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引文資料
題名:
以不銹鋼網覆膜奈米光觸媒TiO₂光催化偶氮染料Orange G脫色影響之研究
書刊名:
弘光學報
作者:
張明琴
/
蘇弘毅
/
張詠禎
作者(外文):
Chang, Ming-chin
/
Shu, Hung-yee
/
Chang, Yung-chen
出版日期:
2009
卷期:
57
頁次:
頁119-129
主題關鍵詞:
二氧化鈦
;
光催化
;
浸鍍
;
偶氮染料
;
脫色
;
TiO₂
;
Photocatalysis
;
Dip coating
;
Azo dye
;
Color removal
原始連結:
連回原系統網址
相關次數:
被引用次數:期刊(0) 博士論文(0) 專書(0) 專書論文(0)
排除自我引用:0
共同引用:0
點閱:42
染整廢水結構複雜,具有高色度、高COD及生物難分解等特性,若未妥善處理而排入自然水體 時,將直接造成對水質衝擊。因一般傳統程序如混凝及生物處理等無法有效符合放流水標準,故急 需研發有效處理染整廢水之技術。 利用UV/TiO2程序已被證實可有效處理多種環境汙染物,故本研究擬以此程序處理偶氮染料 Orange G廢水,且為改善TiO2粉末懸浮(slurry)系統操作問題,本研究將不鏽鋼網基材浸漬於Degussa P-25 TiO2懸浮液中,經乾燥處理形成TiO2覆膜,即以此浸鍍(dip coating)方式固定披覆TiO2粉末於不 鏽鋼網上。且探討時間效應、TiO2添加/披覆劑量、染料初始濃度及染料初始pH值條件對偶氮染料 Orange G降解影響。由FE-SEM、XRD及BET等基本性質分析結果可知,觸媒經浸鍍後能均勻披覆於 不銹鋼載體上,平均顆粒大小皆小於30 nm,主要晶體結構為Anatase,比表面積為5.6717 m2/g。實 驗結果顯示UV/TiO2光催化程序可快速有效降低色度,固定TiO2於不銹鋼網之反應程序去除效率比 懸浮式稍差,且需要較長反應時間,但優勢為省去過濾或離心且操作方便。經過60分鐘反應後,添 加12 g/m2及20 g/m2,脫色效率可分別達50.10及59.51%。若將披覆劑量增加至40 g/m2及60 g/m2, 效率可提升至77.58及86.40%。此外,當染料初始pH調整為3時具最佳脫色效果。且染料初濃度提 高使得染料去除率降低。反應模式可用擬一階反應(Pseudo-first Order Reaction)描述,符合Langmiur– Hinshelwood反應動力式,求出k及KA分別為4.05 L.min/mg及4.80×10-2 L/mg。最後經耐久性測試五 次,證明經120 min反應之脫色效率亦可達 95.83%。
以文找文
Effluent from dye manufacture with complex structure, high color, high COD and recalcitrant for biodegradation directly impact the quality of water body without adequate treatment. The traditional processes such as coagulation and biological treatment may frequently not comply with the effluent standards so that developing the effective technique is very urgent. The process of UV/TiO2 is demonstrated to be effective for many environmental pollutants from research results. In this study, it was applied for color removal of azo dye Orange G. Moreover, the TiO2 (Degussa P-25) particles were dip-coated on the stainless steel net for avoid the operation problem of slurry reactor. The experimental parameters such as time, TiO2 dose/coating dose, initial concentration of azo dye and initial pH were determined for the effect of dye degradation. From FE-SEM, XRD and BET analysis, the results showed the catalyte (anatase) coated homogeneously on the steel net with average particle size less than 30 nm and specific surface area of 5.6717 m2/g. From the results, the removal efficiencies of fixed TiO2 on the steel net were less than the slurry reactor, however, the merit of fixed system was easy to operation for saving filtration or centrifuge. Within 60 minutes, the color removal efficiencies of 50.10 and 59.51% by adding TiO2 particles of 12 g/m2 and 20 g/m2, respectively that enhanced to 77.58 and 86.40% by increasing to 40 g/m2 and 60 g/m2, respectively. Moreover, the initial pH of 3 showed the best color removal. Increasing dye concentrations improved the removal efficiencies that the model meeting Langmiur –Hinshelwood reaction was developed as a pseudo-first order reaction. The k and KA were calculated as 4.05 L.min/mg and 4.80×10−2 L/mg. After 5 times of durable tests within 120 min, the color removal of 95.83% was obtained.
以文找文
期刊論文
1.
Lin, S. H.(1993)。Adsorption of Disperse Dye by Powdered Activated Carbon。J. of Chem. Tech. & Biotech,7(4),387-391。
2.
Crowe, T.、O'Melia, C. R.、Little, L.(1978)。Coagulation of Disperse Dyes。American Dyestuff Reporter,67(12),52-57。
3.
Shu, H. Y.、Chang, M. C.(2005)。Decolorization effects of six azo dyes by O3, UV/O3 and UV/H2O2 processes。Dyes and Pigments,65,25-31。
其他
1.
Bauer, C. Jacques, P. and Kalt, A.(2001)。Photooxidation of an azo dye induced by visible light incident on the surface of TiO2.。
2.
Kao, C. M. Chou, M. S. Fang, W. L. Liu, B. W. and Huang, B. R.(2001)。Regulating colored textile wastewater by 3/31 wavelength admi methods in taiwan。
3.
Brown, M. A. DeVito, S. C.(1993)。Predicting azo dye toxicity。
4.
蘇弘毅、張明琴、簡韶儀、鄭仲甫(2006)。以Fenton程序處理兩種染料廢水脫色及降低TOC之研究。
延伸查詢
5.
Shu, H. Y. and Chang, M. C.(2006)。Development of a rate expression for predicting decolorization of C.I. acid black 1 in a UV/H2O2 process。
6.
Tang, W. Z. and An, H.(1995)。UV/TiO2 photo catalytic oxidation of commercial dyes in aqueous solutions。
7.
Muruganandham, M. and Swaminathan, M.(2006)。Photocatalytic decolourisation and degradation of Reactive Orange 4 by TiO2- UV process。
8.
Baran, W. Adamek, E. and Makowski, A.(2008)。The influence of selected parameters on the photocatalytic degradation of azo-dyes in the presence of TiO2 aqueous suspension。
9.
Saien, J. and Soleymani, A. R.(2007)。Degradation and mineralization of direct blue 71 in a circulating upflow reactor by UV/TiO2 process and employing a new method in kinetic study。
10.
Daneshvar, N. Salari, D. and Khataee, A. R.(2003)。Photocatalytic degradation of azo dye acid red 14 in water: Investigation of the effect of operational parameters.。
11.
Guillard, C. Lachheb, H. Houas, A. Ksibi, M. Elaloui, E. and Herrmann, J. M.(2003)。Influence of chemical structure of dyes, of pH and of inorganic salts on their photocatalytic degradation by TiO2 comparison of the efficiency of powder and supported TiO2。
12.
Sun, J. Wang, X. Sun, J. Sun, R. Sun, S. and Qiao, L.(2006)。Photocatalytic degradation and kinetics of orange G using nano-sized sn(IV)/ TiO2/AC photocatalyst。
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