Alumina Supported Fenton-Like Systems for the Catalytic Wet Peroxide Oxidation of Phenol Solutions Carla di Luca, Fernando Ivorra, Paola Massa,* and Rosa Fenoglio INTEMA/Fac. de Ingeniería-Universidad Nac. de Mar del Plata, Juan B. Justo 4302, 7600, Argentina ABSTRACT: Fe 2 O 3 /Al 2 O 3 catalysts (2% Fe) were prepared and characterized by XRD, BET, Raman, and SEM-EDAX. The systems were tested for the catalytic oxidation of phenol solutions (5000 ppm) with H 2 O 2 . The eects of reaction temperature, catalyst loading, phenol initial concentration, and H 2 O 2 :phenol molar ratio were evaluated. The relatively low oxidant consumption rates favored increased mineralization levels at substoichiometric H 2 O 2 initial concentrations. The stability of the catalytic system was improved by means of a thermal treatment at 900 °C, which did not seriously aect the overall reaction performance. INTRODUCTION Hydroxyl radicals have been eectively applied in the eld of environmental remediation. Because of their strong oxidizing potential, these species are capable of degrading a wide range of pollutants. Dierent Advanced Oxidation Processes (AOPs) have been used to generate the OH radicals. 1-5 Among them, the classic Fenton and Fenton-like reagents (Fe II or Fe III / H 2 O 2 ) remain attractive alternatives for the treatment of nonbiodegradable contaminants, such as phenol. 3,6-8 However, these systems are seriously aected by the typical problems of homogeneous catalysis (separation, regeneration) and also by ineective consumption of H 2 O 2 and acid-range pH adjustment requirements. 5,8 Thus, dierent Fenton-like heterogeneous catalysts have been developed by immobilizing transition cations on adequate supports, such as zeolites, pillared clays, silica, activated carbon, or CeO 2 . 8-10 So far, only a few Catalytic Wet Peroxide Oxidation (CWPO) studies have been reported using iron catalysts supported on alumina. 11-18 Al-Hayek and co-workers 15,16 studied the oxidation of phenol solutions over Fe 2 O 3 /Al 2 O 3 powdered catalysts with an iron content of 7.7%. The catalysts were oxidized at 450 °C. The authors used a batch system at room temperature with 100 ppm of phenol as the initial concentration and a molar H 2 O 2 :phenol ratio that was nearly stoichiometric. At these reaction conditions, they observed complete phenol conversion and 60% of mineralization (after 120 min of reaction); leaching levels were moderate, on the order of 10%. More recently, Bautista et al. 18 studied the behavior of a Fe 2 O 3 /Al 2 O 3 powdered catalyst (4% Fe) in the CWPO of aqueous phenol. The catalyst was prepared with a 4% iron content, calcined at 300 °C, and tested in a batch reactor at atmospheric pressure, mild temperatures (25-80 °C), and an initial pH 3. These authors worked at a stoichiometric H 2 O 2 :phenol molar ratio of 14, using dierent initial concentrations of phenol (100-1500 ppm). For a typical experiment at 50 °C using 100 ppm of phenol as the initial concentration, the phenol conversion was complete, and the mineralization was partial: 27% after 2 h and 60% after 8 h. The levels of leached active phase were low (<2%). By increasing the initial phenol concentration (up to 1500 ppm), they observed a decrease in mineralization levels (42%) and an increased leaching of the iron species (10%). On the basis of these previous reports, we intended to study the performance of alumina-supported catalysts under more demanding reaction conditions, such as more concentrated phenol solutions (5000 ppm). We evaluated the eect of major CWPO variables: reaction temperature, hydrogen peroxide and phenol concentrations, and catalyst mass. The catalysts were prepared in the form of small pellets of Fe 2 O 3 /Al 2 O 3 with low iron content (2% w). We also investigated the impact of using a high calcination temperature (900 °C) in terms of catalyst stability enhancement (for previous reports, calcination temperatures did not exceed 500 °C). EXPERIMENTAL SECTION Catalyst Preparation and Characterization. The Fe 2 O 3 / γ-Al 2 O 3 catalysts were prepared by incipient wetness impregnation of commercial γ-Al 2 O 3 (ALFA AESAR, spherical pellets of 1-1.2 mm) using an aqueous solution of iron citrate (Cicarelli, p.a.) as precursor. After impregnation, the sample was left for 12 h at room temperature and calcined at two dierent temperatures, 400 and 900 °C, under air current (10 L/min) for 4 h. The catalysts were designed as 2Fe400 and 2Fe900, respectively. The support and the catalysts were characterized using the following techniques: - Surface areas (BET method). Surface areas were calculated from nitrogen adsorption at -196 °C by using a Micromeritics FlowSorb II 2300. - X-ray diraction (XRD). Powder X-ray diraction patterns of the catalysts were obtained with a PANalytical XPert Pro diractometer by using nickel-ltered Cu Kα radiation. The patterns were recorder over 10° <2θ < 70° range and compared to the JCPDS les to conrm phase identities. The main peaks corresponding to the Received: February 15, 2012 Revised: June 5, 2012 Accepted: June 11, 2012 Published: June 11, 2012 Article pubs.acs.org/IECR © 2012 American Chemical Society 8979 dx.doi.org/10.1021/ie300416n | Ind. Eng. Chem. Res. 2012, 51, 8979-8984