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Maximum decolorization efficiency was predicted and experimentally validated.
Furthermore, the series of enzymatic dye decolorization experiments were performed to obtain optimum process parameters for maximum decolorization efficiency.
The maximum decolorization efficiency was predicted to be 87.19% at an AO7 concentration of 49 mg/L, adsorbent dosage of 0.8 g/L, reaction time of 27 min and initial pH of 6.
Optimization results showed that maximum decolorization efficiency was achieved at the optimum conditions: initial dye concentration 10 mg/L, UV light intensity 47.2 W/m2, flow rate 100 mL/min and reaction time 120 min.
The results of optimization predicted by the model showed that maximum decolorization efficiency was achieved at the optimum condition of the initial pH 8, initial dye concentration 10 mg/l, algae amount 4 g and reaction time 75 min.
In the Photo-Fenton process application, maximum decolorization efficiency (96.4%) was obtained at the optimum reaction conditions that were 100 mM H2O2 and 1 mM Fe(II) doses at pH 3, and 10 min of irradiation time.
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Under these conditions, the maximum ACB decolorization efficiency and TOC removal were 99.3% and 73.9%, respectively.
Optimization of the process via response surface methodology (RS M based on central composite design (CCD) showed the maximum sonocatalytic decolorization efficiency of 89.92% in which the initial dye concentration, the ZnO/bentonite ratio, the sonocatalyst dosage, and the initial pH were 6 mg/L, 0.3, 2.5 g/L and 9, respectively.
Bacteria showing maximum MB decolorization efficiency (53%) was selected and identified as Stenotrophomonas maltophilia.
Different physical and nutritional factors including pH, temperature and fungal inoculum density were statistically optimized through Completely Randomized Design (CRD), to enhance the efficiency of S. commune IBL-06 for maximum decolorization of Solar brilliant red 80 dye.
It has been observed that for RO4, the decolorization efficiency increases with increase in pH exhibiting maximum rate of degradation at pH 11.
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