Vapor Pressures and Vaporization Enthalpies of the N-Alkanes from 2 C21 to C30 at T ) 298.15 K by Correlation Gas Chromatography
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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. -
Physical Model for Vaporization
Physical model for vaporization Jozsef Garai Department of Mechanical and Materials Engineering, Florida International University, University Park, VH 183, Miami, FL 33199 Abstract Based on two assumptions, the surface layer is flexible, and the internal energy of the latent heat of vaporization is completely utilized by the atoms for overcoming on the surface resistance of the liquid, the enthalpy of vaporization was calculated for 45 elements. The theoretical values were tested against experiments with positive result. 1. Introduction The enthalpy of vaporization is an extremely important physical process with many applications to physics, chemistry, and biology. Thermodynamic defines the enthalpy of vaporization ()∆ v H as the energy that has to be supplied to the system in order to complete the liquid-vapor phase transformation. The energy is absorbed at constant pressure and temperature. The absorbed energy not only increases the internal energy of the system (U) but also used for the external work of the expansion (w). The enthalpy of vaporization is then ∆ v H = ∆ v U + ∆ v w (1) The work of the expansion at vaporization is ∆ vw = P ()VV − VL (2) where p is the pressure, VV is the volume of the vapor, and VL is the volume of the liquid. Several empirical and semi-empirical relationships are known for calculating the enthalpy of vaporization [1-16]. Even though there is no consensus on the exact physics, there is a general agreement that the surface energy must be an important part of the enthalpy of vaporization. The vaporization diminishes the surface energy of the liquid; thus this energy must be supplied to the system. -
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. -
Section 13. Disposal Considerations Disposal Methods : the Generation of Waste Should Be Avoided Or Minimized Wherever Possible
SAFETY DATA SHEET Flammable Liquid Mixture: Docosane / Dodecane / Dotriacontane / Eicosane / Heptane / Hexacosane / Hexadecane / Hexane / N-Decane / N-Nonane / N- Octadecane / Octacosane / Octane / Tetracosane / Tetradecane / Triacontane Section 1. Identification GHS product identifier : Flammable Liquid Mixture: Docosane / Dodecane / Dotriacontane / Eicosane / Heptane / Hexacosane / Hexadecane / Hexane / N-Decane / N-Nonane / N-Octadecane / Octacosane / Octane / Tetracosane / Tetradecane / Triacontane Other means of : Not available. identification Product use : Synthetic/Analytical chemistry. SDS # : 019981 Supplier's details : Airgas USA, LLC and its affiliates 259 North Radnor-Chester Road Suite 100 Radnor, PA 19087-5283 1-610-687-5253 24-hour telephone : 1-866-734-3438 Section 2. Hazards identification OSHA/HCS status : This material is considered hazardous by the OSHA Hazard Communication Standard (29 CFR 1910.1200). Classification of the : FLAMMABLE LIQUIDS - Category 1 substance or mixture SKIN CORROSION/IRRITATION - Category 2 SERIOUS EYE DAMAGE/ EYE IRRITATION - Category 2A TOXIC TO REPRODUCTION (Fertility) - Category 2 TOXIC TO REPRODUCTION (Unborn child) - Category 2 SPECIFIC TARGET ORGAN TOXICITY (SINGLE EXPOSURE) (Narcotic effects) - Category 3 SPECIFIC TARGET ORGAN TOXICITY (REPEATED EXPOSURE) - Category 2 AQUATIC HAZARD (ACUTE) - Category 2 AQUATIC HAZARD (LONG-TERM) - Category 1 GHS label elements Hazard pictograms : Signal word : Danger Hazard statements : Extremely flammable liquid and vapor. May form explosive mixtures in Air. Causes serious eye irritation. Causes skin irritation. Suspected of damaging fertility or the unborn child. May cause drowsiness and dizziness. May cause damage to organs through prolonged or repeated exposure. Very toxic to aquatic life with long lasting effects. Precautionary statements General : Read label before use. Keep out of reach of children. If medical advice is needed, have product container or label at hand. -
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 ..... -
Sampling Dynamics for Volatile Organic Compounds Using Headspace Solid-Phase Microextraction Arrow for Microbiological Samples
separations Communication Sampling Dynamics for Volatile Organic Compounds Using Headspace Solid-Phase Microextraction Arrow for Microbiological Samples Kevin E. Eckert 1, David O. Carter 2 and Katelynn A. Perrault 1,* 1 Laboratory of Forensic and Bioanalytical Chemistry, Forensic Sciences Unit, Division of Natural Sciences and Mathematics, Chaminade University of Honolulu, 3140 Waialae Ave., Honolulu, HI 96816, USA; [email protected] 2 Laboratory of Forensic Taphonomy, Forensic Sciences Unit, Division of Natural Sciences and Mathematics, Chaminade University of Honolulu, 3140 Waialae Avenue, Honolulu, HI 96816, USA; [email protected] * Correspondence: [email protected] Received: 10 August 2018; Accepted: 27 August 2018; Published: 10 September 2018 Abstract: Volatile organic compounds (VOCs) are monitored in numerous fields using several commercially-available sampling options. Sorbent-based sampling techniques, such as solid-phase microextraction (SPME), provide pre-concentration and focusing of VOCs prior to gas chromatography–mass spectrometry (GC–MS) analysis. This study investigated the dynamics of SPME Arrow, which exhibits an increased sorbent phase volume and improved durability compared to traditional SPME fibers. A volatile reference mixture (VRM) and saturated alkanes mix (SAM) were used to investigate optimal parameters for microbiological VOC profiling in combination with GC–MS analysis. Fiber type, extraction time, desorption time, carryover, and reproducibility were characterized, in addition to a comparison with traditional SPME fibers. The developed method was then applied to longitudinal monitoring of Bacillus subtilis cultures, which represents a ubiquitous microbe in medical, forensic, and agricultural applications. The carbon wide range/polydimethylsiloxane (CWR/PDMS) fiber was found to be optimal for the range of expected VOCs in microbiological profiling, and a statistically significant increase in the majority of VOCs monitored was observed. -
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. -
Certificate of Analysis
National Institute of Standards & Technology Certificate of Analysis Standard Reference Material 2285 Ignitable Liquids Test Mixture This Standard Reference Material (SRM) is intended primarily for use in the calibration of chromatographic instrumentation used for the classification of an ignitable liquid residue. SRM 2285 is a solution of 15 compounds, including even carbon number aliphatic hydrocarbons from hexane to tetracosane, toluene, p-xylene, 2-ethyltoluene, 3-ethyltoluene, and 1,2,4-trimethylbenzene in methylene chloride. A unit of SRM 2285 consists of five 2 mL ampoules, each containing approximately 1.2 mL of solution. Certified Mass Fraction Values: The certified values for the 15 constituents are given in Table 1. These values are based on results obtained from the gravimetric preparation of this solution and from the analytical results determined by using gas chromatography. A NIST certified value is a value for which NIST has the highest confidence in its accuracy in that all known or suspected sources of uncertainty have been investigated or taken into account [1]. Information Concentration Values: Information values for concentrations, expressed as percent volume fractions, are provided in Table 2 for the components. An information value is considered to be a value that will be of interest and use to the SRM user, but insufficient information is available to assess adequately the uncertainty associated with the value or only a limited number of analyses were performed [1]. Expiration of Certification: The certification of SRM 2285 is valid, within the measurement uncertainty specified, until 30 March 2023, provided the SRM is handled and stored in accordance with the instructions given in this certificate (see “Instructions for Handling, Storage, and Use”). -
Vapor Pressures and Vaporization Enthalpies of the N-Alkanes from C31 to C38 at T ) 298.15 K by Correlation Gas Chromatography
BATCH: je3a29 USER: ckt69 DIV: @xyv04/data1/CLS_pj/GRP_je/JOB_i03/DIV_je030236t DATE: March 15, 2004 1 Vapor Pressures and Vaporization Enthalpies of the n-Alkanes from 2 C31 to C38 at T ) 298.15 K by Correlation Gas Chromatography 3 James S. Chickos* and William Hanshaw 4 Department of Chemistry and Biochemistry, University of MissourisSt. Louis, St. Louis, Missouri 63121, USA 5 6 The temperature dependence of gas-chromatographic retention times for henitriacontane to octatriacontane 7 is reported. These data are used in combination with other literature values to evaluate the vaporization 8 enthalpies and vapor pressures of these n-alkanes from T ) 298.15 to 575 K. The vapor pressure and 9 vaporization enthalpy results obtained are compared with existing literature data where possible and 10 found to be internally consistent. The vaporization enthalpies and vapor pressures obtained for the 11 n-alkanes are also tested directly and through the use of thermochemical cycles using literature values 12 for several polyaromatic hydrocarbons. Sublimation enthalpies are also calculated for hentriacontane to 13 octatriacontane by combining vaporization enthalpies with temperature adjusted fusion enthalpies. 14 15 Introduction vaporization enthalpies of C21 to C30 to include C31 to C38. 54 The vapor pressures and vaporization enthalpies of these 55 16 Polycyclic aromatic hydrocarbons (PAHs) are important larger n-alkanes have been evaluated using the technique 56 17 environmental contaminants, many of which exhibit very of correlation gas chromatography. This technique relies 57 18 low vapor pressures. In the gas phase, they exist mainly entirely on the use of standards in assessment. Standards 58 19 sorbed to aerosol particles.