ORIGINAL RESEARCH article
Synthesis and Characterization of TEOS Coating Added With Innovative Antifouling Silica Nanocontainers and TiO2 Nanoparticles
- 1Dipartimento di Scienze, Università degli Studi “Roma Tre”, Rome, Italy
- 2Laboratorio Analisi Superfici, INFN Roma Tre, Rome, Italy
We study the synthesis and characterization of an innovative TEOS-based composite coating, which could improve previous formulations used in the field of monument conservation. The proposed coating is composed by a tetraethoxyorthosilicate matrix (TEOS), containing an elasticiser [hydroxyl-terminated polydimethylsiloxane (PDMS-OH)] and a non-ionic surfactant (n-octylamine). The specific self-cleaning and antifouling properties are obtained by the addition of different kinds of nanofillers: the commercial TiO2 nanoparticles, plus two different silica nanocontainers, loaded with the commercial biocide 2-mercaptobenzothiazole. Through a multi-analytical approach, we evaluate the effect of the nanoparticles concentration on the coatings drying rate, on the variation of their visual aspect and textural properties. Our results show that the addition of the silica nanocontainers at 0.05% (w/v) in sol does not change the color of the coating and reduces the formation of cracks after drying. Moreover, the coating charged with nanocontainers undergoes slower drying, thus improving its penetration into the pores of the treated surface. Further tests of photocatalytic and biocidal properties of this new product on different lithotypes and their potential interactions are in progress.
Most historical buildings and monuments, that are a seamless part of our urban landscape, employ natural and artificial stone materials, which are subject to deterioration processes, due to the interaction with the environment (Jackson et al., 2005; Bourges et al., 2008; Torraca, 2009; Doehne and Price Clifford, 2010). In particular, urban environment accelerates the deterioration and may cause crumble of outdoor surfaces (such as architectural elements and sculptures), due to pollution and high concentration of fine particulate. In addition, biotic factors, especially microorganisms, are among the main agents of stone damage (McNamara and Mitchell, 2005; Caneva et al., 2008; Scheerer et al., 2009). Given the large number and the different nature of the stone materials and the various related degradation processes, finding potential supporting solutions is a challenging issue.
Among the consolidant products used for stone, TEOS-based materials have relevant applications and properties (Kim et al., 2009; Zárraga et al., 2010). When these products are applied on the decaying stone substrate, the tetraethoxysilane polymerizes into the porous structure, thus increasing the intragranular cohesion. Ideally, the TEOS matrix rebinds adjacent mineral grains (Zárraga et al., 2010), appreciably increasing the strength of the stone. However, although TEOS-based coatings are widely applied for consolidation interventions (Zárraga et al., 2010), it is well-known that during the drying phase these products undergo crack formation (Wen and Mark, 1995; Mosquera et al., 2003; Salazar-Hernández et al., 2009; Illescas and Mosquera, 2011; Xu et al., 2012; Pinho et al., 2013; Angulo-Olais et al., 2018).
Different authors have tested the effects of the addition of oxide nanoparticles. To quote a few of them, we mention that Milani et al. (2007) have investigated the realization of a new TEOS-based consolidant with colloidal silica particles. Kim et al. (2009) and the Mosquera's group (Mosquera et al., 2003) have also highlighted that the addition of nanoparticles into the TEOS matrix noticeably decreases the cracking during the drying phase.
Addition of TiO2 nanoparticles, with antifouling and self-cleaning capabilities, seems a promising way in order to scale up the properties of TEOS based products; indeed titanium oxide properties have been widely tested in conservative treatments of stone surfaces (La Russa et al., 2012; Quagliarini et al., 2012, 2013; Kapridaki and Maravelaki-Kalaitzaki, 2013; Munafò et al., 2015; Gherardi et al., 2016; Xu et al., 2019). In the last years, self-cleaning and antifouling coatings have attracted the attention of many researchers in the field of stone conservation (Colangiuli et al., 2015; Lettieri et al., 2019). The self-cleaning properties of titanium oxide are due to its ability to photocatalyze the complete degradation of many organic contaminants and environmental toxins (Liu and Liu, 2016). Moreover, the photocatalytic activity of TiO2 determines a collateral biocidal effect. The photocatalytic killing action by titania has been studied on a wide spectrum of organisms including bacteria, fungi, algae (Ruffolo et al., 2017). However, the structural properties of the target microorganism (e.g., the complexity and thickness of cell envelope) influence the microbiocidal efficacy of TiO2: fungi, for instance, have a complex structure, which protects them from damage due to the radical species produced during the photocatalytic titania activities (Seven et al., 2004; Munafò et al., 2015).
In order to improve the antifouling effects, most coatings are prepared by dispersion of biocides molecules into the wet coating material (Omae, 2003; Almeida et al., 2007). This practice suffers from some drawbacks, such as poor control of the release rate of the antifoulants or degradation of the active substance. On the other hand, increasing the quantity of biocides into the coating, in order to extend its functionality over time is not economically, environmentally, and practically sustainable (Pinna et al., 2012; Fidanza and Caneva, 2019). Moreover, the high concentration of biocides into the coating may induce macroscopic damage of the film, detectable as a phase separation (Trojer et al., 2015).
Since several biocides are effective only for a short period of time after the application (between 6 months and 1 year), due to the cleaning of the surfaces after the treatments or due to the washing out of the compounds by rainfall, a frequent reapplication is needed (Jämsä et al., 2013). Thus, when indirect control methods are not possible (Almeida et al., 2007; Caneva et al., 2008; Pinna et al., 2012; Fidanza and Caneva, 2019), improving the performance of the antifouling coating is necessary from both economical and environmental points of view.
Several biocides have been used in antifouling treatments for buildings conservation (Nugari and Salvadori, 2003; Caneva and Tescari, 2017; Pinna, 2017). A lot of active principles widely used in the past, such as organ-stannic or organotin compounds, have been excluded for toxicological reasons. The quaternary ammonium salts (Quats, e.g., benzalkonium chloride) are among the most used materials, despite their lower efficacy with respect others (Nugari and Salvadori, 2003; Caneva and Tescari, 2017; Pinna, 2017). Considering its chemical properties and the documented efficacy, we selected, as an active principle, 2-mercaptobenziothiazole (MBT), which can be easily encapsulated into silica based nanocapsules (Maia et al., 2015). In commercial products (e.g., Vancide 51, Vanderbilt Company) MBT is included in combination with dimethyldithiocarbamate (Nugari and Salvadori, 2003). Nevertheless, in order to improve the stability of our silica nanocontainers, we have encapsulated and confined only the 2-mercaptobenziothiazole (Ruggiero et al., 2019). The potential oxidation of the biocide induced by the TiO2 nanoparticles is expected to decrease thanks to the confinement into the silica containers that “protect” the biocide against oxidation. In this contest, we tested the addition of two different kinds of nanofillers: the commercial TiO2 nanoparticles and, for the first time, the silica nanocontainers (Si-NC and Si-MNP) loaded with MBT synthesized in our laboratory. The addition of these nanofillers to the TEOS-based coating formulation will improve the physic-chemical properties of the proposed product while providing a multifunctional composite coating with antifouling and self-cleaning properties.
In particular, TiO2 nanoparticles provide self-cleaning properties, while the two silica nanocontainers (hereafter labeled as Si-NC and Si-MNP) loaded with 2-mercaptobenzothiazole (MBT) will contribute to the antifouling action through a controlled release of the biocide. The first silica nanocontainer (Si-NC) shows a core-shell structure, and thus is called NanoCapsule. The second one (Si-MNP) consists instead of Mesostructured NanoParticles. Si-NC and Si-MNP nanocontainers have different size and different textural properties, which affect the loading capability and, consequently, the release rate of the MBT, as measured in water for 120 days (Ruggiero et al., 2019).
This study presents the design and the characterization of a composite coating, which may have application on outdoor stone monuments, while planning the necessary further tests on different lithotypes and biological communities. The incorporation of TiO2 and SiO2 nanocontainers into coating matrices is supposed to increase the quality of a multifunctional composite coating, as it combines the self-cleaning and antibacterial properties of TiO2, the antifouling and mechanical strength of SiO2 nanocontainers, and the controlled release of the encapsulated biocide. In order to select the best composition from a physic-chemical point of view, we compare a series of coatings by mixing in the starting sols different concentrations of nanoparticles.
Materials and Methods
In order to overcome the drawbacks of cracking of conventional TEOS-based materials, the proposed coatings was synthesized by combining three different strategies: (i) the addition of nanofillers, (ii) the addition of an non-ionic surfactant (n-octylamina) (González-Rivera et al., 2018), (iii) the modification of the elastic properties of the gel with Poly(dimethylsiloxane) hydroxy terminated (PDMS-OH) (Tamayo and Rubio, 2010; Zhang et al., 2010).
Preparation of Coatings
The coating matrix has been prepared as described in a recent article (Xu et al., 2012). In short, a typical starting sol has been prepared by mixing TEOS with ethanol, then different amounts of the two nanoparticles have been added, as summarized in Table 1. Technical grade TiO2 (by Sigma-Aldrich), with an average particle size of ~21 nm, has been used as a photocatalytic element into the proposed coating. Two different SiO2 nanocontainers (Si-NC and Si-MNP), synthesized in our laboratory, have been loaded with the 2-mercaptobenzothiazole (MBT, Sigma-Aldrich) and added to the coatings as antifouling agent. As reported in our previous work (Ruggiero et al., 2019), the Si-NC are core-shell structures with porous surface and a diameter of (128 ± 15) nm, while Si-MNP are mesoporous spherical nanoparticles with a diameter of (39 ± 4) nm.
Table 1. Contents of nanoparticles, expressed in percent volume of TEOS, in the multifunctional coatings.
In detail, the mixtures of TEOS and ethanol have been magnetically stirred (350 rpm) for 2 h at room conditions, prior to addition of the fillers (TiO2 and Si-NC or Si-MNP). Afterwards, distilled water and PDMS-OH have been added under vigorous stirring (500 rpm). After 2 min of magnetic stirring, the mixture has been sonicated for 10 min. The n-octylamine has been added to each sol and the mixture has been magnetically stirred for further 20 min. The mole ratios of each mixture are 1 TEOS/16 ETOH/10H2O/0.04 PDMS-OH/0.004 n-octylamine. TEOS (analytical grade reagent), n-octylamine and PDMS-OH (Mn = 550) have been purchased from Sigma-Aldrich and used without further purification.
After completing the synthesis, 500 μL of each sol has been cast in plastic Petri dishes of 1.7 cm diameter and 0.7 cm height. Dried xerogels have been obtained by simple exposure of the sols to laboratory conditions (T = 25°C and RH = 60%). The xerogels are labeled according to Table 1.
Preparation of Colloidal Silica Nanofillers: Si-NC and Si-MNP
The silica nanocapsules (Si-NC) have been synthesized through the dynamic self-assembly of TEOS and CTAB (Ruggiero et al., 2018, 2019, 2020). After the dissolution of the cationic surfactant (CTAB) in deionized water, an ammonia aqueous solution (25–28% V) has been added. Then, the biocide (MBT) has been dissolved in the organic solvent (diethyl ether) and this second solution has been mixed to the aqueous solution under constant magnetic stirring. Once the miniemulsion stabilized, 2 mL of TEOS have been slowly dripped. The reaction has proceeded at room temperature for 24 h (Ruggiero et al., 2019). The obtained product has been finally filtered under vacuum, repeatedly washed and dried at laboratory conditions.
The silica nanoparticles (Si-MNP) have been obtained starting from the sonication of the CTAB water solution and MBT for 30 min. At the same time, 100 mL of deionized water have been basified by NaOH aqueous solution (2.0 M) and then added to the first solution. After reaching the temperature of 80°C, the silica precursor (TEOS = 1.25 mL) has been dripped and the final mixture is kept under fast stirring for an additional 2 h. Finally, the Si-MNP have been filtrated and washed several times with water (Knezevic et al., 2017; Ruggiero et al., 2019).
The morphology of the nanosystems has been visualized by using a Field Emission Scanning Electron Microscope (FE-SEM, Sigma 300, Carl Zeiss SMT). Before the measurements, each sample has been sputtered with a thin layer of gold.
The BET surface area, the pore volume and pore size distribution have been characterized by the Nitrogen Physisoption at −196°C (Micromeritics Gemini V apparatus). Prior to the N2 adsorption, the sample has been degassed in flowing He at 150°C by using a Micromeritics Flow Prep accessory.
The infrared (IR) spectra of the coatings have been collected using a ThermoFisher Nicolet iS50 FTIR instrument in Attenuated Total Reflection (ATR) mode. The spectra were recorded, on the powdered samples, from 4,000 to 400 cm−1 at 4 cm−1 of resolution; 132 scans have been recorded.
Possible changes in the color of each coating, over time, were evaluated by using a solid reflection spectrophotometer (Chroma-Meter CR-200 Konica Minolta), working with the illuminant D65 and the observer at 2°. For each coating, three spot areas were analyzed and each spot area was measured in triplicate. CIE L*a*b* color space has been used and the variations of color have been quantified by the total color difference ΔE*, defined as: .
Results and Discussion
The coatings have been cast on plastic Petri dishes and examined after drying. First of all, their transparency has been investigated. Within the series shown in Table 2, dry coating (C) without nanoparticles is colorless and transparent but presents cracks. The addition of nanofillers into the sol changes the chromaticity of the final coatings: we notice a whitening of the charged coatings, with intensity depending on the type of nanoparticle and on their concentration. In particular, the addition of TiO2 nanoparticles induces a whitening of the coatings with decreased transparency (first raw of Table 2). The coatings with Si-MNP maintains a good level of transparency with a few cracks. From the optical point of view, the reasonable amount of nanoparticles is 0.1% (w/v) and the best systems seem to be the coatings added with Si-MNP. The smaller size of Si-MNP in comparison with Si-NC allows the dispersion of these nanofillers into the coating matrix, reducing the optical effects correlated with the formation of aggregates.
Table 2. Hybrid coatings after drying under laboratory conditions for different concentration of Si-NC/Si-MNP and TiO2.
In order to evaluate the effect of the nanofillers on the drying time of the gel, the weight loss of each sample has been measured. Figures 1A,B show the weight loss for the sols obtained by the addition of 0.1 and 0.2% w/v nanoparticles, respectively, over time (from 0 to 180 h), showing different drying rates.
Figure 1. Weight loss during the sol-gel process for the coating with 0.1% (A) and 0.2% (B) of fillers, respectively.
The sample without nanoparticles shows the faster drying rate: the weight reaches a plateau after 145 h. Generally, the addition of the nanofillers slows down noticeably the drying rate, indeed the coatings with 0.2% w/v of fillers show a lower weight loss than the coatings with 0.1% w/v of fillers.
Comparing the green and magenta curves in Figures 1A,B, we notice that the coating charged with the Si-NC has a faster drying rate compared to that charged with the smaller sized Si-MNP. This difference persists, although reduced, when also TiO2 particles are added; moreover, the presence of TiO2 particles makes the drying process even slower. These observations, in the light of what reported in the previous paragraph, suggest that the nanoparticles are stratified in the coating, according to their average dimension, with the Si-NC occupying the bottom layers of it. As a matter of fact, it can be verified by naked eye that the Si-NC tend to deposit at the bottom of the coating and thus have a limited effect on the drying rate. On the contrary, the TiO2 and/or Si-MNP, characterized by a smaller size than the Si-NC, seem to be more homogeneously dispersed in the coatings. This implies a slowing of the evaporation of the solvents and, consequently, a longer drying time of the coating. The presence of the nanofillers, distributed into the thickness of the coating, hinders this evaporation process by slowing the gelation and, consequently, the drying of the products. These results suggest that nanofillers interfere with the drying process. The coatings in this way penetrate into the porous substrate before the viscosity naturally increases upon the sol-gel transition (Milani et al., 2007). The most promising system seems to be once again the C_TiO2/Si-MNP.
SEM micrographs, collected with InLens detector on the upper surface of the coating, are compared in Table 3. All the coatings show a homogeneous morphology, consisting of microstructured folds, formed by uniform nanospheres of size of the order of 13–15 nm. These spherical microstructures do not depend on the size distribution and the morphology of the nanofillers. The SEM micrographs are quite similar one to each other and suggest that, during the deposition of the coatings into the petri dish, the nanofillers are preferably distributed through the thickness, or in some cases precipitate at the bottom and for these reasons are not visible on the surface.
Table 3. SEM micrographs at different magnification of the samples added with silica nanoparticles and silica nanoparticles and TiO2.
In order to investigate the textural properties of the hybrid coatings, we have measured the N2 adsorption-desorption isotherms of the most promising samples as the as far as the optical properties and drying rates are concerned, i.e., those containing 0.1% w/v of nanoparticles. The corresponding textural data are reported in Table 4.
Table 4. Surface area (S.A.), total pore volume (BJH P.V.), and pore size (BJH P.S.) of samples added with 0.1% of nanoparticles.
All the analyzed coatings show type IV adsorption isotherms, with a H1 hysteresis loop (see Figure 2A). This loop is more evident for the coatings loaded with TiO2 nanoparticles. These isotherm profiles suggest that the proposed coatings are a network of silica nanoparticles and that the fillers (Si-NC/Si-MNP and TiO2) are embedded and integrated into the porous structures (Milani et al., 2007).
Figure 2. (A) Nitrogen adsorption-desorption isotherms and (B) BJH pore size distribution for the hybrid coatings under study.
The BET surface area of the empty coating is 440 m2g−1, whereas for all sample with the addition of silica nanodevices and/or TiO2 nanoparticles, the BET surface area is around 480 m2g−1. In Figure 2B the peak of sample C is centered at 8.4 nm (BJH P.S.): the addition of Si-NC/Si-MNP and/or TiO2 reduces the pore size to a value between 5.8 and 6.4 nm, without substantially changing the total pore volume (0.67 ÷ 0.76 cm3g−1). These results suggest that the nanoparticles are integrated into the coating matrix, inducing an increase of BET surface area of about 10% and a decrease of the pore size of about 30% in comparison with the empty coating (C). The textural properties outline that the size of the two different silica fillers determines the properties of the coatings. When the TiO2 nanoparticles are added into the coating formulations, the differences in surface area between the coating loaded with Si-NC and Si-MNP are reduced, as shown in Table 4. Moreover, TiO2 nanoparticles induce an increase of the pore size in the coating loaded with Si-NC. This behavior suggests that the TiO2 nanoparticles work in synergy with the Si-NC, positively shaping the network structure. The Si-NC, because of their diameter, tend to precipitate and agglomerate during the sol-gel process. Otherwise, the Si-MNP shape the network modifying the porosity of the coating in comparison with the empty coating. For this reason, when the TiO2 nanoparticles are added to the coating with Si-MNP, the TiO2 is embedded in the porosity created by the Si-MNP, decreasing the pore diameter of the C_ TiO2/Si-MNP (Pinho and Mosquera, 2011).
Structural characterization of dried coatings has been performed by means of Fourier Transformed Infrared Spectroscopy. Figures 3–5 report the FTIR spectra of the coatings under study. The band corresponding to the Si–O–Si vibration (~1,050 cm−1), being the most intense, has been used for the normalization of the infrared spectra. The spectra (Figure 3) show a few bands that are unequivocally assigned to vibrations of an organic fraction, namely PDMS-OH. In particular, the band at 2,907 cm−1 corresponds to the symmetric stretching vibration of the C-H bonds, whereas the bands at 2,929 and 2,964 cm−1 are assigned to the asymmetric stretching vibration of the C-H bonds in CH2 and CH3 groups, respectively (Tamayo and Rubio, 2010; González-Rivera et al., 2018).
Figure 3. Infrared spectra of all the coatings loaded with the different nanoparticles in the range between 2,800 and 3,100 cm−1.
Figure 5. Detail of the Si-O-Si infrared band for the all coatings. The dot lines highlight the shift in the principal component from the empty coating to the coating with nanoparticles.
The symmetric bending vibration of CH3 groups in PDMS-OH contributes to a sharp band centered around 1,260 cm−1 (Zhang et al., 2010; Goffredo et al., 2019) in Figure 4. The band at ~790 cm−1 is related to the rocking modes of methyl groups and to the Si-C stretching in Si-(CH3)n, as reported in Figure 4 (Fidalgo et al., 2005; Johnson et al., 2013).
The copolymerization of Si-OH group of hydrolyzed TEOS and Si-OH of PDMS-OH is suggested by the band at 850 cm−1 (Tellez et al., 2003), as reported in Figure 4. This implies that during the synthesis PDMS-OH and TEOS interact, producing a homogeneous hybrid coating.
Several vibration modes of siloxane bonds contribute to the most intense band of the infrared spectra, in the region between 1,000 and 1,250 cm−1. In detail, the large band centered at 1,050 cm−1 is related to the asymmetric ν(Si–O–Si) stretching of the Si-O-Si network and it can be deconvoluted in four components: two longitudinal (LO) and two transverse (TO) optic modes. These components correspond to the four-membered (SiO)4 and the six-membered (SiO)6 arrangement of siloxane rings (Fidalgo and Ilharco, 2004). The position and the relative intensities of the LO and TO modes, according to the literature, change when chemical groups or organic molecules modify the silica network (Fidalgo and Ilharco, 2004).
In this contest, a shift of the Si-O-Si asymmetric stretching bands toward higher wavelengths in comparison with the empty coating is observed (from 1,042 to ~1,050 cm−1, Figure 5). These shifts are ascribed to the network deformation needed to accommodate the nanoparticles within the hybrid coating matrix, as summarized in Table 5. This phenomenology outlines that the distance between interacting species (e.g., the matrix and the nanoparticles) is reduced by the increase of the long-range Coulomb interactions. This finding is in agreement with the porosity decrease, suggested by N2 adsorption-desorption measurements (Li et al., 2013; Xu and Li, 2013).
As reported in Table 5, the position of the band at ~555 cm−1 (Figure 4), assigned to a coupled mode in four-member siloxane rings (SiO)4, moves from a maximum of 555 cm−1 to a minimum of 543 cm−1, depending on the species and concentration of dispersed nanoparticles (Tamayo and Rubio, 2010).
In order to evaluate the chromatic stability of the coating over time, the total color variation (ΔE*) of the samples has been measured at t = 01 and after 20, 40, and 60 days. All the coatings show a ΔE* below the perceivable threshold. The chromatic feature of the coating does not change over time, regardless of the type and quantity of nanoparticles added as filler. Such absence of chromatic variation will be further tested in direct application of these coatings on outdoor building surfaces, following the standards in the field. Future plans also include investigating the photocatalytic activity of the commercial TiO2 nanoparticles added to the coating, and the long-time effects on the stone properties after the treatment (e.g., color, porosity, and permeability changes).
In this work, we report the synthesis and the multi-analytical characterization of an innovative TEOS-based composite coating with the addition of two different silica nanofillers with antifouling properties. The best results in terms of optical properties (e.g., visual aspect and transparency), porosity and absence of cracking are obtained with the following nanofiller concentrations: 0.05% w/v of TiO2 and 0.05% w/v of Si-MNP or Si-NC loaded with MBT. The coatings with Si-MNP as filler show better properties than the coatings with Si-NC: indeed, the size of the filler shapes the behavior of the coatings, modifying not only the visual aspect, but also the drying rate. Further tests are in progress to check the interaction of this new coating with the most common substrates of interest for conservation of buildings and Cultural Heritage, as for instance its photocatalytic and biocidal activities and long-lasting efficacy on different lithotypes.
Data Availability Statement
The datasets generated for this study are available on request to the corresponding author.
LR made the synthesis, some characterizations, and drafted the manuscript. MI and LT made FT-IR analysis. MF made the colorimetric measurements. GC, MR, and AS coordinated the project and participated in the discussion of the results. All authors contributed to write the article and approved the submitted version.
Conflict of Interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
The authors acknowledge funding from Regione Lazio under the SUPERARE grant Gruppi di Ricerca n. F86C18000650005 and the ADAMO project n. B86C18001220002 of the Centre of Excellence at the Technological District for Cultural Heritage of Lazio (DTC). The Grant of Excellence Departments, MIUR (ARTICOLO 1, COMMI 314 - 337 LEGGE 232/2016) was also greatly acknowledged. SEM micrographs were obtained at LIME (Roma Tre University, Rome, Italy).
1. ^It has been considered as time 0, when the coating reached a constant weight.
Angulo-Olais, R., Illescas, J. F., Aguilar-Pliego, J., Vargas, C. A., and Haro-Pérez, C. (2018). Gel point determination of TEOS-based polymeric materials with application on conservation of cultural heritage buildings. Adv. Condens. Matter Phys. 2018:5784352. doi: 10.1155/2018/5784352
Bourges, A., Fehr, K. T., Simon, S., and Snethlage, R. (2008). Correlation between the micro-structure and the macroscopic behaviour of sandstones. Restor. Build. Monum. Int. J. 14, 157–166. doi: 10.1515/rbm-2008-6214
Caneva, G., and Tescari, M. (2017). “Stone biodeterioration: treatments and preventive conservation,” in Proceedings of International Symposium of Stone Conservation, Conservation Technologies for Stone Cultural Heritages: Status and Future Prospects (Seoul).
Colangiuli, D., Calia, A., and Bianco, N. (2015). Novel multifunctional coatings with photocatalytic and hydrophobic properties for the preservation of the stone building heritage. Constr. Build. Mater. 93, 189–196 doi: 10.1016/j.conbuildmat.2015.05.100
Fidalgo, A., Ciriminna, R., Ilharco, L. M., and Pagliaro, M. (2005). Role of the alkyl-alkoxide precursor on the structure and catalytic properties of hybrid sol-gel catalysts. Chem. Mater. 17, 6686–6694. doi: 10.1021/cm051954x
Gherardi, F., Colombo, A., D'Arienzo, M., Di Credico, B., Goidanich, S., Morazzoni, F., et al. (2016). Efficient self-cleaning treatments for built heritage based on highly photo-active and well-dispersible TiO2 nanocrystals. Microchem. J. 126, 54–62. doi: 10.1016/j.microc.2015.11.043
Goffredo, G. B., Accoroni, S., and Totti, C. (2019). “Nanotreatments to inhibit microalgal fouling on building stone surfaces,” in Nanotechnology in Eco-efficient Construction, 2nd Edn (Woodhead Publishing), 619–647. doi: 10.1016/B978-0-08-102641-0.00025-6
González-Rivera, J., Iglio, R., Barillaro, G., Duce, C., and Tinè, M. R. (2018). Structural and thermoanalytical characterization of 3D Porous PDMS foam materials: the effect of impurities derived from a sugar templating process. Polymers 10:616. doi: 10.3390/polym10060616
Illescas, J. F., and Mosquera, M. J. (2011). Surfactant-synthesized PDMS/silica nanomaterials improve robustness and stain resistance of carbonate stone. J. Phys. Chem. C, 115, 14624–14634. doi: 10.1021/jp203524p
Jackson, M. D., Marra, F., Hay, R. L., Cawood, C., and Winkler, E. M. (2005). The judicious selection and preservation of tuff and travertine building stone in ancient Rome. Archaeometry 47, 485–510. doi: 10.1111/j.1475-4754.2005.00215.x
Jämsä, S., Mahlberg, R., Holopainen, U., Ropponen, J., Savolainen, A., and Ritschkoff, A.-C. (2013). Slow release of a biocidal agent from polymeric microcapsules for preventing biodeterioration. Progress Organic Coat. 76, 269–276. doi: 10.1016/j.porgcoat.2012.09.018
Johnson, L. M., Gao, L., Shields, C. W., Smith, M., Efimenko, K., Cushing, K., et al. (2013). Elastomeric microparticles for acoustic mediated bioseparations. J. Nanobiotechnol. 11:22. doi: 10.1186/1477-3155-11-22
Kapridaki, C., and Maravelaki-Kalaitzaki, P. (2013). TiO2-SiO2-PDMS nano-composite hydrophobic coating with self-cleaning properties for marble protection. Progress Organ. Coat. 76, 400–410. doi: 10.1016/j.porgcoat.2012.10.006
Kim, E. K., Won, J., Do, J.-y., Kim, S. D., and Kang, Y. S. (2009). Effects of silica nanoparticle and GPTMS addition on TEOS-based stone consolidants. J. Cult. Herit. 10, 214–221. doi: 10.1016/j.culher.2008.07.008
Knezevic, N. Z., Mauriello Jimenez, C., Albino, M., Vukadinovic, A., Mrakovic, A., Illes, E., et al. (2017). Synthesis and characterization of core-shell magnetic mesoporous silica and organosilica nanostructures. MRS Adv. 2, 1037–1045. doi: 10.1557/adv.2017.69
La Russa, M. F., Ruffolo, S. A., Rovella, N., Belfiore, C. M., Palermo, A. M., Guzzi, M. T., et al. (2012). Multifunctional TiO2 coatings for cultural heritage. Prog. Org. Coat. 74, 186–191. doi: 10.1016/j.porgcoat.2011.12.008
Lettieri, M., Colangiuli, D., Masieri, M., and Calia, A. (2019). Field performances of nanosized TiO2 coated limestone for a self-cleaning building surface in an urban environment. Build. Environ. 147, 506–516. doi: 10.1016/j.buildenv.2018.10.037
Li, D., Xu, F., Liu, Z., Zhu, J., Zhang, Q., and Shao, L. (2013). The effect of adding PDMS-OH and silica nanoparticles on sol–gel properties and effectiveness in stone protection. Appl. Surf. Sci. 266, 368–374. doi: 10.1016/j.apsusc.2012.12.030
Maia, F., Silva, A. P., Fernandes, S., Cunha, A., Almeida, A., Tedim, J., et al. (2015). Incorporation of biocides in nanocapsules for protective coatings used in maritime applications. Chem. Eng. J. 270, 150–157. doi: 10.1016/j.cej.2015.01.076
Milani, C., Velo-Simpson, M. L., and Scherer, G. W. (2007). Particle-modified consolidants: a study on the effect of particles on sol-gel properties and consolidation effectiveness. J. Cult. Herit. 8, 1–6. doi: 10.1016/j.culher.2006.10.002
Munafò, P., Goffredo, G. B., and Quagliarini, E. (2015). TiO2-based nanocoatings for preserving architectural stone surfaces: an overview. Constr. Build. Mater. 84, 201–218. doi: 10.1016/j.conbuildmat.2015.02.083
Nugari, M. P., and Salvadori, O. (2003). “Biocides and treatment of stone: limitations and future prospects,” in Art, Biology, and Conservation: Biodeterioration of Works of Art, eds R. J. Koestler, V. H. Koestler, A. Elena Charola, and F. E. Nieto-Fernandez (New York, NY: The Metropolitan Museum of Art), 518–535.
Pinho, L., Elhaddad, F., Facio, D. S., and Mosquera, M. J. (2013). A novel TiO2-SiO2 nanocomposite converts a very friable stone into a self-cleaning building material. Appl. Surf. Sci. 275, 389–396. doi: 10.1016/j.apsusc.2012.10.142
Pinna, D., Salvadori, B., and Galeotti, M. (2012). Monitoring the performance of innovative and traditional biocides mixed with consolidants and water-repellents forthe prevention of biological growth on stone. Sci. Total Environ. 423, 132–141. doi: 10.1016/j.scitotenv.2012.02.012
Quagliarini, E., Bondioli, F., Goffredo, G. B., Licciulli, A., and Munafò, P. (2012). Smart surfaces for architectural heritage: preliminary results about the application of TiO2-based coatings on travertine. J. Cult. Herit. 13, 204–209. doi: 10.1016/j.culher.2011.10.002
Quagliarini, E., Bondioli, F., Goffredo, G. B., Licciulli, A., and Munafò, P. (2013). Self-cleaning materials on architectural heritage: compatibility of photo-induced hydro-philicity of TiO2 coatings on stone surfaces. J. Cult. Herit. 14, 1–7. doi: 10.1016/j.culher.2012.02.006
Ruffolo, S. A., De Leo, F., Ricca, M., Arcudi, A., Silvestri, C., Bruno, L., et al. (2017). Medium-term in situ experiment by using organic biocides and titanium dioxide for the mitigation of microbial colonization on stone surfaces. Int. Biodeteriorat. Biodegrad. 123, 17–26 doi: 10.1016/j.ibiod.2017.05.016
Ruggiero, L., Bartoli, F., Fidanza, M. R., Zurlo, F., Marconi, E., Gasperi, T., et al. (2020). Encapsulation of environmentally-friendly biocides in silica nanosystems for multifunctional coatings. Appl. Surf. Sci. 514:145908. doi: 10.1016/j.apsusc.2020.145908
Ruggiero, L., Crociani, L., Zendri, E., El Habra, N., and Guerriero, P. (2018). Incorporation of the zosteric sodium salt in silica nanocapsules: synthesis and characterization of new fillers for antifouling coatings. Appl. Surf. Sci. 439, 705–711. doi: 10.1016/j.apsusc.2017.12.228
Ruggiero, L., Di Bartolomeo, E., Gasperi, T., Luisetto, I., Talone, A., Zurlo, F., et al. (2019). Silica nanosystems for active antifouling protection: nanocapsules and mesoporous nanoparticles in controlled release applications. J. Alloys Compd. 798, 144–148. doi: 10.1016/j.jallcom.2019.05.215
Salazar-Hernández, C., Zárraga, R., Alonso, S., Sugita, S., Calixto, S., and Cervantes, J. (2009). Effect of solvent type on polycondensation of TEOS catalyzed by DBTL as used for stone consolidation. J. Sol Gel Sci. Technol. 49, 301–310. doi: 10.1007/s10971-008-1879-9
Seven, O., Dindar, B., Aydemir, S., Metin, D., Ozinel, M., and Icli, S. (2004). Solar photocatalytic disinfection of a group of bacteria and fungi aqueous suspensions with TiO2, ZnO and Sahara Desert dust. J. Photochem. Photobiol. Chem. 165, 103–107. doi: 10.1016/j.jphotochem.2004.03.005
Trojer, M. A., Nordstierna, L., Bergek, J., Blanckc, H., Holmberg, K., and Nydén, M. (2015). Use of microcapsules as controlled release devices for coatings. Adv. Coll. Interface Sci. 222, 18–43. doi: 10.1016/j.cis.2014.06.003
Wen, J., and Mark, J. E. (1995). Sol-Gel preparation of composites of poly(dimethylsiloxane) with SiO2 and SiO2/TiO2, and their mechanical properties. Polymer J. 27, 492–502. doi: 10.1295/polymj.27.492
Xu, F., and Li, D. (2013). Effect of the addition of hydroxyl-terminated polydimethylsiloxane to TEOS-based stone protective materials. J. Sol Gel Sci. Technol. 65, 212–219. doi: 10.1007/s10971-012-2926-0
Xu, F., Li, D., Zhang, Q., Zhang, H., and Xu, J. (2012). Effects of addition of colloidal silica nanoparticles on TEOS-based stone protection using n-octylamine as catalyst. Progress Organ. Coat. 75, 429–434. doi: 10.1016/j.porgcoat.2012.07.001
Zárraga, R., Cervantes, J., Salazar-Hernandez, C., and Wheeler, G. (2010). Effect of the addition of hydroxyl-terminated polydimethylsiloxane to TEOS-based stone consolidants. J. Cult. Heritage 11, 138–144. doi: 10.1016/j.culher.2009.07.002
Keywords: multifunctional coating, TiO2, SiO2 nanocontainers, antifouling, biocide
Citation: Ruggiero L, Fidanza MR, Iorio M, Tortora L, Caneva G, Ricci MA and Sodo A (2020) Synthesis and Characterization of TEOS Coating Added With Innovative Antifouling Silica Nanocontainers and TiO2 Nanoparticles. Front. Mater. 7:185. doi: 10.3389/fmats.2020.00185
Received: 28 November 2019; Accepted: 20 May 2020;
Published: 23 June 2020.
Edited by:Miloslav Peka, Brno University of Technology, Czechia
Reviewed by:Marián Lehocký, Tomas Bata University in Zlín, Czechia
Mauro La Russa, University of Calabria, Italy
Copyright © 2020 Ruggiero, Fidanza, Iorio, Tortora, Caneva, Ricci and Sodo. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Ludovica Ruggiero, email@example.com