Wu Chung-Hsin, Kuo Chao-Yin, Chang Chung-Liang
Department of Environmental Engineering, Da-Yeh University, 112 Shan-Jiau Road, Da-Tsuen, Chang-Hua, Taiwan, ROC.
J Hazard Mater. 2008 May 30;153(3):1052-8. doi: 10.1016/j.jhazmat.2007.09.058. Epub 2007 Sep 21.
This study adopted O3, UV/TiO2/O3, O3/Mn(II) and O3/MnO2 systems to assess the decolorization efficiency of C.I. Reactive Red 2 (RR2). The decolorization rate increased with concentrations of Mn(II) and MnO2 in the ranges 0.05-0.1 and 0.05-0.8 g/l, respectively. However, when 0.5-3g/l TiO2 was added, the effect of TiO2 dosage for RR2 decolorization was insignificant in the UV/TiO2/O3 system. At pH 2, the decolorization rate constants of O3, O3/Mn(II) (0.05 g/l), O3/Mn(II) (0.1g/l), O3/Mn(II) (0.15 g/l), O3/MnO2 (0.05 g/l) and O3/MnO2 (0.8 g/l) were 0.816, 2.001, 3.173, 3.087, 1.040 and 1.648 min(-1), respectively. After 5 min of reaction, the decolorization rates followed the order O3/Mn(II)>O3/MnO2>O3>UV/TiO2/O3; however, the TOC removal did not vary among these systems. Adding ethanol reduced the decolorization rate of the UV/TiO2/O3 and O3/MnO2 systems and did not affect the decolorization rate of O3/Mn(II). Decolorization in UV/TiO2/O3, O3/Mn(II) and O3/MnO2 systems is suggested to proceed by mainly radical-, surface- and radical-type mechanisms, respectively. Additionally, direct ozonation cannot be ignored in O3/Mn(II) and O3/MnO2 systems.
本研究采用臭氧(O3)、紫外光/二氧化钛/臭氧(UV/TiO2/O3)、臭氧/锰(II)(O3/Mn(II))和臭氧/二氧化锰(O3/MnO2)体系来评估活性艳红2(RR2)的脱色效率。脱色率分别随着锰(II)浓度在0.05 - 0.1 g/L范围内以及二氧化锰浓度在0.05 - 0.8 g/L范围内的增加而提高。然而,当添加0.5 - 3 g/L的二氧化钛时,在紫外光/二氧化钛/臭氧体系中,二氧化钛用量对RR2脱色的影响并不显著。在pH值为2时,臭氧(O3)、臭氧/锰(II)(0.05 g/L)、臭氧/锰(II)(0.1 g/L)、臭氧/锰(II)(0.15 g/L)、臭氧/二氧化锰(0.05 g/L)和臭氧/二氧化锰(0.8 g/L)的脱色速率常数分别为0.816、2.001、3.173、3.087、1.040和1.648 min⁻¹。反应5分钟后,脱色率顺序为臭氧/锰(II)>臭氧/二氧化锰>臭氧>紫外光/二氧化钛/臭氧;然而,这些体系中总有机碳(TOC)的去除率并无差异。添加乙醇降低了紫外光/二氧化钛/臭氧和臭氧/二氧化锰体系的脱色率,而对臭氧/锰(II)体系的脱色率没有影响。紫外光/二氧化钛/臭氧、臭氧/锰(II)和臭氧/二氧化锰体系中的脱色作用分别主要通过自由基型、表面型和自由基 - 表面型机制进行。此外,在臭氧/锰(II)和臭氧/二氧化锰体系中,直接臭氧化作用也不可忽视。