Comparison between O-3/VUV, O-3/H2O2, VUV and O-3 processes for the decomposition of organophosphoric acid triesters

被引:28
作者
Echigo, S
Yamada, H
Matsui, S
Kawanishi, S
Shishida, K
机构
[1] KYOTO UNIV,FAC MED,DEPT PUBL HLTH,SAKYO KU,KYOTO 606,JAPAN
[2] TAKUMA CO LTD,KITA KU,OSAKA 530,JAPAN
关键词
advanced oxidation processes; ESR-spin trapping technique; hydroxyl radical; leachate from solid waste landfill; O-3; H2O2; VUV;
D O I
10.2166/wst.1996.0182
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
O-3/vacuum ultraviolet (VUV, ultraviolet radiation by a low pressure mercury lamp at 185 and 254 nm), O-3/H2O2 and VUV processes rapidly decomposed organophosphoric acid triesters (OPEs) dissolved in distilled water as compared to simple ozonation. The O-3/VUV process was the fastest of the three advanced oxidation processes (AOPs) for the decomposition of 1 mg/l of OPEs in pH 7.5 phosphate buffer solution (0.5 mM). However the difference between the pseudo-first-order rate constants of the O-3/VUV and O-3/H2O2 processes decreased in the condition of increasing OPEsw concentration, and the efficiencies of the two processes were almost the same at an initial concentration of 20 mg/l. Contrary to results in distilled water, in an effluent from a solid waste landfill site, the O-3/H2O2 process was the fastest. This is manily due to the absorption of VUV radiation by nitrate ion. WE confirmed that nitrate ion of more than a few mg/l strongly interfered with the generation of hydroxyl (OH) radicals from VUV radiation while the O-3/H2O2 process was not affected. The use of an ESR-spin trapping technique revealed that AOPs generated more OH radicals than ozonation alone, and the detection of hydrogen atom confirmed that VUV radiation directly generated OH radicals from water. Copyright (C) 1996 IAWQ. Published by Elsevier Science Ltd.
引用
收藏
页码:81 / 88
页数:8
相关论文
共 12 条
[1]   A SIMPLE SPECTROPHOTOMETRIC DETERMINATION OF HYDROGEN-PEROXIDE AT LOW CONCENTRATIONS IN AQUEOUS-SOLUTION [J].
BAGA, AN ;
JOHNSON, GRA ;
NAZHAT, NB ;
SAADALLANAZHAT, RA .
ANALYTICA CHIMICA ACTA, 1988, 204 (1-2) :349-353
[2]  
FUKUSHIMA M, 1986, REPORT OSAKA CITY I, V48, P175
[3]  
GLAZE WH, 1987, OZONE-SCI ENG, V9, P335
[4]   DISINFECTION OF VIRUS IN WATER BY ACTIVE OXYGEN SPECIES [J].
HAMADA, A ;
HAKODA, M ;
UTSUMI, H .
WATER SCIENCE AND TECHNOLOGY, 1993, 28 (07) :239-242
[5]   PHOTOCHEMICAL BEHAVIOR OF ORGANIC PHOSPHATE-ESTERS IN AQUEOUS-SOLUTIONS IRRADIATED WITH A MERCURY LAMP [J].
ISHIKAWA, S ;
UCHIMURA, Y ;
BABA, K ;
EGUCHI, Y ;
KIDO, K .
BULLETIN OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY, 1992, 49 (03) :368-374
[6]  
KAWAAI Y, 1995, P 12 WORLD C INT OZ, P279
[7]  
OGITA T, 1985, J CHEM SOC JAP, P970
[8]   DESTRUCTION OF POLLUTANTS IN WATER WITH OZONE IN COMBINATION WITH ULTRAVIOLET-RADIATION .3. PHOTOLYSIS OF AQUEOUS OZONE [J].
PEYTON, GR ;
GLAZE, WH .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1988, 22 (07) :761-767
[9]   FREE-RADICAL GENERATION BY ULTRASOUND IN AQUEOUS AND NONAQUEOUS SOLUTIONS [J].
RIESZ, P ;
BERDAHL, D ;
CHRISTMAN, CL .
ENVIRONMENTAL HEALTH PERSPECTIVES, 1985, 64 :233-252
[10]   RATE CONSTANTS AND PRODUCTS OF THE REACTIONS OF EAQ-, O-2-, AND H WITH OZONE IN AQUEOUS-SOLUTIONS [J].
SEHESTED, K ;
HOLCMAN, J ;
HART, EJ .
JOURNAL OF PHYSICAL CHEMISTRY, 1983, 87 (11) :1951-1954