| 研究生: |
蘇佳琪 Su, Chia-Chi |
|---|---|
| 論文名稱: |
氧化鋁及氧化鐵插層蒙脫石吸附水中天然有機物之研究 Adsorption of natural organic matter by Al2O3 and Fe2O3 pillared montmorillonite |
| 指導教授: |
申永輝
Shen, Yun-Hwei |
| 學位類別: |
碩士 Master |
| 系所名稱: |
工學院 - 資源工程學系 Department of Resources Engineering |
| 論文出版年: | 2002 |
| 畢業學年度: | 90 |
| 語文別: | 中文 |
| 論文頁數: | 112 |
| 中文關鍵詞: | 氧化鋁,氧化鐵,插層,蒙脫石,天然有機物 |
| 外文關鍵詞: | montmorillonite, natural organic matter, pillared, Al2O3, Fe2O3 |
| 相關次數: | 點閱:81 下載:2 |
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摘要
飲用水原水中之天然有機物(natural organic matter, NOM)是一複雜的污染物,在自來水淨水廠加氯消毒程序中,天然有機前驅物質(如腐植質)會和氯作用形成具有致癌性的三鹵甲烷(trihalomethane,THM),故在加氯消毒程序前預先去除水中天然有機物為必要之處理程序。
本研究旨在探討以氧化鋁及氧化鐵插層(intercalated)進入蒙脫石層間合成柱撐蒙脫石(pillared montmorillonite),進而應用於淨水處理中作為水中天然有機物吸附劑之可行性。
研究結果顯示,未經提純之蒙脫石其陽離子交換容量(CEC)約為48.6 meq/100g,而將蒙脫石置於水中充分膨潤,再以1000 rpm 轉速(110g) 離心1分鐘,上層液中懸浮之蒙脫石CEC值可提高至約73.8 meq/100g。在合成鋁及鐵插層蒙脫石方面,使用[OH-]/[Al3+]莫耳比為2.5,並以每克蒙脫石配合3 mmol鋁離子進行插層後且經300℃煆燒,可有效增加蒙脫石層間距(d001)與BET比表面積。另一方面,使用[OH-]/[Fe3+]莫耳比為2,以每克蒙脫石配合3 mmol鐵離子進行插層後經300℃煆燒,雖無法產生如鋁插層蒙脫石層間存在之穩定氧化鋁支撐,有效的增加蒙脫石之層間距及BET比表面積,但是仍能在鐵插層蒙脫石層間表面形成非晶質氧化鐵或氫氧化鐵局部覆膜。鋁及鐵插層蒙脫石之Stokes粒徑皆大於未插層之蒙脫石,使得插層之蒙脫石在水中沉降速度變快。又鋁及鐵插層蒙脫石沉降後污泥體積明顯小於未插層之蒙脫石,其固液分離效果較佳。更進一步,鋁及鐵插層蒙脫石由於表面鋁及鐵元素含量增加,而表面鋁及鐵離子可對水中天然有機物分子產生有效的錯合,進而造成其對水中天然有機物的吸附能力明顯提升。
綜合而言,將氧化鋁及氧化鐵插層蒙脫石應用於淨水處理中作為水中天然有機物之吸附劑將是一可行的方法。
Abstract
A large portion of the natural organic matter(NOM) in potable water sources are complex contaminants. During the chlorination procedure in water treatment plane, humus will react with chlorine to form carcinogenic trihalomethane(THM) substances, so it is necessary to remove the NOM in water before chlorination.
The purpose of this study is to synthesis pillared montmorillonite by intercalating Al2O3 and Fe2O3 into the layer space of montmorillonite. Then, the effects of using the pillared montmorillonite as an adsorbent for the removal of NOM from water are evaluated.
The cation exchange capacity(CEC) of unpurified montmorillonite is about 48.6meq/100g. The montmorillonite were purified by centrifuging at 1000rpm(110g) for 1min. The CEC of purified montmorillonite is about 73.8meq/100g. To synthesis Al2O3 and Fe2O3 pillared montmorillonite, the purified montmorillonite suspension was vigorously mixed with hydrolized Al3+ solution at room temperature ( 1g of clay reacted with 3mmol Al3+ in which [OH-]/[Al3+]=2.5). The final product after 300℃ heat treatment has a basal spacing of 17.7Å and a specific surface area of about 168.93m2/g .In addition, the montmorillonite suspension was vigorously mixed with hydrolized Fe3+ solution at room temperature ( 1g of clay reacted with 3mmol Fe3+ in which [OH-]/[Fe3+]=2). After calcining at 300℃, the basal spacing and specific surface area of the final product does not increas. The present of Fe2O3 coating film at the interlayer surface of pillared montmorillonite is predicted.
The Stokes particle size of Al2O3 and Fe2O3 pillared montmorillonite is greater than that of unpillared montmorillonite. Thus increase the sedimentation rate of pillared montmorillonite in water. After sedimentation of the pillared montmorillonite, the volume of sludge is smaller than that of unpillared montmorillonite, thus the pillared montmorillonite shows good solid-liquid separation effect. Finally, the sorption capacity of NOM in water progressively increase with the increasing amount of Al2O3 and Fe2O3 intercalated in pillared montmorillonite.
In summary, intercalating of Al2O3 and Fe2O3 into the layers of montmorillonite will form pillared montmorillonite. Experiment results in this study showed that using pillared montmorillonite as an adsorbent for removing NOM from water water is practicable.
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