Dithiothreitol activity by particulate oxidizers of SOA produced from photooxidation of hydrocarbons under varied NOx levels

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Abstract

When hydrocarbons (HCs) are atmospherically oxidized, they form particulate oxidizers, including quinones, organic hydroperoxides, and peroxyacyl nitrates (PANs). These particulate oxidizers can modify cellular materials (e.g., proteins and enzymes) and adversely modulate cell functions. In this study, the contribution of particulate oxidizers in secondary organic aerosols (SOAs) to the oxidative potential was investigated. SOAs were generated from the photooxidation of toluene, 1,3,5-trimethylbenzene, isoprene, and α-pinene under varied NOx levels. Oxidative potential was determined from the typical mass-normalized consumption rate (reaction time t Combining double low line 30min) of dithiothreitol (DTTt), a surrogate for biological reducing agents. Under high-NOx conditions, the DTTt of toluene SOA was 2-5 times higher than that of the other types of SOA. Isoprene DTTt significantly decreased with increasing NOx (up to 69% reduction by changing the HC NOx ratio from 30 to 5). The DTTt of 1,3,5-trimethylbenzene and α-pinene SOA was insensitive to NOx under the experimental conditions of this study. The significance of quinones to the oxidative potential of SOA was tested through the enhancement of DTT consumption in the presence of 2,4-dimethylimidazole, a co-catalyst for the redox cycling of quinones; however, no significant effect of 2,4-dimethylimidazole on modulation of DTT consumption was observed for all SOA, suggesting that a negligible amount of quinones was present in the SOA of this study. For toluene and isoprene, mass-normalized DTT consumption (DTTm) was determined over an extended period of reaction time (t Combining double low line 2h) to quantify their maximum capacity to consume DTT. The total quantities of PANs and organic hydroperoxides in toluene SOA and isoprene SOA were also measured using the Griess assay and the 4-nitrophenylboronic acid assay, respectively. Under the NOx conditions (HC NOx ratio: 5-36ppbCppb-1) applied in this study, the amount of organic hydroperoxides was substantial, while PANs were found to be insignificant for both SOAs. Isoprene DTTm was almost exclusively attributable to organic hydroperoxides, while toluene DTTm was partially attributable to organic hydroperoxides. The DTT assay results of the model compound study suggested that electron-deficient alkenes, which are abundant in toluene SOA, could also modulate DTTm.

Figures

  • Figure 1. (a) Simplified mechanisms for the formation of alkyl and acyl hydroperoxides, PANs, electron-deficient alkenes, and quinones (Eddingsaas et al., 2012b; Jang and Kamens, 2001; Saunders et al., 2003, 1997; Wyche et al., 2009; Xu et al., 2014). Photooxidation products are not limited to the compounds shown. (b) Possible reaction mechanisms between sulfhydryl groups in DTT (represented by R-SH) and SOA products (Grek et al., 2013; Kumagai et al., 2002; Mudd, 1966; Mudd and McManus, 1969; Nair et al., 2014). EWG represents the electron-withdrawing group attached to an alkene.
  • Table 1. Outdoor chamber experiment conditions.
  • Figure 2. DTTt of chamber-generated SOA under varied NOx conditions (HNOX: high NOx ; LNOX: low NOx) and positive controls (i.e., PQN and NQN). The number above each column represents the initial HC /NOx ratio. The x axis represents the mid-collection time (Table 1). The DTTt of PQN and NQN is divided by 400 and 100, respectively. Each error bar was calculated by t0.95× σ/ √ n, where t0.95 is the t score (4.303 for n= 3 replicates) with a two-tail 95 % confidence level.
  • Figure 3. The time profile of DTTm for toluene and isoprene SOA under different NOx conditions. To achieve the completion of the reaction between DTT and SOA, the DTTm of toluene sample (initial HC /NOx = 24 ppbC ppb−1 collected on 17 November 2016) was measured with a 0.8 mM potassium phosphate buffer in the first step of DTT assay (2 times higher than the typical buffer concentration; 0.4 mM). Each error bar was calculated by t0.95× σ/ √ n using three replicates, where t0.95 is the t score (4.303 for n= 3 replicates) with a two-tail 95 % confidence level.
  • Figure 4. Enhancement factors (pmol min−1 µg-SOA−1 µmolimidazole−1) of SOA in the presence of 2,4-dimethylimidazole. The label above each column represents the initial HC /NOx ratio. The enhancement factor is expressed as the mean (±σ) of three replicates. The enhancement factors of PQN and NQN are divided by 60.
  • Figure 5. (a) Concentration of organic hydroperoxides in SOA, [OHP]m (nmol µg−1), measured by NPBA assay. (b) Concentration of PANs in SOA, [PAN]m (nmol µg−1), measured by Griess assay. The number above each column represents the initial HC /NOx ratio. The x axis represents the mid-collection time (Table 1). (c) Comparison of DTTm (t = 2 h) with the sum of [OHP]m and [PAN]m. The [OHP]m, [PAN]m, and DTTm are expressed as the mean (±σ) of three replicates. HNOX represents high-NOx conditions, and LNOX represents low-NOx conditions.
  • Figure 6. The DTTt (t = 30 min) of four different electron-deficient alkenes. Each error bar was calculated by t0.95× σ/ √ n using three replicates, where t0.95 is the t score (4.303 for n= 3 replicates) with a two-tail 95 % confidence level. EWG in the mechanism represents an electron-withdrawing group (Nair et al., 2014).

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Jiang, H., Jang, M., & Yu, Z. (2017). Dithiothreitol activity by particulate oxidizers of SOA produced from photooxidation of hydrocarbons under varied NOx levels. Atmospheric Chemistry and Physics, 17(16), 9965–9977. https://doi.org/10.5194/acp-17-9965-2017

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