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Articles

Wet deposition and scavenging ratio of air pollutants during an extreme rainstorm in the North China Plain

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Pages 348-353 | Received 06 Mar 2017, Accepted 03 May 2017, Published online: 29 Jun 2017

Abstract

Atmospheric wet deposition plays an important role in the supply of nutrients and toxic substances to terrestrial and aquatic environments. Although long-term (e.g. annual, multi-year) wet deposition is recorded well, pronounced and short-term changes in precipitation chemistry are less well investigated. In the present study, the precipitation chemistry and scavenging ratio of air pollutants were observed during an extreme torrential rain event (325.6 mm at the observation site) that occurred over 19–21 July 2016 in the North China Plain (NCP). The scavenging ratio of particles showed a similar spatial distribution to that of the precipitation amount in the NCP, indicating the efficient removal of particulate matter due to the large amount and precipitation intensity of the storm. In addition, the scavenging ratio of water soluble ions was larger than that of organics and gaseous pollutants such as SO2 and NO2, likely due to their differences in water solubility. Consequently, raindrops incorporated more aerosol sulfate than gaseous compounds. Due to the heavy precipitation amount, almost all species in rainwater during this storm showed their lowest concentration but the highest flux compared with other rain events, indicating an important role played by this storm in terms of the substances received by the terrestrial and marine ecosystems of the region. However, the contribution of this storm to the annual chemical flux was lower than that of precipitation amount, indicating that the atmospheric compounds were scavenged below-cloud first and were then diluted by the cloud/rainwater. Future studies are needed in the context of the occurrence of extreme rainfall events in the NCP from the perspective of climate variability.

摘要

大气湿沉降是陆地和水体环境中营养成分和有毒物质的重要来源。以往湿沉降研究较多关注年尺度或年际变化,极端降水事件鲜见报道。通过实验观测,发现2016年7月19–21日华北极端暴雨(北京观测站 325.6 mm)有效清除了区域大气颗粒物,但不同化学成分被湿清除的效率存在差异(无机离子比有机物和气态污染物更容易被湿清除)。此次极端降水铵盐和硝酸盐的湿沉降通量占北京全年的22%和4%,相当于青藏高原一年的氮沉降。考虑到气候背景下极端暴雨出现的频次,极端降水的生态环境影响需要更精细化的评估。

1. Introduction

The removal of pollutants via wet deposition is considered an important pathway in cleansing the atmosphere (Bourcier et al. Citation2012), and equally important as dry deposition in terms of the inputs of nutrients and toxic substances to the affected terrestrial and marine ecosystems (Dentener et al. Citation2006; Pan and Wang Citation2015). Wet deposition of air pollutants is also known to be episodic, i.e. a small proportion of events contribute a large portion of the annual deposition (Smith and Hunt Citation1978). This episodic nature of wet deposition has been investigated over western Europe, Scandinavia, and eastern North America (Brook Citation1995; Smith and Hunt Citation1978), with highly episodic areas tending to be downwind of major emission regions. In the global emissions hotspot of East Asia, however, previous reports have tended to focus on the long-term (e.g. annual, multi-year) wet deposition flux (Pu et al. Citation2017; Wang et al. Citation2012; Li et al. Citation2010), with less attention paid to the basic characteristics of pronounced and short-term changes in precipitation chemistry. Thus, there is a need to address this knowledge gap, particularly with respect to the occurrence of extreme rainfall events in the context of climate variability (Pei et al. Citation2016), but also considering that episodic wet deposition can have a significant biological impact too (Davies et al. Citation1992).

On 19–21 July 2016, an extreme torrential rain event swept across the North China Plain (NCP), resulting in the daily precipitation record being broken at Fangshan station, Beijing, where the amount reached 381.7 mm. This event was named the Beijing ‘720’ rainstorm, and provided a unique opportunity to examine the episodic features of rainstorms in the NCP. The primary goal of the present study was to investigate the spatial distribution of particle removal during this rainstorm event in the NCP. The in situ surface measurements from rainwater, particle composition, and gaseous pollutants in Beijing were also used to examine the scavenging efficiency of the compounds in the air and to provide insight into the wet deposition features of various species during this extreme rainstorm. Overall, our expectation was to provide results that are useful for determining the important sources contributing to wet deposition, validating the removal mechanisms for atmospheric chemistry models, and setting a baseline against which rainstorm chemistry changes can be assessed.

2. Experimental details

2.1. Measurement site

The rainwater sampling for chemical analysis was performed at the Institute of Atmospheric Physics (IAP), Chinese Academy of Sciences, in urban Beijing (39°58′N, 116°22′E). The site description is detailed in Pan et al. (Citation2012).

2.2. Rainfall sampling and chemical analysis

Rainwater was sampled using an automatic collector (APS-2B, Changsha Xianglan Scientific Instruments Co., Ltd.), equipped with a 707-cm2 aperture. The pretreatment and chemical analysis of the rainwater samples is described in Pan et al. (Citation2010, Citation2013).

2.3. Supporting data

The submicron aerosol composition of PM1 at the IAP site was measured with HR-ToF-AMS (Aerodyne Research, Inc., USA), following previously reported procedures (Zhang et al. Citation2014). In addition, the concentrations of PM2.5, SO2, O3, and NO2 in the NCP were derived from the urban air quality real-time publishing platform of the China National Environmental Monitoring Centre (http://106.37.208.233:20035/) and the Beijing Municipal Environmental Protection Bureau (http://zx.bjmemc.com.cn/).

The rainfall amount in the NCP was obtained from the meteorological observation stations available at http://cdc.cma.gov.cn/. In addition, an automatic meteorological observation instrument (Milos520, Vaisala, Finland) at the IAP site was used to observe meteorological parameters, including relative humidity, temperature, wind direction, and wind speed.

3. Results and discussion

3.1. Spatial distribution of the removal of PM2.5 in the North China Plain

The extreme ‘720’ rainstorm covered the main NCP, as illustrated in Figure . The accumulated precipitation amounts ranged from 98.5 to 381.7 mm, averaging 231.7 mm from 20 stations in the Beijing region (Figure ). To examine how the air pollutants were reduced due to this storm, the scavenging ratio (SR) of PM2.5 was calculated based on the equation below:

Figure 1. Spatial distribution of the precipitation amount and scavenging ratio of fine particles during the ‘720’ rainstorm in 2016.

Figure 1. Spatial distribution of the precipitation amount and scavenging ratio of fine particles during the ‘720’ rainstorm in 2016.

Here, Cb and Ca represent the concentration of air pollutants before and after the rain event, respectively. Since aerosol pollution in the NCP is regional in nature, the SR estimated here represents the overall reduction of aerosol concentrations at a large scale in addition to the local site. Regional transport/dispersion contributes approximately 30% of aerosol mass concentrations in Beijing (Tian, Pan, and Wang Citation2016), and this contribution was expected to have decreased during the storm due to the washing effect on aerosol loading in source regions, even though the wind speed was high.

The spatial distribution of the SR of PM2.5 is also shown in Figure (dotted). As is apparent, the SR of PM2.5 in Hebei, Shandong, and Beijing was 75.8%–97.8%, 53.7%–95.8% and 89.4%–97.3%, respectively. The lower values in Shandong Peninsula were due to the lower precipitation amount. In contrast, the higher values were almost all located in the regions with high rainfall in the NCP. These findings indicate the efficient removal of particulate matter due to the storm. This is further evidenced from previous records in Beijing that short-term rainstorms have a stronger washing effect on PM2.5 than that of light rain (Ouyang et al. Citation2015).

To examine the influences of rainfall on the concentrations of various air pollutants during the ‘720’ rainstorm, Figure shows the time series of chemical species in the air and the meteorological parameters before, during, and after the storm at the Beijing site where chemical data were available. As shown, both the aerosol composition (PM2.5 and PM1, as well as organics, , , , and Cl in PM1) and gaseous pollutants (SO2, NO2 and O3) decreased rapidly after the storm began. In addition, most of these species shared a similar temporal pattern, with the exception of SO2. The high wind speeds during the rain event may have brought air masses from outside Beijing into the IAP site and thus supplemented the levels of SO2 (Guo et al. Citation2014). The precipitation scavenging ratio of various chemical species was also calculated, and is discussed below.

Figure 2. Hourly variation of precipitation, wind speed (WS), wind direction (WD) and concentrations of aerosol and gaseous pollutants during 18–22 July 2016.

Figure 2. Hourly variation of precipitation, wind speed (WS), wind direction (WD) and concentrations of aerosol and gaseous pollutants during 18–22 July 2016.

3.2. Scavenging ratio of air pollutants in urban Beijing

In general, the SRs of the mass concentrations and chemical compositions were higher than those of gaseous pollutants during the ‘720’ rainstorm (Table ). For the PM1 compositions, the SRs of , , Cl, and (~0.95) were higher than that of organics (0.85). The difference in the SR between the water soluble species and carbonaceous aerosols may have been due to their differences in water solubility (González and Aristizábal Citation2012; Pan and Wang Citation2015). However, the SRs of gaseous pollutants were lower than 0.65, except for O3 (0.92). The large SR of O3 may be attributable to the removal of precursors and the limited photochemical production of O3.

Table 1. Scavenging ratio (SR) of each species due to rain events in July 2016.

We also calculated the SR for seven other rain events in July 2016 and found that the SRs of most species (except SO2) correlated well with the rain intensity being greater than 2 mm h−1. This finding indicates that rain intensity plays a more important role than the precipitation amount in the removal of air pollutants (González and Aristizábal Citation2012).

To further quantify the relative contributions of aerosol and gaseous pollutants to rainwater chemistry, we assumed that all the scavenged aerosol and SO2 gas was incorporated into the rainwater collected at the surface site, and we then calculated the scavenging amount (SA) of sulfur in the air as follows:

Here, Cb and Ca represent the concentrations of or SO2 before and after the rain event, respectively; and 1.88 is the extrapolation ratio of PM1 to that of total suspended particles (Tian, Pan, and Wang Citation2016).

The results show that the SA of -S was 7.17 times that of SO2-S, indicating that aerosol contributed 88% to rainwater sulfur during this storm. We also calculated the contribution of aerosol to rainwater sulfur during other events in July and found that the values ranged from 0.20 to 7.17. The values depended on both the precipitation amount (R2 = 0.59, p < 0.05) and rain intensity (R2 = 0.86, p < 0.05), indicating heavy rainfall removed more aerosol sulfate than gaseous SO2. Due to the higher solubility of , it was found that high sulfate SRs were associated with increased rain intensity in a mid-sized Andean city (González and Aristizábal Citation2012).

3.3. Wet deposition of water soluble species in urban Beijing

Figure shows the concentrations and fluxes of water soluble ions in rainwater during the ‘720’ rainstorm and other rain events in July. The concentrations of ions during the ‘720’ storm were all lower than the other rainfall events recorded between December 2015 and November 2016 at the IAP site, due to the dilution effect of the extreme rainfall amount. With the exception of Mg2+ and Ca2+, the concentrations of ions during the ‘720’ storm are lower than the values observed in recent decades at the regional background site of Shangdianzi in the NCP (Pu et al. Citation2017; Li et al. Citation2010) and are comparable to the global background site of Waliguan in China (Pu et al. Citation2017). Thus, the precipitation chemistry observed in this study can serve as a baseline against which rainstorm chemistry changes in Beijing in the future can be assessed. The major ions during this storm were Ca2+, , , and , with concentrations of 6.1, 1.7, 1.1, and 0.8 mg L−1 (Table ), respectively, which are orders of magnitude higher than those observed at high-altitude Himalayan stations in eastern India (Roy et al. Citation2016) and a southwest site of Mexico City, Mexico (Báez et al. Citation2007) or the background EMEP station in Víznar (Granada, Spain) (Calvo et al. Citation2010). This finding indicates that, although the major ions during this storm were the lowest on record at the IAP site, the rainwater chemistry in Beijing is significantly affected by anthropogenic emissions.

Figure 3. Concentrations and wet deposition fluxes of water soluble species in rainwater collected in July 2016.

Figure 3. Concentrations and wet deposition fluxes of water soluble species in rainwater collected in July 2016.

Table 2. Concentrations and fluxes of water soluble species in rainwater collected during the ‘720’ rainstorm and from December 2015 to November 2016.

As shown in Table , the wet deposition fluxes of Na+, , K+, Mg2+, Ca2+, Cl, , and were 18.8, 539.9, 0.8, 199.2, 1987.2, 31.52, 270.3, and 351.6 mg m−2 d−1, respectively, which contributed 3%, 21.8%, 0.4%, 22.1%, 27.1%, 1.9%, 3.8%, and 5.2% of the annual deposition of these species between December 2015 and November 2016. This finding highlights that wet deposition during this storm had a more important influence on cations than anions. In addition, the wet deposition of inorganic nitrogen ( and ) during this storm was even higher than the annual flux observed at five remote sites in the Tibetan Plateau (Liu et al. Citation2015) and in mountainous heathland ecosystems in northwestern Spain (Calvo-Fernández, Marcos, and Calvo Citation2017), indicating the importance of the nitrogen input during this storm for the receiving terrestrial and marine ecosystems.

The rainy season of the Beijing area is concentrated mainly in summer, and rainstorms often occur in late July and early August (Guo et al. Citation2015). During 1980–2010, the accumulated precipitation amounts in July contributed one-third of the annual precipitation in Beijing. The precipitation amount of the ‘720’ rainstorm was 325.6 mm at the IAP site, which was 41.4% of the annual precipitation from December 2015 to November 2016. If the major source of certain pollutants dissolved in rainwater was entirely from cloud processing, the contribution of wet deposition of these species to the annual flux would be similar to that of the precipitation amount (41.4%). However, the contributions of these species were all lower than 41.4% (Table ), indicating that the air pollutants were likely scavenged below-cloud first and then diluted by the cloud/rainwater (Celle-Jeanton et al. Citation2009). In future, we suggest the application of a sequential sampling technique to record detailed changes of precipitation chemistry during rainstorms at high temporal resolution (e.g. 5–10 min), thus allowing the differentiation of the in-cloud and below-cloud contribution to be determined.

4. Implications

In recent years, extreme torrential rainfall has often hit the NCP during the summer (Guo et al. Citation2015; Pei et al. Citation2016). During the period 19–21 July 2016, Beijing received approximately 232 mm of precipitation, averaged over 20 stations; and in the storm center, over 382 mm was recorded. On the one hand, the air pollutants were removed from the atmosphere efficiently during this storm, contributing significantly to the improvement of air quality. On the other hand, various chemical species were simultaneously deposited via rainfall into the receiving terrestrial and marine ecosystems. As a result, wet deposition of this storm ranked the highest in 2016 and contributed substantially to the annual flux. In addition, the chemical compounds in rainwater collected during this storm originated both from below-cloud and in-cloud processing. This suggests, assuming that the occurrence of rainstorm events depends mainly on meteorological conditions, that decreases in annual wet deposition amounts due to future emissions reduction measures, could be offset by increases in the frequency of meteorological conditions conducive to such episodes (Brook Citation1995).

Disclosure statement

No potential conflict of interest was reported by the authors.

Funding

This study was supported by the National Natural Science Foundation of China [grant number 41405144]; the National Key Research and Development Program of China [grant number 2017YFC0210100], [grant number 2016YFD0800302], [grant number 2016YFC0201802]; and the Science and Technology Service Network Initiative of the Chinese Academy of Sciences [STS Plan, grant number KFJ-SW-STS-168].

References

  • Báez, A., R. Belmont, R. García, H. Padilla, and M. C. Torres. 2007. “Chemical Composition of Rainwater Collected at a Southwest Site of Mexico City, Mexico.” Atmospheric Research 86 (1): 61–75.10.1016/j.atmosres.2007.03.005
  • Bourcier, L., O. Masson, P. Laj, P. Chausse, J. M. Pichon, P. Paulat, G. Bertrand, et al. 2012. “A New Method for Assessing the Aerosol to Rain Chemical Composition Relationships.” Atmospheric Research 118: 295–303.10.1016/j.atmosres.2012.07.020
  • Brook, J. R. 1995. “Wet Acid Deposition Episodicity in Eastern North America and the Influence of Deposition Episodes on Annual Deposition Amounts.” Atmospheric Environment 29 (15): 1795–1807.10.1016/1352-2310(95)00082-A
  • Calvo, A. I., F. J. Olmo, H. Lyamani, L. Alados-Arboledas, A. Castro, M. Fernández-Raga, and R. Fraile. 2010. “Chemical Composition of Wet Precipitation at the Background EMEP Station in Víznar (Granada, Spain) (2002–2006).” Atmospheric Research 96 (2–3): 408–420.10.1016/j.atmosres.2010.01.013
  • Calvo-Fernández, J., E. Marcos, and L. Calvo. 2017. “Bulk Deposition of Atmospheric Inorganic Nitrogen in Mountainous Heathland Ecosystems in North-Western Spain.” Atmospheric Research 183: 237–244.10.1016/j.atmosres.2016.09.006
  • Celle-Jeanton, H., Y. Travi, M.-D. Loÿe-Pilot, F. Huneau, and G. Bertrand. 2009. “Rainwater Chemistry at a Mediterranean Inland Station (Avignon, France): Local Contribution versus Long-Range Supply.” Atmospheric Research 91 (1): 118–126.10.1016/j.atmosres.2008.06.003
  • Davies, T. D., M. Tranter, P. J. Wigington, and K. N. Eshleman. 1992. “‘Acidic Episodes’ in Surface Waters in Europe.” Journal of Hydrology 132 (1): 25–69.10.1016/0022-1694(92)90172-R
  • Dentener, F., J. Drevet, J. Lamarque, I. Bey, B. Eickhout, A. M. Fiore, D. Hauglustaine, et al. 2006. “Nitrogen and Sulfur Deposition on Regional and Global Scales: A Multimodel Evaluation.” Global Biogeochemical Cycles 20 (4).
  • González, C. M., and B. H. Aristizábal. 2012. “Acid Rain and Particulate Matter Dynamics in a mid-Sized Andean City: The Effect of Rain Intensity on Ion Scavenging.” Atmospheric Environment 60: 164–171.10.1016/j.atmosenv.2012.05.054
  • Guo, S., M. Hu, M. L. Zamora, J. Peng, D. Shang, J. Zheng, Z. Du, et al. 2014. “Elucidating Severe Urban Haze Formation in China.” Proceedings of the National Academy of Sciences 111 (49): 17373–17378.10.1073/pnas.1419604111
  • Guo, C., H. Xiao, H. Yang, and Q. Tang. 2015. “Observation and Modeling Analyses of the Macro- and Microphysical Characteristics of a Heavy Rain Storm in Beijing.” Atmospheric Research 156: 125–141.10.1016/j.atmosres.2015.01.007
  • Liu, Y. W., R. Xu, Y. S. Wang, Y. P. Pan, and S. L. Piao. 2015. “Wet Deposition of Atmospheric Inorganic Nitrogen at Five Remote Sites in the Tibetan Plateau.” Atmospheric Chemistry and Physics 15 (20): 11683–11700.10.5194/acp-15-11683-2015
  • Ouyang, W., B. Guo, G. Cai, Q. Li, S. Han, B. Liu, and X. Liu. 2015. “The Washing Effect of Precipitation on Particulate Matter and the Pollution Dynamics of Rainwater in Downtown Beijing.” Science of the Total Environment 505: 306–314.10.1016/j.scitotenv.2014.09.062
  • Pan, Y. P., and Y. S. Wang. 2015. “Atmospheric Wet and Dry Deposition of Trace Elements at 10 Sites in Northern China.” Atmospheric Chemistry and Physics 15 (2): 951–972.10.5194/acp-15-951-2015
  • Pan, Y. P., Y. S. Wang, G. Q. Tang, and D. Wu. 2012. “Wet and Dry Deposition of Atmospheric Nitrogen at Ten Sites in Northern China.” Atmospheric Chemistry and Physics 12 (14): 6515–6535.10.5194/acp-12-6515-2012
  • Pan, Y. P., Y. S. Wang, G. Q. Tang, and D. Wu. 2013. “Spatial Distribution and Temporal Variations of Atmospheric Sulfur Deposition in Northern China: Insights into the Potential Acidification Risks.” Atmospheric Chemistry and Physics 13 (3): 1675–1688.10.5194/acp-13-1675-2013
  • Pan, Y., Y. Wang, J. Xin, G. Tang, T. Song, Y. Wang, X. Li, et al. 2010. “Study on Dissolved Organic Carbon in Precipitation in Northern China.” Atmospheric Environment 44 (19): 2350–2357.10.1016/j.atmosenv.2010.03.033
  • Pei, L., J. Xia, Z. Yan, and H. Yang. 2016. “Assessment of the Pacific Decadal Oscillation’s Contribution to the Occurrence of Local Torrential Rainfall in North China.” Climatic Change 1–13.
  • Pu, W., W. Quan, Z. Ma, X. Shi, X. Zhao, L. Zhang, Z. Wang, et al. 2017. “Long-term Trend of Chemical Composition of Atmospheric Precipitation at a Regional Background Station in Northern China.” Science of the Total Environment 580: 1340–1350.
  • Roy, A., A. Chatterjee, S. Tiwari, C. Sarkar, S. K. Das, S. K. Ghosh, and S. Raha. 2016. “Precipitation Chemistry over Urban, Rural and High Altitude Himalayan Stations in Eastern India.” Atmospheric Research 181: 44–53.10.1016/j.atmosres.2016.06.005
  • Smith, F. B., and R. D. Hunt. 1978. “Meteorological Aspects of the Transport of Pollution over Long Distances.” Atmospheric Environment 12 (1): 461–477.10.1016/0004-6981(78)90229-9
  • Tian, S. L., Y. P. Pan, and Y. S. Wang. 2016. “Size-resolved Source Apportionment of Particulate Matter in Urban Beijing during Haze and Non-Haze Episodes.” Atmospheric Chemistry and Physics 16 (1): 1–19.10.5194/acp-16-1-2016
  • Wang, Y., W. Yu, Y. Pan, and D. Wu. 2012. “Acid Neutralization of Precipitation in Northern China.” Journal of the Air & Waste Management Association 62 (2): 204–211.10.1080/10473289.2011.640761
  • Li, Y., X. Yu, H. Cheng, W. Lin, J. Tang, and S. Wang. 2010. “Chemical Characteristics of Precipitation at Three Chinese Regional Background Stations from 2006 to 2007.” Atmospheric Research 96 (1): 173–183.10.1016/j.atmosres.2009.12.011
  • Zhang, J. K., Y. Sun, Z. R. Liu, D. S. Ji, B. Hu, Q. Liu, and Y. S. Wang. 2014. “Characterization of submicron aerosols during a month of serious pollution in Beijing, 2013.” Atmospheric Chemistry and Physics 14 (6): 2887–2903.