Biosorption of Sirius Blue azo-dye by Agaricus campestris biomass: Batch and continuous column studies

Author(s):  
Aslı Göçenoğlu Sarıkaya ◽  
Emre Erden Kopar
2012 ◽  
Vol 129 (1) ◽  
pp. 15-27 ◽  
Author(s):  
Aparna Roy ◽  
Sumit Chakraborty ◽  
Sarada Prasad Kundu ◽  
Basudam Adhikari ◽  
Subhasish Basu Majumder

2012 ◽  
Vol 2 (7) ◽  
pp. 424-426
Author(s):  
Suchita Dahiwade ◽  
◽  
Dr. A. O. Ingle Dr. A. O. Ingle ◽  
Dr. S. R. Wate Dr. S. R. Wate

2014 ◽  
Vol 0 (3(79)) ◽  
pp. 34-37
Author(s):  
A. S. Materiienko ◽  
V. O. Grudko ◽  
V. A. Khanin ◽  
V. A. Georgiyants

2000 ◽  
Vol 42 (5-6) ◽  
pp. 329-336 ◽  
Author(s):  
M. Quezada ◽  
I. Linares ◽  
G. Buitrón

The degradation of azo dyes in an aerobic biofilter operated in an SBR system was studied. The azo dyes studied were Acid Red 151 and a textile effluent containing basic dyes (Basic Blue 41, Basic Red 46 and 16 and Basic Yellow 28 and 19). In the case of Acid Red 151 a maximal substrate degradation rate of 288 mg AR 151/lliquid·d was obtained and degradation efficiencies were between 60 and 99%. Mineralization studies showed that 73% (as carbon) of the initial azo dye was transformed to CO2 by the consortia. The textile effluent was efficiently biodegraded by the reactor. A maximal removal rate of 2.3 kg COD/lliquid·d was obtained with removal efficiencies (as COD) varying from 76 to 97%. In all the cycles the system presented 80% of colour removal.


2015 ◽  
Vol 15 (8) ◽  
pp. 829-840 ◽  
Author(s):  
Marie Stiborova ◽  
Heinz Schmeiser ◽  
Eva Frei ◽  
Petr Hodek ◽  
Vaclav Martinek
Keyword(s):  
Azo Dye ◽  

2014 ◽  
Vol 3 (1) ◽  
pp. 115-122
Author(s):  
Abuzar Khan ◽  
Niyaz Mir ◽  
Mohammad Muneera ◽  
Zaki Seddigi

1990 ◽  
Vol 55 (6) ◽  
pp. 1508-1517 ◽  
Author(s):  
Jiří Barek ◽  
Dagmar Civišová ◽  
Ashutosh Ghosh ◽  
Jiří Zima

The polarographic reduction of the title azo dye was studied and optimal conditions were found for its analytical utilization in the concentration range 1 . 10-6 - 1 . 10-7 mol l-1 using differential pulse polarography and 1 . 10-6 - 1 . 10-8 mol l-1 using fast scan differential pulse voltammetry or linear scan voltammetry at a hanging mercury drop electrode. When the latter technique is combined with adsorptive accumulation of the studied substance on the surface of the hanging mercury drop, the determination limit can be further decreased to 3 . 10-9 mol l-1.


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