Long-term changes in wet nitrogen and sulfur deposition in Nanjing
Introduction
China has become one of the global hotspots of acid deposition due to the increased energy consumption in recent years (Vet et al., 2014). To control acid pollution and improve air quality, the Chinese government has enacted a series of policies to decrease the acid deposition precursors SO2 and NOx since the mid-1990s (Hao et al., 2000). Before the 12th Five-year Plan (2011–2015), only SO2 emissions were controlled, and the joint control on SO2 and NOx emissions began with the 12th Five-year Plan. As a result, the SO2 emissions decreased beginning in 2006, and the NOx emissions decreased beginning in 2012 across China (Duan et al., 2016). The changes in SO2 and NOx emissions will change the acid components in precipitation, which have rarely been studied (Fang et al., 2013).
Studies on long-term acid deposition require long-term monitoring in specific areas. For example, three decades of monitoring on the acid composition of precipitation at Guangzhou showed that SO42− deposition has decreased since 2001, NO3− has remained unaltered, and a marked recovery of precipitation pH has occurred since 2005 (Fang et al., 2013). A regional background station in northern China exhibited a significant increasing trend of NO3− deposition and a decreasing trend of the SO42−/NO3− ratio in precipitation from 2003 to 2014 (Pu et al., 2017). The deposition of NO3− in a subtropical rainforest significantly decreased while precipitation pH remained relatively stable from 1994 to 2013 (Chang et al., 2017). The acid composition of precipitation varies from site to site and region to region due to the different emission sources, the long-range transport trajectories, and the policies for controlling SO2 and NOx emissions. Therefore, the long-term trends in other areas should be addressed to fully understand the changes of acid deposition across China.
Nanjing is located in one of the developed areas in China, the Yangtze River Delta (YRD). This area is undergoing rapid economic growth, urbanization, and industrialization and thus is one of the first areas to suffer from acid rain (Tang et al., 2010). Highly developed industries and transportation emit large amounts of SO2 and NOx. With the 10th Five-year Plan, a series of air quality policies were enacted to control SO2 emissions. Under such conditions, SO42− concentrations decreased while NO3− concentrations increased from 1992 to 2003, and a significant trend in precipitation pH was not observed in Nanjing (Tu et al., 2005). However, a goal was set to reduce 21.2% of the NOx emissions in 2015 compared with that in 2010 in the 12th Five-year Plan in Nanjing, and the NOx emissions decreased by 24.9% in 2015 (https://www.xzbu.com/1/view-7261236.htm). These NOx emission control policies decreased the NO2 concentrations in the atmosphere beginning in the 12th Five-year Plan (Ma et al., 2017), which might change the NO3− concentration in precipitation. However, the mechanisms underlying the change in acid deposition based on policies to control NOx emissions remain unclear. Studying changes in the components and deposition of acid in Nanjing will provide a scientific basis for establishing policies on the economic development of other areas.
This study aims to investigate wet acid deposition in Nanjing based on collected precipitation samples under the influence of industry development and air quality policies. First, the concentration of acid in precipitation and wet deposition in Nanjing from 2015 to 2016 is presented; second, the seasonal variations in acid deposition are analysed; and finally, the long-term trends in acid deposition are detected based on ground-monitoring data from 1990 to 2016.
Section snippets
Study area and sampling sites
Nanjing has a humid subtropical climate under the influence of the East Asian monsoon. The four seasons are distinct, and the area has an annual mean temperature of 15.9 °C and rainfall of 1058.1 mm (Yin, 2015). Chemical, electronics, automobile and machinery are the four pillar industries in Nanjing (2010 Nanjing Economic and Social Development Bulletin). In 2010, the value added by industry in Nanjing was 2.0 × 1011 CNY (China Yuan), thus accounting for 40% of the Gross Domestic Product
Acid concentration and deposition of SO42− and NO3− with precipitations in Nanjing
To understand the acid deposition from precipitation in Nanjing, the minimum, maximum, arithmetic mean, and VWM of the SO42− and NO3− concentration in precipitation from 2015 to 2016 were calculated, and the results are provided in Table 1. Both of the SO42− and NO3− concentrations showed a large range, with values of 0.52–40.80 mg L−1 and 0.39–20.60 mg L−1, respectively. Furthermore, the arithmetic mean concentration of SO42− and NO3− was higher than its VWM value, suggesting that higher
Conclusions
This study presented the acid concentrations in precipitation and deposition in Nanjing based on ground measurements and detected the long-term trends of acid deposition from 1990 to 2016. Compared with other provincial capitals and the cities close to Nanjing, the SO42− pollution in Nanjing was low while the NO3− pollution was still high. Uncertainties from different years of rainwater sampling should be considered when comparing the acid concentration and deposition with those in other
Acknowledgment
This study is supported by the National Natural Science Foundation of China (No. 41471343), and the Fundamental Research Funds for the Central Universities (020914380047).
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