Photodegradation of Triphenylamino Methane (Magenta) by Photosensitizer in Oxygenated Solutions

被引:41
作者
Herath, Ajith C.
Rajapakse, R. M. G.
Wicramasinghe, Anura
Karunaratne, Veranja [1 ]
机构
[1] Univ Peradeniya, Dept Chem, Peradeniya, Sri Lanka
关键词
WATER; FENTON; SENSITIZER; KINETICS;
D O I
10.1021/es801765t
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Reactive oxygen species (ROS), namely superoxide anion (O-2(center dot-), singlet oxygen (O-1(2)), are potentially important substances for the mineralization of toxic organic molecules. The utility of hematoporphyrindihydrochloride (HPDHC) as a photosensitizer to generate ROS and their subsequent role in the destruction of magenta (MaG) in aqueous media is the main concern. The light irradiation of oxygenated aqueous solution of HPDHC and 1.5 x 10(-5) mol dm(-3) MaG at PH 3 yielded micromolar levels of NO3- ions. A higher rate of photodegradation (1.02 mol dm(-3) min(-1) at PH 3 was observed compared to that of at PH 6 (0.68 mol dm(-3) min(-1)). Experiments were carried out in the presence of 1, 4-diazabicyclo[2.2.2]octane (DABCO) as singlet oxygen (O-1(2)) quencher and bezoquinone (BQ) as superoxide anion (O-2(center dot-)) quencher. Only BQ was able to stop photodegradation suggesting that the photooxidation of MaG is mainly caused by O-2(center dot-), which is generated by an electron transfer from the excited HPDHC to ground-state oxygen. The presence of iron(II) at PH 3.0, compared to that without iron(II),showed a higher rate of photodegradation due to the formation of extremely reactive hydroxyl radicals (HO center dot) upon dismutation of O-2(center dot-) anion through H2O2 intermediate. The formation of O-2(center dot-), H2O2, and HO center dot is therefore evident, which may act as active sites for subsequent photodegradation of MaG.
引用
收藏
页码:176 / 180
页数:5
相关论文
共 36 条
[1]  
American Public Health Association, 1995, STAND METH EX WAT WA, P4
[2]   Degradation/decoloration of concentrated solutions of Orange II. Kinetics and quantum yield for sunlight induced reactions via Fenton type reagents [J].
Bandara, J ;
Morrison, C ;
Kiwi, J ;
Pulgarin, C ;
Peringer, P .
JOURNAL OF PHOTOCHEMISTRY AND PHOTOBIOLOGY A-CHEMISTRY, 1996, 99 (01) :57-66
[3]   TRANSFORMATION OF DYES AND RELATED-COMPOUNDS IN ANOXIC SEDIMENT - KINETICS AND PRODUCTS [J].
BAUGHMAN, GL ;
WEBER, EJ .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1994, 28 (02) :267-276
[4]   Role of quinone intermediates as electron shuttles in Fenton and photoassisted Fenton oxidations of aromatic compounds [J].
Chen, RZ ;
Pignatello, JJ .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1997, 31 (08) :2399-2406
[5]  
CHEVES W, 1973, J AM CHEM SOC, P2987
[6]  
CHUNCHENG C, 2006, ENVIRON SCI TECHNOL, V40, P3965
[7]   Kinetic studies of depollution process in TiO2 slurries: Interdependences of adsorption and UV-intensity [J].
Cunningham, J ;
Sedlak, P .
CATALYSIS TODAY, 1996, 29 (1-4) :309-315
[8]   DNA cleavage by the antitumor agent 3-amino-1,2,4-benzotriazine 1,4-dioxide (SR4233): Evidence for involvement of hydroxyl radical [J].
Daniels, JS ;
Gates, KS .
JOURNAL OF THE AMERICAN CHEMICAL SOCIETY, 1996, 118 (14) :3380-3385
[9]   Comparative study of photodegradation of three hematoporphyrin derivative:: Photofrin®, Photogem® and Photosan [J].
Ferreira, J. ;
Menezes, P. F. C. ;
Kurachi, C. ;
Sibata, C. H. ;
Allison, R. R. ;
Bagnato, V. S. .
LASER PHYSICS LETTERS, 2007, 4 (10) :743-748
[10]   Reduction of O2 to superoxide anion (O2•-) in water by heteropolytungstate cluster-anions [J].
Geletii, Yurii V. ;
Hill, Craig L. ;
Atalla, Rajai H. ;
Weinstock, Ira A. .
JOURNAL OF THE AMERICAN CHEMICAL SOCIETY, 2006, 128 (51) :17033-17042