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高屏地區氣象與空氣品質三度空間觀測與分析計畫

中文摘要 本計畫第一年之目標為量測海陸風之現象與分析其對高屏空品區空氣品質之影響,量測內容為包括氣象與空氣品質而量測方式為10月中旬到11月底之連續量測與10月21至10月26日、10月30日至11月5日與11月17日至11月20日之三次密集觀測。連續觀測項目包括有林園站逐時風速風向剖面分佈、小琉球、林園、社皮國小與海豐國小之地面氣象與小琉球之空氣品質。而密集觀測之項目包括有小琉球、林園、社皮國小與海豐國小之測風氣球、混合層高度、氣象、臭氧與前驅物等濃度及粒狀物粒徑之垂直剖面分佈與光化指標,除了測風氣球以外,密集觀測地點主要以林園為中心。密集觀測的16日中有7日為臭氧事件日,而且其中有四日為超過三站之區域性臭氧事件日,兩日為僅一站之局部性臭氧事件日,且局部性污染均是位於林園站與潮州站附近。 觀測結果顯示高屏空品區之海陸風現象甚為顯著,海風之厚度約為500~800m,而迴流高度可達1200m,但是陸風之厚度僅約為200~400m,而迴流高度約為600~800m。伴隨海風之作用,於林園地區有顯著的內部邊界層造成於中午時之混合層高度僅約為400m,故造成臭氧濃度之快速上升。另外,由於內部邊界層僅約為400m,而無線氣象儀的上升速度快,故有時無法正確的量測,而須藉由臭氧等污染物濃度之垂直剖面分佈,以更精確的判定混合層高度。 小琉球之空氣污染物濃度與林園站等高度的相關性,而且有約2小時的時間差異,故小琉球站可作為日間海風作用時之上風處預警。汕尾國小處量測之SO2與NOx濃度的垂直分佈顯示最高濃度主要是在200~400m左右,尤其夜間受工業區排放之影響時,而日間則是隨高度至600m而略微上升;NMHC濃度之垂直剖面分佈於日間與SO2 、NOx相似,但是在夜間在200m以上則是隨高度遞減。由於內部邊界層的作用,日間高O3濃度主要是分佈在400m以內,而風向以西北偏西風為主;夜間之O3濃度同時有儲流與消耗之現象,消耗作用分別發生於高度為400m以下、400~600m與800~1200m三層,而且有時會有合併現象,風向以北風為主,故為工業區排放之NO滴定效應;但是在800~1200m高度之風向有時為南風,其原因有待進一步分析。粒狀物之粒徑分佈可歸納為三個峰之分佈,分別為小於1m、2.4m與4.5m,而於臭氧消耗層內粒狀物濃度較高,尤其是大粒徑之粒狀物,顯示消耗層內之粒狀物主要來自直接排放。另外,於高度1000~1400m處,有時觀測到大顆粒之高粒狀物濃度,其可能來源尚待進一步研究。由地面光化指標之量測顯示採樣期之臭氧敏感物種主要為NOx。
中文關鍵字 海陸風;垂直剖面分佈;臭氧;NO滴定效應;粒徑分佈

基本資訊

專案計畫編號 EPA-94-FA11-03-A202 經費年度 094 計畫經費 3600 千元
專案開始日期 2005/05/06 專案結束日期 2005/12/31 專案主持人 吳義林
主辦單位 空保處 承辦人 執行單位 吳義林

成果下載

類型 檔名 檔案大小 說明
期末報告 EPA-94-FA11-03-A202-open.pdf 15MB [期末報告]公開版

Three-dimensional Measurements of Meteorology and Air Quality Variations in Kaoping Area

英文摘要 The purposes of the first year for this project are to study the sea-land breeze and to evaluate its effects on the ambient air quality in Kaoping air basin. Therefore, both the meteorological factors and air pollutant concentrations were measured simultaneously during this study. The field measurements can be classified into two groups: continuous measurements and intensive field measurements. The continuous measurements, which were conducted during mid-October to the end of November, included hourly vertical profiles of wind speed and wind direction, ground micro-meteorological measurements at four sites, and the air quality measurements at Luchu, an off-shore island. The intensive field measurements were conducted during October 21st to 26th, October 31st to November 5th, and November 17th to 20th and includes pibal, the measurement of the vertical profiles for wind speed, wind direction, temperature, relative humidity, pollutant concentrations, particle size distributions and the ozone-sensitivity indicators. Among the 16 days of intensive field measurements, there were 7 ozone episodic days with 4 days of regional pollution and two days of local pollution. The local ozone pollution all occurred near Linyuan, the major sampling site. The sea-land breeze was very significant during all the measurements. The vertical height of sea breeze was about 500 to 800 m and that of the recirculating flow could reach 1200 m. But the vertical height of land breeze was only about 200 to 400 m. Accompanying with the sea-land breeze, an internal boundary layer could develop up to 400 m near the coast region. Therefore, the mixing height near noon could be only 400 m and the ozone concentrations built up very quickly. The air pollutant concentrations at Luchu were highly correlated with those at Linyuan with time differences of about two hours. Therefore, the data at Luchu can be used as alarming indicators for air pollution in Kaoping air basin during the daytime. The vertical profiles for SO2 and NOx showed the maximum concentrations at 200 to 400 m, especially during nighttime due to the effects of industrial parks. However, their concentrations generally increased with height up to 600 m during daytime; similar results were found for the concentrations of NMHC. But the NMHC concentrations generally decreased with height during nighttime. The maximum daytime ozone concentrations generally occurred within the 400 m due to the effect of internal boundary layer and the dominant wind direction was NWW. Both the residence and depletion of ozone concentrations were found during nighttime with three layers of ozone depletion: less than 400 m, 400 to 600 m, and 800 to 1200m. The ozone depletion generally happened during northern wind and was caused by NO titration from the industrial park emission. The ozone depletion at 800 to 1200m sometimes was with southern wind and further study is needed to determine the causes. The particle size distributions at all heights were with three modes: less than 1 m, 2.4 m, and 4.5 m. Higher particle concentrations were found during the ozone depletion layer, especially for supermicron particles. Therefore, the particle within the ozone depletion layers were mainly from the emission sources directly. Significantly high supermicron particle concentrations up to two or three orders of magnitudes were found occasionally at 1000 to 1400 m and the sources for these particles were still unknown. Based on the measurements of ozone-sensitivity indicators, most of time was NOx-limited.
英文關鍵字 Sea-Land breeze;Vertical profile;Ozone;No titration ;Particle size distributeon