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研究生:郭奕伶
研究生(外文):Kuo, I-Ling
論文名稱:高屏地區光化學煙霧成因之研究
論文名稱(外文):The formation of the photochemical smog in Kao-Ping area
指導教授:吳義林
指導教授(外文):Wu Yee-Lin
學位類別:碩士
校院名稱:國立成功大學
系所名稱:環境工程學系
學門:工程學門
學類:環境工程學類
論文種類:學術論文
論文出版年:1997
畢業學年度:85
語文別:中文
論文頁數:110
中文關鍵詞:轉化速率臭氧形成速率
外文關鍵詞:conversion rateozone formation rate
相關次數:
  • 被引用被引用:17
  • 點閱點閱:540
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  • 收藏至我的研究室書目清單書目收藏:1
摘 要本研究針對PM10與臭氧污染嚴重之高屏地區進行實地採樣,依據逆
軌跡分析結果選定屏東、美濃、楠梓、潮州、小港、鳳山、大寮與林園等
採樣點後,進行多點同步、時間解析度為2小時之採樣以收集空氣中之懸
浮微粒、HCHO、NO2等污染物,研究中將就實測結果探討污染物之空間分
佈與季節變化並配合環保署自動監測資料進行逆軌跡分析計算衍生性硝酸
鹽與硫酸鹽之轉化速率及臭氧形成速率。自84年10月至86年3月於高屏地
區之量測結果顯示,各測站夏季時空氣品質較好,而以秋冬兩季的污染較
嚴重,幾乎所有測站的日平均濃度都超過法規標準,無論是位於都會區的
鳳山、屏東,工業區的大寮、林園或偏遠地區的美濃及潮州,懸浮微粒都
常高過法規標準125 ug/m3,有時甚至大於200 ug/m3。其中屏東站之季節
變化最為顯著,污染嚴重的秋冬所測得之濃度約為夏季的3∼4倍,而林園
與大寮即使在夏季,懸浮微粒濃度卻仍高於100ug/m3。懸浮微粒中所含的
可溶性化學成份包括Cl-、NO3-、SO42-、Na+、NH4+、K+、Mg2+及Ca2+大
約佔總懸浮微粒濃度的20~40%,其中以SO42- 與NO3-所佔比例較高,
SO42-日平均濃度大都介於3至30 ug/m3,NO3-日平均濃度則約為1~20 ug/
m3之間。除了濃度有顯著之季節性變化之外NO3-與SO42-在懸浮微粒中所
佔比例之季節也有秋季與冬季較高而夏季較低之趨勢。85年10月與86年3
月在大寮站同時採集PM2.5與PM10濃度之結果顯示,Na+、K+及Mg2+等惰性
離子在PM10中PM2.5所佔比例大都低於50%,然而NO3-、SO42-與NH4+等反
應性成份則佔較大比例,其中SO42-所佔比例更高達90%以上,由於小粒徑
的污染物由直接排放而來的比例較少,主要是由大氣中的化學反應所導致
,此量測結果顯示PM10中之NO3-與SO42-中衍生性氣膠部份佔有相當大的
比例。另外粒徑分佈之量測結果亦顯示NO3-與SO42-在Condensation mode
與droplet mode的粒徑範圍內亦有相當大的比例,再加上分析同時於各站
測得之離子成份濃度的結果顯示,各測站NO3-與SO42-之相關性極高,因
而推估有一大部份之NO3-與SO42-是由大氣中之化學反應衍生而來。以逆
軌跡分析配合實測結果推估衍生性NO3-與SO42-轉化速率之結果顯示其值
分別介於0.04∼4.28%/h與0.27∼34%/h之間,轉化速率之高低與光化反應
強度之相關性並不高,探討其形成機制後發現除了氣相反應外,由於高屏
地區相對濕度較高,液相反應亦對衍生性NO3-與SO42-有不可忽略之貢獻
。雖然夏季時硫酸鹽之轉化速率高於秋季與冬季,但由於冬季時東北季風
將SO2吹至高屏地區,使得硫酸鹽之形成速率反高於夏季,導致冬季時高
屏地區受到嚴重之PM10污染。進行與臭氧形成相關物種之量測則發現,高
屏地區HCHO兩小時平均濃度範圍介於0.04(屏東,86年3月)與86.38ppb(大
寮,85年10月),雖然濃度變化很大,但並無顯著之日夜變化,除了光化
學反應外,可能有其他直接排放源。推估各測站汽機車對HCHO貢獻量之結
果則顯示約有10∼50%的HCHO是來自汽機車的貢獻,將此部份扣除後,只
有林園8月時有較明顯的日夜變化,且與臭氧濃度的相關較高,r=0.78。
在大寮站所測得之JNO2為4*10-3sec-1,以光化穩態法(PSS)推估臭氧形成
速率之結果顯示預估值與實測值之差異為-17~22ppb/hr,而中位數為-5.6
ppb/hr,未來的研究中應考慮臭氧之去除速率及過氧化物之影響以修正模
式。關鍵字:轉化速率、氧化速率
ABSTRACTThe purposes of this study are to investigate the
spatial and seasonal variations of pollutants in photochemical
smog such as PM10、formaldehyde(HCHO) and NO2 in southern Taiwan
where the pollution of photochemical smog is the most serious in
Taiwan. The formation rates of nitrate and sulfate were
evaluated by using the measured data with back-trajectory
analysis. In addition, the potolysis rate of NO2 was measured
to evaluate the ozone formation rate with photostationary state
method. The measurements were conducted simutaneously for five
runs in the following sites : Ping-Tung、May-Nong、Nan-Z、Hsiao-
Gang、Feng-Shan、Da-Liao and Lin-Yuan from October 1995 to March
1997 and the temporal resolution was two hours.The results show
that the pollution of PM10 is more serious during autumn and
winter while the air quality is better in summer. The
concentrations of PM10 in Ping-Tung showed significantly
seasonal variations:the concentration of PM10 were 4~5 times
greater in autumn and winter then those in summer. The water
soluable chemical species such as Cl-、NO3-、SO42-、Na+、NH4+、
K+、Mg2+ and Ca2+ are about 20~40% of PM10. The concentrations
of the most abuntant species, NO3-and SO42-, in PM10, are abuot
3~30 and 1~20ug/m3. Besides concentrations, the ratios of NO3-
and SO42- in PM10 are also greater in autumn and winter then in
summer.The measurements of PM2.5 and PM10 show that the ratios
of PM2.5 in PM10 of the inert species , such as Na+、K+ and
Mg2+, are less then 50%, but the ratios of the reactive species
NO3-、SO42- and NH4+ are up to 85%. In addition, the
measurements of particle size distribution also show that NO3-
and SO42- have a large portion in fine particle, implying the
significant contribution of secondary aerosol formed in
photochemical smog.The conversion rates of NO and SO2 are about
0.04~4.28%/hr and 0.27~34%/hr, respectively. Besides gas phase
reaction, a large portion of secondary aerosol comes from
aqueous reaction due to the high humidity in Taiwan. Therefore,
the correlation between conversion rate and O3 formation is not
significant.The concentrations of two-hour average for HCHO are
0.04~86.38ppb, while the contribution of vehicles is 10~50%.
Without vehicle contribution, the diurnal variation of HCHO is
only obvious at Lin-Yuan site in August. The non-vehicle
contributed HCHO shows strong correlation with ozone with the
correlation coefficient between them of 0.78.The measured
photolysis rate of NO2 at Da-Liao site was about 4*10-3sec-1 and
the differences between the predicted and measured ozone
formation rates were -17 to 22 ppb/hr with the median value of
-5.6ppb. More study is needed in the future to modify the model
for ozone formation rate, for example the loss rate ozone and
the contributions of peroxides.keywords:conversion rate、ozone
formation rate
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