Synthesis and characterization of Fe2O3/SiO2 nanocomposites.

Fe2O3/SiO2 nanocomposites based on fumed silica A-300 (S(BET)=337 m2/g) with iron oxide deposits at different content were synthesized using Fe(III) acetylacetonate (Fe(acac)3) dissolved in isopropyl alcohol or carbon tetrachloride for impregnation of the nanosilica powder at different amounts of Fe(acac)3 then oxidized in air at 400-900 degrees C. Samples with Fe(acac)3 adsorbed onto nanosilica and samples with Fe2O3/SiO2 including 6-17 wt% of Fe2O3 were investigated using XRD, XPS, TG/DTA, TPD MS, FTIR, AFM, nitrogen adsorption, Mössbauer spectroscopy, and quantum chemistry methods. The structural characteristics and phase composition of Fe2O3 deposits depend on reaction conditions, solvent type, content of grafted iron oxide, and post-reaction treatments. The iron oxide deposits on A-300 (impregnated by the Fe(acac)3 solution in isopropanol) treated at 500-600 degrees C include several phases characterized by different nanoparticle size distributions; however, in the case of impregnation of A-300 by the Fe(acac)3 solution in carbon tetrachloride only alpha-Fe2O3 phase is formed in addition to amorphous Fe2O3. The Fe2O3/SiO2 materials remain loose (similar to the A-300 matrix) at the bulk density of 0.12-0.15 g/cm3 and S(BET)=265-310 m2/g.

Carbon-mineral adsorbents from waste materials: case study.

Waste bleaching earth from the food industry obtained in the process of fruit juice purification was utilized for preparation of carbon-mineral adsorbents. The waste material, containing 25.8 wt% C, was subjected to three kinds of treatment: (1) direct pyrolysis at 400 degrees C with a suitable temperature program; (2) preliminary hydrothermal modification (200 degrees C, 8 h, 15.3 atm) and then pyrolysis as in method 1; (3) preliminary thermal treatment (400 degrees C) and then chemical treatment (boiling in 3% solution Na(2)CO(3)), followed by heating at 400 degrees C (10 min). Moreover, the materials obtained by these methods were subjected to additional thermal treatment at 700 degrees C with a suitable temperature program. Both the morphology and the topography of carbon deposits and, in consequence, the porous structure of the obtained adsorbents depend on the method of their preparation. The additional thermal treatment of these samples at 700 degrees C makes it possible to obtain adsorbents of more thermally stable carbon deposits possessing better parameters of the porous structure. Carbon-mineral adsorbents of different specific surface areas (S(BET) from 17.6 to 153 m(2)/g) and pore volumes (from 0.035 to 0.093 cm(3)/g) were prepared. The mechanism of phenol and p-nitrophenol adsorption on the obtained adsorbents was discussed and their properties were compared with the suitable literature data.