Design of Novel Photocatalytic Films for the Protection of Architectural Surfaces via the Incorporation of Green Photocatalysts

: In conservation science the demand of multifunctional green materials displaying water repellency, consolidation, resistance to organic pollutants and pigments is constantly increasing. This research developed a green nanocomposite exhibiting photocatalytic, hydrophobic, consolidation and self-cleaning properties. This was achieved by synthesizing a TiO 2 photocatalyst enriched with carbon dots (C-dots) and successfully incorporated into a tetraethoxysilane nanocomposite modiﬁed with nano-calcium oxalate and polydimethylsiloxane. The TiO 2 /C-dots that were prepared with a simple, low temperature, cost-effective and large-scale procedure were assessed via analytical and spectroscopic techniques and were resulted in anatase structure ranging in size from 10 to 40 nm. Photooxidation measurements displayed that TiO 2 /C-dots nanoparticles could photodegrade completely Methyl Orange (MO) under UV and visible irradiation after 120 min. The photocatalytic performance of the nanocomposite with TiO 2 /C-dots resulted promising under UV after longer irradiation time. The degradation of MO was faster on bulk xerogels containing the TiO 2 /C-dots than the corresponding ones with TiO 2 . The treatment of concrete, limestone and lime mortars with the nanocomposite proved to be compatible with the substrates in terms of aesthetical aspects. This study demonstrates encouraging potential for large-scale production of a multifunctional protective composite that offers hydrophobicity, self-cleaning properties and consolidation to architectural surfaces.


Introduction
Nanotitania (TiO 2 ) is among the highest widely used photocatalytic material due to its semiconductor characteristics [1]. The basic principle of TiO 2 's photocatalytic action involves the absorption of electromagnetic radiation; afterwards, an electron is excited from the valence band and transferred to conduction band, generating a positive electron deficiency in the valence band. The existence of TiO 2 nanoparticles generates electrons and holes that consequently participate to chemical reactions. TiO 2 is polymorphous, existing in three fundamental crystal forms: (a) brookite, (b) rutile and (c) anatase [2]. Nanotitania has gained considerable attention due to its scientific and technological importance, in a broad range of fields, including solar cells, environmental remediation, photocatalysis, sensors and clean energy production [3]. Titania nanoparticles offer significant advantages including non-toxicity, chemical stability, low-cost production, and biocompatibility [4].
However, TiO 2 suffers from several disadvantages, limiting its practical efficiency in photocatalysis. Among them, the large band energy gap and relative slow reaction rate of TiO 2 considerably limits the utilization of solar energy as a sustainable source. This leads Furthermore, there is a tendency towards the development of multifunctional protective coatings that combine various properties such as consolidation, water repellency, along with reduction of polluting molecules, stain resistance and self-sterilization. Towards this goal, various studies have explored the potential of embedding the photocatalyst into the bulk of construction materials, such as mortars and concrete [20], or incorporating it in already existing organic and inorganic binders and coatings [21][22][23]. The major concerns regarding these applications are the maintenance of the photocatalysis yield and the eventual deterioration of the substrate.
In this research study, two simple and low-cost chemical compounds, citric acid and hydroxylamine, were utilized as precursors for the synthesis of C-dots. Subsequently, a simple and large-scale synthesis of TiO 2 was carried out in the presence of C-dots yielding the TiO 2 /C-dots. Both C-dots and TiO 2 /C-dots were physicochemically characterized by a variety of techniques, including spectroscopies, SEM and TEM microscopies, and X ray diffraction (XRD). Finally, the ability of TiO 2 /C-dots to produce reactive radicals was studied via the photodegradation of an organic dye, Methylene Orange (MO). The innovation of this work is related to the facile and convenient synthesis of the enriched TiO 2 with C-dots, as well as the effective degradation of MO after radiation in visible region. Moreover, this study manages to incorporate the developed photocatalyst into a novel protective/consolidation agent previously designed in the laboratory named FX-C and tested on limestone, lime mortar and concrete specimens [24].
FX-C is an innovative material used to consolidate and protect monumental surfaces. Its main components are tetraethoxysilane (TEOS), polydimethyl siloxane (PDMS) and nano calcium oxalate (nano-CaO x ). Silicon compounds, such as TEOS, are used as consolidants on architectural surfaces, due to their ability as oligomers to penetrate deeply into the surface and polymerize into its pores. The silicon-oxygen groups form strong bonds with the substrates that contain hydroxyl groups [25,26]. PDMS is a hydrophobic agent and, as an organosilane, develops chemical bonds with TEOS forming a protective silica network, contributing to the prevention of cracking of the treated surface. FX-C performance is also enhanced with nano-CaO x , which is found as a component of patina layer onto monumental surfaces, formed by the degradation of previously applied protective treatments and/or biological corrosion [27]. The nano-CaO x increases the chemical affinity between the protective agent and treated surface and simultaneously performs as an extra protective layer. The sol product derived from a one pot synthesis can be easily applied onto architectural surfaces, enhancing their mechanical properties and forming a hydrophobic film [24]. The dispersion of photocatalysts into FX-C intends to deliver self-cleaning properties to the protective film, thus contributing to the decomposition of organic stains and pollutants. The photocatalytic properties of the nanocomposite were studied, as above, via the photodegradation of MO. The results break new ground for the development of green smart building materials and protective coatings for the improvement of air quality as well as for disinfection purposes, taking into consideration the excellent antifungal and antibacterial properties of TiO 2 against a broad range of microorganisms [28].

Synthesis of C-Dots
C-dots were prepared by modifying an already published method [29]. Briefly, citric acid and hydroxylamine, at a molar ratio of 1:3, were dissolved into 5 mL ultrapure water. The solution was inserted into a 50 mL round-bottom flask and was boiled in a preheated oven at 200 • C for 5 min. During this procedure, the colorless solution rapidly begins to boil and finally evaporates leaving a dark brown solid on the bottom of the flask. An appropriate amount of water is added to the round-bottom flask of the reaction in order to form a yellow-colored suspension. Finally, the product was filtered with 0.2 µm filter to remove the aggregates and the supernatant liquid was collected.

Synthesis of TiO 2 /C-Dots and Pure TiO 2
A solution of 200 mg/mL C-dots was added into a solution of ethanol and nanopure water (1:1) (designated as Sol A). The adjustment of pH close to 2.5 was carried out with drops of sulfuric acid. Next, TTIP was dissolved in ethanol, producing solution B, following by drop-by-drop addition into Sol A. The solution was incubated overnight at room temperature, producing solution C. In the next step, solution C was heated for 8 h at 80 • C, so as the hydrolysis of TTIP and the disaggregation procedure of the prepared nanotitania to be carried out. Afterwards, the mixture of TiO 2 with incubated C-dots was separated after centrifugation. The precipitate was dried at 80 • C and powdered. Eventually, the pulverized material was heated for 120 min at 200 • C to develop the functional TiO 2 /C-dots nanoparticles. The prepared product displays a slightly yellow color ( Figure 1).
The same procedure was followed for the synthesis of TiO 2 without the addition of Cdots (control). TTIP dissolved in ethanol was added into a solution of ethanol and nanopure water, drop-by-drop and incubated overnight under magnetic stirring. Afterwards, the mixture of TiO 2 was heated for 8 h at 80 • C under reflux conditions. In the next step, the prepared TiO 2 nanoparticles were separated with centrifugation and washed with water. The precipitate was dried at an oven and powdered. Finally, this powder was heated for 120 min at 200 • C to produce TiO 2 nanoparticles.

Incorporation of Photocatalysts into the Protective Agent
The prepared photocatalysts were dispersed into the protective agent FX-C that was previously synthesized in the laboratory and stored in the form of sol. The concentration of the photocatalyst into the protective agent is 3.33% w/w.

Application of Photocatalytic Films onto Substrates
In order to evaluate the performance of the novel photocatalytic films in conservation applications, the protective agents were applied onto three different types of building materials: (a) porous biomicritic limestone, called Alfas, with a porosity ranging from 25 to 35% and pore size distribution from 1 to 10 µm; (b) concrete samples that were prepared with coarse calcareous and fine siliceous aggregates and (c) lime mortars prepared with natural hydraulic lime (NHL), metakaolin, coarse carbonaceous and quartz aggregates and carbonaceous sand ranging in diameter from 0.4 mm. Further information on the mix design of the treated specimens can be found in Table S1. The protective agent was brushed gently onto the specimens' surface until saturation. The amount of the protective agent used for each specimen is presented in Table S2. The aesthetic modification of the substrates' surface was evaluated by colorimetric analysis using a portable Konica Minolta spectrophotometer CM-2600d.

Characterization
High-resolution TEM images of C-dots and TiO 2 /C-dots were obtained on a JEOL JEM-2100 Transmission Electron Microscope (JEOL Ltd, Tokyo, Japan), operated at 80 and 200 kV, respectively. TEM sample preparation includes the evaporation of sample suspension after drop-casting on Formvar/Carbon coated TEM grids (Analytical Instruments S.A. Thane, India). Statistical size-distribution histograms were determined by using transmission electron microscope, upon counting and measuring the diameter distribution, utilizing the ImageJ software (Version 1.46r). The interlayer distance of TiO 2 planes was estimated with Digital Micrograph (Gatan Inc., Pleasanton, CA, USA). SEM images were recorded according to standard procedure. TiO 2 /C-dots nanoparticles were sprinkled on a two-sided carbon tape, coated with 100 Å gold utilizing a BAL-TEC SCD 050 Sputter Coater (BAL-TEC, Los Angeles, CA, USA). Samples were examined by using a JEOL JSM-6390LV Scanning Electron Microscope (JEOL Ltd, Tokyo, Japan), at 20 kV electron voltage. The determination of the chemical structure and composition of the prepared photocatalysts, TiO 2 and TiO 2 /C-dots, and enhanced protective films were obtained via the Fourier Transform Infrared Spectroscopy (FTIR) (Thermo Fisher ScientificWaltham, MA, USA) absorption spectra. The spectra were recorded with a Thermo iS50 FTIR spectrometer (Thermo Fisher Scientific, Waltham, MA, USA), in the spectral range from 4.000 to 400 cm −1 . Raman measurements were recorded utilizing an equipped Raman module in the sample compartment of the Scientific Nicolet iS50 spectrometer (Thermo Fisher Scientific, Waltham, MA, USA) operating with a laser at 1064 nm. Powder XRD patterns of the TiO 2 /C-dots nanoparticles were recorded on a D8 Advance X-Ray Diffractometer (Bruker, Billerica, MA, USA), with Cu Ka radiation at 35 mA and 35 kV and a Bruker Lynx Eye strip silicon detector Bruker, Billerica, MA, USA. Photoluminescence spectroscopic measurements were carried out on a Jobin-Yvon Horiba, Fluoro Max-P (SPEX) (Horiba, New York, NY, USA), with a CW Xenon arc lamp excitation source at 300 nm, with an emission range 290-700 nm. The UV-VIS diffuse reflectance spectra (DRS) of the photoactive TiO 2 nanoparticles were obtained in the range of 200-800 nm utilizing UV-VIS Perkin-Elmer Lambda 35 spectrophotometer (Perkin Elmer, Waltham, MA, USA) equipped with a Labsphere RSA-PE 20. Optical bandgap energy was determined by analogous Tauc plots.

Quantum Yield Measurements
The photoluminescence quantum yield (Φ) of C-dots solution was calculated by comparing the integrated photoluminescence emission intensity against two reference fluorophores: anthracene (An) (λ exc : 340 nm) and quinine sulphate (QS) (λ exc : 348 nm). Anthracene (literature Φ = 0.27) was dissolved in ethanol (refractive index, n = 1.360). Quinine sulphate (literature Φ = 0.54) was dissolved in 0.1 M H 2 SO 4 (refractive index, n = 1.333 [29]. C-dots were dissolved in distilled water (n = 1.333). The photoluminescence quantum yield was calculated using the following equation: where ST and X represent the standard and analyte, respectively. Φ: photoluminescence quantum yield, Grad: the slope of the line fitting integrated photoluminescence intensity vs. solution absorbance, n: refractive index of the solvent [30]. Absorbance values of solutions were maintained below 0.10 at the excitation wavelengths (340, 348 nm) in order to avoid absorption effects. Typically, a 10 mm optical path length cuvette was utilized. Excitation and emission slit widths were set such that excitation and emission bandwidths were 1.0 and 5.0 nm, respectively, when recording the photoluminescence emission spectra.

Photocatalytic Activity of TiO 2 /C-Dots Nanoparticles
The photocatalytic properties of TiO 2 and TiO 2 /C-dots samples (photocatalysts) were studied for their ability to degrade aqueous solution of MO. The photodegradation of MO was carried out through simulation of solar radiation. As a light source, a 150 W Xenon lamp was utilized (solar simulator, Oriel-Newport 96000, Newport, Irvine, CA, USA) for the photocatalysis measurements. A filter with wavelength cut-off lower than 420 nm was utilized to sever UV light. During the photodegradation experiment, TiO 2 was dispersed in 50 mL of MO aqueous solution (5 ppm), giving a concentration of TiO 2 nanoparticles (with or without C-dots) equal to 0.8 mg/mL Before dye degradation experiment, the mixture of TiO 2 with MO was incubated in the absence of light for 0.5 h to reach the adsorptiondesorption equilibrium between MO and TiO 2 samples. Finally, a beaker with a dispersion of MO with the photocatalyst was irradiated under the solar lamp at a distance of 10 cm. Periodically, the dispersion sample was collected and analyzed by UV-VIS spectroscopy.

Photocatalytic Activity of Protective Films
In the first place, the photocatalytic properties of the enhanced protective films were measured via the same method described above. The quantity of the enhanced protective films was selected accordingly, in order to keep the photocatalysts concentration in the aqueous MO solution equal to 0.8 mg/mL. The xerogel was grinded to thin powder, and the ability of the incorporated photocatalyst to generate radicals that decompose MO was tested under simulation of UV and solar radiation.
In addition, a supplementary experiment was carried out in order to determine the photocatalytic ability of the bulk xerogel. A thicker xerogel was formed by letting 3 gr of sol to solidify, and a drop of MO was placed onto its surface. The photocatalytic degradation of the drop was determined macroscopically and spectrophotometrically with a portable Konica Minolta spectrophotometer CM-2600d adapted with a D65 illuminant at 8-degree viewing, in wavelength range from 360 to 740 nm. Specifically, the decolorization of the applied drop was monitored by measuring differences in color of the spotted area with the passage of time. These differences were expressed as values of the CIELab color space: a*, b* and L*. The positive a* and b* values represent red and yellow, respectively, whereas the negative a* and b* values represent green and blue, accordingly. The L* value represents the luminance and ranges between 0, that corresponds to black, and 100, that corresponds to white. The color difference can be then calculated as follows [31]:

TEM and Optical Characterization of C-Dots
As displayed in Figure 2, the UV-VIS absorption spectrum of the aqueous C-dots solution was broad with a weak absorption maximum at 334 nm that corresponds to n-π* (C = O/C = N) transitions [32]. The photoluminescence spectra of the same C-dots solution exhibit the most robust emission and excitation at approximately 425 and 348 nm, respectively (Figure 2a). Figure 2b,c illustrates the photoluminescence spectra of C-dots, in which the emission peaks of C-dots are observed to be excitation-independent, especially for the wavelength range 250-400 nm, which is attributed to a single transition mode. On the contrary, when C-dots are excited above 400 nm, a typical behavior of C-dots is observed, emitting a red-shifted photoluminescence, ranged from the visible into the near-infrared (NIR) [11].
The photoluminescence quantum yield (Φ) of C-dots was estimated comparing the results of Equation (1) to both anthracene and quinine sulfate. It was calculated to be around 13%, undergoing excitation at 335 nm (Figure 2d). The fluorescence spectra of TiO 2 /C-dots is displayed in Figure S1. Transmission electron microscope (TEM) images showed a uniform dispersion of the Cdots in water ( Figure 3). As expected, C-dots exhibit quasi-spherical, discrete nanoparticles with sizes below 10 nm. C-dots form a stable suspension in water, and typically exhibit disk-shaped structures. TEM images reveal that the as-synthesized C-dots are uniform and monodisperse. Statistical evaluation of the size distribution revealed that the average size of the C-dots is 1.67 nm, ranged from 0.7 to 3.2 nm. The majority of the C-dots has sizes in the range of 1.0-2.1 nm.

Structure and Morphology of TiO 2 /C-Dots
The X-ray diffraction pattern of the synthesized TiO 2 /C-dots nanoparticles is shown in Figure 4. The XRD pattern of TiO 2 /C-dots reveals that the major crystalline structure of TiO 2 consists of anatase crystal form. Indeed, the diffraction peaks at 25.1 • , 37.9 • and 47.8 • correspond to anatase lattice parameter (101), (004) and (200), respectively [33]. The specific form of TiO 2 usually exhibits higher photocatalytic activity and has attracted the interest in photocatalytic procedures [34]. Moreover, anatase form is considered more stable than the rutile structure [35]. The XRD pattern of pure TiO 2 displays a low order material exhibiting non range order, as it is shown in Figure 4. It should be noted that this almost amorphous material is the result of the particular synthesis methodology. Therefore, it should not be confused with conventional TiO 2 photocatalysts.  The scanning electron micrographs of powdered TiO 2 /C-dots illustrated in Figure 5. SEM images display size and morphological analysis of the prepared composite, with their observation to reveal irregular agglomerates and their size ranges from nanometres scale up to several tens of micrometres, as a result of the drying process. TiO 2 /C-dots nanoparticles are in spherical shape (Figure 5d), and the morphology of agglomerates was characterized by a rough and compact surface. Similarly, pure TiO 2 particles exhibit dense agglomeration of particles with irregular in shape form ( Figure 6).   Figure 7 shows TEM images of the TiO 2 /C-dots, which exhibited relatively uniform size nanoparticles, with their size distribution ranging approximately from 10 to 40 nm (index Figure 7b). TEM analysis displays that the nanoparticles are in a highly quality crystalline form. The nanoparticles appeared to have a shape partly irregular, although tetragonal shape is the predominant. The main crystallographic phases were confirmed to be anatase, according to crystal lattice. Crystal planes are obviously visible, in the TEM images (Figure 7d), displaying the lattice fringes from TiO 2 /C-dots nanoparticles with an interlayer distance of 0.354 nm perfectly compared to the 0.352 nm lattice spacing of the (101) planes in anatase TiO 2 [36]. TEM images confirm the synthesis of highly crystalline TiO 2 at a relative low temperature, assisted by C-dots. Traditionally, the synthesis of pure anatase requires calcinations at 500 • C within several hours [37]. TEM images of pure TiO 2 ( Figure 8) are totally differentiated. Aggregates of a wide variety of size are observed in contrast to TiO 2 /C-dots; pure TiO 2 does not display crystal planes or any organized structure.  As shown in Figure 9a, the FTIR spectrum of C-dots confirms the presence of amide functional groups. In particular, the characteristic absorption band of the primary amide I stretching band of C = O is observed at 1697 cm −1 . A single broad band is observed at about 1584 cm −1 due to the overlapping of amide II band with asymmetric vibration of COOone. Furthermore, the peak appearing at 1401 cm −1 is assigned to symmetric stretching vibration of COO−. The peaks at 3131 and 3038 cm −1 can be attributed to CH 3 asymmetric and symmetric stretching vibrations, respectively. The band at 2810 cm −1 corresponds to the C−H (alkyne) stretching mode [38,39]. In addition, a sharp band at 1176 cm −1 is attributed to the stretching vibration bands of C−O of the carboxylic group [40]. FTIR spectrum of TiO 2 /C-dots displays 3 distinct bands at 1224, 1382 and 1608 cm −1 , which are attributed to C-O, symmetric and asymmetric carboxylate stretch modes, respectively. Given that the FTIR spectrum of TiO 2 shows a wide band at around 3300 and a small one at 1640 cm −1 corresponding to the stretching and bending vibration of O-H of the absorbed water (see Figure S1), the results of FTIR spectra prove the incorporation of C-dots into TiO 2 .
It could be considered that the TiO 2 crystal face consists of anatase phase after treatment with C-dots, which is also confirmed by Raman spectroscopy (Figure 9b) [41]. In particular, the Raman spectrum of TiO 2 /C-dots shows the bands of anatase at 152, 404, 513, 634 cm −1 ; these fundamental phonons are attributed to the (a) Eg, (b) B1g, (c) combination of A1g and B1g, and (d) Eg modes, respectively [42,43]. Indeed, the intensity of photoluminescence is very low ( Figure S1). On the contrary, it was not possible to collect Raman spectra of C-dots, probably due to their photoluminescence. The energy gap value of the TiO 2 /C-dots nanoparticles was calculated from the measurement of the diffuse reflectance of powder sample by Tauc's plot [44]. The band gap of the TiO 2 /C-dots was determined to be 3.21 eV (Figure 10b). This value is very close to the band gap of anatase. In particular, the majority of authors reported that TiO 2 anatase has only an indirect band gap of 3.23 eV as opposed to the rutile, which has a direct band gap of 3.06 eV and an indirect one of 3.10 eV [45,46].

Photocatalytic Activity of TiO 2 /C-Dots
The photocatalytic performance of TiO 2 /C-dots was estimated utilizing MO as an indicator of photodegradation. In particular, Figure 11 shows the photocatalytic efficiency curves of the aqueous solution of MO during the first 120 min of radiation in the presence of TiO 2 /C-dots. Two studies were carried out; in the first study, MO was radiated with UV light (red line) and in the second one with visible light (green line), as a filter wavelength cut-off lower than 420 nm was used. The next stage includes the radiation of MO with UV light. The UV-VIS spectra of MO degradation over time are displayed in Figure S2. The existence of TiO 2 /C-dots nanoparticles causes the complete disappearance of both MO bands at λ max = 463 and 272 nm, which was assigned to N = N bonded aromatic rings. These results indicate the cleavage of the azo group of MO. Indeed, it was observed that about 50% of MO was degraded within 40 min, while the dye has almost been completely degraded in 120 min under UV radiation (Figure 11). In contrast, pure TiO 2 displays a MO degradation of about 40% during the first 120 min. Photodegradation was also observed in the case of visible radiation, after the activation of TiO 2 /C-dots. The rate of visible degradation is relatively reduced in comparison to UV one. A noticeable decrease of MO amount is observed under visible irradiation, having the potential of further degradation after 120 min. An amount of 40% MO is degraded after the visible radiation in the presence of TiO 2 /C-dots. As opposed to that, TiO 2 shows almost zero degradation of MO under visible irradiation. The above diagrams reveal the capability of TiO 2 /C-dots to interact with organic compounds and degrade them in the UV as well as in the visible region, thus indicating its self-cleaning properties. This significant visible-light photocatalytic activity of TiO 2 /C-dots nanoparticles could open the paths to various environmental applications, especially for water and air purification. The macroscopic evaluation of the photodegradation process is reported in Figures S3 and S4. The rates of photocatalytic activity of TiO 2 and TiO 2 /C-dots fit with a pseudo 1st order kinetic model, confirming the experimental data of photocatalytic degradation of MO. The photocatalysis rates exhibit a high degree of correlation, with the equation below that displays the calculation of MO concentration at various time intervals (C) vs. the reaction time (t): C = Co e −kt , where Co is the MO concentration for t = 0 min and k is the pseudo 1st order adsorption kinetic constant [47]. Both the values of k and the corresponding regression coefficients (R 2 ) were determined for visible to be 30.84 × 10 −3 min −1 and 0.984 and for UV 28.53 × 10 −3 min −1 and 0.999, respectively. Pure TiO 2 displays a remarkable reduction of MO photocatalytic degradation. In particular, the constant k was estimated to be 26.73 × 10 −3 and 1.79 × 10 −3 min −1 under UV and visible radiation, respectively.
Undoubtedly, the incorporation of C-dots into TiO 2 significantly improves the photocatalytic degradation rate of MO, as a result of the increased photocatalytic activity of TiO 2 . In comparison to pure TiO 2 , the increased photocatalytic activity of TiO 2 /C-dots could be associated to the intermolecular charge transfer between organic (C-dots) and inorganic (TiO 2 ) nanomaterials, leading to a remarkable efficiency of MO photodegradation ( Figures S2-S4) [15].
The information provided by XRD and Raman spectroscopy did not fully support the correlation between C-dots fluorescence and TiO 2 /C-dots photocatalytic properties, which is subject of further analyses with relevant analytical techniques.
TiO 2 /C-dots nanoparticles might be successfully recovered by filtration or centrifugation and possibly be reused for several times. Therefore, this system could be useful for cleaning wastewater using sunlight. In addition, these nanoparticles have the potential for indoor air purification applications, due to their ability of photooxidation with visible light. Apart from their favorable preparation, TiO 2 /C-dots have the potential for a large-scale production of efficient photocatalytic materials.

Macroscopical Evaluation of Photocatalytic Films onto Substrates
The protective agent FX-C enhanced with the photocatalysts was applied onto three different substrates: concrete, micritic limestone and lime mortar. The application was performed by brushing two homogeneous layers of the sol onto the surfaces and letting it dry at room temperature. As presented in Figure 12, the incorporation of either TiO 2 , or TiO 2 enriched with C-dots does not affect the color of the formed protective film and also, does not promote cracking effects. This was further confirmed by the results of the colorimetric analysis demonstrated in Table 1. The aesthetic alteration of the concrete specimen is considered negligible as it is far below the required value for surface treatments onto monuments (∆E* ≤ 5) [24]. Concerning limestone and lime mortar, the protective agent containing undoped TiO 2 modified less the surface and the alteration is within the acceptable limits. The presence of C-dots in the incorporated photocatalyst, caused a slightly higher chromatic shift, though it still cannot be observed with naked eye.

Photocatalytic Activity of Multifunctional Protective Films
The photocatalytic assessment of the protective films was carried out with the same organic pigment MO as an indicator, under UV and visible radiation. The degradation of MO was spectrophotometrically measured, via the decrease of MO bands at 463 nm. The study was realized for both FX-C xerogels containing pure TiO 2 and TiO 2 enriched with C-dots. Under UV radiation, the photocatalytic performance of the non-enhanced catalyst is not affected by its incorporation into the siliceous film. Specifically, the 50% of MO is decomposed after only 15 min of irradiation, whereas after 120 min the percentage reaches the 90% (Figure 13). The kinetic constant k, considering a pseudo 1st order photocatalytic reaction approach, was determined at 24.11 × 10 −3 min −1 . The results under visible radiation demonstrated that the photocatalytic constant of the degradation reaction is reduced at 1.86 × 10 −3 min −1 . In the case of the TiO 2 /C-dots, the photocatalytic degradation of MO is notably affected by the dispersion of the photocatalyst into the protective agent. Under neither UV nor solar radiation the multifunctional film manages to decompose a significant amount of the pigment, at least for the first 120 min of the experiment. As a result, the k constant was not able to be estimated. However, in order to evaluate if there is any photocatalytic action, the study was re-conducted for 24 h. At the end of the experiment the photocatalytic film successfully decomposes the 97% of the organic pigment, proving the retardation and not the absence of photocatalytic action.
Subsequently, bulk xerogels were tested for their photocatalytic properties via the degradation of drops of the same organic dye, MO, from their surface ( Figure S5). A drop of MO was placed onto a marked spot of the xerogels' surface that were then irradiated with visible light. The decolorization of the spot because of the photocatalytic degradation of the dye was monitored with a spectrophotometer with wavelength range from 360 to 740 nm, by measuring differences in color of the spotted area after several days from the application. As shown in Figure 14, the color difference between the xerogel's surface before and immediately after the application of the MO drop is obviously lower in the case of the xerogel containing the photocatalyst TiO 2 /C-dots. Moreover, after only one day of application, the drop is completely decolorized on the enhanced xerogel, proving its photocatalytic activity, while on the FX-C xerogel, the MO drop can be still seen even after 3 days from the application.

Conclusions
Titanium dioxide nanoparticles treated with C-dots (TiO2/C-dots) were efficiently synthesized through a simple, low-temperature, cost-effective and large-scale procedure and were successfully incorporated into a siliceous protective agent, forming a multifunctional protective solution. Two simple and affordable compounds, citric acid and hydroxylamine, were utilized as precursors for the preparation of C-dots. XRD, Raman spectroscopy and TEM microscopy results identified anatase structure of TiO2/C-dots for as-synthesized materials. TiO2/C-dots were prepared by a cost-effective, and simple process. A comparison of the energy gap of pure TiO2 versus TiO2/C-dots shows the narrowing of the latter by 0.13 eV. TiO2/C-dots nanoparticles were studied for their ability to act as a catalyst. Indeed, the catalyst displays efficient photoactivity for the degradation of MO under visible and UV light. During the photocatalytic oxidation, the photodegradation of MO is completely effective and rapid after activation with UV light, following satisfactorily the pseudo first-order kinetic. Additionally, significant degradation of MO was observed in visible region. On the contrary, the synthesized TiO2 under the same conditions without C-dots displays remarkable lower activity under solar radiation by a factor of 10.
The incorporation of C-dots into TiO2 was crucial for the increasing activity of the latter. The photocatalytic performance of the multifunctional film with pure TiO2, under UV radiation, exhibited values comparable to the pure TiO2, proving the activation's independence of the catalyst after being incorporated in the protective agent. On the other hand, the enhanced TiO2/C-dots photocatalyst within the protective film did not perform as expected especially in the visible region, whereas in the UV region dissociated the MO in longer irradiation time. The photocatalytic activity of bulk xerogels was also evaluated by

Conclusions
Titanium dioxide nanoparticles treated with C-dots (TiO 2 /C-dots) were efficiently synthesized through a simple, low-temperature, cost-effective and large-scale procedure and were successfully incorporated into a siliceous protective agent, forming a multifunctional protective solution. Two simple and affordable compounds, citric acid and hydroxylamine, were utilized as precursors for the preparation of C-dots. XRD, Raman spectroscopy and TEM microscopy results identified anatase structure of TiO 2 /C-dots for as-synthesized materials. TiO 2 /C-dots were prepared by a cost-effective, and simple process. A comparison of the energy gap of pure TiO 2 versus TiO 2 /C-dots shows the narrowing of the latter by 0.13 eV. TiO 2 /C-dots nanoparticles were studied for their ability to act as a catalyst. Indeed, the catalyst displays efficient photoactivity for the degradation of MO under visible and UV light. During the photocatalytic oxidation, the photodegradation of MO is completely effective and rapid after activation with UV light, following satisfactorily the pseudo first-order kinetic. Additionally, significant degradation of MO was observed in visible region. On the contrary, the synthesized TiO 2 under the same conditions without C-dots displays remarkable lower activity under solar radiation by a factor of 10. The incorporation of C-dots into TiO 2 was crucial for the increasing activity of the latter. The photocatalytic performance of the multifunctional film with pure TiO 2 , under UV radiation, exhibited values comparable to the pure TiO 2, proving the activation's independence of the catalyst after being incorporated in the protective agent. On the other hand, the enhanced TiO 2 /C-dots photocatalyst within the protective film did not perform as expected especially in the visible region, whereas in the UV region dissociated the MO in longer irradiation time. The photocatalytic activity of bulk xerogels was also evaluated by monitoring the discoloration of a drop of MO on the xerogels' surface. In this case, the degradation of the dye was faster when the protective agent contained TiO 2 /C-dots.
The synthesized protective agents with the photocatalysts altered neither the color nor the consistency of the concrete, limestone or lime mortars surfaces.
In conclusion, the study succeeded in developing a multifunctional protective xerogel that combines hydrophobicity [48] and consolidation with photocatalytic properties under UV radiation, thus breaking new ground on conservation materials. Likewise, the TiO 2 /Cdots nanoparticles were characterized by advanced methods, including spectroscopic, microscopic and analytical techniques, whose results shed light on the structure, constitution and morphology of TiO 2 /C-dots evidencing that the synthesis followed resulted in the effectively photocatalytic anatase form of TiO 2 .
Supplementary Materials: The following are available online at https://www.mdpi.com/article/10 .3390/coatings11080934/s1. Figure S1: Fluorescence spectra of TiO 2 /C-dots, Figure S2: TiO 2 /C-dots: UV-VIS spectra of MO before (black line) and after 180 min irradiation with UV (green line) and Vis (red line), Figure S3: TiO 2 /C-dots: Macroscopic image of Methylene Orange photodegradation by UV, Figure S4: TiO 2 /C-dots: Macroscopic image of Methylene Orange photodegradation by Vis, Figure S5: FX-C (a,d), FX-C with TiO 2 (b,e), FX-C with TiO 2 /C-dots (c,f) in the form of sol and xerogel, respectively. Xerogels' diameter is about 30 mm, Table S1: Mix design of the concrete and lime mortars treated with the proposed nanocomposite FX-C with TiO 2 -Cdots, Table S2. Protective agent uptake on concrete, limestone and lime mortar specimens.