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2014
DOI: 10.1080/19443994.2014.980325
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Two-regime kinetic study and parameter optimization of degradation of 3,4-dichloroaniline using TI–N/S catalyst under visible light

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Cited by 1 publication
(3 citation statements)
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“…The kinetic plot suggested bi-phasic kinetics, with a sharp increase in rate after 45 minutes; further bench scale reactor experiments showed 85% degradation in 106 minutes [11] and Figure 2 shows the intermediate species formed. confirmed by HPLC and GC-MS analysis [11] Biphasic kinetics were also observed in the photocatalytic degradation of 3,4-DCA using Ti-N and Ti-S catalysts; [28] the former showing a higher surface area, and lower particle size and band-gap energy. Higher specific surface area increases the degree of contact of the pollutant with the catalyst surface, while smaller particle size means a reduced degradation time, due to shorter distances between the charge carrier and the surface, where the reaction occurs.…”
Section: Chlorination Ozonisation Chemical Precipitation and Fe 0 /mentioning
confidence: 82%
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“…The kinetic plot suggested bi-phasic kinetics, with a sharp increase in rate after 45 minutes; further bench scale reactor experiments showed 85% degradation in 106 minutes [11] and Figure 2 shows the intermediate species formed. confirmed by HPLC and GC-MS analysis [11] Biphasic kinetics were also observed in the photocatalytic degradation of 3,4-DCA using Ti-N and Ti-S catalysts; [28] the former showing a higher surface area, and lower particle size and band-gap energy. Higher specific surface area increases the degree of contact of the pollutant with the catalyst surface, while smaller particle size means a reduced degradation time, due to shorter distances between the charge carrier and the surface, where the reaction occurs.…”
Section: Chlorination Ozonisation Chemical Precipitation and Fe 0 /mentioning
confidence: 82%
“…[5] Although there is no exposure risk for vulnerable groups from direct use of 3,4-DCA, indirect contact is expected via food, primarily fruit and vegetables, [5] as a result of the hydrolysis and biological degradation of phenylurea, phenylcarbamates and acylchloroanilide pesticides present in soils, [19][20][21][22][23][24][25][26][27] by field waters and plant enzymes. [28] Furthermore, industrial wastewater [11] may contain 3,4-DCA, mainly from microbial conversion of 3,4-dichloro-1-nitrobenzol within water treatment plants. [5,28] In this manuscript, we summarize the current knowledge concerning the introduction, movement, and fate of 3,4-DCA in the environment.…”
Section: Introductionmentioning
confidence: 99%
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