Increases in the formation of water soluble organic nitrogen during Asian dust storm episodes
Graphical abstract
Section snippets
Introductions
Water soluble organic nitrogen (WSON) is an essential compound of reactive nitrogen species and plays an important role in the biogeochemical nitrogen cycle (Bhattarai et al., 2019; Liu et al. 2019a). WSON in reduced forms such as amine and urea could make significant contributions of the nutrient budgets to marine environment (Violaki and Mihalopoulos 2011; Neff et al. 2002). Milne and Zika (1993) estimated the inputs amounts of N flux in the form of amine to ocean was ~600 kg N yr−1.
Sampling collections
As discussed above, the role of PM2.5 in biogeochemical cycle of WOSN resulting from Asian dust storm was not explicit illustrated. Thus, PM2.5 samples were collected from April1 to May 21, 2012 at Zhangjiakou, Hebei province (40。75,14”N, 114。88,30.0″E) and at Tianjin (40。75,1.8”N, 117。40,88.3″E), respectively. Zhangjikou is located in northern Hebei Province, which is close to semi-desert area in Inner Mongolia (Fig. S1B). The air quality in Zhangjiakou during spring season is prone to the
Impacts of dust storm on mass concentrations
The average mass concentration of PM2.5 from April 1 to May 21, 2012 at urban site (S1) was 51 μg m−3, the minimum was 21 μg m−3 and the maximum was 120 μg m−3 (Table S3). The mass concentration of PM2.5 from April 1 to May 21, 2012 at coastal site (S2) was observed to be in the range of 24–158 μg m−3, with a mean level of 54 μg m−3 (Table S3). No geographical differences in the average concentration of PM2.5 mass concentration was observed within two sampling sites from April 1 to May 21, 2012.
Conclusions
This study collected PM2.5 samples from April 1 to May 21, 2012 at the two sampling sites, which are located at the urban area of Zhangjiakou, Heibei province and the rural area of Tianjin near the coastal line, respectively. The Asian dust storm spread over the two sampling sites during the periods from April 25 to 28, 2012. Increases in PM2.5 mass and chemical components including ions, metals, carbonaceous particles and WSON were observed at the two sampling sties. The levels of WSON
Declaration of Competing Interest
The authors declare that they have no known competing financial interestsor personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgement
This study was finically supported by National Science Foundation of China (No. 41175104, 41305110, 41475133). Dr. Qingyang Liu would like to thank the support from Scientific Research Foundation for High-Level Talents of Nanjing Forestry University (GXL2019034).
References (48)
- et al.
Characterization of Asian Dust during ACE-Asia
Glob. Planet. Chang.
(2006) - et al.
Size-resolved airborne particulate oxalic and related secondary organic aerosol species in the urban atmosphere of Chengdu, China
Atmos. Res.
(2015) - et al.
Dust characteristics over the North Pacific observed through shipboard measurements during the ACE-Asia experiment
Atmos. Environ.
(2007) - et al.
Gaseous and particulate water-soluble organic and inorganic nitrogen in rural air in southern Scotland
Atmos. Environ.
(2010) - et al.
Characteristics of water-soluble organic nitrogen in fine particulate matter in the continental area of China
Atmos. Environ.
(2015) - et al.
Size-segregated water-soluble N-bearing species in the land-sea boundary zone of East China
Atmos. Environ.
(2019) - et al.
Impacts of crystal metal on secondary aliphatic amine aerosol formation during dust storm episodes in Beijing
Atmos. Environ.
(2016) - et al.
Chemical characteristics and source apportionment of PM10 during Asian dust storm and non-dust storm days in Beijing
Atmos. Environ.
(2014) - et al.
Source apportionment of Beijing air pollution during a severe winter haze event and associated pro-inflammatory responses in lung epithelial cells
Atmos. Environ.
(2016) - et al.
Oxidative potential of ambient PM2.5 in Wuhan and its comparisons with eight areas of China
Sci. Total Environ.
(2020)