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研究生: 洪嘉陽
Hung, Chia-Yang
論文名稱: 榕樹葉片中戴奧辛/呋喃之特徵
Characteristics of Polychlorinated Dibenzo-p-dioxins∕Dibenzofurans in the Leaves of Ficus Species
指導教授: 李文智
Lee, Wen-Jhy
學位類別: 碩士
Master
系所名稱: 工學院 - 環境工程學系
Department of Environmental Engineering
論文出版年: 2003
畢業學年度: 91
語文別: 中文
論文頁數: 198
中文關鍵詞: 榕樹葉片粒徑分佈大氣戴奧辛降解係數半衰期氣固相分佈
外文關鍵詞: PCDD/Fs, Gas/Particle partition, atmosphere, particle size distribution, Ficus leaf, degradation
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  • 本研究針對TD地區周界環境進行大氣及榕樹葉片中PCDD/Fs之檢測,期望能建立起PCDD/Fs在大氣濃度與榕樹葉片含量中彼此相互影響之關係,亦提供關於大氣中PCDD/Fs進入榕樹葉片的可能途徑,進而建立起榕樹葉片可能吸收或吸附戴奧辛/呋喃之含量、總降解係數與半衰期。所得結論歸納如下: 1.TD地區周界大氣中PCDD/Fs濃度為介於0.129 ~ 1.115 pg/Nm3之間,平均為0.493 pg/Nm3;總I-TEQ則介於0.009 ~ 0.103 I-TEQ-pg/Nm3之間,平均為0.033 I-TEQ-pg/Nm3。 2.TD地區大氣中PCDD/Fs之氣固相分佈,利用公式Kp=(F/TSP)/A;LogKp=mp×log PL°+bp估算而得。十七種PCDD/Fs一年四季之固相分佈百分比介於48.9%(2,3,7,8-TCDF)~96.9%(OCDD)之間。 3.大氣中PCDD/Fs之粒徑分佈,以榕樹葉片氣孔允許進入之平均最大孔徑3.2μm,平均佔大氣中粒狀相總PCDD/Fs之92.4%。 4.TD地區榕樹葉片中PCDD/Fs含量為介於2.72 ~ 49.9 pg/g之間,平均為12.7 pg/g;總I-TEQ則介於0.178 ~ 1.86I-TEQ-pg/g之間,平均為0.467I-TEQ-pg/g;葉片表面PCDD/Fs含量為介於0.0747 ~ 0.2987 pg/g之間,平均為0.1517 pg/g;總I-TEQ則介於0.0021 ~ 0.0084I-TEQ-pg/g之間,平均為0.0062I-TEQ-pg/g。 5.TD地區榕樹葉片中與葉片表面吸附之PCDD/Fs含量平均百分比分別為99.07%與0.93%。因此附著於榕樹葉片表面藉由清洗可去除之PCDD/Fs者,僅佔非常微小部分。 6.過去文獻討論大氣中PCDD/Fs進入植物體中的路徑多為氣相收。而以本研究結果顯示,除了氣相傳輸的路徑之外,懸浮微粒所含PCDD/Fs中,從氣孔進入至葉片當中而被吸收或吸附所佔之含量亦不容忽視。本研究顯示以懸浮微粒型態進入榕樹葉片PCDD/Fs平均約佔86.4%,而由氣相進入者僅佔13.6%,明顯與國外文獻所指出PCDD/Fs進入葉片係以氣相傳輸為主之機制不同。 7.關於榕樹葉片對PCDD/Fs降解常數(光降解與榕樹葉片酵素降解常數之和),我們利用似一階之降解動力式求解:Cr= Cee-ktott;總PCDDs之ktot為0.0390 day-1、總PCDFs之ktot為0.0603 day-1、總PCDD/Fs之ktot為0.0499 day-1。十七種PCDD/Fs物種之ktot以OCDD之0.0363day-1最小,而以1,2,3,7,8,9-HxCDF之0.0693day-1最大。 8.PCDD/Fs在榕樹葉片中之半衰期。以PCDDs而言,各物種的半衰期平均為426小時,從1,2,3,4,7,8-HxCDD之半衰期為327小時最短,而OCDD之半衰期為458小時;依PCDFs而言,各物種之半衰期平均為276小時,以1,2,3,7,8,9-HxCDF之半衰期240小時最短,1,2,3,7,8-PeCDF之半衰期297小時最長。

    This study investigates the characteristics of polychlorinated
    dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) in leaves of the Ficus species in rural areas, Taiwan. The main objective of this study is to evaluate the transfer of atmospheric compounds into leaves. Additionally, a model to estimate the leaf content is developed and its results compared with the actual leaf content in Ficus species. Furthemore, the total degradation coefficient and half-life of PCDD/Fs in Ficus is estimated. The following conclusions are drawn. 1. The PCDD/Fs concentration in the atmosphere are between 0.129~1.115 pg/Nm3, the average is 0.493pg/ Nm3.The PCDD/Fs concentrations in the atmosphere in the TD area is from 0.009 to 0.103 I-TEQ-pg/Nm3 with a nean value of 0.033 I-TEQ-pg/ Nm3. 2. The percentage of particle-bound of PCDD/Fs range from 48.9%(2,3,7,8-TCDF) to 96.9%(OCDD). 3.The maximum pore diameter that allowed suspension particle entering in the leaves of Ficus species is 3.2 μm and the particle-bound of PCDD/Fs with aerodynamic diameter(dae)<3.2 μm is 92.4%. 4.The PCDD/Fs leaf content in Ficus Species of TD area is form 0.178~1.861 I-TEQ-pg/g(mean=0.467 I-TEQ-pg/g). The PCDD/Fs content , adsorbed on the leaves’ surfaces, is from 0.0021 to 0.0084I-TEQ-g/g (mean = 0.0062 pg-I-TEQ/g). 5.The average percentage of PCDD/Fs content absorded in and adsorbed on the surfaces of the leaves of Ficus are 99.07% and 0.93%,respectively. 6. The result of this study revealed that the primary pathway for PCDD/Fs entering the leaves was by particle phase absorption (86.4%). This result is different from the report by previous study that the gas phase PCDD/Fs was the main pathway entering the leaves. 7. The degradation coefficient ktot(including the photolysis and the biodegradation coefficient)of total PCDDs was determined as 0.0390 day-1 by using pseudo first kinetics:Cr=Cee-ktott, while that of total PCDFs was 0.0603 day-1 and the degradation coefficient of total PCDD/Fs was 0.0499 day-1, respectively. 8.The degradtion half-life of PCDD/Fs, estimated the pseudo first-order rate constant kp for photolysis and kb for biodegradation, were as follows . The half-life time of PCDDs in Ficus leaves is from 327 hours (1,2,3,4,7,8-HxCDD) to 458 hours (OCDD)and the average is 426 hours. The half-life time of PCDFs in Ficus leaves is from 240 hours(1,2,3,7,8,9-HxCDF) to 297 hours(1,2,3,7,8-PeCDF)and the mean half-life of seventeen PCDD/F congeners was 276 hours.

    一 前言 1 二 文獻回顧 3 2-1 PCDD/Fs之物理化學性質 3 2-2 PCDD/Fs對人體健康及環境的可能影響 7 2-3 PCDD/Fs之來源與形成機制 12 2-3-1 de Novo合成反應 12 2-3-2 經由前驅物質之異相觸媒合成 16 2-3-3 PCDDs與PCDFs形成機制之相異處 16 2-4 PCDD/Fs在環境中的流向 19 2-5 PCDD/Fs氣固相模式與粒徑分佈 20 2-5-1 SOCs粒徑分佈 20 2-5-2 PCDD/Fs氣固相模式 27 2-6 半揮發性空氣污染物與植物相互關係 30 三 實驗設備與方法 33 3-1 採樣規劃 33 3-1-A大氣與榕樹葉片之採樣規劃 33 3-2 大氣中PCDD/Fs採樣 37 3-1-A大氣中PCDD/Fs濃度採樣 37 3-1-B大氣中PCDD/Fs粒徑分佈採樣 43 3-3 榕樹葉片採樣方法 46 3-4大氣PCDD/Fs樣品前處理 50 3-5 榕樹葉片前處理步驟 57 3-6葉片氣孔導度及蒸散速率 65 3-7葉片氣孔孔徑及氣孔密度 66 四 品質保證與品質控制 67 4-1 實驗藥品與試劑 67 4-2 採樣品質保證與品質控制之執行 72 4-2-A 大氣採樣 72 4-2-B 榕樹葉片採樣 74 4-3 PCDD/Fs樣品分析前處理品質保證與品質控制之執行 75 4-3-A 大氣PCDD/Fs樣品 75 4-3-B 榕樹葉片PCDD/Fs樣品 76 4-3-C 實驗室PCDD/Fs測試能力範圍 76 4-4 高解析度氣相層析儀與高解析度質譜儀 78 4-5質譜圖鑑定準則 83 4-6實驗室品管程序 83 五 結果與討論 85 5-1 大氣中PCDD/Fs之濃度 85 5-2 大氣中PCDDDFs之氣固相分佈與粒徑分佈 110 5-2-A PCDD/Fs之氣固相模式 110 5-2-B PCDD/Fs之粒徑分佈 112 5-3 榕樹葉片之PCDD/Fs含量 115 5-3-A 榕樹葉片中 115 5-3-B 榕樹葉片表面 137 5-4 大氣與榕樹葉片中PCDD/Fs之相關性 153 5-4-A討論國外文獻與榕樹葉片生理性質 153 5-4-B TD地區大氣中與榕樹葉片中PCDD/Fs特徵剖面比較 157 5-4-C 估計可能為榕樹葉片吸收含量與實際分析值相比 164 六 結論與建議 174 6-1結論 174 6-2建議 176 七 參考文獻 177 八 自述 197

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