Modification of commercial acetate membranes with titanium dioxide to apply in dinking water treatment F. Silva1, R. Bergamasco1, M.T. Pessoa de Amorim2, C. Tavares3 1 Department of Chemical Engineering, University of Maringá, Av. Colombo, 5790 Maringá Brazil 2 Department of Textile Engineering, University of Minho, Campus de Azúrem, 4800058 Guimarães, Portugal 3 Department of Physics, University of Minho, Campus de Azúrem, 4800-058 Guimarães, Portugal (E-mail : mtamorim@det.uminho.pt) Abstract The modification of organic membranes with titanium dioxide has been applied to avoid the membrane fouling. In this paper is studied the immobilization of titanium dioxide onto commercial acetate membranes of different porosity is done by deposition of titanium dioxide films at room temperature by pulsed-frequency reactive magnetron sputtering from a high purity Ti target in Ar/O 2/N2 atmosphere. The characterization of the modified membranes is done by SEM, FTIR and the contact angle. All these membranes will be applied in drinking water treatment. Keywords. Titanium dioxide - immobilization – membranes - characterization. INTRODUCTION Fouling is a major constraint during separations using membranes. Its occurrence leads to a decline in the membrane permeability and can occur either by the deposition of a new layer onto the membrane surface (cake filtration) or by intermediate, total or internal porous blocking (Hermia, 1982), besides mechanisms as spacer clogging and adsorptive fouling. These several modes of porous blocking are due to the size and shape of the solid/solute in relation to the distribution of the membrane pore sizes. Fouling is a complex phenomena depending on specific interactions of that particular membrane solution and also on a number of parameters. Previously, attempts have been made to relate fouling to flux decline resulting from an increase in flow resistances (Jiraratananon and Chanachai, 1996). Chemical modification of membrane surface using the deposition of titanium dioxide technique on its surface is of special interest. It aims to reduce the hydrophobic interactions between membrane surface and water solutes, the main cause of fouling (Morão et al., 2005). This technique improves the membrane performance in terms of fouling reduction and permeates flux (Luo, 2005; Bae and Tak, 2005). Besides this, it is possible to use the photocatalytic properties of titanium dioxide, largely applied in degradation of pathogenic contaminants (Kim et al., 2003). The application of the modified membranes in a laboratorial pilot has been tried with success. (Silva F et al, 2010) METHODS Cellulose acetate microfiltration membrane of pore diameter 0.45, 0.8 and 3 µm was purchased from Advantec. The immobilization of titanium dioxide onto membranes has been made by deposition of titanium dioxide films at room temperature by pulsed-frequency d.c reactive magnetron sputtering from a high purity Ti target in Ar/O2/N2 atmosphere with cathode current of 0.3 A and a deposition time of 5 hours. The conditions of titanium dioxide deposition can be obtained in C. J. Tavares et al. Ft-IR spectra were obtained using a Nicolet Avatar 360 spectrophotometer using an ATR. The resolution of each spectrum was 8cm -1 and the number of co added scans was 30. Contac angle measurements were carried out in OCA 20, Data physics Instruments GmbH, Filderstadt apparatus using distilled water. SEM study was carried using Nano SEM, model FEI Nova 200, FEG/SEM. RESULTS The Ft-IR spectra of the unmodified and modified membranes with titanium dioxide are shown in figure 1. All the modified membranes show a most intense band of the characteristic peaks of the C=O at 1740 cm-1 a Figure 1. (a)FT-IR spectrum of the unmodified membrane and (b) FT-IR spectrum of the modified membrane The contact angle of the modified membranes is always larger than its of the unmodified membranes. The TiO2 particles were revealed by SEM (figure not show) at the surface of the membranes and also inside of the pores. CONCLUSION The modification of the commercial acetate cellulose membranes with TiO 2 immobilization films at room temperature by pulse- frequency dc reactive magnetron sputtering allows an increase of the hydrophilitcity of the membrane as the measurements of the contact angle and the Ft-IR spectrum indicates. The experiments of the hydraulic permeability, fouling, and life time of these membranes will be presented in another paper. REFERENCES Jiraratananon, R., Chanachai, A.. (1996) A study of fouling in the ultrafiltration of passion fruit juice. Journal of Membrane Science 111, 39-48. Kim, S.H., Kwak, S.Y., Sohn, B.H., Park, T.H. (2003) Design of TiO 2 nanoparticle self-assembled aromatic polyamide thin-film-composite (TFC) membrane as an approach to solve biofouling problem. Journal of Membrane Science 211, 157–165 Luo, M.-L., Zhao, J.-Q., Tang, W., Pu, C.-S., (2005) Hydrophilic modification of poly(ether sulfone) ultrafiltration membrane surface by self-assembly of TiO2 nanoparticles. Applied Surface Science 249, 76– 84. Morão, A., Escobar, I.C., Pessoa De Amorim, M.T., Lopes, A., Gonçalves, I.C. (2005) Postsynthesis modification of a cellulose acetate ultrafiltration membrane for applications in water and wastewater treatment. Environmental Progress 24(4), 367-382. Silva, F. V., Pessoa de Amorim, M.T., Bergamasco, R.,Tavares, C.R. G., Yamaguchi, N. U.., Silva Jr, A. T., Tavares C.J. (2010) Study of membranes modification with titanium dioxide to apply in drinking water treatment Sumeted at Water Research Tavares C.J., Marques S.M., Lanceros-Méndez S., Rebouta L, Alves E,.Barradas N.P., Munnik F.,Girardeau T. and. Rivière J.-P (2010) Journal of Nanoscience and Nanotechnology 10 1072-1077.