Basic and applied aspects in the microbial degradation of azo dyes

被引:834
作者
Stolz, A [1 ]
机构
[1] Univ Stuttgart, Inst Mikrobiol, D-70569 Stuttgart, Germany
关键词
D O I
10.1007/s002530100686
中图分类号
Q81 [生物工程学(生物技术)]; Q93 [微生物学];
学科分类号
071005 ; 0836 ; 090102 ; 100705 ;
摘要
Azo dyes are the most important group of synthetic colorants. They are generally considered as xenobiotic compounds that are very recalcitrant against biodegradative processes. Nevertheless, during the last few years it has been demonstrated that several microorganisms are able, under certain environmental conditions, to transform azo dyes to non-colored products or even to completely mineralize them. Thus, various lignolytic fungi were shown to decolorize azo dyes using ligninases, manganese peroxidases or laccases. For some model dyes, the degradative pathways have been investigated and a true mineralization to carbon dioxide has been shown. The bacterial metabolism of azo dyes is initiated in most cases by a reductive cleavage of the azo bond, which results in the formation of (usually colorless) amines. These reductive processes have been described for some aerobic bacteria, which can grow with (rather simple) azo compounds. These specifically adapted microorganisms synthesize true azoreductases, which reductively cleave the azo group in the presence of molecular oxygen. Much more common is the reductive cleavage of azo dyes under anaerobic conditions. These reactions usually occur with rather low specific activities but are extremely unspecific with regard to the organisms involved and the dyes converted. In these unspecific anaerobic processes, low-molecular weight redox mediators (e.g. flavins or quinones) which are enzymatically reduced by the cells (or chemically by bulk reductants in the environment) are very often involved. These reduced mediator compounds reduce the azo group in a purely chemical reaction. The (sulfonated) famines that are formed in the course of these reactions may be degraded aerobically. Therefore, several (laboratory-scale) continuous anaerobic/aerobic processes for the treatment of wastewaters containing azo dyes have recently been described.
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页码:69 / 80
页数:12
相关论文
共 146 条
[41]   2-STAGE ANAEROBIC-AEROBIC TREATMENT OF SULFONATED AZO DYES [J].
FITZGERALD, SW ;
BISHOP, PL .
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART A-ENVIRONMENTAL SCIENCE AND ENGINEERING & TOXIC AND HAZARDOUS SUBSTANCE CONTROL, 1995, 30 (06) :1251-1276
[42]   FATE OF AZO DYES IN SLUDGES [J].
GANESH, R ;
BOARDMAN, GD ;
MICHELSEN, D .
WATER RESEARCH, 1994, 28 (06) :1367-1376
[43]  
Ghosh Dilip K., 1993, Indian Journal of Experimental Biology, V31, P951
[44]  
GHOSH DK, 1992, FEMS MICROBIOL LETT, V98, P229, DOI 10.1016/0378-1097(92)90161-G
[45]  
GILL M, 1984, Z NATURFORSCH C, V39, P1027
[46]  
GLASSER A, 1992, DECHEMA BIOTECHNOL B, V5, P1085
[47]   MN(II) OXIDATION IS THE PRINCIPAL FUNCTION OF THE EXTRACELLULAR MN-PEROXIDASE FROM PHANEROCHAETE-CHRYSOSPORIUM [J].
GLENN, JK ;
AKILESWARAN, L ;
GOLD, MH .
ARCHIVES OF BIOCHEMISTRY AND BIOPHYSICS, 1986, 251 (02) :688-696
[48]   NEW PATHWAY FOR DEGRADATION OF SULFONATED AZO DYES BY MICROBIAL PEROXIDASES OF PHANEROCHAETE-CHRYSOSPORIUM AND STREPTOMYCES-CHROMOFUSCUS [J].
GOSZCZYNSKI, S ;
PASZCZYNSKI, A ;
PASTIGRIGSBY, MB ;
CRAWFORD, RL ;
CRAWFORD, DL .
JOURNAL OF BACTERIOLOGY, 1994, 176 (05) :1339-1347
[49]  
Hardin IR, 2000, TEXT CHEM COLOR AM D, V32, P38
[50]   TRANSFORMATION OF AZO DYE AO-7 BY WASTE-WATER BIOFILMS [J].
HARMER, C ;
BISHOP, P .
WATER SCIENCE AND TECHNOLOGY, 1992, 26 (3-4) :627-636