Azo dye decolorization by halophilic and halotolerant microorganisms

被引:47
作者
Amoozegar, Mohammad Ali [1 ]
Hajighasemi, Mahbod [1 ]
Hamedi, Javad [1 ]
Asad, Sedigheh [1 ]
Ventosa, Antonio [2 ]
机构
[1] Univ Tehran, Dept Microbiol, Fac Biol, Coll Sci, Tehran, Iran
[2] Univ Seville, Dept Microbiol & Parasitol, Fac Pharm, Seville, Spain
基金
美国国家科学基金会;
关键词
Azo dyes; Halophile; Halotolerant; Decolorization; Biodegradation; SHEWANELLA-DECOLORATIONIS S12; SIMULATED TEXTILE EFFLUENT; ANAEROBIC-AEROBIC SYSTEM; AROMATIC-AMINES; REACTIVE DYES; WASTE-WATER; MICROBIAL DECOLORIZATION; BACTERIAL CONSORTIUM; REDUCTASE-ACTIVITY; MASS-SPECTROMETRY;
D O I
10.1007/s13213-010-0144-y
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
Different types of microorganisms are capable of degrading azo dyes due to their high metabolic potentials. However, many of them cannot be used as degrading agents due to the harsh conditions of dye-polluted environments. Here, halophilic and halotolerant microorganisms can be the best candidates for a practical biodecolorization process as they are able to grow easily at high concentrations of salts. In addition, some of them can tolerate the presence of other stress factors such as toxic oxyanions and heavy metals which are so common in industrial wastewaters. In recent years, several studies have been focused on halophilic and halotolerant microorganisms and their abilities for decolorization of azo dyes. For example, Shewanella putrefaciens was determined to be capable of the complete removal of Reactive Black-5, Direct Red-81, Acid Red-88 and Disperse Orange-3 (all 100 mg l(-1)) within 8 h in the presence of 40 g l(-1) NaCl. Another halophilic example is Halomonas sp. GTW which has shown a remarkable performance in the removal of different azo dyes within 24 h in the presence of 150 g l(-1) NaCl. Although these approaches need to be studied in more detail, some studies have designed different types of fermentation processes and even specific fermentors to provide a practical methodology for industrial wastewater remediation. Sequential anaerobic EGSB (expanded granular sludge blanket) and aerobic reactor was the result of an important attempt to design an effective approach to large-scale biodecolorization.
引用
收藏
页码:217 / 230
页数:14
相关论文
共 112 条
[61]   Purification and partial characterization of azoreductase from Enterobacter agglomerans [J].
Moutaouakkil, A ;
Zeroual, Y ;
Dzayri, FZ ;
Talbi, M ;
Lee, K ;
Blaghen, M .
ARCHIVES OF BIOCHEMISTRY AND BIOPHYSICS, 2003, 413 (01) :139-146
[62]   Chromium(VI) reductase activity is associated with the cytoplasmic membrane of anaerobically grown Shewanella putrefaciens MR-1 [J].
Myers, CR ;
Carstens, BP ;
Antholine, WE ;
Myers, JM .
JOURNAL OF APPLIED MICROBIOLOGY, 2000, 88 (01) :98-106
[63]   IRON AND MANGANESE IN ANAEROBIC RESPIRATION - ENVIRONMENTAL SIGNIFICANCE, PHYSIOLOGY, AND REGULATION [J].
NEALSON, KH ;
SAFFARINI, D .
ANNUAL REVIEW OF MICROBIOLOGY, 1994, 48 :311-343
[64]   Microbial process for the decolorization of textile effluent containing azo, diazo and reactive dyes [J].
Nigam, P ;
Banat, IM ;
Singh, D ;
Marchant, R .
PROCESS BIOCHEMISTRY, 1996, 31 (05) :435-442
[65]  
NORTEMANN B, 1994, ARCH MICROBIOL, V161, P320
[66]  
NORTEMANN B, 1986, APPL ENVIRON MICROB, V52, P1195
[67]   Azo-dye degradation in an anaerobic-aerobic treatment system operating on simulated textile effluent [J].
O'Neill, C ;
Lopez, A ;
Esteves, S ;
Hawkes, FR ;
Hawkes, DL ;
Wilcox, S .
APPLIED MICROBIOLOGY AND BIOTECHNOLOGY, 2000, 53 (02) :249-254
[68]   Anaerobic-aerobic biotreatment of simulated textile effluent containing varied ratios of starch and azo dye [J].
O'Neill, C ;
Hawkes, FR ;
Hawkes, DL ;
Esteves, S ;
Wilcox, SJ .
WATER RESEARCH, 2000, 34 (08) :2355-2361
[69]  
O'Neill C, 1999, J CHEM TECHNOL BIOT, V74, P1009, DOI 10.1002/(SICI)1097-4660(199911)74:11<1009::AID-JCTB153>3.0.CO
[70]  
2-N