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Secondary Aerosol Formation from Gas and Particle Phase Reactions of Aromatic Hydrocarbons. Richard Kamens and Di Hu. Funded by the USEPA STAR program July 30, 2003 to July 29, 2006. Department of Environmental Science and Engineering UNC, Chapel Hill.
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Secondary Aerosol Formation from Gas and Particle Phase Reactions of Aromatic Hydrocarbons Richard Kamens and Di Hu Funded by the USEPA STAR program July 30, 2003 to July 29, 2006 Department of Environmental Science and Engineering UNC, Chapel Hill
The overall goal of this project is to represent new chemistry as a unified, multi-phase, chemical reaction mechanism that will explain the observed chemical phenomena and amounts of secondary organic aerosol that result from aromatics reacting in an urban atmosphere.
Current Approaches do not incorporate newly discovered particle phase heterogeneous reactions that lead to significant SOA formationA “next generation” chemical mechanistic approach is needed that captures the essence of the fundamental chemistry that leads to secondary aerosol formation
Volatile aromatic compounds comprise a significant part of the urban hydrocarbon mixture in the atmosphere, up to 45% in urban US and European locations
Toluene, m- & p-xylenes,benzene and 1,2,4-trimethyl benzene, o-xylene and ethylbenzene make up 60-75% of this load. In the US, transportation sources contributed ~67% to the total aromatic emissions which range from 2.4 x 106 to 1.9 x 106 tons/year.
Laboratory studies show that gas phase reactions ofaromaticsandbiogenics form a host of oxygenates secondary organic aerosol material (SOA) • hydroxy unsaturated dicarbonyls • di and tri carboxylic acids • Nitrated hydroxy carbonyls
Turpin and co-workers • In the LA area estimated on smoggy days {from OC /EC ratios}, that as much as 50 - 80% of the aerosolorganic carbon comes from secondary aerosol formation (1984 and 1987 samples) • On average, organic carbon can make up between 10-40% of the total fine TSP in the US
Spyros Pandis • also recently looked at OC/EC ratios (Pittsburgh area) • He estimates that SOA formation can account for 35-50% of the organic carbon
OC/EC Ratio and Photochemical Activity OC/EC O3 Pittsburgh, 2001
In the context of this work, how much of this SOA comes from aromatic emissions in to an airshed?
Overall Approach • kinetic mechanism development • outdoor chamber experiments Tolune, m-xylene 1,3 5 trimethyl benzenes • Simulation of chamber experiments
Overall Approach • kinetic mechanism development Illustrate this with a simple reaction scheme of toluene
Now let me go back and explain in detail each of the reaction steps in the previous three slides. No, shoot me if I start…..
O=CH CH 3 CH OH 3 + H O 2 O + HO 2 benzaldehyde NO NO o-cresol 2 +O CH 2 * 3 CH . CH 2 3 OH OH OH H . H CH toluene CH CH 3 3 3 OH + . OH NO . O 2 O O2 +O H H 2 H H O NO oxygen bridge rearrangement OH H +O . O 2 H + HO 2 H ring cleavage O + radical H CH H OH 3 H butenedial methylglyoxal O H
Pent-dione + OH 0.5 pent-rad +0.5 pent-oo pent-oo XO2 + 0.5 GLY+ 0.5 MGLY + 0.5 CO + 0.5HO2 +0.25 OHoxybutal +0.25 but-tricarb pent-rad Maleic + 1.5 XO2 + HO2 + HCHO
Aromatic Aldehydes Ring Aldehydes Ring opening carbonyls Oxo acids OH-carbonyls
Historically, from a Modeling perspective Equilibrium Organic Gas-particle partitioning has provided a context for addressing SOA Formation
Gas phase reactions CH3-C-C=O CH3-C-C=O Gas and particle phases can be linked via G/P partitioning Methyl glyoxal 1Cgas + surf 1Cpart particle
CH3-C-C=O O kon koff particle kon koff • [ igas] + [part] [ipart] Kp = kon/koff
Particle Phase reactions Polymerization reactions
Particle Phase Reactions + ozone + acid seeds aerosols a-pinene
ESI-QTOF mass spectrum of SOA from reaction of a-pinene with ozone + acid seed aerosol.
Particle phase pinonaldehyde dimers from acida-pinene +O3 M Na+(ESI-QTOF Tolocka et al, 2003)
GlyP + H2O ----> Gly2OHP Gly2OHP + H2O ----> Gly4OHP Gly4OHP + GlyAcidP ----> pre-Poly1 Pre-Poly1 + C4OHALD ----> Poly1
Particle Phase reactions cis-pinonaldhyde Gas phase reactions C=O C=O O O polymers particle
Particle Phase reactions cis-pinonaldhyde C=O C=O O O Gas phase reactions particle polymers
Particle Phase reactions cis-pinonaldhyde C=O C=O O O Gas phase reactions polymers
Rates of polymerizationmethylglyoxal +NOx chamber experiments these rates may be related to HNO3 gas phase and associated particle HNO3
Quantum yields dicarbonyls multifunctional carbonylsLiu et al. 1999–adsorption cross sections
Pinonaldehyde quantum yields in natural sunlight kphototyis = S ( alfl Il) By adding pinonaldehyde to the chamber in clear sunlight in the presence of an OH scavenger and measuring its rate of decay flcan be fit to the decay data assuming a shape with wave length similar to other aldehydes
Normalized to one O pinonaldehyde O Pinonaldehyde quantum yields in sunlight CH3CH2CH2=O CH2=O pinonaldehyde CH3CH2=O
An Exploratory Chemical Model Toluene + propylene + NOx + Sunlight gas phase prod. + SOA
hexadiene-dicarb butene-dicarbonyl pentene-dicarbonyl benzaldehyde cresol maleic anhydride 43 AROMATIC reactions + Carbon 4