2021
DOI: 10.1038/s41467-021-22091-6
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Sulfate formation is dominated by manganese-catalyzed oxidation of SO2 on aerosol surfaces during haze events

Abstract: The formation mechanism of aerosol sulfate during wintertime haze events in China is still largely unknown. As companions, SO2 and transition metals are mainly emitted from coal combustion. Here, we argue that the transition metal-catalyzed oxidation of SO2 on aerosol surfaces could be the dominant sulfate formation pathway and investigate this hypothesis by integrating chamber experiments, numerical simulations and in-field observations. Our analysis shows that the contribution of the manganese-catalyzed oxid… Show more

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Cited by 172 publications
(238 citation statements)
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“…3a, the PM 2.5 concentration was more than an order of magnitude lower in samples from Hyytiälä than in those from Beijing (∼ 5 and ∼ 200 µg m −3 , respectively), and the volume-specific yields of aqueousphase H 2 O 2 exhibited a similarly large difference (∼ 10 and ∼ 200 µg m −3 , respectively), while the volume-specific yields of aqueous-phase radicals exhibited a much smaller difference (∼ 3 and ∼ 7 pmol m −3 , respectively; Tables S1, S4, and S5). The strong increase in H 2 O 2 with increasing PM 2.5 concentration is consistent with earlier studies identifying a wide range of redox-active organic and inorganic aerosol components that can produce H 2 O 2 in the aqueous phase (Gunz and Hoffmann, 1990;Anastasio et al, 1994;Zuo and Deng, 1997;Arellanes et al, 2006;Chung et al, 2006;Hua et al, 2008;Möller, 2009;Wang et al, 2010Wang et al, , 2012Anglada et al, 2015;Herrmann et al, 2015;Lakey et al, 2016;Tong et al, 2018;Bianco et al, 2020).…”
Section: Yields Of Aqueous-phase Radicals and H 2 O 2 Fromsupporting
confidence: 90%
“…3a, the PM 2.5 concentration was more than an order of magnitude lower in samples from Hyytiälä than in those from Beijing (∼ 5 and ∼ 200 µg m −3 , respectively), and the volume-specific yields of aqueousphase H 2 O 2 exhibited a similarly large difference (∼ 10 and ∼ 200 µg m −3 , respectively), while the volume-specific yields of aqueous-phase radicals exhibited a much smaller difference (∼ 3 and ∼ 7 pmol m −3 , respectively; Tables S1, S4, and S5). The strong increase in H 2 O 2 with increasing PM 2.5 concentration is consistent with earlier studies identifying a wide range of redox-active organic and inorganic aerosol components that can produce H 2 O 2 in the aqueous phase (Gunz and Hoffmann, 1990;Anastasio et al, 1994;Zuo and Deng, 1997;Arellanes et al, 2006;Chung et al, 2006;Hua et al, 2008;Möller, 2009;Wang et al, 2010Wang et al, , 2012Anglada et al, 2015;Herrmann et al, 2015;Lakey et al, 2016;Tong et al, 2018;Bianco et al, 2020).…”
Section: Yields Of Aqueous-phase Radicals and H 2 O 2 Fromsupporting
confidence: 90%
“…The ƒatom signal of N decreased during the haze periods (Ep3: 21%, clean period: 29%) while S increased (Ep3: 1.4%, clean period: 0.67%), consistent with the CHON and CHOS group fraction variations (shown in Figure 2(a)). Although the mechanism of organosulfur and inorganic sulfate formation in heterogeneous reactions is not fully understood, it seems probable that SO2 is rapidly oxidized and sulfate/organosulfur is formed in aerosol water with different types of oxidants and catalysts (Song et al, 2018;Cheng et al, 2016b;Liu et al, 2020a;Wang et al, 2021b).…”
Section: Molecular Composition Of Oamentioning
confidence: 99%
“…Modeling studies greatly underestimated (∼ 54 %) SO 2− 4 concentration in serve pollution events in Beijing if only considering gas-phase oxidation of SO 2 , while the normalized mean bias (NMB) decreased significantly after heterogeneous oxidation of SO 2 being considered (Zheng et al, 2015). Several heterogeneous and/or multiphase oxidation pathways, such as oxidation of SO 2 or sulfite by H 2 O 2 (Huang et al, 2015;Maaß et al, 1999;Ye et al, 2021;Liu et al, 2021), HONO (J. F. , and O 3 (Maahs, 1983) or photochemical oxidation of SO 2 (Yu et al, 2017;Xie et al, 2015), catalytic oxidation of SO 2 by transition metal ions (TMI) (Warneck, 2018;Martin and Good, 1991;Wang et al, 2021) and oxidation of SO 2 by NO 2 (He et al, 2014;Clifton et al, 1988;Wang et al, 2016;Cheng et al, 2016;Wu et al, 2019;Spindler et al, 2003) in aqueous phase and heterogeneous oxidation of SO 2 on black carbon (Zhao et al, 2017;Zhang et al, 2020;Yao et al, 2020), have been proposed based on field measurements and laboratory and modeling studies. However, the relative contribution of these pathways to the SO 2− 4 production is still controversial.…”
Section: Introductionmentioning
confidence: 99%