IJUP08 - Universidade do Porto
IJUP08 - Universidade do Porto
IJUP08 - Universidade do Porto
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Azo-dye Orange II degradation by Fenton-like reaction using as<br />
catalysts transition metals in carbon supports<br />
Filipa Duarte a , F.J. Mal<strong>do</strong>na<strong>do</strong>-Hódar b , Luis M. Madeira a<br />
a LEPAE, Departamento de Engenharia Química, Faculdade de Engenharia da <strong>Universidade</strong> <strong>do</strong><br />
<strong>Porto</strong>, Rua Dr. Roberto Frias, 4200-465 <strong>Porto</strong>, Portugal<br />
b Departamento de Química Inorgánica, Facultad de Ciencias, Universidad de Granada, 18071<br />
Granada, Spain<br />
Pollution of water caused by industries is a serious problem in the developed countries and<br />
its elimination is a great challenge. For instance, to destroy synthetic dyes is very hard<br />
because they are usually stable compounds and often non-biodegradable, formed by long<br />
organic molecules. Advanced chemical oxidation methods can be effective for their<br />
degradation as they can result in almost complete mineralization in a cheap and easy way.<br />
One of the most well-known methods is the oxidation with Fenton’s reagent, where<br />
hydrogen peroxide reacts with iron (or with another transition metal catalyst) in acidic<br />
medium, leading to the production of powerful radicals (HO • ), which are able to attack the<br />
organic compounds.<br />
This reaction can be carried on in a homogeneous or heterogeneous system. The first<br />
process is not adequate because it leads to a very high metal concentration in solution, ca.<br />
50-80 ppm, while European directives <strong>do</strong>n’t allow more than 2 ppm of Fe, for instance, in<br />
discharged water [1]. Thus, heterogeneous reaction has been carried out using transition<br />
metals (Fe, Co, Ni, Cu, Mn, W) as active phase deposited on carbon aerogels. Two<br />
approaches were used to prepared the catalysts: in the first case, the metal precursors were<br />
introduced in the starting solution of the polymer precursors, resulting in metal-<strong>do</strong>ped<br />
carbon aerogels; in the second case, metals were added by impregnation on two carbon<br />
aerogels previously prepared, one mesoporous (support M) and another microporous<br />
(support AS-3). The porosity and dispersion of the catalysts was evaluated by different<br />
techniques: N2 adsorption, mercury porosimetry, TG, XRD, HRTEM and SEM. The dye<br />
degradation experiments were performed in a slurry batch reactor, using a 0.1 mM orange<br />
II (model compound) solution, as well as 6 mM of hydrogen peroxide, at 30 ºC and pH =<br />
3. The absorbance was continuously read by a spectrophotometer and the metal leaching<br />
quantified by atomic absorption.<br />
The best performance was obtained with the Fe, Co and Ni catalysts, although the latter<br />
was not so active and the second provided high leaching values. It is noteworthy that the<br />
Fe-<strong>do</strong>ped catalyst showed the lowest leaching. When employing impregnated catalysts, the<br />
use of mesoporous supports leads to more active catalysts. The AS-3 support has a very<br />
high adsorption capacity, not being relevant for catalytic purposes. Comparing <strong>do</strong>ping and<br />
impregnation techniques, it is observed that impregnation is more efficient probably<br />
because metals (Fe or Co) are more accessible to the dye molecules, in spite the high<br />
porosity of metal-<strong>do</strong>ped carbon aerogels. The combination of the mesoporous support M<br />
with a highly active metal as Fe provided an efficient and promising catalyst for practical<br />
applications, with complete decolourisation of the solution in 2-3h employing soft<br />
oxidation conditions, with leaching values below 2.5%.<br />
References:<br />
[1] Sabhi, S. and Kiwi, J. (2001), Degradation of 2,4-dichlorophenol by immobilized iron catalysts,<br />
Water Research, 35 (8), 1994-2002.<br />
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