Modeling Secondary Organic Aerosol Production from

Apr 3, 2018 - Telephone: (212) 854-2869. ... of this pathway warrants further laboratory studies and representation of this SOA source in atmospheric ...
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Modeling Secondary Organic Aerosol Production from Photosensitized Humic-like Substances (HULIS) William Gang Tsui, and V. Faye McNeill Environ. Sci. Technol. Lett., Just Accepted Manuscript • DOI: 10.1021/acs.estlett.8b00101 • Publication Date (Web): 03 Apr 2018 Downloaded from http://pubs.acs.org on April 5, 2018

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Modeling Secondary Organic Aerosol Production from Photosensitized Humic-like

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Substances (HULIS)

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William G. Tsui, V. Faye McNeill*

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Department of Chemical Engineering, Columbia University, New York, NY 10027

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*Corresponding author. E-mail: [email protected], Telephone: (212)-854-2869

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Abstract Humic-like substances (HULIS) are ubiquitous in atmospheric aerosols. Despite

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experimental evidence that HULIS can catalyze secondary organic aerosol (SOA) formation

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through photosensitizer chemistry, the potential contribution of this pathway to ambient SOA has

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not been quantified. In this study, GAMMA, a photochemical box model, was used to analyze

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the experimental data of Monge et al. (2012) in order to quantify the uptake kinetics of limonene

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to particles containing humic acid, a laboratory proxy for HULIS. The results indicate that

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limonene is taken up to irradiated particles containing humic acid efficiently, with a reactive

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uptake coefficient of 1.6×10-4. Consequently, simulations of limonene-HULIS photosensitizer

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chemistry under ambient conditions, simultaneously with other aqueous SOA formation

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processes, show that this pathway could contribute up to 65% of total aqueous SOA at pH 4. The

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potential importance of this pathway warrants further laboratory studies and representation of

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this SOA source in atmospheric models.

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Introduction

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Atmospheric aerosols affect air quality, health, climate, and visibility. Organic material

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and liquid water make up a significant portion of total atmospheric aerosol mass, and much of

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the organic portion of atmospheric aerosols is secondary in origin.1–4 Thus, an understanding of

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the formation and evolution of secondary organic aerosols (SOA) is necessary for modeling air

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quality. However, many models are currently unable to accurately represent organic aerosols due

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to uncertainties in SOA production.3,5,6 Recent studies suggest that heterogeneous or multiphase

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reactions of volatile compounds in aqueous aerosols can be important pathways of SOA

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formation.7 These processes may contribute to the discrepancy between model predictions and

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observed atmospheric aerosol content.

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Humic-like substances (HULIS) are a class of macromolecular water-soluble organic

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species typically several hundred daltons in molecular weight.8 They can comprise 10 – 35% of

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fine organic material in atmospheric aerosols, and have been observed to account for as high as

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72% of water-soluble organic carbon in some ambient aerosol samples.9,10 They are likely

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formed through biomass burning and secondary aqueous reactions.8–17 HULIS are named as such

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due to apparent similarities to humic acids, such as their polyacidic and amphiphilic nature,

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aromaticity, and light absorption. As a result of these characteristics, HULIS can affect aerosol

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properties, including optical properties and CCN activity.

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Some light-absorbing organic aerosol species can participate in SOA formation by acting

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as photosensitizers. A photosensitizer is excited to a triplet state when irradiated. In the excited

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triplet state, the photosensitizer can then reduce O2 to form oxidizing radicals or directly oxidize

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a VOC to form SOA, as shown in Figure 1 with HULIS as a photosensitizer in the presence of

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limonene and isoprene. Trace aerosol species such as 2-imidazole carboxaldehyde18–22 (IC) and

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non-phenolic aromatic carbonyls23,24 have been shown to contribute to SOA formation via

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photosensitizer chemistry.

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Figure 1 – HULIS reaction pathways as a photosensitizer with VOCs limonene and isoprene

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In aerosol flow tube experiments performed by Monge and coworkers, particles

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containing humic acid, a proxy for HULIS, were observed to grow when exposed to limonene

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under UV-A irradiation.25 Mass spectrometry analysis indicated the presence of higher molecular

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weight limonene reaction products, and control experiments suggested that O2 was a source of

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oxidizing radicals in the photosensitizer pathway. They also observed isoprene uptake to thin

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films containing humic acid.

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Due to the high abundance of HULIS in atmospheric aerosols, the potential contribution of HULIS photosensitizer chemistry to ambient SOA formation is larger than for trace species

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such as IC.9,10,22,26 Here, we apply GAMMA (Gas-Aerosol Model for Mechanism Analysis), a

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photochemical box model of multiphase atmospheric chemistry developed by the McNeill

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group,27 to quantify the kinetics of limonene SOA formation due to the HULIS photosensitizer

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pathway in the laboratory experiments of Monge et al (2012).25 We then use the calculated

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reactive uptake coefficient to compare SOA formation from this pathway to other important

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aqueous SOA formation pathways under ambient conditions.

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Materials and Methods

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In this study, we performed two sets of model simulations. All simulations use GAMMA 4.0.22

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First, we modeled the laboratory experiments of Monge et al.25 Then, we used the results of

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those simulations to model aerosol growth through photosensitizers and other atmospherically

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relevant processes under ambient conditions.

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GAMMA 4.0. GAMMA is a photochemical box model developed by the McNeill group that

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couples detailed gas and aqueous aerosol phase chemistry of organic species and includes mass

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transfer between the gas and aqueous phases. The time-dependent evolution of the partial

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pressure of a gas-phase species i, Pi, and the concentration of an aqueous phase species i, Ci, in

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GAMMA follows Schwartz28 and is given by the following equations:

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, ∗

,

,



,

,

,

1

2

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where kmt,i is the gas-aerosol mass transfer coefficient, aL is the aqueous aerosol liquid volume

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fraction, Hi* is the effective Henry’s Law constant, Ei is the emission rate, Di is the deposition

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rate, R is the gas constant, T is temperature, and rij,gas and rij,aq are the gas and aqueous phase

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reactions of species i respectively, which may be positive or negative corresponding to formation

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or consumption of species i.

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Aqueous phase chemistry of organic material in GAMMA includes oxidative and dark

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formation of SOA and organosulfate species by water soluble VOC precursors such as glyoxal

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and methylglyoxal. Aqueous processing of isoprene epoxydiols (IEPOX) to form 2-methyltetrols

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(tetrol) and IEPOX organosulfate (IEPOXOS) is expressed in GAMMA as a branching reaction

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→ 1





3

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with branching ratio β = 0.4 being used based on the work of Eddingsaas et al.29 Imidazole

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photosensitizer reactions were added in the recent 4.0 update.22 McNeill et al. (2012) and Tsui et

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al. (2017) provide a more detailed discussion of GAMMA and the 4.0 update, respectively.22,27

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Reactive uptake of limonene. Photosensitizer SOA formation can be modeled using a reactive

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uptake formulation, which represents the mass transfer and particle-phase chemical kinetics of

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the process.22 The reactive uptake of limonene to humic acid-containing particles was added to

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GAMMA using the following equations for the change in partial pressure of limonene, where

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reactive uptake replaces the partitioning terms from Equation 1.27,28

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,

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where 1

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100

,

,

2

1

,

,

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and

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,

4

3

1

0.38 1

6

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In the equations above, species i is gas-phase limonene, R is the aerosol particle radius, Dg,i is the

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gas phase diffusivity, γi is the reactive uptake coefficient, Sa is the aerosol surface area per

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volume, ωi is the thermal velocity, and Kn is the Knudsen number, which is the ratio of the mean

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free path of air to the particle radius. Emissions and depositions are only considered for ambient

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simulations. The amount of SOA formed is assumed to be equal to the amount of limonene taken

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up. Although it is possible that the SOA products may be (semi)volatile and repartition to the gas

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phase, here any loss to the gas phase is already accounted for in the reactive uptake coefficient

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since it was calculated based on the net observed particle growth.30

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Experimental simulation conditions. Full details of the simulation initial conditions can be

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found in the Supporting Information. Simulations of laboratory experiments of humic acid-

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containing particle growth followed the conditions used by Monge et al.25 In these experiments,

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ammonium nitrate aerosols containing humic acid and succinic acid, a proxy for other organic

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species in ambient aerosols, were used. The initial aerosol composition for aerosols containing

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humic acid, succinic acid, and ammonium nitrate was determined by using the relative humidity

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and the weight ratio of these species in the aqueous solution (1:10:1) prior to aerosolizing to

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calculate equilibrium concentrations of each species with E-AIM Model II, a thermodynamic

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aerosol model which includes inorganic species H+, NH4+, SO42-, and NO3- and H2O in the liquid

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phase and HNO3, NH3, H2SO4 and H2O in the gas phase.31,32 Organic compounds, such as

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succinic acid, can be added to the E-AIM model by accessing multiple publicly available

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libraries via the E-AIM interface. Since they are not well-defined molecules, thermodynamic

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calculations for HULIS or humic acid are not available in E-AIM. Therefore, succinic acid was

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used as a proxy for humic acid in our E-AIM calculations. In order to account for the

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concentration effect associated with bringing the aerosols to