (2) accurate and reproducible measure of the sample injection volumes, (3) maximizing trap, column and detector performances, and (4) minimizing sample carry-over. Importance of these factors and how they can be implemented in routine measurements are presented with examples from vehicle exhaust and ambient air analyses. TEXT Hydrocarbons remain a major pollutant in our atmosphere. Much of the problem generated is from incomplete combustion and unburned fuel in vehicle exhaust. Accurate measure of atmospheric and exhaust levels for hydrocarbons is on-going in many facilities in the world. This analysis is undoubtedly one of the most complex in chromatography due to large number of individual hydrocarbon components found, the low levels required to be measured, and high concentrations of potential inferences to the measuring process. -
Safety Data Sheet Acc
Page 1/8 Safety Data Sheet acc. to OSHA HCS Printing date 03/18/2019 Reviewed on 03/18/2019 1 Identification · Product identifier · Product Name: EVEN ALK (C16-C36) · Part Number: ENC-EVEN-1K · Application of the substance / the mixture Certified Reference Material · Details of the supplier of the safety data sheet · Manufacturer/Supplier: SPEX CertiPrep, LLC. 203 Norcross Ave, Metuchen, NJ 08840 USA · Information department: product safety department · Emergency telephone number: Emergency Phone Number (24 hours) CHEMTREC (800-424-9300) Outside US: 703-527-3887 2 Hazard(s) identification · Classification of the substance or mixture GHS02 Flame Flam. Liq. 2 H225 Highly flammable liquid and vapor. GHS08 Health hazard Carc. 2 H351 Suspected of causing cancer. GHS07 Acute Tox. 4 H302 Harmful if swallowed. · Label elements · GHS label elements The product is classified and labeled according to the Globally Harmonized System (GHS). · Hazard pictograms GHS02 GHS07 GHS08 · Signal word Danger · Hazard-determining components of labeling: dichloromethane · Hazard statements H225 Highly flammable liquid and vapor. H302 Harmful if swallowed. H351 Suspected of causing cancer. · Precautionary statements Keep away from heat/sparks/open flames/hot surfaces. - No smoking. Use explosion-proof electrical/ventilating/lighting/equipment. Wear protective gloves/protective clothing/eye protection/face protection. If on skin (or hair): Take off immediately all contaminated clothing. Rinse skin with water/shower. Store locked up. Dispose of contents/container in accordance with local/regional/national/international regulations. · Classification system: · NFPA ratings (scale 0 - 4) Health = 1 3 Fire = 3 1 0 Reactivity = 0 (Contd. on page 2) US 48.1.17.1 Page 2/8 Safety Data Sheet acc. -
Managing Health Risks of Solvent
BEST PRACTICE GUIDELINES Managing the Health Risks of Solvent Exposure Managing the Health Risks of Solvent Exposure September 2015 CONTENTS 1 Introduction 5 1.1 SCOPE AND OBJECTIVES 5 2 The regulatory landscape 6 2.1 CAD 6 2.2 REACH 6 2.3 CLP 8 3 Health effects and properties of solvents 9 3.1 EFFECTS OF SOLVENTS VIA SKIN AND EYE CONTACT 9 3.2 EFFECTS VIA INHALATION 10 3.3 CLASSIFICATION AND LABELLING OF SOLVENTS 10 3.4 HAZARD AND RISK 11 4 Exposure scenarios (es) - Basic principles 12 4.1 DEVELOPING AN ES 13 4.2 SOLVENTS MANUFACTURERS MEET THE CHALLENGE OF DEVELOPING ES 13 5 The solvents industry’s approach to REACH 14 5.1 NAMING CONVENTION FOR HYDROCARBON SOLVENTS 14 5.2 DEVELOPMENT OF GENERIC EXPOSURE SCENARIOS (GES) 14 5.2.1 THE USE DESCRIPTOR SYSTEM (UDS) (REF 15) 15 5.2.2 THE ESIG GES LIBRARY 15 6 Exposure limit values for solvents 17 6.1 OELs AND DNELs 17 6.2 INDUSTRY-BASED OELs FOR HYDROCARBON SOLVENTS 18 ManagingFlammability: the Health Risks A safety of Solvent guide Exposurefor users 7 Responsibilities of solvent users 19 8 Role of solvent vapour monitoring 23 9 Key messages 24 10 List of acronyms 25 11 References 28 APPENDIX 1 Overview of control approaches for solvents required by CAD 29 APPENDIX 2 CLP Classification phrases for solvents 30 APPENDIX 3 Hydrocarbon solvents registered under REACH - key data 31 APPENDIX 4 Oxygenated solvents registered under REACH - key data 43 APPENDIX 5 Example ES for a hydrocarbon solvent containing N-Hexane (>5-80%) 50 APPENDIX 6 List of common solvent uses matched to ESIG generic exposure scenario (GES) title with examples of relevant solvent types 53 APPENDIX 7 Mixtures 62 3 Managing the Health Risks of Solvent Exposure DISCLAIMER The information contained in this paper is intended for guidance only and whilst the information is provided in utmost good faith and has been based on the best information currently available, it is to be relied upon at the user’s own risk. -
The Enthalpy of Formation of Organic Compounds with “Chemical Accuracy”
chemengineering Article Group Contribution Revisited: The Enthalpy of Formation of Organic Compounds with “Chemical Accuracy” Robert J. Meier Pro-Deo Consultant, 52525 Heinsberg, North-Rhine Westphalia, Germany; [email protected] Abstract: Group contribution (GC) methods to predict thermochemical properties are of eminent importance to process design. Compared to previous works, we present an improved group contri- bution parametrization for the heat of formation of organic molecules exhibiting chemical accuracy, i.e., a maximum 1 kcal/mol (4.2 kJ/mol) difference between the experiment and model, while, at the same time, minimizing the number of parameters. The latter is extremely important as too many parameters lead to overfitting and, therewith, to more or less serious incorrect predictions for molecules that were not within the data set used for parametrization. Moreover, it was found to be important to explicitly account for common chemical knowledge, e.g., geminal effects or ring strain. The group-related parameters were determined step-wise: first, alkanes only, and then only one additional group in the next class of molecules. This ensures unique and optimal parameter values for each chemical group. All data will be made available, enabling other researchers to extend the set to other classes of molecules. Keywords: enthalpy of formation; thermodynamics; molecular modeling; group contribution method; quantum mechanical method; chemical accuracy; process design Citation: Meier, R.J. Group Contribution Revisited: The Enthalpy of Formation of Organic Compounds with “Chemical Accuracy”. 1. Introduction ChemEngineering 2021, 5, 24. To understand chemical reactivity and/or chemical equilibria, knowledge of thermo- o https://doi.org/10.3390/ dynamic properties such as gas-phase standard enthalpy of formation DfH gas is a necessity. -
Adsorption of Light Alkanes on the Surface of Substrates with Varying Symmetry and Composition
University of Tennessee, Knoxville TRACE: Tennessee Research and Creative Exchange Doctoral Dissertations Graduate School 5-2018 Adsorption of Light Alkanes on the Surface of Substrates with Varying Symmetry and Composition Nicholas Allan Strange University of Tennessee Follow this and additional works at: https://trace.tennessee.edu/utk_graddiss Recommended Citation Strange, Nicholas Allan, "Adsorption of Light Alkanes on the Surface of Substrates with Varying Symmetry and Composition. " PhD diss., University of Tennessee, 2018. https://trace.tennessee.edu/utk_graddiss/4967 This Dissertation is brought to you for free and open access by the Graduate School at TRACE: Tennessee Research and Creative Exchange. It has been accepted for inclusion in Doctoral Dissertations by an authorized administrator of TRACE: Tennessee Research and Creative Exchange. For more information, please contact [email protected]. To the Graduate Council: I am submitting herewith a dissertation written by Nicholas Allan Strange entitled "Adsorption of Light Alkanes on the Surface of Substrates with Varying Symmetry and Composition." I have examined the final electronic copy of this dissertation for form and content and recommend that it be accepted in partial fulfillment of the equirr ements for the degree of Doctor of Philosophy, with a major in Chemistry. John Z. Larese, Major Professor We have read this dissertation and recommend its acceptance: Takeshi Egami, Jeffrey D. Kovac, Brian K. Long Accepted for the Council: Dixie L. Thompson Vice Provost and Dean of the Graduate School (Original signatures are on file with official studentecor r ds.) Adsorption of Light Alkanes on the Surface of Substrates with Varying Symmetry and Composition A Dissertation Presented for the Doctor of Philosophy Degree The University of Tennessee, Knoxville Nicholas Allan Strange May 2018 Copyright © 2018 by Nicholas A. -
Measurements of Higher Alkanes Using NO Chemical Ionization in PTR-Tof-MS
Atmos. Chem. Phys., 20, 14123–14138, 2020 https://doi.org/10.5194/acp-20-14123-2020 © Author(s) 2020. This work is distributed under the Creative Commons Attribution 4.0 License. Measurements of higher alkanes using NOC chemical ionization in PTR-ToF-MS: important contributions of higher alkanes to secondary organic aerosols in China Chaomin Wang1,2, Bin Yuan1,2, Caihong Wu1,2, Sihang Wang1,2, Jipeng Qi1,2, Baolin Wang3, Zelong Wang1,2, Weiwei Hu4, Wei Chen4, Chenshuo Ye5, Wenjie Wang5, Yele Sun6, Chen Wang3, Shan Huang1,2, Wei Song4, Xinming Wang4, Suxia Yang1,2, Shenyang Zhang1,2, Wanyun Xu7, Nan Ma1,2, Zhanyi Zhang1,2, Bin Jiang1,2, Hang Su8, Yafang Cheng8, Xuemei Wang1,2, and Min Shao1,2 1Institute for Environmental and Climate Research, Jinan University, 511443 Guangzhou, China 2Guangdong-Hongkong-Macau Joint Laboratory of Collaborative Innovation for Environmental Quality, 511443 Guangzhou, China 3School of Environmental Science and Engineering, Qilu University of Technology (Shandong Academy of Sciences), 250353 Jinan, China 4State Key Laboratory of Organic Geochemistry and Guangdong Key Laboratory of Environmental Protection and Resources Utilization, Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, 510640 Guangzhou, China 5State Joint Key Laboratory of Environmental Simulation and Pollution Control, College of Environmental Sciences and Engineering, Peking University, 100871 Beijing, China 6State Key Laboratory of Atmospheric Boundary Physics and Atmospheric Chemistry, Institute of Atmospheric Physics, Chinese