UDK 66 ISSN 1580-2949 Original scientific article/Izvirni znanstveni članek MTAEC9, 46(1)19(2012) STABILIZATION OF RUTILE TiO2 NANOPARTICLES WITH GLYMO IN POLYACRYLIC CLEAR COATING STABILIZACIJA RUTIL TiO2 NANODELCEV Z GLYMO V POLIAKRILNEM TRANSPARENTNEM PREMAZU Jerneja Godnjavec1, Bogdan Znoj1,2, Jelica Vince2, Miha Steinbucher2, Andrej @nidar{i~3, Peter Venturini1,2 1Center of Excellence for Polymer Materials and Technologies, Tehnološki park 24, 1000 Ljubljana, Slovenia 2Helios Group, Količevo 2, 1230 Domžale, Slovenia 3Kolektor Nanotesla Institut Ljubljana, Stegne 29, 1521 Ljubljana, Slovenia jerneja.godnjavec@polimat.si Prejem rokopisa - received: 2011-02-15; sprejem za objavo - accepted for publication: 2011-07-06 Titanium dioxide (TiO2), in the crystal form of rutile with high refractive index, 2.7, is one of the most important inorganic pigments. In the recent years nano TiO2 has attracted interest as an inorganic material for nanocomposites. It is used for the development of photocatalysts12, semiconductors in solar cells34 and for the protection of materials from UV damage5-8. To achieve high UV absorbing efficiency of TiO2 nanoparticles into polymer matrix and to yield a better compatibility with polymeric materials surface treatment of TiO2 nanoparticles with 3-glycidyloxypropyltrimethoxysilane (GLYMO) in a polyacrylic clear coating was investigated. The grafting of GLYMO on the TiO2 nanoparticles surface was characterized with TGA and FTIR techniques. The stability of TiO2 nanoparticles in a acrylic clear coating was evaluated by zeta potential measurement. Microstructural analysis of nanoparticles was done by SEM and the influence of surface treatment on stability of nanoparticles in dispersion and acrylic coating was analysed. Finally the UV absorption effectivness of acrylic clear coating with treated nanoparticles of rutile TiO2 was measured to determine the effect of improved dispersion. The performance of nanocomposite coatings was demonstrated trough accelerated weathering by gloss measurement. The results showed that surface treatment of TiO2 nanoparticles with GLYMO improves nanoparticles dispersion and preserves UV protection of the acrylic clear coating. Keywords: titanium dioxide, nanoparticles, polyacrylic clear coating, surface treatment, GLYMO, UV protection Titanov dioksid (TiO2), v rutilni kristalni obliki z visokim lomnim količnikom, 2.7, je eden najbolj pomembnih anorganskih pigmentov. V zadnjih letih je nano TiO2 pritegnil pozornost kot anorganski material za nanokompozite. Uporablja se za razvoj fotokatalizatorjev1,2, polprevodnikov in soalrnih celic34 in za UV zaščito materialov5-8. Da bi dosegli ustrezno dispergiranje TiO2 nanodelcev v polimerni matrici in boljšo kompatibilnost s polimernimi materiali smo preiskovali površinsko obdelavo TiO2 nanodelcev v poliakrilnem transparentnem premazu. Za optimizacijo dispergiranja je bila površina nanodelcev obdelana z 3-glicidiloksipropiltrimetoksisilanom (GLYMO). Pripenjanje GLYMO na površino TiO2 nanodelcev smo ovrednotili z termogravimetrično analizo (TGA) in s FTIR spektroskopsko analizo. Stabilnosti TiO2 nanodelcev v akrilnem transparentnem premazu smo analizirali z meritvijo zeta potenciala. Mikrostrukturno analizo nanodelcev izvedli s SEM. Na koncu smo analizirali učinkovitost UV absorpcije akrilnega transparentnega premaza z površinsko obdelanimi rutil TiO2 nanodelci, da bi določili efekt izboljšane disperzibilnosti. Z izpostavo pospešenega staranja smo določili funkcionalnost nanokompozitnih premazov na osnovi meritve sijaja. Rezultati so pokazali da povšinska obdelava TiO2 nanodelcev z GLYMO izboljša disperziblnost nanodelcev in ohrani UV zaščito akrilnega transparentnega premaza. Ključne besede: titanov dioksid, nanodelci, poliakrilni transparentni premaz, površinska obdelava, GLYMO, UV zaščita 1 INTRODUCTION Second, for producing suitable nanocomposites, it is necessary to disperse the nano-particles without agglo- Architectural coatings are usually used to enhance meration in organic binders11,12. Due to their extremly the durability of wood in exterior environment. Inorganic large surface-area/particle-size ratio, nano-particles have UV absorbers are often used in coatings formulations, high tendency of agglomeration13. Many efforts have since they increase polymer stability. TiO2 possesses a been taken in order to overcome the problem of agglo- lot of attracting advantages, like thermal stability and meration. Polymeric dispersants containing different long-term life time, compared to traditional organic UV functional groups are usuallly used in order to prevent absorbers9,10. the high tendency of nanoparticles to form aggregates in There are two limitations of using TiO2 as UV the wet state of coating and in the dry paint film. absorber. First, TiO2 particularly in anatase crystale form Polyacrylic acid, polyacrylamide and their copolymers and less in rutile form exhibits strong photocatalytic are widely used to disperse inorganic particles in behavior when absorbing UV-rays, which is harmful for aqueous film14. Recently, to suppress the photocatalytic the photostability of polymer materials5. As a result, property of TiO2, usually silica15-17 or silane18-20 were TiO2 nanoparticles as catalyst can create , which can coated onto TiO2 cores. Kang et al. suppressed the produce highly reactive free radicals and exert strong photocatalytic property of a TiO2 by coating them with oxidizing power. the SiO2 shell in chloroform17. Toni et. al. coated dense SiO2 shells onto TiOi particles by seeded sol-gel process of tetraethyl silicate (TEOS) in ethanol16. The use of different coupling agents such as trialkoxy silanes for surface modification of nanoparticles is recommended. For example, Ukaji et. al. coated thin aminoethylamino-propyltrimethoxysilane layers onto TiO2 particles in ethanol by adding silane during ball-milling dispersing procedure8. Shafi et. al. coated octadecyltrihydrosilane layers on TiO2 surfaces in heptane by ultrasonic irradi-ation21. M. Sabzi et. al. showed that surface treatment of TiO2 with aminopropyl trimethoxysilane improves nano-particles dispersion and UV protection of the urethane clear coating22. The purpose of this study was to investigate the influence of TiO2 nanoparticles surface modifiction by different wt. % of 3-glycidyloxypropyltrimethoxysilane on transparency and UV absorbing efficiency of poly-acrylic coating. 2 EXPERIMENTAL WORK Sample name GLYMO/TiO2 (/) A 0/1 B 0.1/1 C 1/1 D 2/1 TiO2 nanoparticles with rutile crystal structure were prepared by co-precipitation method which is described elsewhere23. Deagglomerated rutile nanoparticles were prepared as dispersion in water and propilenglycol in high-energy horizontal attrition mill. 2.2 Surface modification of TiO2 nanoparticles in dispersion with silane coupling agent As silane coupling agent we used 3-glycidyloxy-propyltrimethoxysilane (GLYMO) with chemical for- CH2-CH-CH20-(CH2)3Si(0CH3)3 which is a bifunctional organosilane, possessing reactive organic epoxide and hydrolyzable inorganic metoxysilyl groups. It bounds chemically to both inorganic material and organic polymers. According to the producer in the presence of water the methoxy groups hydrolyze to form reactive silanol groups which bound to inorganic substance24. We prepared dispersions of TiO2 nanoparticles grafted with GLYMO according to the following Table 1: Weight ratio of GLYMO and nano TiO2, dispersed in water Tabela 1: Utežno razmerje GLYMO in nano TiO2, dispergiranih v vodi Sample name A D GLYMO/TiO9 (/) 0/1 0 1/1 1/1 2/1 procedure. First, TiO2 nanopowder in dispersion with wetting and defoaming agent was milled for 1,5 hour at 25 °C with organic surface active agent with zirconia balls 1 mm diameter. Than silane coupling agent of different concentrations was added as shown in Table 1 and the dispersion was milled additionally for 1 hour at the same conditions. 2.3 Preparation of clearcoat with integrated rutile crystalline nanoparticles of TiO2 We prepared clearcoat in the laboratory as described elsewhere23. Water based dispersions of TiO 2 nanoparticles were than added to clearcoat of 0,6 wt. %, stirred at approximatly 1000 rpm for 20 minutes and prepared for the testing. 2.4 Characterization of the samples Surface morphology of coated sample was studied by scanning electron microscopy (SEM, ZEISS Gemini Supra 35 VP), with a maximum resolution up to 5 nm. Nanoparticles were dried on brass holders by adhesive carbon band with thin layer of gold. The samples were placed in the vacuum chamber of the instrument and then were examined at various magnifications. Grafting of GLYMO on TiO2 nanoparticles was analysed by FT-IR. The infrared spectra of original and modified TiO2 were conducted using a FT-IR spectrometer (PERKIN ELMER Spectrum 100) and thermogravimetrical analysis by TGA/DSC 1, METTLER TOLEDO. Zeta potential was obtained to investigate the surface character of original TiO2 and TiO2 modified with GLYMO. The electro-phoretic mobility data, measured also by Zetasizer Nano series HT by of the dispersions were transformed into ^-potential according to25 (eq. 1): " Arniu C = (1) where e is a dielectric constant of the dispersing medium and ^ the solvent viscosity. pH was measured by pH meter (Mettler Toledo). UV-VIS transmittance of modified samples was measured for estimating UV-shielding ability and transparency. 0.6 wt. % of surface treated TiO2 nanoparticles was integrated into acrylic clear coating and 200 ^m films were prepared. The different free film systems (coating-UV absorber) were analysed by UV-VIS spectrophotometer Varian Cary 100. The film transmittance was measured in the wavelength range 280 to 720 nm. At the end, wood blocks measuring 15x7 cm2 (longitudinal X tangential) x 0,5 cm width were cut from air dried boards from the specie pine. Two layers of clear coat of thickness of 200 pm were applied on pine blocks. Coated wood plates were used to assess weathering exposure degradation (QUV accelerated weathering tester, Q - PANEL LAB PRODUCTS). Simulation of exterior use was done by six weeks weathering by an r optimised cycle defined: 4h at (60 ± 3) °C and 4h water shower at (50 ± 3) °C. Only light of the solar type was activated on the QUV with sources type UVA-340 nm26. Gloss at 60° was measured by Micro-TRI-gloss (Byk Gardner). 3 RESULTS AND DISCUSSION 3.1 SEM characterization The size of the nanoparticles, grafted with GLYMO was analysed by scanning electron microsope (SEM). SEM images at two different magnifiations of sample C are shown on Figure 1. Agglomeration tendency of TiO2 nanoparticles in the dispersion cannot be determined because of the preparation of the sample, however we assume, that some agglomerates are probably present as seen on SEM image. Individual particles can be identified, which appears to be polydisperse in size but below 100 nm. 3.2 TGA analysis To estimate the amount of GLYMO grafted on nanoparticles, the various percentage of GLYMO -grafted nano-TiO2 particles were analyzed by TGA technique. Figure 2 shows the TGA curves of untreated TiO2 nanoparticle, GLYMO alone and treated TiO2 nanoparticles with different percentages of GLYMO. For untreated nanoparticles (sample A), the weight loss from 120 till 600 °C is almost negligible and is probably due to desorption of physisorbed water27. For GLYMO alone the weight loss begins at 120 °C and ends at 200 °C. As can be seen for sample B, C and D, the various weight percentages of GLYMO grafted nanoparticles show sharp weight loss, beginning near 220 °C, continues till 620 °C, which is a consequence of oxidative thermal decomposition of grafted GLYMO as quantitatively Figure 2: TGA curves of untreated TiO2 nano-particle (sample A) and treated TiO2 nano-particle (sample B-D). The composition of all samples is described in Table 1. Slika 2: TGA krivulje površinsko neobdelanih (vzorec A) ter površinsko obdealnih (vzorci B-D) nanodelcev TiO2. Sestava vseh vzorcev je podana v Tabeli 1. shown in Table 2. The largest amount of grafted GLYMO was in the case of sample C. Table 2: TGA-based weight losses caused by grafting of GLYMO and the amount grafted/added GLYMO of various GLYMO - grafted nanoparticles TiO2. The composition of all samples is described in Table 1. Tabela 2: Izguba mase vzorcev nanodelcev TiO2 ter razmerje vezan/dodan GLYMO površinsko obdelanih in neobdelanih z GLYMO glede na TGA analizo. Sestava vseh vzorcev je podana v Tabeli 1. Sample GLYMO:TiO2 (/) Weight loss caused by grafting of GLYMO The amount grafted/added GLYMO (%) A 0 / / B 0,1 1,00 67 C 1 11,40 76 D 2 20,20 67 GLYMO / / / Figure 1: SEM image of sample C with inserted image at higher magnification Slika 1: SEM posnetek vzorca C z vstavljenim posnetkom pri višji povečavi 3.3 FTIR spectroscopy The hydroxyl groups on the surface of the TiO2 nanoparticles (TiOH) are reactive sites for the reaction with alkoxy groups of silane compounds, however corresponding bands are not present in spectrum of unmodified TiO2, since it was dried at 130 °C for 24h. The efficiency of silane grafting on TiO2 nano-particles was determined by Fourier transform infrared spectro-scopy (FTIR). Figure 3 shows normalised FTIR spectra of unmodified TiO2 nanoparticles (sample A), grafted TiO2 nanoparticles with GLYMO (sample B-D), GLYMO alone and GLYMO with addition of water. In the spectra of all TiO2 nano-particles the broad band between 400 and 800 cm-1 correspond to Ti-O-Ti network. GLYMO posseses two functional groups: epoxi and metoxysilyl, which both hydrolize and condensate. Epoxy band in FTIR spectra is preserved, while the intensity of Si-O-Me band is decreased. Also two bands of hydroxyl groups appear at ~3300 and ~1640 cm-1 because of hydrolysis of Si-O-Me groups. In spectra of GLYMO with addition of water peak at 1050 cm1 appears, which we can assign to formation of Si-O-Si groups. Compared with the spectrum of non-modified TiOa, FTIR spectrum of GLYMO modified sample exhibits some new characteristic absorption peaks. Peak at ~1200 and 1093 cm-1 which belongs to Si-O-Me groups28 29, was observed in the spectra of samples C and D, however not in the spectruum of sample B, which indicates that only in the case of sample B complete hydrolysis and condensation of GLYMO takes place. In contrast to GLYMO spectruum, we cannot observe in GLYMO modified TiO2 spectra peak at 914 and 1254 cm-1 which corresponds to epoxi group30-34. We presume that the epoxi group opens and reacts with -OH groups which were formed by the hydrolysis of metoxysilyl groups. The broad bend at ~1050 cm-1 represent the Si-O-Si bond is observed which indicates the formation of Si-matrix35. The small peak in spectra of samples B -D at around 930 cm-1 reconfirms condensation reaction between methoxysilyl groups of GLYMO and the TiO2 surface hydroxyl groups36 8. To sum up, Si-O-Me groups of GLYMO have reacted completley only in the case of sample B, in samples C and D are still present. Epoxi groups of GLYMO have reacted completely in all GLYMO modified TiO2 nanoparticles samples. The results of FTIR analysis confirm that Si-O-Si network has been formed probably around the TiO2 nanoparticles and in small amount Si-atoms of GLYMO are bound to TiO2 surface. Similarly, F. Bauer and coauthors reported about a polymerization-active siloxane shell formed around the nanoparticles Al2O3, when surface treated by GLYMO37. The reaction of GLYMO with TiO2 nanoparticles leads to different kind of stabilization of nanoparticles in the Figure 3: FTIR spectra of untreated nano-TiO2 (sample A), grafted TiO2 nano-particles with GLYMO (sample B-D), pure GLYMO and GLYMO with addition of water. The composition of all samples is described in Table 1. Slika 3: FTIR spektri neobdelanega nano-TiO2 (vzorec A), površinsko obdelanih nanodelcev TiO2 z GLYMO (vzorec B-D), samo GLYMO, GLYMO z dodatkom vode. Sestava vseh vzorcev je podana v Tabeli 1. dispersion as suggested by the producers of GLYMO, since they claim that in the presence of water the methoxysilyl groups hydrolyze to form reactive silanol groups which bound to inorganic substance24. 3.4 pH and ^-potencial measurement pH and ^-potential measurement were used to quantify the conditions leading to the stability of TiO2 dispersions. Relevant values of the pH - measurements and ^-potential of unmodified and modified TiO2 with GLYMO are collected in Table 3 and in Figure 4. The pH variation from 4,6 to 5,9 upon adsorption of GLYMO was detected. An increase of the pH from 5,6 up to 5,94 when increasing GLYMO/TiO2 from 0 to 1 (sample A, B and C) was accompanied with an increase of ^-potential from ~-33 to around —39 mV, with subsequent increase in colloid stability. We assume that TiO2 surface is probably mostly covered with modifier in monolayer. As ratio GLYMO/TiO2 increases to 2, the pH decreases to 5,43, resulting in decrease in zeta potential to -35,5 mV. We predict that the reason for decrease in pH and ^-potential is the excess amount of GLYMO or formatation of multilayer on TiO2 surface as observed by E. Ukaji et. al.8. It is supposed that thicker layer could be formed due to subsequent growth of layer to dimers, oligomers, and polymers. Table 3: pH values for TiO2 dispersions, in the presence of different amounts of GLYMO (sample A-D). The composition of all samples is described in Table 1. Tabela 3: pH vrednosti disperzij TiO2 v prisotnosti različnih deležev GLYMO (vzorec A-D). Sestava vseh vzorcev je podana v Tabeli 1. Sample name pH A 5,60 B 5,78 C 5,94 D 5,43 3.5 Ageing behaviour Artificial weathering results in surface degradation of the coatings, which affect the appearance of the coating, GLYMOmOl {D Figure 4: Zeta potential measurement vs. ratio GLYMO/TiO2 Slika 4: Diagram meritev zeta potenciala v odvisnosti od razmerja GLYMO/TiO2 2 3 4 runa of exposum (number of weeitej Figure 5: Gloss measurement vs. irradiation time in a QUV apparatus for the exterior use clearcotings with different UV absorbers, samples A-D, with their composition described in Table 1 Slika 5: Meritve sijaja v odvisnosti od časa izpostave v UV komori za premaz za zunanjo uporabo z različnimi UV absorberji, vzorci A-D, njhova sestava je podana v Tabeli 1 is the information on photostabilisation performances of UV absorbers8,38,39. M. Beyer and C. Jobos investigated the use of nano-scale light absorbers in water based glaze for outdoor applications. They showed that TiO2 proved to be effective additives6 in concentration 0,25 - 4 wt. % TiO29. For outdoor weathering simulation of clearcoating gloss measurement during the exposure in QUV chambre for six weeks are displayed in Figure 5. Figure 5 shows gloss 60° vs. time of exposure in QUV chambre for clearcoating with modified TiO2 nanoparticles of different wt. ratios of GLYMO/TiO2. The results illustrated that addition of GLYMO decreases the gloss 60°. During accelerated weathering the gloss changes are strongly correlated with the degradation level of the surface coating. In some composite materials the polymer around the filler particles will degrade due to the particle catalytic effect40. The accelerated weathering with water spray induced the washing out of degradation products on the coatings surface and consequently a fresh surface was further exposed. During the accelerated weathering a pronounced loss of gloss was observed for coatings formulated with nanoparticle UV absorber41. We can conclude that the surface treatemtnof TiO2 nanoparticles with GLYMO reduces the gloss 60° of acrylic coating before exposure to accelerated weathering. The gloss change after six week exposure to accelerated weathering is the smalest in the case of sample C, which shows that the UV efficiency was improved the most, when ratio GLYMO/TiO2 was 1. 4 CONCLUSIONS Surface modification and characterization of TiO2 nano-particles with GLYMO at different wt. percentages as an additive in a polyacrylic clear coating were investigated. TGA and FTIR analysis show that grafting of GLYMO on the nano-particles has occurred successfully. According to C-potential measurements the most stable TiO2 nanoparticle dispersions are with ratio GLYMO:TiO2 0,1 and 1. At the end, artificial weathering results confirm that surface treatment of TiO2 nano-particles with GLYMO with ratio GLYMO:TiO2 = 1 improves nanoparticles dispersion and consequently its transparency the most and improves UV protection of acrylic clear coating. Acknowledgement The authors acknowledge the financial support from the Ministry of Higher Education, Science and Technology of the Republic of Slovenia through the contract No. 3211-10-000057 (Center of Excellence Polymer Materials and Technologies). 5 REFERENCES I A. L. Linsebigler, G. Lu, J. T. Yates, Photocatalysis on TiO2 surfaces: principles, mechanisms, and selected results, Chem. Rev. 95 (1995), 735-758 2H. Choi, Y.J. Kim, R.S. Varma, D.D. Dionysiou, Thermally stable nanocrystalline TiO2 photocatalysts synthesized via sol-gel methods modified with ionic liquid and surfactant molecules, Chem. Mater. 18 (2006), 5377-5384 3 U Bach, D. Lupo, P. Comte, J. E. Moser, F. Weissortel, J. Salbeck, H. Spreitzer, M. Gratzel, Solid-state dye-sensitized mesoporous TiOi solar cells with high photon-to-electron conversion efficiencies, Nature 395 (1998), 583-585 4M. Anpo, M. Takeuchi, The design and development of highly reactive titanium oxide photocatalysts operating under visible light irradiation, J. Catal. 216 (2003), 505-516 5 H. Y. Yang, S. K. Zhu, N. Pan, Studying the mechanisms of titanium dioxide as ultraviolet blocking additive for films and fabrics by an improved scheme, J. Appl. Polym. Sci. 92 (2004), 3201-3210 6F. Aloui, A. Ahajji, Y. Irmouli, B. George, B. Charrier, A. Merlin, Inorganic UV absorbers for the photostabilisation of wood-clear-coating systems: comparison with organic UV absorbers, Appl. Surf. Sci. 253 (2007), 3737-3745 7B. Mahltig, H. Bottcher, K. Rauch, U. Dieckmann, R. Nitsche, T. Fritz, Optimized UV protecting coatings by combination of organic and inorganic UV absorbers, Thin Solid Films 485 (2005), 108-114 8E. Ukaji, T. Furusawa, M. Sato, N. Suzuki, The effect of surface modification with silane coupling agent on suppressing the photo-catalytic activity of fine TiO2 particles as inorganic UV filter, Appl. Surf. Sci. 254 (2007), 563-569 9N. S. Allen, M. Edgea, A. Ortega, G. Sandovla, C. M. Liauwa, J. Verrana, Degradation and stabilisation of polymers and coatings: nano versus pigmentary titania particles, Polym. Degrad. Stab. 85 (2004), 927-946 10 M. Sangermano, E. Borlatto, F. D. D' Herin Bytner, A. Priola, G. Rizza, Photostabilization of cationic UV-cured coatings in the presence of nano TiOi, Prog. Org. Coat. 59 (2007), 122-125 II C. Lu, Z. Cui, J. Guan, B. Yang, J. Shen, Research on Preparation, Structure and Properties of TiO2/Polythiourethane Hybrid Optical Films with High Refractive Index Macromol. Mater. Eng. 288 (2003), 717-723 12 C. Lu, Z. Cui, B. Yang., J. Shen, High refractive index thin films of ZnS/polythiourethane nanocomposites, J. Mater. Chem. 13 (2003), 526-530 13 J. Jordan, K. I. Jacob, R. Tannenbaum, M.A. Sharaf, I. Jasiuk, Experimental trends in polymer nanocomposites—a review, Mater. Sci. Eng. A 393 (1e2) (2005), 1 14 S. Farrokhpay, A review of polymeric dispersant stabilisation of titania pigment, Advances in Colloid and Interface Science, 151 (2009), 24-32 15 O. K. Park, Y. S. Kang, B. G. Jo, Synthesis of TiO2 nanoparticles coated with SiO2 for suppression of photocatalytic activity and increased dispersion stability, J. Ind. Eng. Chem. 10 (2004), 733-738 16 A. M. El-Toni, S. Yin, T. Sato, Control of silica shell thickness and microporosity of titania-silica core-shell type nanoparticles to depress the photocatalytic activity of titania, J. Colloid Interface Sci. 300 (2006), 123-130 17 O. K. Park, Y. S. Kang, Preparation and characterization of silica-coated TiO2 nanoparticle, Colloids Surf. A 257-258 (2005), 261-265 18 P. Katangur, P. K. Patra, S. B. Warner, Nanostructured ultraviolet resistant polymer coatings, Polym. Degrad. Stab. 91 (2006), 2437-2442 19 A. M. Djerdjev, J. K. Beattie, R. W. O'Brien, Coating of silica on titania pigment particles examined by electroacoustics and dielectric response, Chem. Mater. 17 (2005), 3844-3849 20 J. N. Ryan, M. Elimelech, J. L. Baeseman, R. D. Magelky, Silica-coated titania and zirconia colloids for subsurface transport field experiments, Environ. Sci. Technol 34 (2000), 2000-2005 21 K. V. P. M. Shafi, A. Ulman, X. Yan, N. L. Yang, M. Himmelhaus, M. Grunze, Sonochemical preparation of silane-coated titania particles, Langmuir 17 (2001), 1726-1730 22 M. Sabzi, S.M. Mirabedini, J. Zohuriaan-Mehr, M. Atai, Surface modification of TiO2 nano-particles with silane coupling agent and investigation of its effect on the properties of polyurethane composite coating, Progress in Organic Coatings 65 (2009), 222-228 23 J. Godnjavec, B. Znoj, P. Venturini, A. Žnidaršič. The application of rutile nano-crystalline titanium dioxide as UV absorber. Inf. MIDEM, 40 (2010) 1, 6-9 24 http://svn.assembla.com/svn/camsi-x/src/fe/LITERATURA/ Degussa-GLYMO.pdf 25 Adamson AW Physical Chemistry of Surfaces, 5th edn. Wiley, New York, 1991, 218 26SISTENISO 11507:2002 27 L. Jun, J.A. Siddiqui, R. M. Ottenbrite, Surface modification of inorganic oxide particles with silane coupling agent and organic dyes, Polym. Adv. Technol. 12 (2001), 285-292 28 I. C. McNeill, M. H. Mohammed, Thermal analysis of blends of low density polyethylene, poly(ethyl acrylate) and ethylene ethyl acrylate copolymer with polydimethylsiloxane, Polymer Degradation and Stability, 50 (1995) 3, 285-295 29Wenxui Que, Y. Zhou, Y. L. Lam, Y. C. Chan, C. H. Kam, Optiocal and microstructural properties of sol-gel derived titania/organically modified silane thin films, Thin Solid Films, 358 (2000) 1-2, 16-21 30 J. Macan, H. Ivankovic, Influence of hydrolysis conditions on curing and properties of an epoxy-silane based hybrid material, 11. Conference on Materials, Processes, Friction and Wear MATRIB 06, Vela Luka, 22-24. 6. 2006, 99-104 31 N. Eidelman, D. Raghavan, A. M. Forster, E. J. Amis, A. Karim, Combinatorial Approach to characterizing epoxy curing, Macromol. Rapid Commun., 25 (2004), 259-263 32 http://www.shimadzu.com.br/analitica/aplicacoes/ espectrofotometros/ftir/2_22-1.pdf 33 G. Nikolic, S. Zlatkovic, M. Cakic, S. Cakic, C. Lacnjevac, Z. Rajic, Fast Fourier transform IR characterization of epoxy GY systems crosslinked with aliphatic and cycloapliphatic EH polyamine adducts, Sensors, 10 (2010), 684-696 34http://www.thefreelibrary.com/Insitu+monitoring+of+the+ curing+of+epoxy+resins+by+DSC,+FTIR+and...-a0216041185 35 N. Grošelj, M Gaberšček, U. Opara Krašovec, B. Orel, G. Dražič, P. Judeinstein, Electrical and IR spectroscopic studies of peroxopo-lytungstic acid/organic-inorganic hybrid gels, Solid State Ionics, 125 (1999) 1-4, 125-133 36 Q. Cheng, C. Li, V. Pavlinked, P. Saha, H. Wang, Appl. Surf. Sci. 252 (2006), 4154-4160 37 F. Bauer, U. Decker, H. Ernst, M. Findeisen, H. Langguth, R. Meh-nert, V. Sauerland and R. Hinterwaldner, Functionalized inorganic/ organic nanocomposites as new basic raw materials for adhesives and sealants International, Journal of Adhesion and Adhesives, 26 (2006) 7, 567-570 38 M. Sakamoto, H. Okuda, J. Jpn. Soc. Colour. Mater. 68 (1995) 4, 203-210 39 Y. Q. Li, S. Y. Fu, Y. Yang, Y. W. Mai, Facile synthesis of highly transparent polymer nanocomposites by introduction of core-shell structured nanoparticles, Chem. Mater. 20 (2008), 2637-2643 40 A. C. Dodd, A. J. McKinley, M. Saunders, T. Tsuzuki, J. Nanopart. Res. 8 (2006), 43-51 41 M. V. Cristeaa, B. Riedla, P. Blancheta, Enhancing the performance of exterior waterborne coatings for wood by inorganic nanosized UV absorbers, Progress in Organic Coatings, 69 (2010), 432-441