Effect of some operational parameters on textile dye biodegradation in a sequential batch reactor

被引:155
作者
Lourenço, ND [1 ]
Novais, JM [1 ]
Pinheiro, HM [1 ]
机构
[1] Univ Tecn Lisboa, Ctr Engn Biol & Quim, Inst Super Tecn, P-1049001 Lisbon, Portugal
关键词
textile effluents; anaerobic-aerobic biotreatment; sequencing batch reactor; sulfonated azo dyes; reactive dyes; color removal;
D O I
10.1016/S0168-1656(01)00313-3
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
The combination of anaerobic and aerobic periods in the operation cycle of a Sequencing Batch Reactor (SBR) was chosen to study biological color removal from simulated textile effluents containing reactive, sulfonated, monoazo and diazo, dyes, respectively, Remazol Brilliant Violet 5R and Remazol Black B. 90% color removal was obtained for the violet dye in a 24-h cycle with a Sludge Retention Time (SRT) of 15 days and an aerated reaction phase of 10 h. For the black dye only 75% color removal was achieved with the same operational conditions and no improvement was observed with the increase of the SRT to 20 days. For the violet dye a reduction of the color removal values from 90 to 75% was observed with the increase of the aerated reaction phase from 10 to 12 h. However, this increase did not promote the aerobic biodegradation of the produced aromatic amines. Abiotic tests were performed with sterilized SBR samples and no color removal was observed in cell-free supernatants. However color removal values of 30 and 12% were observed in the presence of sterilized cells and supernatants with violet and black dye, respectively and could be attributed to the presence of active reducing principles in the sterilized samples. (C) 2001 Elsevier Science B.V. All rights reserved.
引用
收藏
页码:163 / 174
页数:12
相关论文
共 35 条
[1]  
*AM PUBL HLTH ASS, 1995, STAND METH EX WAT WA
[2]   SBR technology used for advanced combined municipal and tannery wastewater treatment with high receiving water standards [J].
Banas, J ;
Plaza, E ;
Styka, W ;
Trela, J .
WATER SCIENCE AND TECHNOLOGY, 1999, 40 (4-5) :451-458
[3]   Combined anaerobic-aerobic sbr for the treatment of piggery wastewater [J].
Bernet, N ;
Delgenes, N ;
Akunna, JC ;
Delgenes, JP ;
Moletta, R .
WATER RESEARCH, 2000, 34 (02) :611-619
[4]  
BUMPUS JA, 1995, BIOTRANSFORMATIONS M, P157
[5]  
CARLIELL CM, 1995, WATER SA, V21, P61
[6]   Strategies for dealing with piggery effluent in Australia: the sequencing batch reactor as a solution [J].
Edgerton, BD ;
McNevin, D ;
Wong, CH ;
Menoud, P ;
Barford, JP ;
Mitchell, CA .
WATER SCIENCE AND TECHNOLOGY, 2000, 41 (01) :123-126
[7]   ENHANCED BIODEGRADATION OF AROMATIC POLLUTANTS IN COCULTURES OF ANAEROBIC AND AEROBIC BACTERIAL CONSORTIA [J].
FIELD, JA ;
STAMS, AJM ;
KATO, M ;
SCHRAA, G .
ANTONIE VAN LEEUWENHOEK INTERNATIONAL JOURNAL OF GENERAL AND MOLECULAR MICROBIOLOGY, 1995, 67 (01) :47-77
[8]   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
[9]   FATE OF AZO DYES IN SLUDGES [J].
GANESH, R ;
BOARDMAN, GD ;
MICHELSEN, D .
WATER RESEARCH, 1994, 28 (06) :1367-1376
[10]  
Goncalves I.M., 1996, TECNOLOGIAS AMBIENTE, V11, P35