Recent studies have highlighted the increased occurrence of reactive chlorine, drawing significant attention to the process of chlorinated chemical oxidation of oxygenated aromatics emitted from biomass burning (BB) in the formation of secondary organic aerosols (SOA). This study selected an oxygenated aromatic, anisole, as a representative of BB, and investigated the products and mechanisms of its reaction with Cl•, as well as exploring the implications of precursor-to-oxidant ratio ([anisole/Cl2]0), NOx levels, and seed particles on SOA generation. The gas-phase composition, SOA composition, and particle information were determined using a single-photon ionization time-of-flight mass spectrometry (SPIMS), a thermal desorption unit gas chromatography mass spectrometry (TDU-GC/MS), and a scanning mobility particle sizer (SMPS), respectively. Experimental results indicate that within minutes of turning on the ultraviolet (UV) lights, a large quantity of ultrafine particles (UFPs) (diameter <100 nm) is immediately formed. The SOA yield is significantly dependent on [anisole/Cl2]0, decreasing from 66.2% to 20.0% as the [anisole/Cl2]0 increases. Upon oxidation by Cl•, anisole promptly released organic chlorides, including 2-chlorophenol and 2,4,6-trichlorophenol. The addition of NOx decreased the SOA yield, enhanced the role of OH• in the reaction process, and led to the formation of organic nitrogen products, such as C6H5NO3 and C7H7NO4. Furthermore, Cl• primarily initiates reactions through H-abstraction and Cl-substitution, resulting in the oxidation products largely retaining the benzene ring. This provides a potential explanation for the high SOA yield induced by Cl• in this study. Overall, our work suggests that the release of UFPs and organic chlorides can be found in the Cl-initiated oxidation of anisole, which contributes to high SOA yields. Against the backdrop of increasing wildfire frequency due to global warming, it is necessary to consider the contributions and sources of UFPs and organic chlorides caused by the reaction of wildfire emissions with Cl atoms.
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