Dergiler / Atmospheric Pollution Research / 2016 / Cilt: 7 - Sayı: 4

The phenomena of spreading ambient ozone at the west coast air basin of Taiwan

Sayfa
698–705
DOI
—
🏛️Bu makalenin bibliyografik verileri ve tam metin bağlantısı DergiPark üzerinden sağlanmıştır.
DergiPark Kaydı ↗
✨

Yapay Zeka Hızlı Bakış & Çıkarımlar

AI Insight
⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

Thediversion of river valleys and the mountainous barrier between the basin/hill and mountains exertobvious influences on the local wind field, strongly affecting the ozone-spreading phenomena

📌 3 Maddede Bu Makale

🎯
Amaç & Hipotez:The total air pollution model (TAPM, www.cmar.csiro.au/research/tapm) was used to explore the phenomenaof spreading ambient ozone in the complex 196 km 196 km terrain of the west coast air basinof Taiwan (including ocean area).
📊
Temel Bulgular & Veri:The altitude in the air basin ranges from 0 m (sea level) to 3000þ m(high mountain).
💡
Sonuç & Katkı:Thediversion of river valleys and the mountainous barrier between the basin/hill and mountains exertobvious influences on the local wind field, strongly affecting the ozone-spreading phenomena
🔬Tür:Modelleme & Sayısal Simülasyon
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Alan Parametreleri

Özet

The total air pollution model (TAPM, www.cmar.csiro.au/research/tapm) was used to explore the phenomenaof spreading ambient ozone in the complex 196 km 196 km terrain of the west coast air basinof Taiwan (including ocean area). The altitude in the air basin ranges from 0 m (sea level) to 3000þ m(high mountain). The data of 2010e2014 from 21 air-quality monitoring stations were used to ensure theaccuracy of the simulation results in accordance with an average index of agreement (IOA) > 0.61. Fourozone-spreading phenomena were observed among the air basin: the northesouth spreading on theoffshore (NeS SOO), northesouth spreading around the coast (NeS SAC), eastewest spreading from theocean (EeW SFO), and eastewest spreading around the mountain front (EeW SAMF). The results indicatethat when two prevailing flows meet and interact at their boundaries, they form a convergencezone. The convergence zone presents distinctive weather conditions and accumulates air pollutants.More than wind direction, the ozone concentration is dependent on the topography and surroundingconditions. The results clearly show that the ozone-spreading phenomena follow certain rules. The NeSSOO, NeS SAC, EeW SFO, and EeW SAMF phenomena are during the northeaster, fore-southwester,southwester, and fore-northeaster monsoon months, respectively. Wind fields are a major factor inthe high concentration of ozone and ozone spreading, especially downdraft and onshore winds. Thediversion of river valleys and the mountainous barrier between the basin/hill and mountains exertobvious influences on the local wind field, strongly affecting the ozone-spreading phenomena

🔖

Bu Makaleye Atıf Yap

LİANG, C. J., XUE, Y. S., LİANG, J. J. (2016). The phenomena of spreading ambient ozone at the west coast air basin of Taiwan. Atmospheric Pollution Research, Cilt: 7 - Sayı: 4, 698–705. https://ajindex.com/articles/351534

Kaynakça (1)

  1. Barna, M., Lamb, B., 2000. Improving ozone modeling in regions of complex terrain using observational nudging in a prognostic meteorological model. Atmos. Environ. 34, 4889e4906. Bronnimann, S., Schuepbach, E., Zanis, P., Buchmann, B., Wanner, H., 2000. € A climatology of regional background ozone at different elevations in Switzerland (19921998). Atmos. Environ. 34, 5191e5198. Chen, C.F., Liang, J.J., 2013. Integrated chemical species analysis with sourcereceptor modeling results to characterize the effects of terrain and monsoon on ambient aerosols in a basin. Environ. Sci. Pollut. Res. 20, 2867e2881. Chen, C.S., Chen, W.C., Chen, Y.L., Lin, P.L., Lai, H.C., 2005. Investigation of orographic effects on two heavy rainfall events over southwestern Taiwan during the Meiyu season. Atmos. Res. 73, 101e130. Cheng, W.L., 2001. Synoptic weather patter ns and their relationship to high ozone concentrations in the Taichung Basin. Atmos. Environ. 35, 4971e4994. Cheng, W.L., 2002. Ozone distribution in coastal central Taiwan under sea-breeze conditions. Atmos. Environ. 36, 3445e3459. Cheng, W.L., Lai, L.W., Den, Q., Wu, M.T., Hsueh, C.A., Lin, P.L., Pai, C.L., Yan, Y.L., 2014. The relationship between typhoons' peripheral circulation and ground-level ozone concentrations in central Taiwan. Environ. Monit. Assess. 186, 791e804. Coelingh, J.P., van Wijk, A.J.M., Holtslag, A.A.M., 1998. Analysis of wind speed observations on the North Sea coast. J. Wind Eng. Ind. Aerodyn. 73, 125e144. Diem, J.E., 2000. Comparisons of weekday-weekend ozone: importance of biogenic volatile organic compound emissions in the semi-arid southwest USA. Atmos. Environ. 34, 3445e3451. Gao, H.O., 2007. Day of week effects on diurnal ozone-NOx cycles and transportation emissions in Southern California. Transp. Res. Part D Transp. Environ. 12, 292e305. Glavas, S.D., Sazakli, E., 2011. Ozone long-range transport in the Balkans. Atmos. Environ. 45, 1615e1626. Hanna, S.R., Davis, M., 2002. Evaluation of a photochemical grid model using estimates of concentration probability density functions. Atmos. Environ. 36, 1793e1798. He, H.D., Lu, W.Z., 2012. Decomposition of pollution contributors to urban ozone levels concerning regional and local scales. Build. Environ. 49, 97e103. Huang, H., Akustu, Y., Arai, M., Tarnura, M., 2001. Analysis of photochemical pollution in summer and winter using a photochemical box model in the center of Tokyo, Japan. Chemosphere 44, 223e230. Hurley, P.J., Physick, W.L., Luha