Dergiler / Atmospheric Pollution Research / 2017 / Cilt: 8 - Sayı: 6

Identification of the potential regions contributing to ozone at a coastal site of eastern China with air mass typology

Sayfa
1044–1057
DOI
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⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

Besides, favorable climate conditions (e.g. high temperature) could also significantlycontribute to the O3 pollution during the study period.

📌 3 Maddede Bu Makale

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Amaç & Hipotez:he concentrations of O3 and CO at a coastal site of eastern China were analyzed using hourly data from February 2015 to January 2016.
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Temel Bulgular & Veri:Conditional probability function, bivariate correlation, trajectory clustering and potential source contribution function were applied to determine the potential regions contributing to surface O3 at the study site.
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Sonuç & Katkı:Besides, favorable climate conditions (e.g. high temperature) could also significantlycontribute to the O3 pollution during the study period.
🔬Tür:Araştırma Makalesi
📍Kapsam:2015 Verileri
⚙️Değişkenler:Alan Parametreleri

Özet

he concentrations of O3 and CO at a coastal site of eastern China were analyzed using hourly data from February 2015 to January 2016. Conditional probability function, bivariate correlation, trajectory clustering and potential source contribution function were applied to determine the potential regions contributing to surface O3 at the study site. The O3 and CO concentrations reached their maxima in autumn and winter, respectively. Relatively high exceeding rate (8.8%) over the national 8-h O3 standard of China (75 ppb) was observed, which indicated significant health risks of O3 exposure to people. The results of all the analyses suggested that the major potential regions contributing to O3 were located in the coastal and marine areas of eastern China. The highest O3 levels occurred with relatively high wind speeds (5 m/s), revealing significant contributions of external sources. Based on the cluster analyses of backward trajectories, the air masses associated with the coastal and marine clusters contributed to 32.2% and 37.4% of surface O3 at the study site, respectively. The domain of major potential region varied with seasons, with larger areas appearing in summer and autumn, and smaller area in winter, which suggested more contributions to the O3 pollution from distant transport during warm seasons. As to the influence mechanisms on surface O3, the spatial position of the study site, mesoscale process and longrange transport of pollutants from northern China might play important roles. Besides, favorable climate conditions (e.g. high temperature) could also significantlycontribute to the O3 pollution during the study period.

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Bu Makaleye Atıf Yap

Tong, L., ZHANG, J., Xiao, H., Cai, Q., Huang, Z., Zhang, H., Zheng, J., He, M., Peng, C., Feng, J., Qian, F. (2017). Identification of the potential regions contributing to ozone at a coastal site of eastern China with air mass typology. Atmospheric Pollution Research, Cilt: 8 - Sayı: 6, 1044–1057. https://ajindex.com/articles/351410

Kaynakça (9)

  1. Adame, J.A., Hernandez-Ceballos, M.A., Sorribas, M., Lozano, A., De la Morena, B.A., 2014. Weekend-weekday effect assessment for O3, NOx, CO and PM10 in Andalusia, Spain (2003-2008). Aerosol Air Qual. Res. 14, 1862-1874.
  2. Ashbaugh, L.L., Malm, W.C., Sadeh, W.Z.,1985. A residence time probability analysis of sulfur concentrations at Grand Canyon National Park. Atmos. Environ. 19, 1263-1270.
  3. Carslaw, D.C., Ropkins, K., 2012. Openair e an R package for air quality data analysis. Environ. Model. Softw. 27e28 (0), 52-61.
  4. Chameides, W.L., Saylor, R.D., Cowling, E.B., 1997. Ozone pollution in the rural United States and the new NAAQS. Science 276, 916, 916. Chan, C.Y., Chan, L.Y., Harris, J.M., Oltmans, S.J., Blake, D.R., Qin, Y., Zheng, Y.G., Zheng, X.D., 2003. Characteristics of biomass burning emission sources, transport, and chemical speciation in enhanced springtime tropospheric ozone profile over Hong Kong. J. Geophys. Res.-Atmos. 108. Cheung, V.T.F., Wang, T., 2001. Observational study of ozone pollution at a rural site in the Yangtze Delta of China. Atmos. Environ. 35, 4947-4958.
  5. Choi, K.C., Lee, J.J., Bae, C.H., Kim, C.H., Kim, S., Chang, L.S., Ban, S.J., Lee, S.J., Kim, J., Woo, J.H., 2014. Assessment of transboundary ozone contribution toward South Korea using multiple source-receptor modeling techniques. Atmos. Environ. 92, 118-129.
  6. Choi, Y., Souri, A.H., 2015. Seasonal behavior and long-term trends of tropospheric ozone, its precursors and chemical conditions over Iran: a view from space. Atmos. Environ. 106, 232-240.
  7. Cooper, O.R., Parrish, D.D., Stohl, A., Trainer,M., Nedelec,P.,Thouret,V., Cammas, J.P., Oltmans, S.J., Johnson, B.J., Tarasick, D., Leblanc, T., McDermid, I.S., Jaffe, D., Gao, R., Stith, J., Ryerson, T., Aikin, K., Campos, T., Weinheimer, A., Avery, M.A., 2010. Increasing springtime ozone mixing ratios in the free troposphere over western North America. Nature 463, 344-348.
  8. Cristofanelli, P., Fierli, F., Marinoni, A., Calzolari, F., Duchi, R., Burkhart, J., Stohl, A., Maione, M., Arduini, J., Bonasoni, P., 2013. Influence of biomass burning and anthropogenic emissions on ozone, carbon monoxide and black carbon at the Mt. Cimone GAW-WMO global station (Italy, 2165 m a.S.L.). Atmos. Chem. Phys. 13, 15-30.
  9. Cuevas, E., Gonzalez, Y., Rodriguez, S., Guerra, J.C., Gomez-Pelaez, A.J., AlonsoPerez, S., Bustos, J., Milford, C., 2013. Assessment of atmospheric processes driving ozone variations in the subtropical North Atlantic free troposphere. At