臺灣博碩士論文加值系統

本研究以微波能量誘導溶液中的改質堇青石，使其快速氧化而加速氯苯的脫氯作用。在改質堇青石降解水中氯苯試驗方面，2g的改質堇青石可有效的降解污染物，在常溫的去除率為16%，其2g的改質堇青石去除率明顯高於1g的改質堇青石，較多的改質堇青石會提高較多的去除率；氯苯溶液反應溫度在40 ℃、50 ℃、60 ℃條件下，降解率提高至26%、38%、49%。反應溶液溫度的增加使得分子的動能增加，單位時間內碰撞的次數亦增加，使的去除率增加。在微波場下改質堇青石降解水中含氯有機物的試驗方面，以微波250W進行氯苯與四氯乙烯之降解，在相同重量的條件下(2g)，氯苯與四氯乙烯的去除率分別為81%、88％。在微波功率250W進行改質堇青石重覆使用次數為第一次、第二次、第三次，去除率分別為84％、74％、71％。在微波功率150W、250W、350W的條件下，去除率分別為55%、84%、95%。較長的微波時間與微波功率的增加，亦提供了更多的微波能量讓改質堇青石吸收，證明了在微波能量能有效的誘導改質堇青石降解水中含氯有機物，其縮短處理時間與增加去除率。

In this research, modification of the cordierite in aqueous solution is induced by microwave energy which accelerates oxidation and the dechlorination rate. In the experiment which modification of the cordierite degrades chlorobenzene in water, 2g of modification of the cordierite can degrade contaminants, and the degradation rates in the normal atmospheric temperature are 16%. Obviously, 2g of modification of the cordierite has a higher removal rate than 1g, and thus the more the modification of the cordierite, the higher the removal rates. When the reaction temperature for chlorobenzene in aqueous solution is kept at 40℃, 50 ℃, and 60 ℃, the degradation rates increase to 26%, 38%, and 49%, respectively. The increase of reaction temperature in aqueous solution will enhance the molecular kinetic energy and the number of collision per unit time; thus, lead to a higher removal rate. In the experiment which modification of the cordierite degrades chlorinated organic compounds in water under a microwave field, chlorobenzene and perchloroethylene are degraded in 250 Watts. Under the same conditions, which the quantity is 2g, the removal rates of chlorobenzene and perchloroethylene are 81% and 88%, respectively. With 250 watts microwave power and the number of repetitions as once, twice, and three times, the removal rates for modification of the cordierite are 84%, 74% and 71, respectively. When the microwave power is as 150 watts, 250 watts, and 350 watts, the removal rates are 55%, 84% and 95%, respectively. Because of longer microwave functioning time and more microwave power, more microwave energy is absorbed by modification of the cordierite. Therefore, it is proved that microwave energy can effectively induce modification of the cordierite, and thus degrade chlorinated organic compounds in water. Furthermore, it decreases reaction time and increases removal rates.

目 錄
中文摘要I
英文摘要II
誌謝IV
目錄V
表目錄VIII
圖目錄IX
一、緒論1
1.1前言1
1.2研究動機2
1.3研究內容2
1.4研究目的3
二、文獻回顧4
2.1.含氯有機物4
2.1.1污染來源4
2.1.2氯苯物理及化學特性5
2.1.2.1氯苯對人體健康與環境危害的影響6
2.1.3四氯乙烯物理及化學特性7
2.1.3.1四氯乙烯對人體健康與環境危害的影8
2.2含氯有機物污染物各種處理技術9
2.2.1熱處理方法9
2.2.2生物分解法10
2.2.3高等氧化化學法10
2.2.4吸附法11
2.2.5可見光還原脫氯法11
2.2.6微波處理技術12
2.3零價鐵12
2.3.1零價鐵還原脫氯之基本原理12
2.4堇青石簡介15
2.4.1堇青石特性15
2.4.2堇青石的應用15
2.5觸媒16
2.5.1觸媒的種類16
2.5.2觸媒的形狀17
2.5.3觸媒的製備17
2.5.4擔體效應19
2.5.5觸媒在污染上的應用20
2.5.5.1車輛廢氣排放處理-觸媒轉化器20
2.5.5.2氮氧化物和硫氧化物的廢氣處理21
2.5.5.3有機揮發性氣體、臭氣的處理-觸媒焚化技術22
2.5.5.4其他-空氣清潔處理與毒性有機物質的處理23
2.6微波特性24
2.6.1微波理論24
2.6.2微波介質25
2.6.3微波處理技術的應用26
2.6.4影響微波加熱因子27
2.6.5微波加熱特性28
2.6.6微波與傳統加熱之差異29
三、研究材料與方法30
3.1研究架構30
3.2研究材料與設備30
3.2.1研究材料30
3.2.2研究設備33
3.2.3 GC/MS設定條件33
3.3研究方法34
3.3.1基礎試驗34
3.3.1.1改質堇青石降解氯苯之參數探討34
3.3.1.1.1不同添加量改質堇青石降解氯苯之影響試驗34
3.3.1.1.2比較不同溫度對改質堇青石降解氯苯之影響試驗34
3.3.2微波試驗34
3.3.2.1微波誘導改質堇青石降解氯苯條件之探討34
3.3.2.1.1比較不同微波反應時間之影響試驗34
3.3.2.1.2比較不同污染物對於改質堇青石降解之影響試驗35
3.3.2.1.3比較改質堇青石重覆使用之微波影響試驗35
3.3.3觸媒結構定35
3.3.3.1 BET比表面積分析儀35
3.3.3.2 掃描式電子顯微鏡35
3.3.4品質保證與品質管制36
四、結果與討論37
4.1觸媒結構分析37
4.1.1比表面積（BET）37
4.1.2掃描式電子顯微（SEM）38
4.2基礎試驗41
4.2.1不同添加量改質堇青石降解水中氯苯之影響41
4.2.2比較不同溫度對改質堇青石降解水中氯苯之影響43
4.3微波試驗45
4.3.1比較不同微波反應時間降解水中氯苯之影響45
4.3.2比較不同污染物對於改質堇青石降解水中氯苯之影響48
4.3.3比較微波重覆使用改質堇青石降解水中氯苯之影響49
4.4微波對於溶液溫度的影響51
4.5產物鑑定與反應機制推估51
4.6改質堇青石降解水中氯苯的技術應用可行性52
五、結論與建議53
5.1結論53
5.2建議54
六、參考文獻55
表 目 錄
表2-1含氯有機化合物4
表2-2氯苯基本物理及化學性表5
表2-3氯苯對人體健康之危害效應6
表2-4四氯乙烯基本物理及化學性表7
表2-5四氯乙烯對人體健康之危害效應8
表2-6一般常見堇青石組成與物理特性15
表4-1堇青石之表面性質38
表4-2微波對於溶液溫度的影響51
表4-3 常溫改質堇青石降解水中氯苯的參數與結果52
表4-4 微波誘導改質堇青石降解水中氯苯的參數與結果52
圖 目 錄
圖2-1第一種模式途徑：直接接觸應13
圖2-2第二種模式途徑：腐蝕反應14
圖2-3第三種模式途徑：觸媒氫化反應14
圖3-1研究架構31
圖3-2零價鐵塗覆堇青石試驗32
圖4-1以掃描式電子顯微鏡拍攝之表面結構（未微波堇青石）39
圖4-2以掃描式電子顯微鏡拍攝之表面結構（微波250W堇青石）39
圖4-3以掃描式電子顯微鏡拍攝之表面結構（未微波改質堇青石）40
圖4-4以掃描式電子顯微鏡拍攝之表面結構（微波250W改質堇青石）40
圖4-5比較不同添加量改質堇青石降解100 mg/L之氯苯42
圖4-6比較不同添加量改質堇青石K值之改變42
圖4-7比較常溫下2g空白堇青石與2g改質堇青石降解100 mg/L之氯苯43
圖4-8不同溫度對於改質堇青石降解氯苯之影響44
圖4-9不同溫度對於改質堇青石K值之變化44
圖4-10比較微波250W空白堇青石與改質堇青石降解100 mg/L之氯苯46
圖4-11微波150W改質堇青石降解100 mg/L之氯苯46
圖4-12微波350W改質堇青石降解100 mg/L之氯苯47
圖4-13不同微波功率對於改質堇青石降解氯苯之影響47
圖4-14不同微波功率對於改質堇青石K值之影響48
圖4-15微波250W改質堇青石降解氯苯與四氯乙烯之影響49
圖4-16比較微波250W重覆使用改質堇青石降解氯苯之影響50
圖4-17比較微波250W重覆使用改質堇青石K值之影響50

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