Abstract
Abstract. As one of the intense anthropogenic emission regions across the relatively high-latitude (>40∘ N) areas on Earth, northeast China faces the serious problem of regional haze during the heating period of the year. Aerosols in polluted haze in northeast China are poorly understood compared with the haze in other regions of China such as the North China Plain. Here, we integrated bulk chemical measurements with single-particle analysis from transmission electron microscopy (TEM), nanoscale secondary ion mass spectrometry (NanoSIMS), and atomic force microscopy (AFM) to obtain morphology, size, composition, aging process, and sources of aerosol particles collected during two contrasting regional haze events (Haze-I and Haze-II) at an urban site and a mountain site in northeast China and further investigated the causes of regional haze formation. Haze-I evolved from moderate (average PM2.5: 76–108 µg m−3) to heavy pollution (151–154 µg m−3), with the dominant PM2.5 component changing from organic matter (OM) (39–45 µg m−3) to secondary inorganic ions (94–101 µg m−3). Similarly, TEM observations showed that S-rich particles internally mixed with OM (named S-OM) increased from 29 % to 60 % by number at an urban site and 64 % to 74 % at a mountain site from the moderate Haze-I to heavy Haze-I events, and 75 %–96 % of Haze-I particles included primary OM. We found that change of wind direction caused Haze-I to rapidly turn into Haze-II (185–223 µg m−3) with predominantly OM (98–133 µg m−3) and unexpectedly high K+ (3.8 µg m−3). TEM also showed that K-rich particles internally mixed with OM (named K-OM) increased from 4 %–5 % by number to 50 %–52 %. The results indicate that there were different sources of aerosol particles causing the Haze-I and Haze-II formation: Haze-I was mainly induced by accumulation of primary OM emitted from residential coal burning and further deteriorated by secondary aerosol formation via heterogeneous reactions; Haze-II was caused by long-range transport of agricultural biomass burning emissions. Moreover, abundant primary OM particles emitted from coal and biomass burning were considered to be one typical brown carbon, i.e., tar balls. Our study highlights that large numbers of light-absorbing tar balls significantly contribute to winter haze formation in northeast China and they should be further considered in climate models.
Highlights
Haze pollution is mainly caused by high levels of fine particulate matter (PM2.5), and it has spread widely over the globe to places such as Mexico City (Adachi and Buseck, 2008), Paris, France (Fortems – Cheiney et al, 2016), north India (Chowdhury et al, 2019), north China (Huang et al, 2014), and the Arctic (Frossard et al, 2011)
Regional haze pollution was observed in northeast China from 31 October to 5 November 2016 (Fig. S3)
To understand the formation mechanisms of winter haze in northeast China, we carried out an aerosol experiment at an urban site and a mountain site in the south part of northeast China from 25 October to 6 November 2016
Summary
Haze pollution is mainly caused by high levels of fine particulate matter (PM2.5), and it has spread widely over the globe to places such as Mexico City (Adachi and Buseck, 2008), Paris, France (Fortems – Cheiney et al, 2016), north India (Chowdhury et al, 2019), north China (Huang et al, 2014), and the Arctic (Frossard et al, 2011). J. Zhang et al.: Exploring wintertime regional haze regional haze events with high concentrations of PM2.5 have frequently occurred in China following rapid economic development. Current hot issues on haze pollution concentrate on the formation processes of regional haze in various atmospheric environments and their potential optical and health influences Current hot issues on haze pollution concentrate on the formation processes of regional haze in various atmospheric environments and their potential optical and health influences (J. Chen et al, 2017; Gao et al, 2017)
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