The washout effects of rainfall on atmospheric particulate pollution in two Chinese cities☆
Graphical abstract
Introduction
With increasing attention to dust-haze and related harmful health effects in China, air pollution has become a significant environmental concern for the public and policy makers (WHO, 2011, Rauhala, 2013, Xu et al., 2013). One of the major factors that causes dust-haze is atmospheric particles, especially PM2.5 (particulate matter with an aerodynamic diameter less than 2.5 μm), which originates mainly from fuel combustion, construction dust and vehicle exhaust (Vingarzan and Li, 2006). The natural and anthropogenic processes for reducing atmospheric particle levels are important to improve air quality.
Rainfall is recognized as one of the main natural processes to improve air quality (Duhanyan and Roustan, 2011, Elperin et al., 2011), and it can greatly enhance the positive reductions achieved by anthropogenic control measures (Leung and Gustafson, 2005). Our previous study assessed the rainfall removal efficiency for total suspended particles (TSP) and found that artificial rain interventions may worsen air quality due to the lower removal of TSP without rainfall (Guo et al., 2014). However, there is limited information about the washout of particles and improvement in air quality following a single rain event and corresponding lag effects, as previous studies usually combined several rain events in one sample or focused on insufficient daily samples (Mattiot and Scafe, 1999, Encinas et al., 2004, He and Balasubramanian, 2009, Huang et al., 2009, Guo et al., 2014). Moreover, the results for analyzing washout of TSP are not applicable to a more narrowly defined specific size range of particle (e.g., PM2.5), as the washout effects are variable among different sizes of particles (Baklanov and Sørensen, 2001, Wang et al., 2010).
Numerous studies have conducted experimental and theoretical assessments on scavenging coefficients; a microphysical approximation of the particle washout effect by raindrops (Slinn, 1984, Flossmann et al., 1985, Volken and Schumann, 1993, Mircea et al., 2000, Andronache, 2003, Laakso et al., 2003, Loosmore and Cederwall, 2004, Bae et al., 2006, Feng, 2007, Wang et al., 2010, Quérel et al., 2014a, Quérel et al., 2014b, Wang et al., 2014). However, due to the complex collection of microphysical parameters (e.g., raindrop diameter, particle diameter, collision efficiency between raindrop and atmospheric particles, etc.) and huge computing resources required (Mircea et al., 2000, Bae et al., 2006, Wang et al., 2010), the scavenging coefficient is not easy to calculate, and therefore not suitable to evaluate air quality directly. Instead of linking air quality to scavenging coefficient, an approach is needed that links it to observable meteorological parameters such as rainfall conditions (Quérel et al., 2014b). Also, focusing on observable parameters may allow a more direct evaluation of the change in air quality following rain. For example, rainfall may worsen air quality following low amounts of precipitation (Levin and Cotton, 2008, Feng and Wang, 2012, Yuan, 2014) and identifying the critical threshold which corresponds to precipitation amount may help to discriminate and forecast changes in air quality.
In view of this knowledge gap, we assessed the removal effects of rainfall by collecting daily PM2.5 and PM2.5–10 (particulate matter with an aerodynamic diameter between 2.5 and 10 μm) concentrations and meteorological factors (wind speed and precipitation) in Guangzhou and Xi'an during 2013 and 2014. This study aims to provide a quantitative description of the rainfall washout effect using a new approach, which can enhance the knowledge for evaluating particulate pollution, and hence assist in implementing efficient control measures to cope with worsening air quality.
Section snippets
Study setting and data collection
Two cities were selected to explore rainfall washout effects on particles. One is Guangzhou, a coastal city in South China with high amounts of precipitation, e.g., annual average precipitation of 2200 mm in 2014 (http://cdc.nmic.cn/home.do). The other is Xi'an, an inland city in Northwest China with low amounts of precipitation, e.g., annual average precipitation of 660 mm in 2014 (http://cdc.nmic.cn/home.do). The two cities have a similar annual wind speed (2.3 ± 0.97 km h−1 for Guangzhou and
Results
Average daily concentrations of PM2.5 and PM2.5–10 in Guangzhou were relatively lower than those in Xi'an. In Guangzhou, concentrations of PM2.5 and PM2.5–10 were 50 ± 26 μg m−3 (range: 9.3–160 μg m−3) and 21 ± 9.9 μg m−3 (range: 0.53–66 μg m−3), respectively (Table 1). In Xi'an, the concentrations of PM2.5 and PM2.5–10 were 89 ± 77 μg m−3 (range: 9.6–900 μg m−3) and 75 ± 56 μg m−3 (range: 4.1–640 μg m−3), respectively (Table 1). The daily average rainfall was 6.0 ± 15 mm in Guangzhou and
Discussion
We observed different relative effects on particulate concentration with different particle sizes, namely PM2.5 and PM2.5–10, suggesting that the washout effect of rainfall on particle is dependent on particle size, with greater effects for the coarser particle fraction. Similar conclusions were made in previous studies that used a microphysical approach, i.e., theoretical and experimental research on scavenging coefficients (Slinn, 1984, Flossmann et al., 1985, Volken and Schumann, 1993,
Conclusions
We calculated the relative effect of rainfall on atmospheric particle concentrations; an approach which directly describes the decreases in atmospheric particle levels using a precipitation amount. Given the theory relating to scavenging coefficients and the differing characteristics for each of the two city study locations described here, it can be deducted that the relative effect of particle washout was influenced by particle size and raindrop size. The existence of a rainfall threshold
Acknowledgements
The present study was financially supported by the public welfare research program of National Health and Family Planning Commission of China (No. 201402022) and China Postdoctoral Science Foundation (No. 2015M572282).
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