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--> --> -->Several researchers have investigated the pollution situation over the YRD from monthly, seasonal and annual mean perspectives (Yu et al., 2011; Zhao et al., 2017; Sun et al., 2019). Affected by urbanization, large cities in the YRD have higher aerosol optical depths than remote areas (Sun et al., 2019), as well as high anthropogenic heat release (Wang et al., 2015), as verified by high-resolution Weather Research and Forecasting model results. In addition to impacts of anthropogenic emissions on the long-term trend of haze pollution in the YRD, a few studies have investigated the roles of weather–climate conditions in the YRD. He et al. (2019b) pointed out that PM2.5 throughout the Yangtze River Basin is negatively correlated with surface wind speed, precipitation and planetary boundary layer height (PBLH) but positively correlated with temperature. High wind speed, more precipitation and a well-developed boundary layer could facilitate the dispersion of aerosols and lead to a decrease in PM2.5 (He et al., 2019b). The positive relationship between temperature and PM2.5 is possibly due to the enhancement in oxidation of aerosol precursors at high temperatures (He et al., 2019b). Compared to the conditions in NC, He et al. (2019a) also indicated that wet removal of haze brought by precipitation over southern China (south of 30°N) is important. Furthermore, winter haze extremes in India at lower latitudes are even affected by El Ni?o sea surface temperature and signals from the Southern Hemisphere (Gao et al., 2019).
NC is the most haze-polluted area in China, and the associated atmospheric circulations have already been examined in previous studies. The number of winter haze days (HDs) in NC (WHDNC) has been found to be directly dominated by local anticyclonic circulations (Chen and Wang, 2015; Yin and Wang, 2016), connected by two Rossby wave trains [i.e., the East Atlantic/West Russia (EA/WR) and Eurasia patterns] over the continent and one Rossby wave train (i.e., the West Pacific pattern) over the ocean (Wallace and Gutzler, 1981; Barnston and Livezey, 1987). These wave trains provide the favorable atmospheric conditions associated with haze pollution, such as a lower planetary boundary layer, lower wind speed, anomalous southerlies, and higher relative humidity (RH), which restrict the horizontal and vertical ventilation of haze particles (Yin et al., 2017).
The number of HDs in December over the YRD (DHDYRD), as well as those in January (JHDYRD), slowly increased from 1981 to 2017, while those over NC (DHDNC and JHDNC) slightly decreased from 1981 to 2010 but increased from 2011 to 2017 (Fig. 1). In this study, we pay more attention to the interannual variations of monthly haze pollution. The correlation coefficient (CC) between DHDNC and JHDNC is 0.71; however it decreases to 0.33 in the YRD, indicating significant differences in haze variations in December and January over the YRD. The time series of DHDYRD and DHDNC (JHDYRD and JHDNC) during 1981–2017 has a CC of 0.49 (0.2), which are not high for two adjacent economically developed regions (Figs. 1a and b). Furthermore, we also compared the variations in emissions (i.e., the difference of emissions in different months and regions) with the associated differences in HDs and found the CCs between them were all lower than 0.2 [non-significant; Fig. S1 in electronic supplementary material (ESM) ]. The above statistical results illustrate the need for an analysis of the monthly variations of atmospheric circulations associated with haze pollution (i.e., the impacts of meteorology) in the YRD and NC.
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As for haze pollution, the number of HDs in each month in the winters of 1981–2017 were adopted owing to the lack of long-term PM2.5 data. Haze was calculated by defining visibility less than a certain threshold, which was 10 km before 1 January 2014 for most stations and 7.5 km after because of the switch in visibility observation means (i.e., from manual observation to automatic observation) according to a report of the China Meteorological Administration in 2014 (Yin et al., 2017) and RH less than 90% (Chen and Wang, 2015; Yin and Wang, 2016). One HD at a station was defined as a day with haze at any time, after excluding other weather phenomena that affected visibility. All the HDs of a month at all stations in the region were accumulated, and then the average value of all stations in the region was calculated as the HDs in the region. HDs over the YRD (27.05°–33.77°N, 118.15°–121.95°E) and NC (34°–42°N, 114°–120°E) were computed as the HD average value in these two areas, respectively. For more detail, readers are referred to Chen and Wang (2015), Yin and Wang (2016), and Yin et al. (2017).
Several statistical methods were used in this study, as follows. When the linear trend was removed, the linear trend was calculated firstly and then subtracted from the original series. The standardized data refer to the original data minus the average and then divided by the standard deviation. Correlation analysis and regression analysis were also utilized, with the statistical significance tested with the Student’s t-test. Multiple linear regression (MLR) was used to establish equations between atmospheric circulation factors and HDs in order to measure the importance of atmospheric circulation factors. MLR is expressed as
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3.1. Atmospheric circulations drive the monthly variations in haze
The atmospheric circulations associated with December and January haze pollution in the YRD were investigated. As illustrated in Fig. 2a, a Rossby wave–like train at middle and high latitudes of continental Eurasia strongly contributes to the variations in DHDYRD. In comparison, in January, the Rossby wave train becomes non-significant, and the only significant centers are the local AAC located in the northwest of the YRD (Fig. 2c). That is, the large-scale atmospheric circulation affecting HDs degenerate to the local anticyclone from December to January. Lower PBLH (Fig. 3c) in December is apparent because of anomalous descending motions (Fig. 3a) over the YRD. Weak surface wind speed, induced by anomalous southerly wind, is apparent in January over the YRD (Fig. 3d). Thus, the vertical movement (Figs. 3a and c) is restricted in December and the horizontal movement (Figs. 3b and d) is restricted in January, over the YRD, leading to high contemporaneous HDs. Furthermore, the anomalous precipitation plays a critical role in the removal of haze particles over the YRD (Figs. 4a and b). Precipitation and HDs over the YRD show a significant out-of-phase relationship in both December (CC = ?0.34) and January (CC = ?0.46) (Figs. 4a and b).
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Atmospheric circulations associated with haze pollution in NC in December and January were also examined. In the mid-troposphere, a Rossby wave–like train clearly affects the haze pollution over NC in December (Fig. 2b). However, in January, the associated atmospheric circulations become relatively local (Fig. 2d), which is different from the results revealed in many previous studies for the whole winter season (Chen and Wang, 2015; Yin and Wang, 2016). Anomalous ascending motion (Figs. 5a and b), warming near the surface (Figs. 5a and b), southerly wind (Figs. 5c and d), weak surface wind speed (Figs. S2a in the ESM and 5d), low PBLH (Figs. 5c and S3a), high potential of thermal inversion, i.e., the air temperature at 925 hPa minus the air temperature at 1000 hPa (Figs. S2b and S3b), and high RH (Figs. 5a and b, Figs. S2c and S3c), are favorable for both DHDNC and JHDNC. That is, the monthly variations of associated local weather conditions are similar. However, precipitation makes different contributions to DHDNC and JHDNC. December precipitation is almost unrelated to DHDNC (Fig. 4c), while January precipitation has a significantly positive relationship with DHDNC (CC = 0.33, exceeding the 95% confidence level; Fig. 4d).
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From the data in Table 1, we can see that the AAC index is crucial for both DHDYRD and DHDNC, while the SAT diff. index and precipitation index (SAT index, RH index, PBLH index and UV speed index) play important roles in the YRD (NC). To quantify the contributions of atmospheric circulations to haze pollution, the highly correlated variables (≥ 95% confidence level) were selected to regress on the number of HDs. In other words, the AAC, SAT diff. and precipitation indices (ACC, SAT, RH, PBLH and UV speed indices) in December were selected as regression factors of DHDYRD (DHDNC). The predicted DHDYRD and DHDNC did not include the observed trend here, and in the last calculation step we added the trend as fitted values, shown in Fig. 6. The fitted and observed DHDYRD and DHDNC had a CC of 0.77 and 0.67 for the YRD and NC, respectively (Figs. 6a and b). That is, atmospheric circulations made variance contributions of 59% and 45%, respectively (Figs. 6a and b), confirming that these circulation variables have large influences on DHDYRD and DHDNC. DHDYRD had the same sign as the AAC (SAT difference between the north and the south of the YRD) in 33 (31) of 37 years, while it had opposite signs to precipitation in 25 of 37 years (Fig. 7a). DHDNC shared the same mathematical sign as the AAC, local SAT and RH in 24, 28 and 28 of 37 years, respectively, while it had opposite mathematical signs to the PBLH and surface wind in 26 and 25 of 37 years, respectively (Fig. 7b). As can be seen from Fig. 7a, three variables correspond to DHDYRD in the minimum year of 2010, while it is two variables in the maximum year of 2013. In contrast, as shown in Fig. 7b, all five variables correspond to DHDNC in the minimum (maximum) year of 2010 (2015), which highlights the importance of meteorological and climate conditions.
Month | CCs | AAC | SAT | SAT diff. | RH | PBLH | UV speed | Precipitation |
December | HDYRD | 0.48*** | / | 0.61*** | / | / | / | ?0.34** |
HDNC | 0.59*** | 0.46*** | / | 0.45*** | ?0.56*** | ?0.41** | / | |
January | HDYRD | 0.40** | / | 0.46*** | / | / | / | ?0.46*** |
HDNC | 0.37** | / | / | 0.47*** | ?0.36** | ?0.48*** | 0.33** |
Table1. The correlation coefficients (CCs) between atmospheric circulation indices and haze days (HDs) of two regions (the YRD and NC) in early winter (December and January). The linear trends in all data were removed. Double asterisks (**) and triple asterisks (***) indicate the results pass the 95% and 99% confidence level, respectively. A forward-slash (/) indicates the significance level is below 95%.
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Similarly, CCs were calculated between circulation indices in January and JHDYRD (JHDNC), as shown in Table 1, and the significant indices (exceeding the 95% confidence level) were selected to fit JHDYRD (JHDNC). Three (five) circulation indices, including the AAC, SAT diff. and precipitation indices (the ACC, RH, PBLH, UV speed and precipitation indices), were demonstrated to be useful for the formation of JHDYRD (JHDNC). The fitted circulation indices explain 56% (42%) of the variance of JHDYRD (JHDNC) with the trend, indicating large contributions of these atmospheric circulations (Figs. 6c and d). In Fig. 7c, the AAC, SAT and precipitation all show corresponding results with JHDYRD in the minimum (maximum) year of 1993 (2015). Meanwhile, in Fig. 7d, five meteorological variables show corresponding results with JHDNC in the minimum year of 2011; however, only RH shows corresponding results with JHDNC in the maximum year of 2016. Regardless, meteorological and climate conditions play important roles in the interannual variabilities of HDs rather than other elements.
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3.2. Comparison of atmospheric circulations associated with DHDNC and DHDYRD
The wave activity flux (WAF) demonstrates the wave energy propagation paths (Takaya and Nakamura, 2001; Hsu and Lin, 2007; Honda et al., 2009). A quasi-stationary planetary wave route (i.e., the Scandinavia pattern) is apparent, with an anomalous negative center over Scandinavia and an anomalous positive center over Mongolia (Fig. 2a). The CC between the Scandinavia pattern and DHDYRD is ?0.48 (significant at the 99% confidence level). In contrast, the WAF associated with DHDNC (Fig. 2b) shows a positive EA/WR phase (CC = 0.56). These results demonstrate that the Scandinavia and EA/WR patterns contribute to the variations of DHDYRD and DHDNC, respectively. The AAC near Northeast Asia is located in the crossover regions of the Scandinavia and EA/WR patterns and might explain the close relationship between DHDYRD and DHDNC.Local meteorological conditions associated with DHDYRD and DHDNC were also compared (Figs. 3–5). The climate-mean vertical motion is weak in the downward direction over the YRD (not shown), and the AAC enhances the anomalous descending movement (Fig. 3a). Besides, anomalous reversion of the north–south temperature is favorable for DHDYRD (Fig. 3a), which restricts the invasion of the East Asian winter monsoon (EAWM) into the YRD. Low PBLH also restricts the vertical dispersion (Fig. 3c). Against the background of intensive descending motion over the YRD, dry air is carried from the top to the ground, causing the weak negative RH anomaly (Fig. 3a) and less precipitation. As we know, some pollutants can be removed via wet removal, i.e., precipitation, especially in southern areas with large precipitation. In Fig. 4a, precipitation has a negative CC with DHDYRD (CC = ?0.34, ≥ 95% confidence level). Local meteorological conditions related to DHDNC are correspondingly discussed (Figs. 5a and c). Different from DHDYRD, anomalous upward movement (Fig. 5a), southerly wind near the surface (Fig. 5a), high RH (Figs. 5a and S2c), high surface temperature (Fig. 5a), high potential of temperature inversion (Fig. S2b), and low surface wind speed (Fig. S2a), are favorable for DHDNC. In addition, precipitation has little influence on the elimination of haze pollution over NC (Fig. 4c), as compared to that over the YRD (Fig. 4a). As shown in Figs. 3c and 5c, the PBLH shows negative anomalies over both NC and the YRD, indicating a negative contribution to the elimination of haze pollution.
It is common knowledge that the wintertime weather and climate of East Asia is affected by the EAWM, so the monthly EAWM [i.e., the East Asian December (January) monsoon, abbreviated as EADM (EAJM)] was separately analyzed to study the effects on DHDYRD and DHDNC. Here, the definitions of the EADM and EAJM refer to previous studies (Wang and Jiang, 2004; He and Wang, 2012) and are shown in Table S1 (in the ESM), including the sub-indices and synthetic index. The CCs of the EADM and DHDYRD (DHDNC) show that specific members, such as the East Asian deep trough, westerly jet, as well as the synthetic index, have an influence on DHDYRD, while all members of the EADM have a significant impact on DHDNC (Table 2). The question, then, is how does the EADM affect DHDYRD and DHDNC? A strong EADM may weaken the temperature difference between the north and south of the YRD (Fig. 8a) and bring cold air from the mid–high latitudes to China. Meanwhile, there is sufficient water vapor in the YRD, so the intrusion of cold air may enhance the precipitation over the YRD (Fig. 8b). When precipitation increases, haze pollution in the YRD will be removed. In addition, a strong EADM may also increase the surface wind speed in the YRD (not shown), strengthening the conditions of horizontal dispersion. As for DHDNC, a strong EADM may lead to favorable local ventilation conditions and unfavorable growth conditions for haze particles, such as low SAT (Fig. 8c), low RH (Fig. 8d), high PBLH (Fig. 8e), and high surface wind speed (Fig. 8f).
CCs | December HDs | January HDs | |||
YRD | NC | YRD | NC | ||
SHI | ?0.26 | ?0.39** | ?0.35** | ?0.39** | |
ALI | 0.10 | ?0.37** | ?0.04 | ?0.39** | |
MW850I | ?0.13 | ?0.42*** | ?0.14 | ?0.33** | |
EADTI | ?0.41** | ?0.58*** | ?0.28 | ?0.2 | |
WJI | ?0.46*** | ?0.45*** | ?0.28 | ?0.17 | |
SI | ?0.45*** | ?0.56*** | ?0.36** | ?0.3 | |
WS850I | ?0.09 | ?0.34** | 0.17 | ?0.2 |
Table2. The CCs between East Asian early winter (December and January) monsoon indices and HDs of two areas (the YRD and NC) in December and January, respectively. Double asterisks (**) and triple asterisks (***) indicate the results pass the 95% and 99% confidence level, respectively.
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3.3. Comparison of atmospheric circulations associated with JHDNC and JHDYRD
The CCs of JHDYRD and JHDNC become non-significant (Fig. 1b), indicating weak synergistic variations of JHDYRD and JHDNC. The associated wave-like train is significantly weakened (Figs. 2c and d) in January rather than that in December. Consequently, the influence of Eurasian wave trains on local HDs is weakened. Local anticyclones affect local HDs in both areas, with CCs of 0.40 and 0.37 (Table 1), significant at the 95% confidence level. Additionally, the AAC in January is also relatively weaker than that in December (Fig. 2, Table 1).It was shown in Zhong et al. (2019) that the directions of vertical motion vary according to the locations of the AAC. Because the YRD is located in the east of the bottom of the AAC (Fig. 2c), descending motion was delivered to the region (Fig. 3b). Although the descending motion only exists in the south of the YRD, other local meteorological conditions induced by the AAC, such as the SAT diff. (Fig. 3b), weak UV speed (Fig. 3d), anomalous southerly wind (Fig. 3d), and less precipitation (Fig. 4b), are crucial for high JHDYRD. By contrast, for JHDNC, anomalous ascending motion (Fig. 5b), high SAT (Fig. 5b), high RH (Figs. 5b and S3c in the ESM), anomalous southerly wind (Figs. 5b and d), weak UV speed (Fig. 5d), low PBLH (Fig. S3a), and high potential of temperature inversion (Fig. S3b), provide adverse conditions for the dispersion of haze particles. Besides, in January, precipitation makes different contributions to HDs over NC and the YRD, i.e., more precipitation brings more JHDNC (Fig. 4d). Light rain is dominant when precipitation happens over NC, which is conducive to the hygroscopic growth of haze particles.
As for the EAJM, the significant impact factors are the Siberian high index and synthetic index (Siberian high index, Aleutian low index and meridional wind at 850 hPa index) for JHDYRD (JHDNC). Additionally, the influential process of the EAJM is as follows. A strong EAJM can reduce the temperature difference between the north and south of the YRD and enhance the precipitation over the YRD (Figs. 9a and b). Meanwhile, for JHDNC, the Siberian high can affect local meteorological conditions (Figs. 9c–e), including RH (Fig. 9c), PBLH (Fig. 9d), and UV speed (Fig. 9e). In other words, a strong EAJM, represented by the Siberian high, creates an unstable environment for high JHDNC.
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Utilizing these significant circulation indices to establish regression models of HDs, results showed that these circulation indices make large contributions and can explained more than 40% of the variance of DHDYRD, JHDYRD, DHDNC and JHDNC. Owing to the switch in the observation methods of visibility in January 2014, the reliability of HDs after January 2014 has been tested. It was found that the conclusions are still robust if the data after January 2014 are removed. The collinearity of the indices can be ignored because the variance inflation factors of most selected factors are lower than five in the four regression equations (Fig. 6). In Fig. 11 in Zhang et al. (2019), the adverse weather conditions in autumn and winter might reduce the effect of emissions reduction in the Beijing–Tianjin–Hebei region in 2014 and 2015. Yin and Zhang (2020) investigated the pollution situation in the winters of 2017 and 2018 under almost the same emission conditions, finding that haze pollution rebounded in 2018 compared with that in 2017, indicating the important effect of climate and weather conditions.
Acknowledgements. This research was supported by the National Key Research and Development Plan (Grant No. 2016YFA0600703), the National Natural Science Foundation of China (Grant Nos. 91744311, 41991283 and 41705058), and the funding of the Jiangsu Innovation & Entrepreneurship Team.
Electronic supplementary material: Supplementary material is available in the online version of this article at