Temporal-spatial characteristics and source apportionment of PM 2.5 as well as its associated chemical species in the Beijing-Tianjin-Hebei region of China

• Published in: Environmental pollution (1987) Vol. 233; p. 714
• Main Authors: Gao, Jiajia, Wang, Kun, Wang, Yong, Liu, Shuhan, Zhu, Chuanyong, Hao, Jiming, Liu, Huanjia, Hua, Shenbing, Tian, Hezhong
• Format: Journal Article
• Language: English
• Published: England 01.02.2018
• Subjects: Beijing-Tianjin-Hebei region; Spatial and temporal characteristics; PM(2.5); Chemical composition; Source apportionment
• ISSN: 1873-6424

PM and its major chemical compositions were sampled and analyzed in January, April, July and October of 2014 at Beijing (BJ), Tianjin (TJ), Langfang (LF) and Baoding (BD) in order to probe the temporal and spatial characteristics as well as source apportionment of PM in the Beijing-Tianjin-Hebei (BTH) region. The results showed that PM pollution was severe in the BTH region. The average annual concentrations of PM at four sampling sites were in the range of 126-180 μg/m , with more than 95% of sampling days exceeding 35 μg/m , the limit ceiling of average annual concentration of PM regulated in the Chinese National Ambient Air Quality Standards (GB3095-2012). Additionally, concentrations of PM and its major chemical species were seasonally dependent and demonstrated spatially similar variation characteristics in the BTH region. Concentration of toxic heavy metals, such as As, Cd, Cr, Cu, Mn, Ni, Pb, Sb, Se, and Zn, were higher in winter and autumn. Secondary inorganic ions (SO , NO , and NH ) were the three-major water-soluble inorganic ions (WSIIs) of PM and their mass ratios to PM were higher in summer and autumn. The organic carbon (OC) and elemental carbon (EC) concentrations were lower in spring and summer than in autumn and winter. Five factors were selected in Positive Matrix Factorization (PMF) model analysis, and the results showed that PM pollution was dominated by vehicle emissions in Beijing, combustion emissions including coal burning and biomass combustion in Langfang and Baoding, and soil and construction dust emissions in Tianjin, respectively. The air mass that were derived from the south and southeast local areas around BTH regions reflected the features of short-distant and small-scale air transport. Shandong, Henan, and Hebei were identified the major potential sources-areas of secondary aerosol emissions to PM .