Comparison of chemical composition and acidity of size-resolved inorganic aerosols at the top and foot of Mt. Hua, Northwest China: The role of the gas-particle distribution of ammonia.

Sci Total Environ

State Key Laboratory of Loess and Quaternary Geology, Key Lab of Aerosol Chemistry and Physics, Institute of Earth Environment, Chinese Academy of Sciences, Xi'an 710061, China; National Observation and Research Station of Regional Ecological Environment Change and Comprehensive Management in the Guanzhong Plain, Shaanxi, China. Electronic address:

Published: December 2023

Aerosol pH is not only a diagnostic indicator of secondary aerosol formation, but also a key factor in the specific chemical reaction routes that produce sulfate and nitrate. To understand the characteristics of aerosol acidity in the Mt. Hua, the chemical fractions of water-soluble inorganic ions in the atmospheric PM and size-resolved particle at the top and foot of Mt. Hua in summer 2020 were studied. The results showed the mass concentrations of PM and water-soluble ions at the foot were 2.0-2.6 times higher than those at the top. The secondary inorganic ions, i.e., SO, NO, and NH (SNA) were 56 %-61 % higher by day than by night. SO was mainly distributed in the fine particles (D < 2.1 μm). NO showed a unimodal size distribution (peaking at 0.7-1.1 μm) at the foot and a bimodal (0.7-1.1 μm and 4.7-5.8 μm) size distribution at the top. At the top site, the distribution of NO in coarse particles (> 2.1 μm) was mainly attributed to the gaseous HNO volatilized from fine particles reacting with cations in coarse particles to form non-volatile salts (such as Ca(NO)). The pH values of PM were 2.7 ± 1.3 and 3.3 ± 0.42 at the top and foot, respectively. NH/NH(g) plays a decisive role in stabilizing aerosol acidity. In addition, the increase of the liquid water content (LWC) at the foot facilitates the gas-particle conversion of NH, while the H concentration was diluted, resulting in a decrease in acidity at the foot. NH/NH had good linear correlations with SO, NO, and LWC during the daytime at both sites, indicating that SO, NO, and LWC together affect the gas-particle distribution of ammonia by day: however, the effect of LWC at night was not evident.

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http://dx.doi.org/10.1016/j.scitotenv.2023.166985DOI Listing

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