Investigating the Role of Methane on the Growth of Aromatic Hydrocarbons and Soot in Fundamental Combustion Processes

Total Page:16

File Type:pdf, Size:1020Kb

Investigating the Role of Methane on the Growth of Aromatic Hydrocarbons and Soot in Fundamental Combustion Processes Combustion and Flame 134 (2003) 249–260 Investigating the role of methane on the growth of aromatic hydrocarbons and soot in fundamental combustion processes J. F. Roeslera,*, S. Martinota, C.S. McEnallyb, L.D. Pfefferleb, J.-L. Delfauc, C. Vovellec aIFP, 1 et 4 av. de Bois-Pre´au, 92852 Rueil-Malmaison Cedex, France bDepartment of Chemical Engineering and Center for Combustion Studies, Yale University, New Haven, CT 06520-8286 USA cLaboratoire de Combustion et Syste`mes Re´actifs, CNRS, 45701 Orle´ans Cedex 2, France Received 30 November 2002; received in revised form 24 March 2003; accepted 1 April 2003 Abstract Experimental results are presented on the effect of methane content in a non-aromatic fuel mixture on the formation of aromatic hydrocarbons and soot in various fundamental combustion configurations. The systems considered consist of a laminar flow reactor, a laminar co-flow diffusion flame burner, and a laminar, premixed flame burner, all of which operate at atmospheric pressure. In the flow reactor, the experiments are performed at 1430 K, constant C-atom flow rates, 98% nitrogen dilution, C/O ratio ϭ 2, and with fuel mixtures consisting of ethylene and methane. The diffusion flames are performed with fuel mixtures of methane and ethylene diluted in nitrogen to maintain a constant adiabatic flame temperature. The premixed flame experiments are performed with n-heptane and methane mixtures at a C/O ratio ϭ 0.67 with nitrogen-impoverished air. The results show the existence of synergistic chemical effects between methane and other alkanes in the production of aromatics, despite reduced acetylene concentrations. This effect is attributable to the ability of methane to enhance the production of methyl radicals that will then promote production channels of aromatics that rely on odd-carbon- numbered species. Benzene, naphthalene, and pyrene show the strongest sensitivity to the presence of added methane. This synergy on aromatics trickles down to soot via enhanced inception and surface growth rates by polycyclic aromatic hydrocarbon condensation, but the overall effects on soot volume-fraction are smaller due to a compensating reduction in surface growth from acetylene. These results are observed under the very fuel-rich environments existing in the flow reactor and diffusion flames. In the premixed flames, however, instabilities did not permit investigation of conditions with sufficiently high equivalence ratios to perturb the aromatic and soot-growth regions. © 2003 The Combustion Institute. All rights reserved. Keywords: Soot; Aromatic hydrocarbons; PAH; Methane; Combustion; Flow reactor; Diffusion flame; Premixed flame 1. Introduction tion are complex. Early mechanistic models [1,2] suggested that the first aromatic ring was formed by The molecular growth-processes leading to poly- the addition of acetylene to C radicals and that the cyclic aromatic hydrocarbons (PAH) and soot forma- 4 key growth process toward increasingly larger PAH occurred by continuous addition of C2H2. Bi-aryl * Corresponding author. Tel: ϩ(33)1-47-52-5811; fax: formation by aromatic-ring addition was considered ϩ(33)1-47-52-7069. feasible only in the case of aromatic fuels. This type E-mail address: [email protected] (J.F. Roesler). of pioneering model was able to reproduce most of 0010-2180/03/$ – see front matter © 2003 The Combustion Institute. All rights reserved. doi:10.1016/S0010-2180(03)00093-2 250 J.F. Roesler et al. / Combustion and Flame 134 (2003) 249–260 the major PAH and soot trends observed experimen- The product samples are quenched and collected tally in combustion processes [1,3,4]. However, it along the center-line axis by means of an oil-cooled neglected other reaction pathways that are increas- probe at 180°C. Only 20% of the total flow is sam- ingly shown to be of importance. pled; therefore, the measurements correspond to the In 1990, Miller and Mellius [5] published work products along the center-line and not to the bulk that suggested that benzene could be formed, in large mean. part, from the re-combination of the odd-carbon- At the probe exit, the soot is filtered at 180°C, and numbered, resonantly-stabilized propargyl radicals. condensable species are then trapped. In a first pass, While this specific reaction is now well-recognized the trap is at ambient temperature, and the low-mo- and has been implemented in many recent kinetic lecular-weight gas-phase species, up to benzene, are models [6-9], there is growing evidence that many analyzed on-line with a Fourier-transform infrared other such radical species are involved in the produc- spectrometer (FTIR). The gas-phase species are then tion of at least the smaller PAH. This evidence is collected for subsequent analysis by gas chromatog- found in various theoretical analyses of reaction raphy (GC) with a flame ionization detector (FID) in channels and in experimental flame and modeling studies [10–14]. order to more accurately quantify the hydrocarbon If these reactions are indeed important, then add- gas-phase species with up to eight carbon atoms. The ing methane to the PAH and soot-forming regions in species quantified solely by FTIR are CO, CO2, and combustion systems should, under some conditions, H2O. The higher-molecular-weight species are col- promote their growth. The premixed flame results of lected on a second pass, with the trap at dry-ice Senkan and Castaldi [15] that show a methane, lam- temperature (Ϫ70°C) that is then washed with inar, premixed, flat flame to produce more benzene CH2Cl2. The detailed speciation of the PAH from the and PAH than a similar ethane flame confirm this line trap is obtained by GC-FID and GC-mass spectrom- of thought. More direct evidence of this effect of etry (MS) analysis. All other wetted surfaces (probe, methane was obtained in flow-reactor studies [16,17]. Teflon liner, and soot filter) are washed ultrasonically The addition of methane was found to enhance the with CH2Cl2. Analysis of the collected solutions formation of aromatics and soot in n-heptane oxida- showed Ͻ 5% loss of any one of the reported PAH to tive pyrolysis. Detailed reaction mechanisms from these surfaces. The total masses of condensable spe- the literature were found to reproduce these effects, cies (hereafter referred to as “tar”) of molecular provided PAH formation was appropriately described weight, corresponding roughly to masses greater than with odd-carbon-numbered radical species. acenaphthylene, and the mass of soot (non-dichlo- The present work further investigates experimen- romethane-soluble, condensable species) are deter- tally the influence of methane as a parameter to be mined gravimetrically. considered in the formation of soot and PAH. Our In the experiments presented here, the fuel was goal was to further quantify the effect, under flow- initially C H that was gradually substituted with reactor conditions, and to determine whether or not 2 4 CH at a constant total-carbon molar content of 3%. these were applicable to classic, laminar, premixed 4 and diffusion flame conditions. A mixture parameter characterizing the initial fuel composition is defined as: XCH 2. Experimental set-ups ␤ ϭ 4 (1) X ϩ 2X CH4 C2H4 2.1. The flow-reactor system and represents the fraction of fuel carbon injected as methane. This parameter was varied from 0 to 0.5. The flow-reactor device and the analytical tech- The oxygen content was also held constant to main- niques for quantifying the composition of the sam- ϳ pled products have been described in detail previ- tain a C/O ratio of 2.0, leading to an equivalence ously [17,18]. The reactor is made of quartz, with a ratio varying slightly between 6 and 7 due to added 30-mm inside diameter. It is inserted in a three-zone hydrogen in the presence of methane. The experi- furnace. The premixed reactants are rapidly heated in mental conditions investigated were for a tempera- the first zone through a coiled 1.5-m-long tube with ture of 1430 K, atmospheric pressure, and a total flow an inside diameter of 4 mm. The flow enters the rate of 0.54 slpm (standard liters per minute) with larger-diameter test section and is laminarized by nitrogen as the carrier gas. The product samples were passing through a porous quartz disk. The test section collected at a fixed position of 0.25 m downstream of is at atmospheric pressure and is isothermal within the porous quartz disk, corresponding to a bulk mean 5 K throughout a distance of 35 cm. residence time of 0.42 s. J.F. Roesler et al. / Combustion and Flame 134 (2003) 249–260 251 2.2. The laminar co-flow diffusion flame system Table 1 Volumetric flowrates for the laminar diffusion flames* The laminar co-flow diffusion flame burner and ␤ N CH C H Ar the analytical techniques have been described in de- 2 4 2 4 tail previously [19]. The flames are generated with an 0.00 500 0 220 7.27 atmospheric pressure, axisymmetric, co-flowing 0.03 484 11 213 7.15 burner. The fuel mixture flows from an un-cooled 0.05 468 23 206 7.04 12-mm-diameter vertical brass tube. The air flows 0.08 452 35 199 6.93 0.11 436 48 192 6.83 between this tube and a surrounding 108-mm inside- 0.14 417 61 183 6.68 diameter chimney. 0.18 397 75 175 6.53 Temperatures are measured with an un-coated 0.21 378 90 166 6.40 125-␮m wire-diameter/260-␮m junction-diameter 0.25 358 105 158 6.28 type R (Pt-Pt/13% Rh) thermo-couple. Further details 0.29 336 121 148 6.10 are provided elsewhere [20].
Recommended publications
  • Hydrogen Transfer and Activation of Propane and Methane on ZSM5-Based Catalysts
    Catalysis Letters 21 (1993) 55-70 55 Hydrogen transfer and activation of propane and methane on ZSM5-based catalysts Enrique Iglesia 1 and Joseph E. Baumgartner Corporate Research Laboratories, Exxon Research and Engineering, Route 22 East, Annandale, NJ08801, USA Received 12 April 1993; accepted 4 June 1993 Hydrogen exchange between undeuterated and perdeuterated light alkanes (CD4-C3Hs, C3Ds-C3Hs) occurs on H-ZSM5 and on Ga- and Zn-exchanged H-ZSM5 at 773 K. Alkane conversion to aromatics occurs much more slowly because it is limited by rate of disposal of H-atoms formed in C-H scission steps and not by C-H bond activation. Kinetic coupling of these C-H activation steps with hydrogen transfer to acceptor sites (Ga n+, Znm+) and ulti- mately to stoichiometric hydrogen acceptors (H+, CO2, 02, CO) often increases alkane activa- tion rates and the selectivity to unsaturated products. Reactions of 13CH4/C3H8 mixtures at 773 K lead only to unlabelled alkane, alkene, and aromatic products, even though exchange between CD4 and C3H8 occurs at these reaction conditions. This suggests that the non- oxidative conversion of CH4 to higher hydrocarbons on solid acids is limited by elementary steps that occur after the initial activation of C-H bonds. Keywords: Hydrogen transfer; light alkane reactions; deuterium cross-exchange reactions; alkane aromatization 1. Introduction Recent studies suggest that electrophilic activation of light alkanes occurs on superacid catalysts [1] and on Hg-based organometallic complexes [2] at low tem- peratures, and on weaker solid acids at higher temperatures [3-9], apparently via heterolytic cleavage of C-H bonds or intermediate partial oxidation of methane to methanol.
    [Show full text]
  • ITP Chemicals: from Natural Gas to Ethylene Via Methane
    . INDUSTRIAL TECHNOLOGIES PROGRAM From Natural Gas to Ethylene via Methane Homologation and Ethane Oxidative Dehydrogenation New catalysts promise higher selectivity, Benefits for Our Industry and Our throughput, and economic competitiveness Nation As an alternative to thermal cracking, Ethylene is an important building block This technique has not yet been implemented oxydehydrogenation will save more than 640 in the production of many common and because of high capital investment in existing trillion British thermal units (Btu) per year commercially important materials, such as equipment and techniques. while reducing emissions of many pollutants. plastics and chemicals. Currently, ethylene is This project seeks to develop catalysts that New ethylene plants will save 50 percent in produced in a highly energy-intensive two-step will enable direct production of ethylene capital costs over plants installing cracking process. Ethane is firstrecovered from natural by the oxydehydrogenation of crude ethane furnaces. gas and refinery streams through catalytic found in natural gas. This exothermic process cracking and hydrocracking processes, and will offer high selectivity and throughput of then it is thermally cracked in the presence of ethylene from ethane-concentrated gas streams steam to produce ethylene. A more efficient in addition to saving energy and reducing Applications in Our Nation’s but not yet commercialized alternative to emissions. It will also lower capital costs this method is catalytic oxydehydrogenation, Industry through the use crude ethane, which is cheaper which directly produces ethylene from crude than ethane purified through other processes. Catalytic oxydehydrogenation will find ethane found in natural gas in a single step. immediate application in the petrochemicals industry, which uses ethylene as a primary O2 feedstock for manufacturing plastics and Ethane- Depleted C B chemicals.
    [Show full text]
  • Environlmental ASSESSMENT METHYL CHLORIDE VIA
    DOEEA-1157 ENVIRONlMENTAL ASSESSMENT METHYL CHLORIDE VIA OXYHYDROCHLOFUNATION OF METHANE: A BUILDING BLOCK FOR CHEMICALS AND FUELS FROM NATURAL GAS DOW CORNING CORPORATION CARROLLTON, KENTUCKY SEPTEMBER 1996 U.S. DEPARTMENT OF ENERGY PITTSBURGH ENERGY TECHNOLOGY CENTER CUM ~~~~~~~~ DOEEA-1157 ENVIRONlMENTAL ASSESSMENT METHYL CHLORIDE VIA OXYHYDROCHLORINATION OF METHANE: A BUILDING BLOCK FOR CHEMICALS AND FUELS FROM NATURAL GAS DOW CORNING CORPORATION CARROLLTON, KENTUCKY SEPTEMBER 1996 U.S. DEPARTMENT OF ENERGY PITTSBURGH ENERGY TECHNOLOGY CENTER Portions of this document may be illegible in electronic image products. Image are produced from the best available original document. &E/,Etq --,/s7 FINDING OF NO SIGNIFICANT IMPACT FOR THE PROPOSED METHYL CHLORIDE VIA OXYHYDROCHLORINATION OF METHANE PROJECT AGENCY: U.S. Department of Energy (DOE) ACTION: Finding of No Significant Impact (FONSI) SUMMARY: DOE has prepared an Environmental Assessment (EA) (DOE/EA-1157) for a project proposed by Dow Corning Corporation to demonstrate a novel method for producing methyl chloride (CH,Cl). The project would involve design, construction, and operation of an engineering-scale oxyhydrochlorination (OHC) faci 1 i ty where methane, oxygen, and hydrogen chloride (HC1) would be reacted in a fixed-bed reactor in the presence of highly selective, stable catalysts. Unconverted methane, light hydrocarbons and HC1 would be recovered and recycled back to the OHC reactor. The methyl chloride would be absorbed in a solvent, treated by solvent stripping and then purified by distillation. Testing of the proposed OHC process would be conducted at Dow Corning's production plant in Carrollton, Carroll County, Kentucky, over a 23-month period. Based on the analyses in the EA, the DOE has determined that the proposed action is not a major Federal action significantly affecting the quality of the human environment as defined by the National Environmental Policy Act (NEPA) of 1969.
    [Show full text]
  • Catalytic Reaction of Carbon Dioxide with Methane on Supported Noble Metal Catalysts
    catalysts Review Catalytic Reaction of Carbon Dioxide with Methane on Supported Noble Metal Catalysts András Erd˝ohelyi Institute of Physical Chemistry and Materials Science, University of Szeged, Rerrich Béla tér 1, H-6720 Szeged, Hungary; [email protected]; Tel.: +36-62-343-638; Fax: +36-62-546-482 Abstract: The conversion of CO2 and CH4, the main components of the greenhouse gases, into synthesis gas are in the focus of academic and industrial research. In this review, the activity and stability of different supported noble metal catalysts were compared in the CO2 + CH4 reaction on. It was found that the efficiency of the catalysts depends not only on the metal and on the support but on the particle size, the metal support interface, the carbon deposition and the reactivity of carbon also influences the activity and stability of the catalysts. The possibility of the activation and dissociation of CO2 and CH4 on clean and on supported noble metals were discussed separately. CO2 could dissociate on metal surfaces, this reaction could proceed via the formation of carbonate on the support, or on the metal–support interface but in the reaction the hydrogen assisted dissociation of CO2 was also suggested. The decrease in the activity of the catalysts was generally attributed to carbon deposition, which can be formed from CH4 while others suggest that the source of the surface carbon is CO2. Carbon can occur in different forms on the surface, which can be transformed into each other depending on the temperature and the time elapsed since their formation. Basically, two reaction mechanisms was proposed, according to the mono-functional mechanism the activation of both CO2 and CH4 occurs on the metal sites, but in the bi-functional mechanism the CO2 is activated on the support or on the metal–support interface and the CH on the metal.
    [Show full text]
  • ETHYLENE from METHANE (January 1994)
    Abstract Process Economics Program Report No. 208 ETHYLENE FROM METHANE (January 1994) This report evaluates two routes for the production of ethylene from methane: the direct synthesis based on the oxidative coupling of methane, and the less direct chemistry of converting methanol (which is derived from methane via synthesis gas) in the presence of an aluminophosphate molecular sieve catalyst. Our evaluations indicate that at the present state of development, the economics of both routes are unattractive when compared with the steam pyrolysis of hydrocarbons. We analyze the results of our evaluations to define the technical targets that must be attained for success. We also present a comprehensive technical review that examines not only the two routes evaluated, but also some of the more promising alternative approaches, such as synthesis gas conversion via a modified Fischer-Tropsch process, ethanol synthesis by the homologation of methanol, and ethylene production via methyl chloride. This report will be of interest to petrochemical companies that produce or consume ethylene and to energy-based companies (or equivalent government organizations in various countries) that have access to or control large resources of methane-rich natural gas. PEP’91 SCN CONTENTS 1 INTRODUCTION 1-1 2 SUMMARY 2-1 TECHNICAL REVIEW 2-1 Oxidative Coupling 2-1 Methanol Conversion to Ethylene 2-3 Modified Fischer-Tropsch (FT) Process 2-3 Methanol Homologation 2-3 Conversion via Methyl Chloride 2-4 SRI’S PROCESS CONCEPTS 2-4 Ethylene from Methane by Oxidative
    [Show full text]
  • Basis for Listing Hazardous Waste
    NEBRASKA ADMINISTRATIVE CODE Title 128 - Department of Environmental Quality Appendix II - BASIS FOR LISTING HAZARDOUS WASTE EPA Hazardous Hazardous Constituents For Which Listed Waste No. F001 Tetrachloroethylene; methylene chloride; trichloroethylene; 1,1,1-trichloroethane; carbon tetrachloride; chlorinated fluorocarbons. F002 Tetrachloroethylene; methylene chloride; trichloroethylene; 1,1,1-trichloroethane; 1,1,2-trichloroethane; chlorobenzene; 1,1,2-trichloro-1,2,2-trichfluoroethane; ortho- dichlorobenzene; trichlorofluoromethane. F003 N.A. F004 Cresols and cresylic acid, nitrobenzene. F005 Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, 2-ethoxyethanol, benzene, 2-nitropropane. F006 Cadmium, hexavalent chromium, nickel, cyanide (complexed). F007 Cyanide (salts). F008 Cyanide (salts). F009 Cyanide (salts). F010 Cyanide (salts). F011 Cyanide (salts). F012 Cyanide (complexed). F019 Hexavalent chromium, cyanide (complexed). F020 Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetrachlorophenols and their chlorophenoxy derivative acids, esters, ethers, amine and other salts. Effective Date: 01/03/07 II-1 Title 128 Appendix II EPA Hazardous Hazardous Constituents For Which Listed Waste No. F021 Penta- and hexachlorodibenzo-p-dioxins; penta- and hexachlorodibenzofurans; pentachlorophenol and its derivatives. F022 Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and hexachlorodibenzofurans. F023 Tetra-, and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans;
    [Show full text]
  • Radical-Radical Reactions, Pyrene Nucleation, and Incipient Soot
    Available online at www.sciencedirect.com Proceedings of the Combustion Institute 36 (2017) 799–806 www.elsevier.com/locate/proci Radical–radical reactions, pyrene nucleation, and incipient soot formation in combustion a b b K. Olof Johansson , Tyler Dillstrom , Paolo Elvati , a a c ,d Matthew F. Campbell , Paul E. Schrader , Denisia M. Popolan-Vaida , c c b ,e Nicole K. Richards-Henderson , Kevin R. Wilson , Angela Violi , a , ∗ Hope A. Michelsen a Combustion Research Facility, Sandia National Laboratories, P. O. Box 969, MS 9055, Livermore, CA 94551, USA b Department of Mechanical Engineering, University of Michigan, Ann Arbor, MI 48109, USA c Chemical Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, CA 94720, USA d Department of Chemistry, University of California, Berkeley, CA 94720, USA e Departments of Chemical Engineering, Biomedical Engineering, Macromolecular Science and Engineering, Biophysics Program, University of Michigan, Ann Arbor, MI 48109, USA Received 3 December 2015; accepted 31 July 2016 Available online 12 October 2016 Abstract We present a combined experimental and probabilistic simulation study of soot-precursor. The experi- ments were conducted using aerosol mass spectrometry coupled with tunable vacuum ultraviolet radiation from the Advanced Light Source at Lawrence Berkeley National Laboratory. Mass spectra and photoion- ization efficiency (PIE) curves of soot precursor species were measured at different heights in a premixed flat flame and in a counter-flow diffusion flame fueled by ethylene and oxygen. The PIE curves at the pyrene mass from these flames were compared with reference PIE scans recorded for pyrene. The results demonstrate that other C 16 H 10 isomers than pyrene are major components among species condensed onto incipient soot in this study, which is in agreement with the simulations.
    [Show full text]
  • Temperature-Induced Oligomerization of Polycyclic Aromatic Hydrocarbons
    www.nature.com/scientificreports OPEN Temperature-induced oligomerization of polycyclic aromatic hydrocarbons at ambient Received: 7 June 2017 Accepted: 10 July 2017 and high pressures Published: xx xx xxxx Artem D. Chanyshev 1,2, Konstantin D. Litasov1,2, Yoshihiro Furukawa3, Konstantin A. Kokh1,2 & Anton F. Shatskiy1,2 Temperature-induced oligomerization of polycyclic aromatic hydrocarbons (PAHs) was found at 500–773 K and ambient and high (3.5 GPa) pressures. The most intensive oligomerization at 1 bar and 3.5 GPa occurs at 740–823 K. PAH carbonization at high pressure is the fnal stage of oligomerization and occurs as a result of sequential oligomerization and polymerization of the starting material, caused by overlapping of π-orbitals, a decrease of intermolecular distances, and fnally the dehydrogenation and polycondensation of benzene rings. Being important for building blocks of life, PAHs and their oligomers can be formed in the interior of the terrestrial planets with radii less than 2270 km. High-pressure transformations of polycyclic aromatic hydrocarbons (PAHs) and benzene become extremely important due to wide applications for example in graphene- and graphene-based nanotechnology1–3, synthesis of organic superconductors4, 5, petroleum geoscience, origin of organic molecules in Universe and origin of life. In particular, PAHs were found in many space objects: meteorites6–8, cometary comae9, interstellar clouds and planetary nebulas10–12. Although the prevalent hypothesis for the formation of these PAHs is irradiation-driven polymerization of smaller hydrocarbons13, alternative explanation could be shock fragmentation of carbonaceous solid material11. PAH-bearing carbonaceous material could contribute to the delivery of extraterrestrial organic materials to the prebiotic Earth during the period of heavy bombardment of the inner Solar System from 4.5 to 3.8 Ga ago14–16.
    [Show full text]
  • The Methane CO2 Equivalence 1
    Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Earth Syst. Dynam. Discuss., 3, 1–29, 2012 www.earth-syst-dynam-discuss.net/3/1/2012/ Earth System doi:10.5194/esdd-3-1-2012 Dynamics ESDD © Author(s) 2012. CC Attribution 3.0 License. Discussions 3, 1–29, 2012 This discussion paper is/has been under review for the journal Earth System The methane CO Dynamics (ESD). Please refer to the corresponding final paper in ESD if available. 2 equivalence O. Boucher Comparison of physically- and Title Page Abstract Introduction economically-based CO2-equivalences for methane Conclusions References Tables Figures O. Boucher J I Laboratoire de Met´ eorologie´ Dynamique, Institut Pierre Simon Laplace, UMR8539, CNRS – Universite´ Pierre et Marie Curie, 4 place Jussieu, 75252 Paris Cedex 05, France J I Received: 4 January 2012 – Accepted: 9 January 2012 – Published: 13 January 2012 Back Close Correspondence to: O. Boucher ([email protected]) Full Screen / Esc Published by Copernicus Publications on behalf of the European Geosciences Union. Printer-friendly Version Interactive Discussion 1 Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Abstract ESDD There is a controversy on the role methane (and other short-lived species) should play in climate mitigation policies and no consensus on what an optimal methane 3, 1–29, 2012 CO2-equivalence should be. We revisit this question by discussing the relative mer- 5 its of physically-based (i.e. Global Warming Potential or GWP and Global Temperature The methane CO2 change Potential or GTP) and socio-economically-based climate metrics. To this effect equivalence we use a simplified Global Damage Potential (GDP) that was introduced by earlier au- O.
    [Show full text]
  • Methane Emissions in the United States: Sources, Solutions & Opportunities for Reductions
    Methane Emissions in the United States: Sources, Solutions & Opportunities for Reductions May 23, 2019 Presentation Overview • U.S. methane emissions & sources • Why methane matters • Methane mitigation by emission source • Spotlight on Renewable Natural Gas • Helpful tools and resources 2 U.S. Greenhouse Gas Emission Sources Source: Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2017 3 2017 U.S. Methane Emissions, by Source Other Coal Mining 38.3 MMTCO2e 55.7 MMTCO2e Coal Mining 8% Wastewater Treatment 14.2 MMTCO2e Oil and Natural Gas Systems 31% Landfills 107.7 MMTCO2e Oil and Natural Total Methane Gas Systems Agriculture 36% Emissions 203.3 MMTCO2e 656.3 MMTCO2e Waste 19% Enteric Fermentation Other 6% 175.4 MMTCO2e Manure Management 61.7 MMTCO2e Source: Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2017 4 Why Methane Matters Positive Outcomes of Capturing and Using Methane Methane Emissions Better air and water quality Trap 28 times more Methane Mitigation heat than carbon dioxide over 100 years Improved human health Opportunity to capture Contribute to ground- and convert methane Increased worker safety level ozone pollution to useful energy Enhanced energy security Create industrial safety problem Economic growth Reduced odors 5 Methane Mitigation by Emission Source • Coal Mines • Oil and Natural Gas Systems • Agriculture (Manure Management and Enteric Fermentation) • Waste (Wastewater Treatment and Landfills) 6 8% 55.7 MMTCO2e Coal Mines Total 656.3 Methane is released from MMTCO2e coal and surrounding rock ▪ Coal strata due to mining activities. In abandoned mines and surface mines, methane might also escape to the atmosphere through natural fissures or other diffuse sources.
    [Show full text]
  • BENZO[A]PYRENE AS a TOXIC AIR CONTAMINANT
    EXECUTIVE SUMMARY BENZO[a]PYRENE AS A TOXIC AIR CONTAMINANT Prepared by the Staffs of the California Air Resources Board and the Office of Environmental Health Hazard-Assessment APPROVED BY THE SCIENTIFIC REVIEW PANEL APRIL 1994 July 1994 Preface This report was developed in response to the provisions of Health and Safety Code, sections 39650-39662, which became effective January 1984. This legislation requires a two-phase process which separates risk assessment (identification) from risk management. During the identification phase, a report is developed which considers whether there are adverse health effects of a substance which may be, or is, emitted in California. However, in January 1993, AB 2728 was enacted and the procedure for toxic air contaminant (TAC) identification of federal hazardous air pollutants (HAPs) was changed. Pursuant to the new legislation, the state Air Resources Board (ARB/Board) was required to identify, by regulation, any substance listed as a federal HAP a TAC. Although this report was developed under Health and Safety Code, sections 39650-39662, benzo[a]pyrene (BaP) is within the group of chemicals known as Polycyclic organic matter which is listed as a HAP and, therefore, was identified as a TAC on April 8, 1993. This report, “Benzo[a]pyrene as a Toxic Air Contaminant,” was the basis for the Scientific Review Panel (SRP) review of exposure, the cancer potency number for benzo[a]pyrene, four potencies provided under Proposition 65 (California Safe Drinking Water and Enforcement Act of 1986), and potency equivalency factors (PEFs) for 20 other Polycyclic aromatic hydrocarbons (PAHs) which were also identified as TACs at the April 8, 1993, Board hearing.
    [Show full text]
  • GLOBAL METHANE ASSESSMENT Summary for Decision Makers Copyright © United Nations Environment Programme, 2021
    GLOBAL METHANE ASSESSMENT Summary for Decision Makers Copyright © United Nations Environment Programme, 2021 This publication may be reproduced in whole or in part and in any form for educational or non-profit purposes without special permission from the copyright holder, provided acknowledgement of the source is made. The United Nations Environment Programme would appreciate receiving a copy of any publication that uses this publication as a source. No use of this publication may be made for resale or for any other commercial purpose whatsoever without prior permission in writing from the United Nations Environment Programme. DISCLAIMER The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning delimitation of its frontiers or boundaries. Moreover, the views expressed do not necessarily represent the decision or the stated policy of the United Nations Environment Programme, nor does citing of trade names or commercial processes constitute endorsement. Suggested citation: United Nations Environment Programme and Climate and Clean Air Coalition (2021). Global Methane Assessment: Benefits and Costs of Mitigating Methane Emissions. Nairobi: United Nations Environment Programme. ISBN: 978-92-807-3854-4 Job No: DTI/2352/PA Global Methane Assessment / ACKNOWLEDGEMENTS 3 ACKNOWLEDGEMENTS ASSESSMENT CHAIR Drew Shindell AUTHORS A. R. Ravishankara, Johan C.I. Kuylenstierna, Eleni Michalopoulou, Lena Höglund- Isaksson, Yuqiang Zhang, Karl Seltzer, Muye Ru, Rithik Castelino, Greg Faluvegi, Vaishali Naik, Larry Horowitz, Jian He, Jean-Francois Lamarque, Kengo Sudo, William J.
    [Show full text]