M. LE[NIK et al.: HYDROTHERMAL SYNTHESIS OF Mn-DOPED TiO2 WITH A STRONGLY SUPPRESSED ... 411–416 HYDROTHERMAL SYNTHESIS OF Mn-DOPED TiO 2 WITH A STRONGLY SUPPRESSED PHOTOCATALYTIC ACTIVITY HIDROTERMALNO SINTENTIZIRAN Z Mn DOPIRAN TiO 2 Z MO^NO INHIBIRANO FOTOKATALITSKO AKTIVNOSTJO Maja Le{nik 1 , Dejan Verhov{ek 1 , Nika Veronovski 1 , Mitja Gra~ner 1 , Goran Dra`i} 2 , Kristina @agar Soder`nik 3 , Mihael Drofenik 4 1 Cinkarna Celje, d.d. Inc., Kidri~eva 26, SI-3001 Celje, Slovenia 2 National Institute of Chemistry Slovenia, Hajdrihova 19, 1001 Ljubljana, Slovenia 3 Jo`ef Stefan Institute, Department for Nanostructured Materials, Jamova cesta 39, 1000 Ljubljana, Slovenia 4 University of Maribor, Faculty of Chemistry and Chemical Engineering, Smetanova ulica 17, 2000 Maribor, Slovenia maja.lesnik@cinkarna.si Prejem rokopisa – received: 2017-01-26; sprejem za objavo – accepted for publication: 2018-01-16 doi:10.17222/mit.2017.012 Nanocrystalline rutile TiO2 doped with various amounts of manganese (Mn) atoms was prepared using a hydrothermal synthesis route and a polycrystalline TiO2 precursor. The diffuse reflectance spectra of the highly doped rutile nanocrystallites display a notable red shift in the band-gap transition. The absorbing band edge moved to the visible range when the Mn content in the rutile nanocrystallite exceeded 0.4 %. The doped rutile nanocrystallites were analysed using X-ray powder diffraction (XRD), transmission electron microscopy (TEM), high-resolution transmission electron microscopy (HRTEM) and UV-Vis spectro- scopy. The Kubelka–Munk band-gap approximation was used to examine the narrowing of the band gap in comparison with the pure rutile TiO2 nanocrystallites. The doped rutile nanocrystallites displayed a remarkable decrease in the photocatalytic activity due to the formation of recombination sites induced by Mn ions incorporated into the crystal structure of the TiO2. Keywords: suspension, TiO 2 , rutile, doped with inorganic metal elements, UV absorber Z uporabo hidrotermalne sinteze in polikristalinini~ne rutilne oblike nanodelcev TiO2, smo pripravili nanokristalini~ne rutilne delce, dopirane z Mn. S pomo~jo UV-VIS difuzivno refleksijske spektroskopije smo zaznali izrazit premik absorpcijskega roba k valovnim dol`inam vidne svetlobe. Energijska vrzel z Mn dopiranega TiO2 se je z nara{~anjem koncentracije dopanta o`ala. Za analizo dopiranih rutilnih TiO2 nanodelcev smo uporabili rentgensko pra{kovno difrakcijo (XRD), elektronsko mikroskopijo (TEM, HRTEM), UV-Vis spektroskopijo, kalkulacijo energijskih vrzeli s Kubelka Munk pribli`kom. Pri merjenju fotokatalitske aktivnosti, z metodo degradacije izopropanola v alkohol, smo ugotovili, da dopiranje rutilne oblike TiO2 z Mn povzro~i inhibicijo fotokatalitske aktivnosti, kar smo pripisali tvorbi rekombinacijskih centrov, ki nastanejo pri dopiranju z Mn ioni v kristalno re{etko TiO2. Klju~ne besede: suspenzija, TiO2, s kovinami dopiran rutil, UV absorber 1 INTRODUCTION Titanium dioxide (TiO 2 ) crystallites are very efficient at scattering incident light and are therefore applied in some of the finest white pigments. In addition, TiO 2 has a wide range of photocatalytic applications in the protec- tion of the environment, where an enhanced photo- catalytic activity is desired. On the other hand, TiO 2 is an excellent UV absorber and shows no UV-induced degradation over time. 1 For this reason it is also used in a variety of applications where it acts as an UV-protective material, including various coatings, sunscreens and plastics. Using TiO 2 as a UV-protective material requires that the material is modified in such a way as to prevent the formation of free radicals upon the absorption of UV photons, which are otherwise preferred in environment- protection applications. 2 Thus, the free radicals that are involved in a number of potential health concerns, such as skin aging, must be reduced as much as possible. One possibility for reducing the photocatalytic activity of TiO 2 is a nanocrystallite surface coating with inorganic oxides that are transparent with respect to UV photons, such as SiO 2 and Al 2 O 3 , so isolating the surface from adsorbents, particularly moisture. 3 However, a thin layer on the crystallite surfaces has not been shown to be efficient in terms of significantly reducing the photocata- lytic activity of the material. Another option to suppress the photocatalytic activity of TiO 2 is doping the material with transition-metal ions (TMIs), which induced defects, and that function mainly as carrier-recombination centres when migrating from the inside to the surface of the photocatalyst and represent the key to a low photocatalytic activity, for instance, in the case of manganese doping. 4–7 Recently, some works were published that report on the enhanced photocatalytic activity of Mn-doped TiO 2 . 8,9 Here, the superior reactivity might be ascribed to the anatase crystallites’ morphology and structure as one of the main reasons for the improved photocatalytic activity in these samples. To the best of our knowledge the inhibition of photocatalytic activity in pure rutile Mn-doped samples prepared by hydrothermal synthesis, Materiali in tehnologije / Materials and technology 52 (2018) 4, 411–416 411 UDK 54.057:549.514.6:546.711:544.526.5 ISSN 1580-2949 Original scientific article/Izvirni znanstveni ~lanek MTAEC9, 52(4)411(2018) from prefabricated TiO 2 , has not been reported yet. Here, we must emphasize that the hydrothermal method was crucial in synthesizing the Mn-doped rutile phase, which strongly inhibits the photocatalytic activity. 2 EXPERIMENTAL PART 2.1 Preparation method The hydrothermal synthesis of Mn-doped rutile TiO 2 nanocrystallites was performed in a Teflon-lined, stain- less-steel autoclave with a volume of 80 mL. To prepare the TiO 2 -doped sample the reactor was loaded with a 50-mL aqueous suspension of polycrystalline rutile TiO 2 nanocrystallites provided by Cinkarna Celje, Inc. having a mass concentration of 60–150 g/L (calculated as TiO 2 ) and 1 % of mass fractions (based on TiO 2 content) of manganese chloride (MnCl 2 ,9 6%w/w, Merck). The mixture of polycrystalline rutile TiO 2 nanocrystallites and dopant was then stirred for at least 15 min. The autoclave was put into a preheated oven and was hydro- thermally treated at 180 °C for 24 h. At the end of the heating process the autoclave was taken out of the oven and left to cool at room temperature. The as-prepared product was diluted with distilled water, washed on a laboratory centrifuge (MPW 350 – Med. Instruments, High brushless centrifuge, 4000 min –1 , 20 min). The washing was performed until the conductivity of the material was less than 900 μS/cm. The final product was an aqueous suspension of doped rutile having a 10 % of mass fraction of monosized TiO 2 nanocrystallites with a light-brown colouration. Samples with anticipated con- centrations of Mn (0.4 %, 0.8 % and 2 %) of mass fractions, labelled as samples: B, C and D, were also prepared by the same process by varying the content of added MnCl 2 . The sample A was prepared using the same process, but without the addition of MnCl 2 as a dopant. 2.2 Characterization of samples The morphology and size of the particles were examined with a transmission electron microscope (TEM, Jeol JEM-2100, Jeol Ltd., Tokyo, Japan). To prepare the TEM specimens, the samples were ultrasoni- cally dispersed and the suspension was collected using carbon-supported copper grids. The presence of the manganese was verified using energy-dispersive X-ray spectroscopy (EDXS). The crystal structure, the concen- tration of Mn and the valence state of the titanium in sample B (nominally 0.8 % of mass fractions manga- nese-doped TiO 2 ) were characterized with probe- corrected scanning transmission electron microscopy (STEM, Jeol ARM 200 CF) and electron-energy-loss spectroscopy (EELS, Gatan Quantum ER dual). The crystallinity of the particles was examined using X-ray diffraction (XRD) performed on a Cubi X PRO PW 3800 instrument (PANanalytical) (Cu-K radiation ( = 0.15418 nm)). In order to acquire the TiO 2 powders for the X-ray powder diffraction (XRD) investigation, the suspensions were dried at 80 °C, ground and the powder was pressed into pellets that were used to perform the measurements. The UV–Vis diffuse reflectance spectra were collected on an Agilent-Cary 300 UV-Vis spectrophoto- meter equipped with an integrating sphere (Varian Inc., USA). The measurements of the photocatalytic activity were performed in a sealed gas-solid reactor at room tempe- rature and a relative humidity of 60 %, utilizing FT-IR spectroscopy (Spectrum BX model Perkin Elmer spec- trometer). The model pollutant was isopropanol in the gas phase. During the photocatalytic reaction the isopropanol oxidizes into acetone and subsequently into carbon dioxide and water under UV irradiation (Xe lamp, 300 W). The light imitates the solar spectrum and emits both ultraviolet (UV) and visible (VIS) light. The reactor is at a distance of 4 cm from the lamp. The sam- ples were dried under ambient conditions and prepared by milling 50 mg of the material. To perform the measurements, 20 μL of isopropanol was injected into the system. This volume represents around 2000 mg/L of gas phase of the isopropanol in the system. The amount and ratio of isopropanol and the formed acetone were monitored in real time. The evaluation of the photo- catalytic activity is based on the acetone-formation kinetics and is given in mg/L h. 10 3 RESULTS AND DISCUSSION 3.1 Hydrothermal synthesis Hydrothermal synthesis is one of the best methods for producing pure oxide nanocrystalline materials. Among the various hydrothermal methods, hydrothermal precipitation is suitable for the synthesis of nanocrys- tallite material using a polycrystalline precursor and transforming it into a nanocrystalline material with a controlled morphology and composition. During this investigation the dissolution of the precursor, polycrys- talline rutile, and afterwards a precipitation in the pre- sence of the dopant, was applied in order to transform it into nanocrystalline material with a controlled morphol- ogy and composition. After the dissolution and subsequent diffusion of TiO 2 in the presence of hydrated Mn ions to the pre- cipitation locations, the precipitation from the solution on the doped rutile nanocrystallites is a relatively sluggish process that determines the final morphology of the crystallites and the concentration of the dopant. The amount of dopant that was not incorporated during the TiO 2 precipitation was washed away at the end of the procedure. In solution the TiO 2 exist as six-fold coordinated structural units (TiO 6 ) that undergo condensation to become the octahedra that bond via corner- and M. LE[NIK et al.: HYDROTHERMAL SYNTHESIS OF Mn-DOPED TiO2 WITH A STRONGLY SUPPRESSED ... 412 Materiali in tehnologije / Materials and technology 52 (2018) 4, 411–416 edge-sharing to form the final crystal structure. Hence, the fundamental structural units are (TiO 6 ) octahedrons, having different modes of arrangement and links, depending on the particular crystal form of the TiO 2 .In the rutile form the (TiO 6 ) octahedra link by sharing an edge along the c-axis to form chains. During the precipi- tation process oxygen coordinated Mn units incorporate into the rutile by replacing the (TiO 6 ) octahedrons in a doped rutile structure. However, the incorporation of coordinated Mn complex ions covering various oxidation states and coordination aggravate the incorporation of the manganese. Thus, the incorporation of Mn at higher nominal concentrations is not straight forward, but exhibits a lag with regards to the nominal concentration of the manganese, Table 1. 3.2 The crystalline phase of particles The XRD patterns of Mn-doped TiO 2 with different nominal concentrations (0, 0.2, 0.8, 2.0) % of Mn in the TiO 2 are shown in Figure 1. The XRD peaks confirm the presence of a rutile crystal structure in all the samples. No manganese-rich phase was identified in the XRD patterns, even when the doping level concentration was as high as 2.0 % of mass fractions. The average crystallite size was determined using diffraction-peak (100) broadening and Scherrer’s formu- la based on the FWHM (Full Width at Half Maximum) of the XRD peaks. The determined crystallite size is shown in Table 1. For up to 0.8 % of mass fractions of dopant the crystallite size is more or less around 30 nm. After that, at 2.0 % of mass fractions of dopant, the diffraction-peak broadening indicates a decrease in the crystallite size accompanied by an increase of the specific surface, Table 1. Thus, with up to 2.0 % of mass fractions of manganese addition in the nanocrystallites the morphology of the crystallites did not change significantly. 3.3 The morphology of the doped TiO 2 particles TEM images of the undoped TiO 2 and 0.8 % of mass fractions of Mn-doped TiO 2 nanocrystallites are shown in Figure 2. The hydrothermally synthesized, doped, rutile TiO 2 nanocrystallites have an oval/spherical mor- phology and are uniform in size. From the TEM images no significant difference in the morphology between the synthesized products, i.e., 0.8 % of mass fractions of Mn-doped TiO 2 and undoped TiO 2 , can be seen, in agree- ment with the XRD patterns, which show a comparable crystallite size up to 0.8 % of mass fractions of Mn, Table 1. M. LE[NIK et al.: HYDROTHERMAL SYNTHESIS OF Mn-DOPED TiO2 WITH A STRONGLY SUPPRESSED ... Materiali in tehnologije / Materials and technology 52 (2018) 4, 411–416 413 Table 1: The nominal concentration vs. real concentration determined by EDXS, BET specific surface area, Scherrer’s crystallite size of the prepared samples and the measured band gap Sample* Nominal Mn concentration (w/%) Real Mn concentration (w/%) Specific surface area (m 2 /g) Crystallite size (nm) Band gap (eV) A - - 70.1 27.8 3.01 B 0.4 0.30±0.1 69.5 29.9 2.98 C 0.8 0.90±0.1 78.3 31.7 2.90 D 2.0 1.50±0.1 93.1 21.8 2.87 Figure 2: TEM image of: a) undoped sample A and b) sample C with a nominal concentration of 0.8 % of mass fractions of Mn Figure 1: XRD patterns of undoped and Mn-doped TiO 2 samples with different Mn contents The average crystallite size and the specific surface data in Table 1 show that the morphology of samples D doped with a nominal concentration of 2.0 % of mass fractions of Mn are different than the other samples in the sequence. They exhibit a smaller crystallite size and a higher specific surface area. An increase in the nominal concentration of Mn in the samples up to 0.8 % of mass fractions is accompanied by a notable increase in the reflectance from 20 % to about 50 %, as well as a band- gap decrease from 3.01 eV to 2.90 eV in sample C. The STEM-EELS analyses of sample C is presented in Figure 3. The doped crystallites have an oval-sphe- rical morphology and are uniform in size (a). No amorphous Mn-rich oxide phase was found on the surface of the particles, which indirectly confirms the incorporation of the Mn phase into the TiO 2 crystal lattice. The presence of a precipitated dopant on the particle surface is a relatively common phenomenon. Evidently, the concentration of 0.8 % Mn is the limit for fully incorporating the dopant into the crystal lattice, which is confirmed by the UV-Vis reflectance spectra, where the absorption of the higher amount of dopant (2 % of mass fractions of Mn) is negligible. At the edges of the rutile nanocrystallites the reconstruction of the surface structure took place. In these areas the presence of Ti 3+ was observed using EELS. The observation is quite interesting, because it is not usual to find such an arranged structure containing Ti 3+ on the surface of a particle. Further investigations are necessary in order to find an appropriate explanation. The excellent match of the experimental and the simulated electron-diffraction patterns shown in Figure 3b confirms the presence of individual rutile nanocrystallites and no anatase or brookite crystal modifications were detected. The EELS analysis identified the presence of Mn, but due to the very low concentration it was not possible to determine the valence state of this Mn. Finally, the Mn phase is not uniformly incorporated inside the particles as not all the EELS spectra from the different nanoparticles contain Mn edges. 3.4 UV–Vis diffuse reflectance spectra The influence of doping on the UV/Vis spectra properties of the rutile TiO 2 is clear from Figure 4. The Mn-doped samples exhibit a notable difference in their colour, which depends on the dopant concentration and extends from light-to-dark yellow to a rose (skin-like) colour. As can be seen in Figure 4, the reflectivity dependence of the wavelength of the undoped TiO 2 has a typical sharp edge of reflection at around 420–400 nm, while the reflection capacity of the visible-light region is relatively poor at that wavelength. Using the relation E(eV) = hc/ (nm) = 1236// (nm) we obtain, for the measured band gaps of the samples, values of 2.94–3.06 eV, which corresponds to an electron exci- tation from the VB to the CB of the rutile. Besides, for the determination of the band-gap energy, the Kubelka–Munk procedure was used. 11,12 The extra- polated values are shown in Table 1. In comparison, from the reflectivity spectra of the Mn-doped samples, Figure 4, it is clear that there is a significant reflection of visible light. 13–16 In addition, two absorption edges are present in the reflective spectra. The primary absorption edge contributes to the reflect- ance at short wavelengths of the visible spectra, while the secondary absorption edge extends into the lowest wavelengths of the visible light spectra, in agreement with previous reports. 7–9 The intensity of both absorption edges changes when increasing the Mn-doping con- centration. Moreover, it is also possible that the Mn doping even induces the reflection of IR light, which is in agreement with Shao’s report. 8,16,17 When the doping level reached a nominal concentration of 0.8 %, the optical reflection was shifted into the infrared spectral range. In addition, samples doped with a nominal con- centration of 0.8 % of mass fractions and 2.0 % of mass M. LE[NIK et al.: HYDROTHERMAL SYNTHESIS OF Mn-DOPED TiO2 WITH A STRONGLY SUPPRESSED ... 414 Materiali in tehnologije / Materials and technology 52 (2018) 4, 411–416 Figure 4: UV/Vis reflectance spectra of the undoped TiO 2 and the TiO 2 doped with different % of mass fractions of Mn ions, indicated in the figure Figure 3: BF-STEM image: a) of hydrothermally treated TiO 2 nano- crystallites with 0.8 % of mass fractions of Mn, b) experimental and simulated selected-area electron-diffraction pattern (SAED) for rutile, c) EELS spectrum where traces of Mn can be seen, d) HAADF-STEM micrograph of rutile nanocrystallites where an approximately 1-nm-thick phase can be seen at the edge of the particle, the edge con- tains a large amount of Ti 3+ , based on the EELS spectra (insets) fractions exhibited a reflectivity of 50 % at a wavelength of 800 nm. As we can see in Figure 4, the reflectivities of the samples C and D were actually the same. Similar results were described by Deng for a nominal concen- tration of 0.8 % of mass fractions and 2.0 % of mass fractions doped samples, respectively, where the samples were synthesized using the sol-gel method and achieved a limiting dopant concentration of 12 % with a 75 % absorbance in the Vis absorption spectra. 8 3.5 Photocatalytic activity measurements To evaluate the photocatalytic activity of the undoped and Mn-doped TiO 2 , the photocatalytic degradation of isopropanol under UV+VIS and Vis irradiation was studied. The results of the photocatalytic activity are presented in Figure 5, based on the acetone-formation kinetics, and are given in μL/L h. It is clear that under UV+Vis irradiation the photocatalytic activity of the Mn-doped TiO 2 drastically decreased to near-zero values. The reduced photocatalytic activity of the Mn-doped TiO 2 particles under UV light was also re- ported by Chauhan. 18 When the Mn-doped TiO 2 particles were exposed to visible light, the same results were obtained. The pure, undoped TiO 2 acts as a visible-light photocatalyst, but when the TiO 2 particles were doped with Mn ions, the inhibition of the photocatalytic activity occurs. The photocatalytic-activity inhibition of the Mn-doped TiO 2 was also established in Chang’s work and in the research of Wakefield. 4,7 Manganese ions are p-type dopants that are incorporated into the Ti 4+ lattice sites and have a crucial effect on the activity, because they serve as Mn 3+/4+ doping trap centres (recombination centres), which have both occupied and unoccupied energy levels within the band gap, trap electrons and holes on the same sites and rapidly annihilate the trapped carriers through intra-atomic relaxation. 4,8 Since the Mn ions serve as recombination centres it should be pointed out that the photocatalytic activity of doped samples decreases when the concentration level of the dopant is increased. 5 In addition, the electronic structure, the coordination number, the electronegativity, and the size of the dopant ions are all major influencing parameters that affect the formation of free radicals, having an impact on the effectiveness of Mn doping with respect to blocking the photocatalytic activity. It is interesting to note that the manganese is a very effective inhibitor of the photocatalytic activity and even a relatively small dopant level, of only 0.8 % of mass fractions of Mn, nearly completely blocks the photocata- lytic activity of rutile nanocrystallites in the UV region and to a relatively large extent also in the VIS part of the spectra. Less prone to photocatalytic reactions is also the relatively high dopant concentration level of 2.0 % of mass fractions of Mn where the smaller crystallites are formed (sample D, Table 1), in spite of a higher specific surface area. The manganese ions have the appropriate characteristics to successfully inhibit the photocatalytic activity, particularly when they are incorporated into the interior of the matrix and the doping-induced defects are operating as carrier-recombination centres when they migrate from the inside of the photocatalyst to the surface. 5 4 CONCLUSIONS Mn-doped rutile TiO 2 nanocrystallites that demon- strate a strong reduction in photocatalytic activity were successfully prepared using the hydrothermal method. The average crystallite particle size is around 30 nm; however, this decreases at the 2 % of mass fractions of dopant concentration level. This could indicate the maxi- mum concentration level of the dopant ions incorporated into the crystal structure. On the surface of the particle no amorphous Mn oxide phase is detected, which indirectly confirms the incorporation of the Mn phase into the TiO 2 crystal structure. The diffuse reflectance spectrum of the Mn-doped TiO 2 has two absorption edges and displays a red shift in the optical absorption range, which increases with the Mn content and narrows the band gap. The Mn-ions-doped TiO 2 nanocrystallites, which can display a red shift in the band-gap transition, reduce strongly the photocatalytic activity. Acknowledgment This work is partially financially supported by the Ministry of Education, Science and Sport of the Republic of Slovenia under the contract 34/2013-SOF. M. LE[NIK et al.: HYDROTHERMAL SYNTHESIS OF Mn-DOPED TiO2 WITH A STRONGLY SUPPRESSED ... Materiali in tehnologije / Materials and technology 52 (2018) 4, 411–416 415 Figure 5: photocatalytic activity of undoped TiO 2 and TiO 2 doped with different amounts of Mn ions (A – undoped TiO 2 ,B–0.2%of mass fractions of Mn doped TiO 2 , C – 0.8 % of mass fractions of Mn doped TiO 2 ,D–2%ofmass fractions of Mn doped TiO 2 ) under a) UV+Vis irradiation and b) Vis irradiation 5 REFERENCES 1 J. Winkler, Titanium Dioxide, Vincentz, Hanover, 2003 2 B. Faure, G. Salazar-Alvarez, A. Ahniyaz, I. Villaluenga, G. Berrio- zabal, Y. R. De Miguel, L. Bergström, Dispersion and surface func- tionalization of oxide nanoparticles for transparent photocatalytic and UV-protecting coatings and sunscreens, Science and Technology of Advanced Materials, 14 (2013), doi:10.1088/1468-6996/14/2/ 023001 3 T. A. Egerton, The influence of surface alumina and silica on the photocatalytic degradation of organic pollutants, Catalysts, 3 (2013), 338–362, doi:10.3390/catal3010338 4 S. Chang, W. Liu, The roles of surface-doped metal ions (V, Mn, Fe, Cu, Ce and W) in the interfacial behaviour of TiO2 photocatalysts, Applied Catalysis B: Environmental, 156–157 (2014), 466–475 5 Z. Li, W. Shen, W. He, X. Zu, Effect of Fe-doped TiO2 nanoparticle derived from modified hydrothermal process on the photo catalytic degradation performance on methylene blue, Journal of Hazardous Materials, 155 (2008), 590–594, doi: 10.1016/j.jhazmat.2007.11.095 6 G. Liu, L. Wang, H. Gui Hang, H.-M. Cheng, G. Q. Lu, Titania- based photocatalysts-crystal growth, doping and heterostructuring, Journal of Materials Chemistry, 20 (2010), 831–843, doi:10.1039/ b909930a 7 G. Wakefield, S. Lipscomb, E. Holland, J. Knowland, The effects of manganese doping on UVA absorption and free radical generation of micronized titanium dioxide and its consequence for the photosta- bility of UVA absorbing organic sunscreen components, Photoche- mical & Photobiological sciences, 3 (2004), 648–652, doi:10.1039/ b403697b 8 Q. R. Deng, X. H. Xia, M. L. Guo, Y. Gao, G. Shao, Mn-doped TiO2 nanopowders with remarkable visible light photocatalytic activity, Materials Letters, 65 (2011), 2051–2054, doi:10.1016/j.matlet.2011. 04.010 9 X. H. Xia, L. Lu, A. S. Walton, M. Ward, X. P. Han, R. Brydson, J. K. Luo, G. Shao, Origin of significant visible-light absorption pro- perties of Mn-doped TiO2 thin films, Acta Materialia, 60 (2012), 1974–1985, doi:10.1016/j.actamat.2012.01.006 10 T. Marolt, A. Sever [kapin, J. Bernard, P. @ivec, M. Gaber{~ek, Photocatalytic activity of anatase-containing facade coatings, Surface and Coatings Technology, 206 (2011), 1355–136, doi:10.1016/ j.surfcoat.2011.08.053 11 S. Valencia, J. M. Marin, G. Restrepo, Study of the bandgap of syn- thesized titanium dioxide nanoparticles using the sol-gel method and a hydrothermal treatment, The Open Materials Science Journal, 4 (2010), 9–14 12 V. D`imbeg-Mal~i~, @. Barari}-Miko~evi}, K. Itri}, Kubelka – Munk theory in describing optical properties of paper, Technical Gazette, 18 (2011), 117–124 13 H. Feng, M. Zhang, L. E. Yu, Hydrothermal synthesis and photo- catalytic performance of metal-ions doped TiO2, Applied Catalysis A: General, 413–414 (2012), 238–244, doi:10.1016/j.apcata.2011. 11.014 14 M. Xue, L. Huang, J. Q. Wang, Y. Wang, L. Gao, J. Zhu, Z. Zou, The direct synthesis of mesoporous structured MnO2/TiO2 nanocom- posite: a novel visible-light active photocatalyst with large pore size, Nanotechnology, 19 (2008), 185604, doi:10.1088/0957-4484/19/ 18/185604 15 Y. Chen, X. Ma, Preparation of visible-light active Mn-doped TiO2 photocatalyst and its photodegradation of methylene blue from solution, Advanced Materials Research Vols., 989–994 (2014), 513–535 16 G. Shao, Red shift in manganese and iron-doped TiO2: A DFT+U analysis, The Journal of Physical Chemistry. C, 113 (2009), 6800–6808, doi:10.1021/jp810923r 17 G. Shao, Q. Deng, L. Wan, M. Guo, X. Xia, Y. Gao, Molecular de- sign of TiO2 for gigantic red shift via sublattice substitution, Journal of Nanoscience and Nanotechnology, 10 (2010) 7092-7096, doi: 10.1166/jnn.2010.2767 18 R. Chauhan, A. Kumar, R. P. Chaudhary, Structural and photo- catalytic studies of Mn doped TiO2 nanoparticles, Sprectrochimica Acta Part A: Molecular and biomolecular spectroscopy, 98 (2012), 256–264, doi:10.1016/j.saa.2012.08.009 M. LE[NIK et al.: HYDROTHERMAL SYNTHESIS OF Mn-DOPED TiO2 WITH A STRONGLY SUPPRESSED ... 416 Materiali in tehnologije / Materials and technology 52 (2018) 4, 411–416