Oxidation kinetics and effect of pH on the degradation of MTBE with Fenton reagent

Burbano, Arturo A.; Dionysiou, Dionysios D.; Suidan, Makram T.; Richardson, Teri L.

doi:10.1016/j.watres.2004.09.008

Cited by 284 publications

(106 citation statements)

References 25 publications

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“…Many studies have revealed that the solution pH can dramatically influence the Fenton degradation of organic compounds and at higher rates in the region 2.5-4, with an optimum at pH 3 [39]. At too high pH, the decomposition rate decreases because of the decrease of the free iron species in the solution, due to the formation of Fe(II) complexes and the precipitation of ferric oxyhydroxides [40].…”

Section: Effect Of Initial Phmentioning

confidence: 99%

Mineralization of an azo dye Acid Red 14 by photoelectro-Fenton process using an activated carbon fiber cathode

Wang

Liu

et al. 2008

Applied Catalysis B: Environmental

165

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Section: Effect Of Initial Phmentioning

confidence: 99%

Mineralization of an azo dye Acid Red 14 by photoelectro-Fenton process using an activated carbon fiber cathode

Wang

Liu

et al. 2008

Applied Catalysis B: Environmental

165

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“…Due to its high solubility in water and low Henry's law constant, MTBE is not easily removed by conventional techniques in water treatment processes. Air stripping [9], adsorption processes on activated carbon [10], synthetic resins [11,12] and zeolites [13,14], as well as advanced oxidation processes such as the Fenton process [15,16] have been used for the removal of MTBE from water.…”

Section: Introductionmentioning

confidence: 99%

Adsorption of Methyl tert‐butyl Ether on Perfluorooctyl Alumina Adsorbents – High Concentration Range

2007

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The performance of two types of perfluorooctyl alumina (PFOAL) adsorbents prepared using c-alumina (PFOAL A ) and alumina-active-basic® (PFOAL B ) is reported. The equilibrium adsorption behavior of the adsorbents was studied for adsorption of methyl tert-butyl ether (MTBE) in a wide range (5-1000 mg/L) of aqueous phase MTBE concentrations. The monolayer adsorption capacities were 3.3 and 3.5 mg MTBE/g adsorbent, and the maximum adsorption capacities were 7.1 and 6.3 mg MTBE/g adsorbent for PFOAL A and PFOAL B, respectively. The application of Freundlich, Langmuir, BET and BDDT (the general form of BET) isotherms were compared for the modeling of aqueous adsorption of MTBE on the surface of PFOAL adsorbents. It was shown that adsorption of MTBE on the surface of PFOAL is a type IV van der Waals adsorption, which is best modeled by the general form of the BET (BDDT) multilayer adsorption isotherm.

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“…Burbano et al [30] reported that MTBE (methyl tertiary butyl ether) could be significantly degraded (90 -99%) by using Fenton's reagent.…”

Section: Introductionmentioning

confidence: 99%

Reaction kinetics for the degradation of phenol and chlorinated phenols using Fenton's reagent

Dutta

Bhattacharjee

2005

Environ. Prog.

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Oxidation kinetics and effect of pH on the degradation of MTBE with Fenton reagent

Cited by 284 publications

References 25 publications

Mineralization of an azo dye Acid Red 14 by photoelectro-Fenton process using an activated carbon fiber cathode

Mineralization of an azo dye Acid Red 14 by photoelectro-Fenton process using an activated carbon fiber cathode

Adsorption of Methyl tert‐butyl Ether on Perfluorooctyl Alumina Adsorbents – High Concentration Range

Reaction kinetics for the degradation of phenol and chlorinated phenols using Fenton's reagent

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