摘要(英) |
Taiwan is surrounded by sea, where local circulation is easily formed. One of the typical examples is the sea-land breeze, which is also one of the most significant factors for transport pollutant in the coastland. In the area of Taipei and Kaoping in the Taiwan have high pollution source. This paper will focus on the influence of sea-land breeze on air quality over highly polluted area of Taipei and Kaoping.
First of all, we would like to define “sea-land breeze day” according to the cause, the situation, and the definition in many papers of sea-land breeze. First, we draw straight a line parallel to the coastline. Then, draw a perpendicular line to it through the station. Take 50 degree, in the direction of clockwise and counterclockwise, as the direction for sea and land breeze. The conditions for sea-land breeze day include, land breeze direction switch to sea breeze direction during daytime and sea breeze direction switch to land breeze direction at night, which occur in the same day with wind direction change duration at least 3 hours long and the wind speed less than 4 m/s.
If we average the daily 24 hours chart by month, the result indicates that ozone concentration of sea-land breeze days is lower than that of non sea-land breeze days among the Taipei area. In daytime, ozone concentration in sea-land breeze days is often higher then in non sea-land breeze days in Taipei area. In summer, due to the expansions of pollution area, including coastland, the influence of sea-land breeze is not obvious. However, in Kaoping area, ozone concentration in sea-land breeze days is almost the same with ozone concentration in non sea-land breeze days.
In addition to analysis of observation data, we used the model to simulate the cases in 2003. In order to understand influence of sea-land breeze on air pollution in the coastland. It is shown that when sea breeze take place during daytime, the air pollution in the land will be transported to upper sky and dropped to coastland and sea with sea breeze circulation. This increased the ozone concentration in the sea-land breeze days.
After analyzing the observation data, it is shown that if the pollutant is away from the coastland, the pollutant transportation will via sea-land breeze. At night, the pollutant in land is transported to the coastland via land breeze to react with ozone, which reduce the concentration of ozone. Till the daytime, land breeze will turn to sea breeze. From the modeling result, sea breeze will bring the pollutant back to land. Due to the sea breeze circulation, the pollutant will be transported from upper sky to the surface near coastland, which increase the concentration of coastland pollution. From observation result, it is also shown that the sea-land breeze will not have influence on the pollution in coastland due to the coastland is also in the range of sea-land pollutant transportation. |
參考文獻 |
行政院環保署網頁,http://www.epa.gov.tw。
王明星,大氣化學,明文書局,民國八十一年。
陳德鈞,季延安,林肇信,大氣污染化學,科技圖書,民國八十年。
行政院環保署,中華民國台灣地區空氣品質監測報告九十二年年報,行政院環
保署,民國九十二年。
劉遵賢,黃賀春,張艮輝,張時禹,鄭福田,台灣空氣品質模式Taiwan Air
Quality Model (TAQM) 操作使用手冊 Version 1.11,民國九十一年。
呂世宗,1977:高雄地區空氣品質污染受海陸風之影響。行政院國家科學
委員會專題研究計畫成果報告,NSC66-0201-M052-02。
張能復,1999:南高屏地區空氣污染總量管制規劃-E1計畫 反應性軌跡模式空
氣污染事件之應用與解析。行政院環境保護署,EPA-88-FA21-03-0012。
張艮輝,張能復,鄭曼婷,吳義林,吳俊傑,林沛練,望熙榮,謝祝欽,
2000:南高屏地區空氣污染總量管制規劃(空氣品質模式組)。行政院環
保署,EPA-89-FA11-03-101。
周仲島、張茂興、何台華,1997:山區雷雨系統之降水與運動場結構分析。
大氣科學,2 5 ,483-506頁。
許武榮,侯昭平,1997:海風環流與陸地對流邊界曾交互影響之數值研究。
,大氣科學,2 5 ,397-416頁。
柳中明,蘇維中,1997:區域氣象環境與高臭氧之相關分析。大氣科學,
2 5 (1 ) ,27-49頁。
柯亙重,2000:高雄市區夏季風向風速日夜變化及海陸風分析。環境與
世界,4,105-113頁。
柯亙重,李西謀,2003:高雄市東下風向量日夜變化分析。環境與世界,
7,47-53頁。
Brümmer, B., B. Hennemuth, A. Rhodin, S. Thiemann, 1995: Interaction of a
cold front with a sea-breeze front observations. Tellus, 47A, 383-402.
Cheng, W.L., 2002: Ozone distribution in coastal central Taiwan under sea-breeze
conditions. Atmos. Environ., 36, 3445-3459.
Chou, Charles C.K., Shaw C. Liu, C.Y. Lin, C.J. Shiu, K.H. Chang, 2006: The trend
of surface ozone in Taipei, Taiwan, and its causes: Implications for ozone
control strategies. Atmos. Environ., 40, 3898-3908.
De Leeuw, Frank, Rob Sluyter, Peter van Breugel, Ferdinand Bogman, 2000:
Air pollution by ozone in Europe in 1999 and summer 2000. European
Environment Agency.
Ding, A., T. Wang, M. Zhao, T. Wang, Z. Li, 2004: Simulation of sea-land breezes
and a discussion of their implications on the transport of air pollution during a
multi-day ozone episode in the Pearl River Delta of China. Atmos. Environ.,
38, 6737-6750.
Fuhrer, J., et. al., (1997)Critical levels for ozone effects on vegetation in Europe.
Environmental Pollution, 97, 91~106.
Galbally, I.E., Roy C.R., 1980: Destruction of ozone at the earth’s surface. Q. J. R.
Meteorol. Soc., 106, 599-620.
Kok, G.L., J.A. Lind, M. Fang, 1997: An airborne study of air quality around the
Hong Kong territory. Journal of Geophysical Research 102, 19,043–19,057.
Liu, KY., Z. Wang, LF. Hsiao, 2002: A modeling of the sea breeze and its impacts on ozone distribution in northern Taiwan. Environmental Modelling & Software, 17,
21-27.
Lu, R., R. P. Turco, 1995: Air pollutant transport in a coastal environment: Part II:
Three-dimensional simulations over Los Angeles basin. Atmos. Environ., 29,
1499-1518.
Lu, R., R. P. Turco, 1995: Air pollutant transport in a coastal environment: Part I:
Two-dimensional simulations of the sea-breeze and mountain effects. J. atmos.
Sci., 51, 2285-2308.
McConnell, R., K. Berhane, F. Gilliland, S. J. London, T. Islam, W. J. Gauderman, E.
Avol, H. G.. Margolis and J. M. Peters, 2002: Asthma in exercising children
exposed to ozone: a cohort study. Lancet, 359, 386-391.
Oh, I.B., Y.K. Kim, Hwa woon Lee, C.H. Kim, 2006: An observational and numerical
study of the effects if the late sea breeze on ozone distributions in the Busan
metropolitan area, Korea. Atmos. Environ., 40, 1284-1298.
Oltmans, S.J., A.S. Lefohn, J.M. Harris, I. Galbally, H.E. Scheel, G. Bodeker, E.
Brunke, H. Claude, D. Tarasick, B.J. Johnson et al., 2006: Long-term changes
in tropospheric ozone. Atmos. Environ., 40, 3156-3173.
Pont, V., J. Fontan, 2000: Local and regional contributions to photochemical
atmospheric pollution in southern France. Atmos. Environ., 34, 5209-5223.
Prospero, J.M., R. Schmitt, E. Cuevas, D.L. Savoie, W.C. Graustein, K.K. Turekian,
A. Volz-Thomas, A. Diaz, S. J. Oltmans, and H. Levy II, 1995:
Temporal variability of summer-time ozone and aerosols in the free troposphere
over the eastern North Atlantic. Geophys. Res. Lett., 22, 2925-2928.
Rao, M.V., H.-I. Lee, R.A. Creelman, J.E. Mullet and K.R. Davis, 2000: Jasmonic
acid signaling modulates ozone-induced hypersensitive cell death. Plant Cell,
12,1633–1648.
Wang, K.Y., D.E. Shallcross, P. Hadjinicolaou and C. Giannakopoulos, 2004:
Ambient vehicular pollutants in the urban area of Taipei: comparing normal
with anomalous vehicle emissions. Water, Air, and Soil Pollution, 156, 29-55.
Wang, T., Joey Y. H. Kwok, 2003: Measurement and Analysis of a multiday
photochemical smog episode in the Pearl River Delta of China. J. Appl. Meteor.,
42, 404-416.
Wang, T., C.N. Poon, Y.H. Kwok, Y.S. Li, 2003: Characterizing the temporal
variability and emission patterns of pollution plumes in the Pearl River Delta of
China. Atmos. Environ., 37, 3539–3550.
Wang, T., Y.Y. Wu, T. F. Cheung, K. S. Lam, 2001: A study of surface ozone
and the relation to complex wind flow in Hong Kong. Atmos. Environ., 35,
3203- 3215.
Yang, Y., Y.L. Chen, 2005: Numerical simulations of the island-induced circulations
over the island of Hawaii during HaRP. Mon. Wea. Rev., 113, 3693-3713. |