Dergiler / Atmospheric Pollution Research / 2017 / Cilt: 8 - Sayı: 1

Spatial and temporal variation of urban air pollutants and their concentrations in relation to meteorological conditions at four sites in Busan, South Korea

Sayfa
89–100
DOI
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⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

Highest daily peak for PM10 is observed in the spring with reduced level on weekends.

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Amaç & Hipotez:This study is based on 10-year period (2005e2014) hourly measurements of six air pollutants (NO, NO2, O3, SO2, CO and PM10) in four different sites (traffic, urban background, commercial and rural background) of Busan, the second largest city in South Korea.
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Temel Bulgular & Veri:An integrated analysis, considering various time periods (annual, seasonal and diurnal as a function of seasons and weekdays/weekends) and a statistical analysis of concentrations in relation to local meteorological conditions has been conducted.
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Sonuç & Katkı:Highest daily peak for PM10 is observed in the spring with reduced level on weekends.
🔬Tür:Araştırma Makalesi
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Alan Parametreleri

Özet

This study is based on 10-year period (2005e2014) hourly measurements of six air pollutants (NO, NO2, O3, SO2, CO and PM10) in four different sites (traffic, urban background, commercial and rural background) of Busan, the second largest city in South Korea. An integrated analysis, considering various time periods (annual, seasonal and diurnal as a function of seasons and weekdays/weekends) and a statistical analysis of concentrations in relation to local meteorological conditions has been conducted. Comparable downward trends for air pollutants over 10 years has been found across the study sites, with the exception for O3 which increases at a rate of ~0.7 ppbv/year. NO, NO2 and CO show a seasonal variation with winter enhancement, and this pattern is most obvious at the traffic site. Ozone has an annual cycle with a spring peak, showing higher peak amplitude at the rural background site. Summer enhancement of SO2 is identified at the site in the proximity of harbours when prevailing air masses have been transported from shipping regions. The distance from sources, particularly road transportation tends to produce spatial variations in the diurnal cycle, and this is particularly evident in the broader and delayed rush hour peak at the rural background site. The meteorological conditions and source strength expressed as weekdays/weekend drive the diurnal variations in terms of peak size, showing the winter enhancement for NO, NO2, SO2 and CO with lower weekend concentrations. Highest daily peak for PM10 is observed in the spring with reduced level on weekends.

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Bu Makaleye Atıf Yap

JANG, E., DO, W., PARK, G., KİM, M., YOO, E. (2017). Spatial and temporal variation of urban air pollutants and their concentrations in relation to meteorological conditions at four sites in Busan, South Korea. Atmospheric Pollution Research, Cilt: 8 - Sayı: 1, 89–100. https://ajindex.com/articles/214887

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Kaynakça (5)

  1. Amato, F., Cassee, F.R., van der Gon, H.A.D., Gehrig, R., Gustafsson, M., Hafner, W., Harrison, R.M., Jozwicka, M., Kelly, F.J., Moreno, T., 2014. Urban air quality: the challenge of traffic non-exhaust emissions. J. Hazard. Mater 275, 31e36. Anttila, P., Tuovinen, J.-P., 2010. Trends of primary and secondary pollutant concentrations in Finland in 1994e2007. Atmos. Environ. 44, 30e41. Bahreini, R., Middlebrook, A., Gouw, J.d., Warneke, C., Trainer, M., Brock, C., Stark, H., Brown, S., Dube, W., Gilman, J., 2012. Gasoline emissions dominate over diesel in formation of secondary organic aerosol mass. Geophys. Res. Lett. 39. Bari, A., Ferraro, V., Wilson, L.R., Luttinger, D., Husain, L., 2003.
  2. Measurements of gaseous HONO, HNO3, SO2, HCl, NH3, particulate sulfate and PM2.5 in New York, NY. Atmos. Environ. 37, 2825e2835. Bell, M.L., Dominici, F., Ebisu, K., Zeger, S.L., Samet, J.M., 2007. Spatial and temporal variation in PM2.5 chemical composition in the United States for health effects studies. Environ. Health Persp 115, 989e995. Bielaczyc, P., Szczotka, A., Woodburn, J., 2014. Cold start emissions of spark-ignition engines at low ambient temperatures as an air quality risk. Arch. Environ. Prot. 40, 87e100. Bigi, A., Harrison, R.M., 2010. Analysis of the air pollution climate at a central urban background site. Atmos. Environ. 44, 2004e2012.
  3. Brockwell, P.J., Davis, R.A., 2002. Introduction to Time Series and Forecasting, second ed. Springer. Busan, T.M.D., 2015. Annual Report for Traffic Volume in Busan. Available at: (Busan Transportation Management Division). http://area.busan.go.kr/.
  4. Cao, J., Lee, S., Zhang, X., Chow, J.C., An, Z., Ho, K., Watson, J.G., Fung, K., Wang, Y., Shen, Z., 2005. Characterization of airborne carbonate over a site near Asian dust source regions during spring 2002 and its climatic and environmental significance. J. Geophys. Res.- Atmosp. (1984e2012) 110. Carslaw, D., 2012. The Openair ManualeOpen-Source Tools for Analysing Air Pollution Data. Manual for Version 0.7-0. King’s College London. Carslaw, D.C., 2005. Evidence of an increasing NO2/NOX emissions ratio from road traffic emissions. Atmos. Environ. 39, 4793e4802. Carslaw, D.C., Ropkins, K., 2012. Openairdan R package for air quality data analysis. Environ. Modell. Softw. 27, 52e61. Chou, C.C.K., Liu, S.C., Lin, C.-Y., Shiu, C.-J., Chang, K.-H., 2006.
  5. The trend of surface ozone in Taipei, Taiwan, and its causes: implications for ozone control strategies. Atmos. Environ. 40, 38