Spatiotemporal variation of atmospheric nitrated polycyclic aromatic hydrocarbons in semi-arid and petrochemical industrialized Lanzhou City, Northwest China

• Published in: Environmental science and pollution research international 2019-01, Vol.26 (2), p.1857-1870
• Main Authors: Liu, Panliang, Ju, Yuanli, Li, Yaojie, Wang, Zhanxiang, Mao, Xiaoxuan, Cao, Hongmei, Jia, Chenhui, Huang, Tao, Gao, Hong, Ma, Jianmin
• Format: Article
• Language: English
• Subjects: Air sampling; Aluminum; Anthracene; Aquatic Pollution; Aridity; Atmospheric Protection/Air Quality Control/Air Pollution; Chemical reactions; Deposition; Dry deposition; Earth and Environmental Science; Ecotoxicology; Environment; Environmental Chemistry; Environmental Health; Environmental science; Fluxes; Fog; Iron and steel plants; Naphthalene; Organic chemistry; Oxidation; Petrochemicals; Petrochemicals industry; Polycyclic aromatic hydrocarbons; Polyurethane; Polyurethane foam; Research Article; Steel industry; Summer; Vehicle emissions; Waste Water Technology; Water Management; Water Pollution Control; Winter
• ISSN: 0944-1344; 1614-7499
• DOI: 10.1007/s11356-018-3633-3

Polyurethane foam-based passive air sampler (PUF-PAS) and passive dry deposition sampler (PAS-DD) were adopted, for the first time ever in China, to investigate the atmospheric levels and spatial-temporal distributions of air burdens and dry deposition fluxes of 12 nitrated polycyclic aromatic hydrocarbons (NPAHs) during winter and summer seasons in a multiple site field campaign in a petrochemical industrialized capital city in Northwest China. The results showed that the highest air concentration and dry deposition fluxes of ∑ 12 NPAHs occurred at a heavy traffic site among 18 sampling sites in both winter and summer season. The lowest air concentration and dry deposition fluxes were observed at the background site. The mean concentrations of ∑ 12 NPAHs in the ambient air were 8.6 ± 8.1 ng m −3 in winter and 15 ± 11 ng m −3 in summer. The mean dry deposition fluxes of ∑ 12 NPAHs were 1.8 × 10 3  ± 1.9 × 10 3  ng (m 2  day) −1 in winter and 1.4 × 10 3  ± 1.3 × 10 3  ng (m 2  day) −1 in summer, respectively. The total concentration of 12 NPAHs was mainly dominated by 1-nitro-naphthalene (1N-NAP) and 2-nitro-naphthalene(2N-NAP) in air, accounting for 32% in winter and 45% in summer of ∑ 12 NPAHs. 7-Nitro-benzo [a] anthracene (7N-BaA) made the largest contribution to dry deposition fluxes of ∑ 12 NPAHs, accounting for 28% in winter and 24% in summer. The ratios of ∑ 12 NPAHs/∑ 15 pPAHs (parent polycyclic aromatic hydrocarbons) were calculated to identify potential sources of NPAHs across the city. The results revealed that the main atmospheric air concentration and dry deposition fluxes of 12 NPAHs could be attributed to the primary emissions in winter and the secondary reaction formation in summer. The sources of primary emissions could be traced back to petrochemical, steel mills, as well as aluminum industries in winter and vehicle exhaust in summer. Higher ∑ 12 NPAH/∑ 15 pPAH concentration ratios in summer indicated that the oxidation of pPAHs contributed to the secondary formation of NPAHs via atmospheric chemical reactions in this petrochemical industrialized mountain-valley city.