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These analyses showed that the genes related to phenol degradation have been well sampled in the phenol degrading sludge, revealing that the phenol enrichment was successful.
Higher oxone concentration in solution enhanced phenol degradation efficiency and reaction temperature also promoted phenol degradation.
Szokol, J. et al. Induction and carbon catabolite repression of phenol degradation genes in Rhodococcus erythropolis and Rhodococcus jostii.
The mechanism of phenol degradation was also discussed.
The results were promising and shown enhanced photocatalytic activity than pure BiPO4 for phenol degradation.
PBD determined the following three factors as significant for phenol degradation viz.
Statistical optimization designs were used to optimize the phenol degradation using Chlorella pyrenoidosa.
The outcomes indicated a slow phenol degradation rate, i.e. 0.02 mg l−1 d−1.
The empirical model and optimum conditions for the phenol degradation were obtained.
The initiate phenol degradation rate on the TiO2 nanocatalyst was ca. 6 times higher than that in the phenol degradation only derived by H2O2.
The main intermediate products of phenol degradation included benzoquinone and organic acids.
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