Atmospheric 2-nitrofluoranthene (2-NFL) and 2-nitropyrene (2-NPY) were two important nitro-polycyclic aromatic hydrocarbons (NPAHs). Especially, 2-NFL was recognized to be the most abundant particle-associated NPAH . In previous studies, these two products were observed in the gas-phase reaction between N 2 O 5 /NO 3 /NO 2 and their parent polycyclic aromatic hydrocarbons (PAHs), while the heterogeneous reaction generated other nitro-PAH isomers (1, 3, 7, 8-NFL and 1-NPY) (Atkinson et al. 1990). To clarify the possible reasons for this difference, the heterogeneous reactions of suspended fluoranthene (FL) and pyrene (PY) particles under different relative humidity (RH; 0.5%−43%) and [NO 3 + (aq)] in the particle surface has an influence on the product distribution of FL and PY in the atmosphere. The experimental results provide evidence for the heterogeneous formations of particle-bound 2-NFL and 2-NPY. However, relative to the gas-phase formation, they will be negligible in the real atmosphere. 2-NFL and 2-NPY observed in the ambient particles should mainly derive from deposition of gas-phase reactions. Additionally, this study also clarifies the reason for different nitro-PAHs isomers observed between gas and particulate reactions.
■ INTRODUCTIONThe atmospheric chemistry between polycyclic aromatic hydrocarbons (PAHs) and gas-phase oxidants (O 3 , OH, NO 3 , and NO 2 ) is the most important source of toxic and mutagenic PAH derivatives (nitro-PAHs and oxy-PAHs) in the atmosphere. 1−6 Nitro-PAHs (NPAHs) have mutagenic potencies up to 100 000 times greater than PAHs 7−10 and constitute 10% of the total mutagenicity of inhalable particles in the ambient atmosphere. 11,12 Additionally, these nitrated species especially have strong narrow band adsorption bands in the UV−visible range, which may enhance the radiative forcing in the atmosphere and therefore contribute to significant climate effects. 13,14 Both 2-nitrofluoranthene (2-NFL) and 2-nitropyrene (2-NPY) are two ubiquitous nitro-PAH pollutants and ambient 2-NFL/2-NPY ratio is generally used to assess the contribution of the NO 3 radical chemistry for NPAHs formation. 15−18 Considering that neither 2-NFL nor 2-NPY have been directly observed from combustion emissions, 19−21 most research has focused on the contribution of the atmospheric reactions of FL and PY with gas-phase oxidants (OH or NO 3 radicals in the presence of NO 2 ). Some studies have suggested that these two nitro-PAHs were formed exclusively via atmospheric gas-phase reactions of FL and PY. 22,23 The production of 2-NFL involves the gas-phase reaction between FL and either OH or NO 3 radicals in the presence of NO 2 , whereas the production of 2-NPY mainly involves the gas-phase reaction of PY initiated by OH radical. 24−27 The formation of both 2-NFL and 2-NPY in the gas phase is a multistep addition−elimination reaction initiated by OH or NO 3 radical species. This radical-initiated reaction is postulated to proceed by an initiated-addition of OH radical (present during the day...