KINETIC-STUDIES IN HETEROGENEOUS PHOTOCATALYSIS .6. AM1 SIMULATED SUNLIGHT PHOTODEGRADATION OVER TITANIA IN AQUEOUS-MEDIA - A 1ST CASE OF FLUORINATED AROMATICS AND IDENTIFICATION OF INTERMEDIATES

被引:85
作者
MINERO, C
ALIBERTI, C
PELIZZETTI, E
TERZIAN, R
SERPONE, N
机构
[1] UNIV TURIN, DIPARTMENTO CHIM ANALIT, I-10125 TURIN, ITALY
[2] CONCORDIA UNIV, DEPT CHEM & BIOCHEM, MONTREAL H3G 1M8, QUEBEC, CANADA
关键词
D O I
10.1021/la00053a020
中图分类号
O6 [化学];
学科分类号
0703 ;
摘要
Fluorinated aromatic compounds have been mineralized to CO2 and fluoride by irradiation of aqueous, air-equilibrated suspensions (pH 3, H2SO4) containing TiO2 (Degussa P-25 anatase) and a fluorinated phenol (2-, 3-, or 4-fluorophenol and 2,4- and 3,4-difluorophenol) with AM1 simulated sunlight (lambda greater-than-or-equal-to 310 nm). Decomposition of the fluorophenols is immediately followed by defluorination (less-than-or-equal-to 30 min) as evidenced by the rate of formation of fluoride; only approximately 75-80% of fluoride is recovered in solution, the remaining quantity being adsorbed on the TiO2 particles. This may have certain consequences on the time needed for CO2 evolution as fluoride may block some of the TiO2 catalytic sites. Evolution of CO2 is 3 times slower (approximately 90 to 240 min) than decomposition/defluorination of the starting fluorinated phenols. Apparent kinetic data have been determined by curve-fitting methods on the basis of a simple phenomenological model which implicates consecutive and parallel reactions: A --> B(i) --> C. The major oxidizing species is the .OH radical formed by oxidation of surface hydroxyl groups and/or surface bound water molecules with the photocatalyst's valence band holes. It is argued that the distinction between a surface bound and a free (in bulk solution) .OH radical is in fact a moot point which kinetic considerations alone cannot delineate. A mechanistic route is summarized to rationalize the various intermediate products formed along the temporal course of the photomineralization process: fluorohydroquinone, fluorocatechol, trihydroxybenzene, hydroquinone, catechol, and benzoquinone. The overall order of the total destruction (to CO2) of the fluorophenols examined is 2,4-difluorophenol > 3-fluorophenol approximately 4-fluorophenol > 2-fluorophenol greater-than-or-equal-to 3,4-difluorophenol.
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页码:928 / 936
页数:9
相关论文
共 49 条
[1]   PULSE RADIOLYSIS OF BENZOQUINONE AND HYDROQUINONE - SEMIQUINONE FORMATION BY WATER ELIMINATION FROM TRIHYDROXYCYCLOHEXADIENYL RADICALS [J].
ADAMS, GE ;
MICHAEL, BD .
TRANSACTIONS OF THE FARADAY SOCIETY, 1967, 63 (533P) :1171-&
[2]   KINETIC-STUDIES IN HETEROGENEOUS PHOTOCATALYSIS .1. PHOTOCATALYTIC DEGRADATION OF CHLORINATED PHENOLS IN AERATED AQUEOUS-SOLUTIONS OVER TIO2 SUPPORTED ON A GLASS MATRIX [J].
ALEKABI, H ;
SERPONE, N .
JOURNAL OF PHYSICAL CHEMISTRY, 1988, 92 (20) :5726-5731
[3]  
ALEKABI H, 1989, PHOTOCATALYSIS FUNDA, pCH14
[4]   ELECTRON-SPIN-RESONANCE AND PHOTOLUMINESCENCE EVIDENCE FOR THE PHOTOCATALYTIC FORMATION OF HYDROXYL RADICALS ON SMALL TIO2 PARTICLES [J].
ANPO, M ;
SHIMA, T ;
KUBOKAWA, Y .
CHEMISTRY LETTERS, 1985, (12) :1799-1802
[5]   PHOTODEGRADATION OF PENTACHLOROPHENOL CATALYZED BY SEMICONDUCTOR PARTICLES [J].
BARBENI, M ;
PRAMAURO, E ;
PELIZZETTI, E ;
BORGARELLO, E ;
SERPONE, N .
CHEMOSPHERE, 1985, 14 (02) :195-208
[6]  
BARBENI M, 1984, NOUV J CHIM, V8, P547
[7]  
BARD AJ, 1980, ELECTROCHEMICAL METH, P500
[8]  
BOLTON JR, 1989, COMMUNICATION
[9]  
BORELLO R, 1989, ENVIRON TOXICOL CHEM, V8, P997, DOI [10.1897/1552-8618(1989)8[997:PDODMI]2.0.CO
[10]  
2, 10.1002/etc.5620081105]