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The importance of vehicle emissions as a source of atmospheric ammonia in the megacity of Shanghai
oleh: Y. Chang, Y. Chang, Z. Zou, C. Deng, C. Deng, K. Huang, K. Huang, K. Huang, J. L. Collett, J. Lin, J. Lin, G. Zhuang, G. Zhuang
Format: | Article |
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Diterbitkan: | Copernicus Publications 2016-03-01 |
Deskripsi
Agricultural activities are a major source contributing to NH<sub>3</sub> emissions in Shanghai and most other regions of China; however, there is a long-standing and ongoing controversy regarding the contributions of vehicle-emitted NH<sub>3</sub> to the urban atmosphere. From April 2014 to April 2015, we conducted measurements of a wide range of gases (including NH<sub>3</sub>) and the chemical properties of PM<sub>2.5</sub> at hourly resolution at a Shanghai urban supersite. This large data set shows NH<sub>3</sub> pollution events, lasting several hours with concentrations 4 times the annual average of 5.3 µg m<sup>−3</sup>, caused by the burning of crop residues in spring. There are also generally higher NH<sub>3</sub> concentrations (mean ± 1 <i>σ</i>) in summer (7.3 ± 4.9 µg m<sup>−3</sup>; <i>n</i> = 2181) because of intensive emissions from temperature-dependent agricultural sources. However, the NH<sub>3</sub> concentration in summer was only an average of 2.4 µg m<sup>−3</sup> or 41 % higher than the average NH<sub>3</sub> concentration of other seasons. Furthermore, the NH<sub>3</sub> concentration in winter (5.0 ± 3.7 µg m<sup>−3</sup>; <i>n</i> = 2113) was similar to that in spring (5.1 ± 3.8 µg m<sup>−3</sup>; <i>n</i> = 2198) but slightly higher, on average, than that in autumn (4.5 ± 2.3 µg m<sup>−3</sup>; <i>n</i> = 1949). Moreover, other meteorological parameters like planetary boundary layer height and relative humidity were not major factors affecting seasonal NH<sub>3</sub> concentrations. These findings suggest that there may be some climate-independent NH<sub>3</sub> sources present in the Shanghai urban area. Independent of season, the concentrations of both NH<sub>3</sub> and CO present a marked bimodal diurnal profile, with maxima in the morning and the evening. A spatial analysis suggests that elevated concentrations of NH<sub>3</sub> are often associated with transport from regions west–northwest and east–southeast of the city, areas with dense road systems. The spatial origin of NH<sub>3</sub> and the diurnal concentration profile together suggest the importance of vehicle-derived NH<sub>3</sub> associated with daily commuting in the urban environment. To further examine vehicular NH<sub>3</sub> emissions and transport, sampling of the NH<sub>3</sub> concentration was performed in (from the entrance to the exit of the tunnel) and out (along a roadside transect spanning 310 m perpendicular to the tunnel) of a heavily trafficked urban tunnel during the spring of 2014. NH<sub>3</sub> concentrations in the tunnel exit were over 5 and 11 times higher than those in the tunnel entrance and in the ambient air, respectively. Based on the derived mileage-based NH<sub>3</sub> emission factor of 28 mg km<sup>−1</sup>, a population of 3.04 million vehicles in Shanghai produced around 1300 t NH<sub>3</sub> in 2014, which accounts for 12 % of total NH<sub>3</sub> emissions in the urban area. Collectively, our results clearly show that vehicle emissions associated with combustion are an important NH<sub>3</sub> source in Shanghai urban areas and may have potential implications for PM<sub>2.5</sub> pollution in the urban atmosphere.