Control Technology Center EPA-600 12-91-061 November 1991

Total Page:16

File Type:pdf, Size:1020Kb

Control Technology Center EPA-600 12-91-061 November 1991 United States Envimnmentai Protection Agency Control Technology Center EPA-600 12-91-061 November 1991 EVALUATION OF VOC EMISSIONS FROM HEATED ROOFING ASPHALT RESEARCH REPORTING SERIES Research reports of the Office of Research and Development. U.S. Environmental Protection Agency, have been grouped into nine series. These nine broad cate- gories were established to facilitate further development and application of en- vironmental technology. Elimination of traditional grouping was consciously planned to foster technology transfer and a maximum interface in related fields. The nine series are: 1. Environmental Health Effects Research 2. Environmental Protection Technology 3. Ecological Research 4. Environmental Monitoring 5. Socioeconomic Environmental Studies 6. Scientific and Technical Assessment Reports (STAR) 7. Interagency Energy-Environment Research and Development 8. "Special" Reports 9. Miscellaneous Reports This report has been assigned to the ENVIRONMENTAL PROTECT1ON TECH- NOLOGY series. This series describes research performed to develop and dem- onstrate instrumentation, equipment, and methodology to repair or prevent en- vironmental degradation from point and non-point sources of pollution. This work provides the new or improved technology required for the control and treatment of pollution sources to meet environmental quality standards. EPA REVIEW NOTICE This report has been reviewed by the U.S. Environmental Protection Agency, and approved for publication. Approval does not signify that the contents necessarily reflect the views and policy of the Agency, nor does mention of trade names or 'commercial products constitute endorsement or recommendation for use. This document is available to the public through the National Technical Informa- tion Service. Springfield. Virginia 22161. EPA-600/2-91-061 November 1991 EVALUATION OF VOC EMISSIONS FROM HEATED ROOFING ASPHALT Prepared by: Peter Kariher, Michael Tufts, and Larry Hamel Acurex Corporation Environmental Systems Division 49 15 Prospectus Drive P.O. Box 13109 Research Triangle Park, NC 27709 EPA Contract Number: 68-DO-0141 Task No. 91-001 Task Officer: Bobby E. Daniel Air and Energy Engineering Research Laboratory U.S. Environmental Protection Agency Research Triangle Park, NC 27711 Prepared for: Control Technology Center U.S. Environmental Protection Agency Research Triangle Park, NC 2771 1 CONTROL TECHNOLOGY CENTER Sponsored by: Emission Standards Division Office of Air Quality Planning and Standards U.S. Environmental Protection Agency Research Triangle Park, NC 2771 1 Air and Energy Engineering Research Laboratory U.S. Environmental Protection Agency Research Triangle Park, NC 2771 1 Center for Environmental Research Information Office of Research and Development U.S. Environmental Protection Agency Cincinnati, OH 45268 ABSTRACT A short-term, in-house project to characterize emissions from a simulated asphalt roofing kettle was performed at EPAfAEERL. Hot asphalt surfacing and resurfacing ha$ been identified as a possible significant source of volatile organic compound (VOC) emissions that may affect human health and contribute to the ozone non-attainment problem. The purpose of the study was to collect, identify, and semiquantitate as many of the compounds as possible that are discharged during the open heating of roofing asphalt and relate them to the amount volatilized into the air. Types 1, 2, and 3 mopping grade asphalts were chosen for this study. They constitute more than 90 percent of roofing asphalt used. Samples of each type of asphalt were placed in a simulated roofing kettle, heated to predetermined temperatures, and sampled for volatile and semi-volatile organic emissions. Compounds identified during this study were alkanes, aromatics, a ketone, and an aldehyde. This work was done at the request of the Control Technology Center (CTC) steering committee to provide information to state and local agencies for use in responding to public concerns. TABLE OF CONTENTS Abstrad .................................................................... ii Listof Figures ............................................................... iv ListofTables ............................................................... v Acknowledgements ........................................................... vi Preface ................................................................... vii Metric to Nonmetric Conversions .................................................. viii Section Paae 1. Introduction .............................................................. 1 2 . Project Description ......................................................... 3 2.1 Experimental Approach ................................................. 3 2.2 Experimental Apparatus ................................................. 4 2.2.1 BumHut ....................................................... 4 2.2.2 Sample Shed .................................................... 6 2.3 Experimental Methods and Procedures ..................................... 10 2.3.1 Simulation of Open Air Asphat! Kettle Heating ........................... 10 2.3.2 Volatile Organics Collection ........................................ 10 2.3.3 Semi-volatile Organics and Particulate Collection ......................... 15 3 . Data. Results. and Discussion ............................................... 19 3.1 Volatile Organic Emission Data ........................................... 19 3.2 Semi-volatile Organic Emissions Data ..................................... 36 5 . References .............................................................. 49 Appendix A. Quality Control Evaluation Report ...................................... 50 iii LIST OF FIGURES 1. SamplingBuildings .......................................................... 5 2 . Heating Apparatus in "Bum Hut" ................................................ 7 3. Diagram of Sampling System Used .............................................. 8 4 . Schematic of Volatile Organic Sampling Train ...................................... 9 5 . AEERUOCB (Organics Control Branch) Sample Log ................................ 12 6 . VOST Field Data Sheet ..................................................... 13 7. Semi-volatile Sampling Worksheet .............................................. 16 8. TCOMassData ........................................................... 34 9 . GRAV Mass Data ......................................................... 35 LIST OF TABLES .Table Paae 1. Compounds Identified by GCIMS from VOST Runs ................................ 20 2 . D-BenzeneData .........................................................20 3 . Type 1 (VOST) Condition 1 ................................................. 21 4 . Type 1 (VOST) Condition 2 .................................................22 5 . Type 1 (VOST) Condition 3 .................................................23 6 . Type 2 (VOST) Condition 1 .................................................24 7 . Type 2 (VOST) Condition 2 ................................................. 25 8 . Type 2 (VOST) Condition 3 ................................................. 26 9 . Type3(VOST)Condition1 ................................................. 27 10 . Type 3 (VOST) Condition 2 .................................................. 28 11. Type 3 (VOST) Condition 3 ................................................... 29 12. SamplingData ........................................................... 30 13. Background Data (VOST) ................................................... 31 14. BlankData(V0ST) ....................................................... 33 15 . GRAVMassData ......................................................... 36 16. Compounds Identified by MS from XAD and Filter Extract Runs ....................... 37 17. Type 1 (TCO) Condition 1 ................................................... 38 18 . Type 1 (TCO) Condition 2 ................................................... 39 19. Type 1 (TCO) Condition 3 ................................................... 40 20 . Type 2 (TCO) Condition 1 ................................................... 41 21 . Type 2 (TCO) Condition 2 ................................................... 42 22 . Type2(TCO)Condition3 ................................................... 43 23 . Type 3 (TCO) Condition 1 ................................................... 44 24 . Type 3 (TCO) Condition 2 ................................................... 45 25 . Type 3 (TCO) Condition 3 ................................................... 46 26 . ASTMStandards ......................................................... 47 A.1 . Percent Bias For VOST PEAS .............................................. 52 A.2 . Results of External Audit .................................................. 54 A.3 . Accuracy and Precision Data for Semi-Volatiles .................................. 54 ACKNOWLEDGEMENTS The authors would like to recognize EPA/AEERL1sRay Steiber for his expertise in identifying compounds. The authors would like to thank Ken Krebs of Acurex for his analytical support and Ray Thomas of Acurex for his sampling support. PREFACE The Control Technology Center (CTC) was established by EPA's Office of Research and Development (ORD) and Office of Air Quality Planning and Standards (OAQPS) to provide technical assistance to state and local air pollution control agencies. Three levels of assistance can be accessed through the CTC. First, a CTC HOTLINE has been established to provide telephone assistance on matters relating
Recommended publications
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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,
    [Show full text]
  • Alteration of Volatile Chemical Composition in Tobacco Plants Due to Green Peach Aphid (Myzus Persicae Sulzer) (Hemiptera: Aphididae) Feeding
    Song et al.: Green peach aphid (Myzus persicae Sulzer) (Hemiptera: Aphididae) feeding alters volatile composition in tobacco plants - 159 - ALTERATION OF VOLATILE CHEMICAL COMPOSITION IN TOBACCO PLANTS DUE TO GREEN PEACH APHID (MYZUS PERSICAE SULZER) (HEMIPTERA: APHIDIDAE) FEEDING SONG, Y. Z.1,2,3 – GUO, Y. Q.1,2 – CAI, P. M.2,3 – CHEN, W. B.1,2 – LIU, C. M.1,2* 1Biological Control Research Institute, College of Plant Protection, Fujian Agriculture and Forestry University, Fuzhou 350002, China e-mail: [email protected] (Song, Y. Z.); [email protected] (Guo, Y. Q.); [email protected] (Chen, W. B.) 2State Key Laboratory of Ecological Pest Control for Fujian and Taiwan Crops, Fuzhou 350002, China e-mail: [email protected] (Cai, P. M.) 3Department of Horticulture, College of Tea and Food Science, Wuyi University, Wuyishan 354300, China *Corresponding author e-mail: [email protected]; phone: +86-0591-8378-9420; fax: +86-0591-8378-9421 (Received 10th Jul 2020; accepted 6th Oct 2020) Abstract. In response to insect pest herbivory, plants can generate volatile components that may serve multiple roles as communication signals and defence agents in a multitrophic context. In the present study, the volatile profiles of tobacco plants Nicotiana tabacum L., with and without infestation by sap-sucking aphids Myzus persicae Sulzer, were measured by gas chromatography-mass spectrometry (GC-MS). The results revealed that a total of 10 compounds were identified from healthy tobacco plants, and a total of 14 and 16 compounds were isolated from aphid-infested tobacco plants at 24 and 48 hours after infestation, respectively.
    [Show full text]
  • 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 .....
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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
    [Show full text]
  • 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'()
    [Show full text]
  • 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.
    [Show full text]