Large-scale COVID-19 viral pneumonia through human-to-human transmission poses a severe and acute public health emergency (C. Huang et al., 2020; Li et al., 2020). As the epidemic worsened, most countries imposed city lockdown and quarantine measures to reduce transmission to control the epidemic. The Chinese government has gradually implemented a city-wide quarantine of Wuhan and several surrounding cities as of 23 January, flights and trains to and from Wuhan have been suspended, and public transport has been halted (Cyranoski et al., 2020; Wu et al., 2020). The entire northern Italy was quarantined since 9 March 2020, and three days later the government extended it to the whole country (Paterlini, 2020). The Spanish government declared a national emergency, starting on 15 March (Legido-Quigley et al., 2020). In Germany, since 18 March, 16 states have closed, public gatherings of more than two people have been banned, and most shops except supermarkets and pharmacies have closed (Dehning et al., 2020). The worldwide lockdown, which was imposed to stop the spread of the novel coronavirus, not only caused an economic downturn but also appeared to result in cleaner air in urban areas usually heavily affected by pollution (Lian et al., 2020; Schiermeier, 2020). The most important measure of the lockdown policy was the reduction of traffic and control personnel flow, and traffic pollution is an important factor influencing air quality and public health. Vehicle exhaust and evaporation emissions are the main emission sources of ozone and secondary particle precursors near the ground in cities and regions (Zhou et al., 2019; Yuan et al., 2013), and the spatial variation of nitrogen dioxide (NO 2), fine particulate matter (PM 2.5), and black carbon (BC) may also be significant affected by traffic flow density (Clougherty et al., 2013). A study in Los Angeles showed that nitrogen oxides (NO x) were identified as a source of pollution for light vehicles, with NO 2 , NO x , carbon dioxide (CO 2), BC, and fine particle number (PN fine) identified as diesel exhaust sources (Fan et al., 2018; Tessum et al., 2018). In South Korea, source analysis studies have shown that there is a high correlation between estimated traffic volume and NO 2 concentration (Kim et al., 2015). NO 2 levels can be used as a proxy for exposure to traffic-related composite air pollution and to assess the impact of scenarios designed to reduce traffic-related emissions (Brnnum-Hansen et al., 2018; Johansson et al., 2017).