Oxidative removal of brilliant green by UV/S2O82-, UV/HSO5- and UV/H2O2 processes in aqueous media: A comparative study

被引:190
作者
Rehman, Faiza [1 ,2 ,3 ]
Sayed, Murtaza [2 ]
Khan, Javed Ali [1 ,2 ]
Shah, Noor S. [1 ,2 ,4 ]
Khan, Hasan M. [2 ]
Dionysiou, Dionysios D. [1 ,5 ]
机构
[1] Univ Cincinnati, Dept Chem & Environm Engn, Environm Engn & Sci Program, Engn Res Ctr 705, Cincinnati, OH 45221 USA
[2] Univ Peshawar, Natl Ctr Excellence Phys Chem, Radiat & Environm Chem Lab, Peshawar 25120, Pakistan
[3] Univ Poonch Rawalakot, Dept Chem, Azad, Jammu & Kashmir, Pakistan
[4] COMSATS Univ Islamabad, Dept Environm Sci, Vehari Campus, Islamabad 61100, Pakistan
[5] Univ Cyprus, Nireas Int Water Res Ctr, POB 20537, CY-1678 Nicosia, Cyprus
关键词
Advanced oxidation processes (AOPs); Brilliant green; Degradation pathways; Dyes; Second order rate constant; Water treatment; CYANOBACTERIAL TOXIN CYLINDROSPERMOPSIN; UV-254 NM ACTIVATION; HYDROXYL RADICALS; RATE CONSTANTS; PHOTOCATALYTIC DEGRADATION; PHOTOCHEMICAL DEGRADATION; MECHANISTIC APPROACH; TOXICITY ASSESSMENT; CHEMICAL OXIDATION; HEATED PERSULFATE;
D O I
10.1016/j.jhazmat.2018.06.012
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The removal of brilliant green (BG), a toxic organic and cationic dye, has been examined by UV/S2O82- (PS), UV/HSO5- (PMS) and UV/H2O2 processes. BG showed insignificant direct photolysis at 254 nm (i.e., 8.6% after 30 min). However, enhanced BG degradation was observed in UV/PS, UV/PMS and UV/H2O2 systems as revealed from 63.1, 47.0 and 34.8% BG degradation, respectively, at 30 min of reaction time, using 0.05 mM BG and 1.0 mM oxidant initial concentration: The bimolecular rate constants of center dot OH and SO4 center dot(-) with BG were determined to be 2.35 x 10(9) and 2.21 x 10(9) M-1 s(-1), respectively. Electrical energy per order (EE/O) values for UV/PS, UV/PMS and UV/H2O2 processes were calculated to be 5.4, 6.8, and 7.8 KWh/m(3)/order, respectively. The addition of humic acid (HA) and inorganic anions inhibited the degradation of BG by UV/PS in the order of NO2- > HA > HCO3- > Cl- > NO3- approximate to SO42-. The results of frontier electron densities (FEDs) showed that C-atom holding the three rings (C7), and C-atoms at para positions to N-alkyl groups of the two rings (C4 and C14) are the predominant sites for radical addition. Furthermore, nine degradation products (DPs) of BG were detected experimentally using LC/MS/MS.
引用
收藏
页码:506 / 514
页数:9
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