The Crystalline Structures of the Odd Alkanes Pentane, Heptane
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A Low Temperature Structure of Nonane-1,9-Diaminium Chloride Chloroacetate: Hydroxyacetic Acid (1:1)
J Chem Crystallogr (2011) 41:703–707 DOI 10.1007/s10870-010-9957-6 ORIGINAL PAPER A Low Temperature Structure of Nonane-1,9-Diaminium Chloride Chloroacetate: Hydroxyacetic Acid (1:1) Agnieszka Paul • Maciej Kubicki Received: 24 February 2010 / Accepted: 31 December 2010 / Published online: 14 January 2011 Ó The Author(s) 2011. This article is published with open access at Springerlink.com Abstract The crystal structure of nonane-1,9-diaminium protons and to form salts with both, organic and inorganic chloride chloroacetate–hydroxyacetic acid (1:1) was deter- acids, together with a significant flexibility of the chain mined by X-ray diffraction at 100(1)K. The asymmetric fragment and tendency towards creation of the highly unit is composed of diaminium dication, chloroacetate and symmetric networks, can be used in so-called crystal chloride anions, and neutral hydroxyacetic acid molecule. engineering [2], i.e. in designing new materials with The aliphatic chain of 1,9-diamine is fully extended and it expected features. Such a predictable motifs in the crystal deviates only slightly from the perfect all-trans confor- structures, giving rise to a layer structure, were already mation. The two acidic residues are also nearly planar. The investigated in the series of hexane-1,6-diamine and layer structure is obtained as a consequence of hydrogen butane-1,4-diamine salts [3, 4]. bond interactions of a different lengths, with N–H and O–H Only five structures deposited in the Cambridge Struc- groups playing the role of donors and oxygen atoms and tural Database [5] (no multiple determinations, herein and chloride cations as acceptors. -
SAFETY DATA SHEET 1,9-Dibromo-Nonane-2,8-Dione According to Regulation (EC) No 1907/2006, Annex II, As Amended
Revision date: 03/01/2020 Revision: 1 SAFETY DATA SHEET 1,9-Dibromo-nonane-2,8-dione According to Regulation (EC) No 1907/2006, Annex II, as amended. Commission Regulation (EU) No 2015/830 of 28 May 2015. SECTION 1: Identification of the substance/mixture and of the company/undertaking 1.1. Product identifier Product name 1,9-Dibromo-nonane-2,8-dione Product number FD173289 CAS number 91492-76-1 1.2. Relevant identified uses of the substance or mixture and uses advised against Identified uses Laboratory reagent. Manufacture of substances. Research and development. 1.3. Details of the supplier of the safety data sheet Supplier Carbosynth Ltd 8&9 Old Station Business Park Compton Berkshire RG20 6NE UK +44 1635 578444 +44 1635 579444 [email protected] 1.4. Emergency telephone number Emergency telephone +44 7887 998634 SECTION 2: Hazards identification 2.1. Classification of the substance or mixture Classification (EC 1272/2008) Physical hazards Not Classified Health hazards Not Classified Environmental hazards Not Classified Additional information Caution. Not fully tested. 2.2. Label elements Hazard statements NC Not Classified 2.3. Other hazards No data available. SECTION 3: Composition/information on ingredients 3.1. Substances Product name 1,9-Dibromo-nonane-2,8-dione 1/8 Revision date: 03/01/2020 Revision: 1 1,9-Dibromo-nonane-2,8-dione CAS number 91492-76-1 Chemical formula C₉H₁₄Br₂O₂ SECTION 4: First aid measures 4.1. Description of first aid measures General information Get medical advice/attention if you feel unwell. Inhalation Remove person to fresh air and keep comfortable for breathing. -
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. -
Chapter 2: Alkanes Alkanes from Carbon and Hydrogen
Chapter 2: Alkanes Alkanes from Carbon and Hydrogen •Alkanes are carbon compounds that contain only single bonds. •The simplest alkanes are hydrocarbons – compounds that contain only carbon and hydrogen. •Hydrocarbons are used mainly as fuels, solvents and lubricants: H H H H H H H H H H H H C H C C H C C C C H H C C C C C H H H C C H H H H H H CH2 H CH3 H H H H CH3 # of carbons boiling point range Use 1-4 <20 °C fuel (gasses such as methane, propane, butane) 5-6 30-60 solvents (petroleum ether) 6-7 60-90 solvents (ligroin) 6-12 85-200 fuel (gasoline) 12-15 200-300 fuel (kerosene) 15-18 300-400 fuel (heating oil) 16-24 >400 lubricating oil, asphalt Hydrocarbons Formula Prefix Suffix Name Structure H CH4 meth- -ane methane H C H H C H eth- -ane ethane 2 6 H3C CH3 C3H8 prop- -ane propane C4H10 but- -ane butane C5H12 pent- -ane pentane C6H14 hex- -ane hexane C7H16 hept- -ane heptane C8H18 oct- -ane octane C9H20 non- -ane nonane C10H22 dec- -ane decane Hydrocarbons Formula Prefix Suffix Name Structure H CH4 meth- -ane methane H C H H H H C2H6 eth- -ane ethane H C C H H H H C H prop- -ane propane 3 8 H3C C CH3 or H H H C H 4 10 but- -ane butane H3C C C CH3 or H H H C H 4 10 but- -ane butane? H3C C CH3 or CH3 HydHrydorcocaarrbobnos ns Formula Prefix Suffix Name Structure H CH4 meth- -ane methane H C H H H H C2H6 eth- -ane ethane H C C H H H H C3H8 prop- -ane propane H3C C CH3 or H H H C H 4 10 but- -ane butane H3C C C CH3 or H H H C H 4 10 but- -ane iso-butane H3C C CH3 or CH3 HydHrydoroccarbrobnsons Formula Prefix Suffix Name Structure H H -
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 -
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'() -
Safety Data Sheet
SAFETY DATA SHEET Flammable Liquid Mixture: Docosane / Dodecane / Hexadecane / Hexane / N-Decane / N-Heptane / N-Nonane / N-Octadecane / N-Octane / N-Tridecane / Octacosane / Tetracosane / Tetradecane / Tricontane Section 1. Identification GHS product identifier : Flammable Liquid Mixture: Docosane / Dodecane / Hexadecane / Hexane / N-Decane / N-Heptane / N-Nonane / N-Octadecane / N-Octane / N-Tridecane / Octacosane / Tetracosane / Tetradecane / Tricontane Other means of : Not available. identification Product use : Synthetic/Analytical chemistry. SDS # : 018776 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) (Respiratory tract irritation) - Category 3 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. May cause respiratory 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. -
Organic Nomenclature: Naming Organic Molecules
Organic Nomenclature: Naming Organic Molecules Mild Vegetable Alkali Aerated Alkali What’s in a name? Tartarin Glauber's Alkahest Alkahest of Van Helmot Fixed Vegetable Alkali Russian Pot Ash Cendres Gravellees Alkali Mild Vegetable Oil of Tartar Pearl Ash Tartar Alkahest of Reapour K2CO3 Alkali of Reguline Caustic Sal Juniperi Potassium Carbonate Ash ood Alkali of Wine Lees Salt of Tachenius W Fixed Sal Tartari Sal Gentianae Alkali Salt German Ash Salt of Wormwood Cineres Clavellati Sal Guaiaci exSal Ligno Alkanus Vegetablis IUPAC Rules for naming organic molecules International Union of Pure and Applied Chemists 3 Name Molecular Prefix Formula Methane CH4 Meth Ethane C2H6 Eth Alkanes Propane C3H8 Prop Butane C4H10 But CnH2n+2 Pentane C5H12 Pent Hexane C6H14 Hex Heptane C7H16 Hept Octane C8H18 Oct Nonane C9H20 Non Decane C10H22 Dec 4 Structure of linear alkanes propane butane pentane hexane heptane octane nonane decane 5 Constitutional Isomers: molecules with same molecular formula but differ in the way in which the atoms are connected to each other 6 Physical properties of constiutional isomers 7 Isomers n # of isomers 1 1 2 1 The more carbons in a 3 1 molecule, the more 4 2 possible ways to put 5 3 them together. 6 5 7 9 8 18 9 35 10 75 15 4,347 25 36,797,588 8 Naming more complex molecules hexane C6H14 9 Naming more complex molecules Step 1: identify the longest continuous linear chain: this will be the root name: this is the root name 2 4 6 longest chain = 6 (hexane) 1 3 5 2 4 3 4 3 2 2 1 5 4 1 3 5 correct 1 incorrect longest chain = 5 (pentane) longest chain = 5 (pentane) 1 3 1 2 2 3 4 4 longest chain = 4 (butane) longest chain = 4 (butane) 10 Naming more complex molecules Step 2: identify all functional group (the groups not part of the “main chain”) CH3 2 4 4 3 2 1 5 1 3 5 CH3 main chain: pentane main chain: pentane CH3 1 3 1 2 2 3 4 4 CH3 CH3 CH3 main chain: butane main chain: butane 11 Alkyl groups: fragments of alkanes H H empty space (point where it H C H H C attaches to something else) H H methane methyl CH4 CH3 12 More generally.. -
Modular and Selective Biosynthesis of Gasoline-Range Alkanes
Modular and selective biosynthesis of gasoline-range alkanes The MIT Faculty has made this article openly available. Please share how this access benefits you. Your story matters. Citation Sheppard, Micah J., Aditya M. Kunjapur, and Kristala L.J. Prather. “Modular and Selective Biosynthesis of Gasoline-Range Alkanes.” Metabolic Engineering 33 (January 2016): 28–40. As Published http://dx.doi.org/10.1016/j.ymben.2015.10.010 Publisher Elsevier Version Author's final manuscript Citable link http://hdl.handle.net/1721.1/108077 Terms of Use Creative Commons Attribution-NonCommercial-NoDerivs License Detailed Terms http://creativecommons.org/licenses/by-nc-nd/4.0/ 1 Title: Modular and selective biosynthesis of gasoline-range alkanes 2 Authors: Micah J. Sheppard1, 2†, Aditya M. Kunjapur1, 3†, Kristala L. J. Prather1, 3* 3 Affiliations: 4 1. Department of Chemical Engineering, Massachusetts Institute of Technology, Cambridge, MA 02139, 5 USA 6 2. Present Address: Ginkgo BioWorks, 27 Drydock Avenue, 8th floor, Boston, Massachusetts 02210, 7 USA 8 3. Synthetic Biology Engineering Research Center (SynBERC), Massachusetts Institute of Technology, 9 Cambridge, MA 02139, USA 10 11 †These authors contributed equally to this work. 12 * Corresponding author: 13 Department of Chemical Engineering 14 77 Massachusetts Avenue 15 Room E17-504G 16 Cambridge, MA 02139 17 Phone: 617.253.1950 18 Fax: 617.258.5042 19 Email: [email protected] 20 Keywords: alkanes, gasoline, biofuel, E. coli, metabolic engineering, synthetic biology 21 1 22 Abstract: 23 Typical renewable liquid fuel alternatives to gasoline are not entirely compatible with current 24 infrastructure. We have engineered Escherichia coli to selectively produce alkanes found in gasoline 25 (propane, butane, pentane, heptane, and nonane) from renewable substrates such as glucose or glycerol. -
Accuracy and Methodologic Challenges of Volatile Organic Compound–Based Exhaled Breath Tests for Cancer Diagnosis: a Systematic Review and Pooled Analysis
1 Supplementary Online Content Hanna GB, Boshier PR, Markar SR, Romano A. Accuracy and Methodologic Challenges of Volatile Organic Compound–Based Exhaled Breath Tests for Cancer Diagnosis: A Systematic Review and Pooled Analysis. JAMA Oncol. Published online August 16, 2018. doi:10.1001/jamaoncol.2018.2815 Supplement. eTable 1. Search strategy for cancer systematic review eTable 2. Modification of QUADAS-2 assessment tools eTable 3. QUADAS-2 results eTable 6. STARD assessment of each study eTable 7. Summary of factors reported to influence levels of volatile organic compounds within exhaled breath eFigure 1. Risk of bias and applicability concerns using QUADAS-2 eFigure 2. PRISMA flowchart of literature search eTable 4. Details of studies on exhaled volatile organic compounds in cancer eTable 5. Cancer VOCs in exhaled breath and their chemical class. eFigure 3. Chemical classes of VOCs reported in different tumor sites. This supplementary material has been provided by the authors to give readers additional information about their work. © 2018 American Medical Association. All rights reserved. Downloaded From: https://jamanetwork.com/ on 10/01/2021 2 eTable 1. Search strategy for cancer systematic review # Search 1 (cancer or neoplasm* or malignancy).ab. 2 limit 1 to abstracts 3 limit 2 to cochrane library [Limit not valid in Ovid MEDLINE(R),Ovid MEDLINE(R) Daily Update,Ovid MEDLINE(R) In-Process,Ovid MEDLINE(R) Publisher; records were retained] 4 limit 3 to english language 5 limit 4 to human 6 limit 5 to yr="2000 -Current" 7 limit 6 to humans 8 (cancer or neoplasm* or malignancy).ti. 9 limit 8 to abstracts 10 limit 9 to cochrane library [Limit not valid in Ovid MEDLINE(R),Ovid MEDLINE(R) Daily Update,Ovid MEDLINE(R) In-Process,Ovid MEDLINE(R) Publisher; records were retained] 11 limit 10 to english language 12 limit 11 to human 13 limit 12 to yr="2000 -Current" 14 limit 13 to humans 15 7 or 14 16 (volatile organic compound* or VOC* or Breath or Exhaled).ab. -
Polycyclic Aromatic Compound (PAC) Standards and Standard Mixtures Solutions for a Greener World Introduction
Polycyclic Aromatic Compound (PAC) Standards and Standard Mixtures Solutions for a Greener World Introduction Polycyclic Aromatic Compound (PAC) Standards and Standard Mixtures isotope.com 13C-Labeled Polycyclic Aromatic Hydrocarbon (PAH) Standards CIL, in cooperation with Cerilliant Corporation, is pleased to In the chromatogram for the deuterated benzo[a]pyrene, the offer 13C-labeled polycyclic aromatic hydrocarbons (PAHs) as a proton losses at M-2, M-4, etc. are supplemented with proton superior alternative to deuterated standards. Although CIL has losses of M-1, M-3, etc. This represents a loss of deuterons traditionally produced high-quality deuterated PAH analogs, from incompletely deuterated species. As a result, the profile of some analysts have observed back-exchange of proton for the deuterated material does not correspond exactly to that of deuterium under harsh extraction conditions and in certain the unlabeled material. 13C-labeled benzo[a]pyrene, however, matrices. If precise quantitation is required, or complete will match the unlabeled material with the 4 AMU shift being recovery information is needed, the non-exchangeable the only difference between the two profiles. 13C isotope label is the right standard to use. Hydroxy PAHs Deuterium Back-Exchange PAH exposure occurs through ingestion, inhalation, and dermal While analysts have been using deuterated PAH standards contact. In the body, these compounds are predominantly for years, labile deuterons are susceptible to back-exchange. metabolized as epoxides, which are converted to phenol The phenomenon is particularly likely to occur in acidic or (hydroxy) and dihydrodiol derivatives. The hydroxylated catalytic matrices, when the importance of a reliable internal metabolites of the PAHs are excreted in human urine both standard is greatest. -
Airborne Volatile Organic Compounds at an E-Waste Site in Ghana: Source Apportionment, Exposure and Health Risks
Journal of Hazardous Materials 419 (2021) 126353 Contents lists available at ScienceDirect Journal of Hazardous Materials journal homepage: www.elsevier.com/locate/jhazmat Airborne volatile organic compounds at an e-waste site in Ghana: Source apportionment, exposure and health risks Nan Lin a,b, Lawrencia Kwarteng c, Christopher Godwin a, Sydni Warner a, Thomas Robins a, John Arko-Mensah c, Julius N. Fobil c, Stuart Batterman a,* a Department of Environmental Health Sciences, School of Public Health, University of Michigan, Ann Arbor, MI, USA 48109 b Department of Environmental Health, School of Public Health, Shanghai Jiao Tong University, Shanghai, PR China 200025 c Department of Biological, Environmental and Occupational Health Sciences, University of Ghana, School of Public Health, P.O. Box LG13, Accra, Ghana ARTICLE INFO ABSTRACT Editor: Dr. H. Zaher Informal e-waste recycling processes emit various air pollutants. While there are a number of pollutants of concern, little information exists on volatile organic compounds (VOCs) releases at e-waste sites. To assess Keywords: occupational exposures and estimate health risks, we measured VOC levels at the Agbogbloshie e-waste site in E-waste Ghana, the largest e-waste site in Africa, by collecting both fixed-siteand personal samples for analyzing a wide Volatile organic compounds range of VOCs. A total of 54 VOCs were detected, dominated by aliphatic and aromatic compounds. Mean and Source apportionment median concentrations of the total target VOCs were 46 and 37 μg/m3 at the fixedsites, and 485 and 162 μg/m3 Exposure Health risk for the personal samples. Mean and median hazard ratios were 2.1 and 1.4, respectively, and cancer risks were 4.6 × 10-4 and 1.5 × 10-4.