Ozonation of 3,3′-dichlorobenzidine in aqueous solution: degradation efficiency and kinetics
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Yu, Li
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Shandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R ChinaShandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R China
Yu, Li
[1
]
Hou, Jiacai
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Shandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R ChinaShandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R China
Hou, Jiacai
[1
]
Ge, Yanan
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Shandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R ChinaShandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R China
Ge, Yanan
[1
]
Zhang, Peilong
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Shandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R ChinaShandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R China
Zhang, Peilong
[1
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Jia, Shouhua
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Shandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R ChinaShandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R China
Jia, Shouhua
[1
]
机构:
[1] Shandong Agr Univ, Coll Chem & Mat Sci, Tai An 271018, Shandong, Peoples R China
The degradation efficiency and kinetics of 3,3 '-dichlorobenzidine (DCB) in aqueous solution by ozonation was investigated in this study. In laboratory-scale experiments, the primary factors affecting the degradation of DCB were investigated. The results showed that pH strongly influenced the degradation process, with a maximum apparent rate of 0.235 min(-1) obtained at pH 4. The reactivity of DCB decreased in the order (C12H10Cl2N2)(2 )> (C12H10Cl2N2)(2)center dot HCl > (C12H10Cl2N2)(2)center dot 2HCl. The degradation rate of DCB increased with increasing ozone dosage and reaction temperature but decreased with increasing initial DCB concentration. We derived a reaction kinetics model of DCB degradation by ozonation in aqueous solution by interpreting the experimental data, and this model showed good stability. The efficiency of DCB degradation by ozonation was also evaluated. DCB could be removed efficiently by ozonation, with greater than 85% removal after 50 min at pH 4 and 16-30 degrees C with a DCB concentration of 1.2-6.5 mg/L and an ozone dosage of 3.7-5.1 mg/min. Most of the intermediate products could not be mineralised by direct oxidation by ozone. The addition of tert-butyl alcohol or Cl- had little effect on the degradation rate of DCB, which indicated that degradation of DCB occurred via direct oxidation by ozone.