Prerpints.org logo
Preprint
Review

TiO2-Based Photocatalytic Building Material for Air Purification in Sustainable and Low-Carbon Cities: A Review

Altmetrics

Downloads

272

Views

104

Comments

0

A peer-reviewed article of this preprint also exists.

Submitted:

18 August 2023

Posted:

21 August 2023

You are already at the latest version

Alerts
Abstract
TiO2-based building materials have air purification, auto-cleaning and sterilization functions, and these innovative green building materials have great potential for energy-saving and emission reduction applications in the future. However, there are still great challenges in improving photocatalytic efficiency and stability from laboratory to practical applications. In recent years, researchers have done a lot of work to improve the efficiency and stability of TiO2-based building materials. This paper briefly discussed the air purification principle by photocatalytic building, and the preparation techniques of TiO2-based building materials and the strategies to improve the efficiency of TiO2. Moreover, this paper has outlined the key factors that affect the photocatalytic building performance in practical applications, and analyzed the limitations and future development trends. Finally, we proposed some suggestions for further research on photocatalytic buildings and its application in practice, aiming to provide an efficient reference for developing highly efficient and stable photocatalytic building materials. The aim of this paper is to provide effective guidance for the application of TiO2-based photo-catalysts in the field of green buildings, helping to develop more efficient and stable low-carbon buildings for the development of sustainable cities.
Keywords: 
Subject: Environmental and Earth Sciences  -   Environmental Science

1. Introduction

In recent years, human activities have caused a significant release of gaseous pollutants into the environment. These pollutants include volatile organic compounds (VOCs), nitrogen oxides (NOx), sulfur oxide (SOx) and particulate matter, which have resulted in severe environmental issues [1]. These harmful substances can negatively impact human health, compromising the immune system and leading to conditions such as skin diseases, asthma, chronic respiratory diseases, cardiovascular diseases, and cancer. Shockingly, air pollution has been linked to approximately 26,000 to 48,000 deaths in European countries alone [2]. In addition, these pollutants can also negatively impact plant growth, water and soil quality, and lead to ecosystem collapse, as well as contribute to climate change and global warming issues [3]. Given the gravity of the situation, extensive research and environmental remediation measures are currently underway to address these concerns.
photocatalytic technology has been widely recognized for its potential to treat air pollutants [4]. This innovative technology works by converting harmful gases into harmless substances, effectively reducing the harmful impacts of air pollution [5]. Unlike conventional treatment methods, photocatalytic technology has low energy consumption and secondary pollution, in addition, photocatalysts are usually renewable and low-toxicity, which provide better environmental sustainability [6]. Additionally, photocatalysis has a wide range of applicability and can be used to treat a variety of pollutants, including nitrogen dioxide, volatile organic compounds, formaldehyde, benzene, etc. [4].
Based on these advantages, photocatalytic technology has been widely used in various fields, such as construction materials, air purifiers, and wastewater treatment. Especially in the field of building materials, photocatalytic building materials have become a new type of building material, and their potential in mitigating air pollution has received widespread attention [7]. Photocatalytic building materials are capable of converting harmful gases, such as VOCs, NOx and SOx, into harmless substances through photocatalytic reactions. Additionally, they can decompose bacteria, viruses, and other microorganisms, improving indoor air quality. In recent years, many countries and regions have started to use photocatalytic building materials to combat air pollution. For example, in Japan, photocatalytic building materials accounted for 60% of the photocatalytic market sales in 2003 [7]. They have developed a range of photocatalytic building materials by adding TiO2 nanoparticles to glass, ceramics, and mortar to achieve photocatalytic functions of building materials, such as self-cleaning, antibacterial, and air purification [8]. In China, many high-rise buildings and public places, including hospitals, schools, outdoor buildings, and roads, have begun using photocatalytic building materials to purify air and improve the indoor environment.
TiO2 has received widely attention due to its simple preparation process, high stability, low toxicity and chemical inertness. [9]. TiO2-based photocatalytic building materials exhibit excellent photocatalytic performance and stability, effectively converting harmful substances in the air into harmless substances under light irradiation. Thus, their applications are of significant importance. Many methods have been studied for preparing TiO2 nanoparticles, including sol-gel, hydrothermal [10], vapor phase deposition [11], and others [12]. All of these methods can produce nanoscale TiO2 particles, thereby improving the specific surface area and reaction activity of photocatalysts. In addition, photocatalytic building materials can be prepared by loading TiO2 onto porous materials, which can improve the stability and mechanical properties of the photocatalytic materials and increase their reactivity [13, 14]. This preparation method is also widely used in the preparation of catalytic materials.
In recent years, TiO2-based photocatalytic building materials have been widely investigated [14, 15]. However, TiO2 has a low photocatalytic efficiency due to the fact that only 4% of UV light can be absorbed, additionally, the fast rate of light-induced electron-hole pair complexation leads to the low photocatalytic efficiency of ordinary TiO2, which greatly limits its practical applications. In order to improve the TiO2 photocatalytic efficiency, researchers have employed various strategies, such as surface chemical structure modification and loading onto nanomaterials to form composites [16]. Moreover, other factors need to be considered in the preparation of TiO2-based building materials, including the size of catalyst nanoparticles, structural stability, light-absorbing properties, catalytic activity, and mechanical strength, to ensure their long-term and effective operation. What is more, TiO2-based building materials in the actual operation are practically optimized and adjusted for specific conditions, such as the angle of installation of the building materials, light conditions, pollutant types, concentrations, rainfall, etc., to achieve the best photocatalytic effect.
This paper reviewed recent advances in TiO2-based building materials for air purification. We discussed various preparation techniques for producing TiO2-based building materials, including sol-gel, hydrothermal, spray-drying, anodic oxidation, and microwave-assisted methods. In addition, to solve the problems of aggregation of TiO2 nanomaterials in suspension, poor adsorption ability, wide band gap, and high recombination rate, we discussed the strategies to improve the catalytic efficiency of TiO2-based building materials. Finally, based on practical application cases, we discussed the effectiveness of photocatalytic building materials in practical applications, the key factors affecting the catalytic efficiency as well as the limitations and future development trends of photocatalytic building materials.The purpose of this paper is to provide an effective reference for the development of highly efficient and stable photocatalytic building materials, and to improve the public's awareness of green buildings.

2. Working Principles and Properties of TiO2-Based Photocatalytic Building Materials

TiO2 photocatalytic materials have received much attention from researchers in recent years as an emerging building material. In the construction field, TiO2-based building materials are widely used for air purification, deodorisation and sterilisation due to their unique photocatalytic properties. This part will focus on the working principle of photocatalytic building materials for pollution and carbon reduction.

2.1. The Basic Principle Mechanism of Photocatalysts

Semiconductor materials are crystals orderly arranged by a large number of atoms or ions, and the dense accumulation of atoms allows the energy-matched adjacent atomic orbits to overlap each other and form different energy bands. The semiconductor material has two energy bands, empty high-energy conduction band (CB) and full-of-low-energy electron valence band (VB), the band gay which is between CB and VB is the forbidden band [17]. As shown in Figure 1 the principle of semiconductor photocatalysis involves the absorption of light by a semiconductor, the VB electron transition to the conduction band of the semiconductor generating photo-generated electron-hole pairs, the photo-generated charge carriers then migrate to the semiconductor surface and transfer to the adsorbed material, which initiates the subsequent oxidation or reduction reactions.
The reaction of electron-hole composite reaction is interdependent and competitive with electron-hole reaction with adsorbed material on the catalyst surface throughout the photocatalytic reaction. The total charge efficiency of the interface charge migration is determined by two important competitive processes: (1) the competition of the carrier complex and capture; (2) the competition between the captured carrier composite and interface charge migration. Interface transfer of captured carriers is a rate-determining step in the photocatalytic process that determines the quantum efficiency of TiO2 photocatalysis.
In the process of electron-hole pair involved in oxidation or reduction reaction, the superoxygen radical (O•-2) was generated by photoelectron reacted with O2, while the hydroxyl radical (OH•) was produced by the photohole reacted with H2O, these reaction oxidation substances (ROS) decomposed various pollutants in atmosphere. The generation of ROS in the photocatalysis process can be depicted as follows:
TiO2 + hv → TiO2（e−CB + h+VB）
TiO2（h+VB） + H2O→ TiO2 + H+OH•
TiO2（h+VB） + OH-→ TiO2 + OH•
TiO2（e−CB） + O2→ TiO2 + O•-2
O•-2 + H+→ HO•2
HO•2 + HO•2 → H2O2 + O2
TiO2（e−CB） + H2O2 → OH- + OH•
The generation ROS further reacted with the target contaminants, and finally mineralized contaminants into non-toxic substances.

2.2. The Mechanism of Photocatalysts for Air Purification and Deodorisation

The presence of air pollutants such as VOCs, NOx and SOx pose a risk to the environment and human health that cannot be ignored. In the following, we will discuss how TiO2-based photocatalytic building materials work in degrading some of these gaseous pollutants.
VOCs is the mainly indoor pollutants which is emitted from various sources, such as building and combustion materials, electronic equipment, coal or oil combustion, indoor fuel gas, consumer products and smoking [3]. These pollutants will damage to the sensory system of human beings, and cause various serious acute irritation and chronic disease, especially for the workers who long-term exposure to air pollutants circumstances and the elderly people and young children with low immunity [19]. Photocatalytic oxidation technology is a promising method for VOCs degradation, it could rapidly degrade the organic pollutants in atmosphere through hydroxyl radicals and superoxygen radicals which produced by photogenerated electron-hole pairs reacted with O2 or H2O [19]. The mechanism of VOCs degradation by photocatalysis can be depicted as follows:
HCHO + •OH → •CHO + H2O
•CHO + •OH→ HCOOH
•CHO + O2•− → HCO3− +H+→ HCOOOH + HCHO → HCOOH
HCOOH− + H+ → HCOO− + •OH → H2O + CO2•−
HCOO− + h+vb → H+ + CO•
CO2•− + •OH + h+vb → CO2
As can be seen from equation 8 to 13, active substances such as •OH, O2•− and electron holes attack the organic matters and mineralize the organic matters into CO2 to improving the air quality.
NOx, which mainly includes NO and NO2, commonly derived from anthropogenic activities, such as exhaust gases which from traffic and the combustion of fossil fuels in industries, leading to various environmental problems such as photochemical smog, acid rain, haze and so on [20]. According to reports, the greenhouse effect of NO2 is 200~300 times that of CO2 which is extremely harmful to the environment [21]. TiO2-based Photocatalysis is a environmental friendly technology which could remove low concentration NOx under solar light or UV light irradition. The photocatalytic degradation of NOx mainly uses the active substances produced by photocatalysts to convert NOx to NO3- to achieve the purpose of reducing NOx. The reaction process can be depicted as follows:
NO + •OH→HNO2
HNO2 + •OH→NO2 + H2O
NO2 + •OH→HNO3
NO + O2•− →NO3−
2NO + O2•− + 3e− → 2NO2
NO2 + 2OH− →2NO3− + NO + H2O
As shown in equations 14 through 19, •OH and O2•− convert NOx to nitrate ions, reducing the concentration of NOx in the air.
The SOx is primarily SO2, which mainly produced by the combustion of sulfur-containing fossil fuels，are extremely harmful for human beings and ecosystems. According to report, SOx in the air are one of the causes of acid rain formation which could erode building surfaces, accelerate materials aging, grow crops and change the acid and alkaline of the soil [22]. TiO2-based photocatalysts can effectively degrade SOx under solar or UV light excitation. The mechanism of photocatalytic degradation of SO2 as follows:
SO2 + •OH → HSO−
SO2 + O2•− → SO42−
SO2 + h+vb + H2O→H2SO4 + H+
As shown in the equation 20 to 21, SO2 was transform into SO42− through free radicals and photogenerated holes.

2.3. The Mechanism of Photocatalysts for Disinfection

Airborne bacteria and viruses are a major source of disease and therefore require effective disinfection and sterilisation measures. In recent years, photocatalytic technology has been widely used in the field of disinfection. It works by producing ROS through photocatalytic materials under light excitation, thus blocking the autosensing signal of colonies and affecting the formation of biofilms to attack bacteria and viruses. As shown in the Figure 2a, ROS attack the bacteria, causing the cell membrane to rupture, ROS enter the cell and attack its intracellular components such as ATP SOD CAT, leading to a reduction in the concentration of the corresponding substances, and ROS also attack DNA, causing it to break. The loss of cytoplasm and the cis-damage of DNA lead to cells that are unable to repair themselves and eventually become fragmented under prolonged light exposure. Similarly, As shown in the Figure 2b, ROS have the same effect on viruses, acting on the RNA of the virus, causing it to break and inactivate the virus.

3. The Study Status of TiO2-Based Photocatalytic Building Materials

In recent years, there has been significant progress in the field of TiO2 photocatalytic construction. TiO2 has garnered considerable attention as a photocatalyst for organic pollutant degradation because of its chemical stability, low cost, and compatibility with most building materials [24]. In fact, studies have shown that TiO2 can react with metal oxides in cement to form stable compounds, such as CaTiO3, which possesses a band gap energy of 3.5 eV and an isoelectric point pH of 3 [25]. Table 1 shows some of the studies on the addition of TiO2-based nanomaterials to building materials to remove airborne pollutants respectively.
Researchers have developed various TiO2 catalysts with different morphological designs, including nanoparticles, nanotubes, hollow fibers, and mesoporous materials, to improve their photocatalytic performance [26]. Recent studies have extensively investigated the relationship between TiO2 crystallinity, crystal phase, crystal size, surface area, pore structure, pore size, and its photocatalytic and adsorption capacities [27]. The use of photocatalysts with building materials began in the early 1990s and since then TiO2-modified building materials have been used for a variety of purposes such as environmental pollution remediation, self-cleaning and self-disinfection [7]. TiO2 is a versatile material that can be used both as a photocatalyst and as a structural component. This has led to its widespread use in a variety of building materials, both for exteriors and interiors, including cement mortars, exterior wall tiles, paving blocks, glass, and PVC fabrics. TiO2-based photocatalytic building materials offer significant advantages and have great potential for a wide range of applications. These materials are compatible with conventional building materials such as cement, without altering any of their original properties. Additionally, they are effective even in ambient atmospheric environments with weak solar radiation [28]. A growing number of research findings proved the viability of the technology in the construction industry. Cárdenas et al. [29] conducted a study demonstrating that TiO2 nanoparticles are highly efficient photocatalysts in cement paste, and the photocatalytic activity increased proportionally with the percentage of TiO2 addition. Their findings revealed that cement paste containing 5% TiO2 exhibited the highest NOx removal rate. Additionally, Cheung et al. [30] developed photocatalytic building materials by combining TiO2 with local waste materials, such as cement, crushed glass, and sand, for NO degradation. Intriguingly, they discovered that lower density materials with higher porosity were more effective for NO degradation when mixed with less cement. Furthermore, Demeestere et al. [31] reported that roofing tiles and corrugated sheets containing TiO2 displayed remarkable photocatalytic activity by effectively removing toluene. They suggested that incorporating TiO2 into building materials for photocatalytic materials has the potential to significantly contribute to air purification.
In summary, TiO2 shows great promise for photocatalytic building applications due to its high photocatalytic activity, compatibility with traditional building materials and effectiveness in ambient atmospheric environments under weak solar radiation.. However, the efficiency of low-cost TiO2-based building materials remains unsatisfactory, especially under visible-light or solar-light irradiation due to the wide band gap of TiO2 (3.2 eV). Consequently, the development of narrow band gap and efficient photocatalysts is essential for practical applications.

4. Preparation of TiO2 Photocatalytic Building Materials

The production of TiO2 photocatalytic construction materials involves several stages, such as selecting the suitable TiO2 nanoparticles, fabricating the construction materials, and integrating the nanoparticles into the materials. Several approaches have been documented in literature for the creation of TiO2 photocatalytic construction materials, which include sol-gel, hydrothermal, and spray-drying methods.

4.1. Sol-Gel Method

The sol-gel technique is a widely employed method for creating TiO2 photocatalytic construction materials. This approach involves the synthesis of TiO2 nanoparticles by hydrolyzing the titania salt in a solvent and incorporating a stabilizer to prevent the aggregation of the nanoparticles. The ensuing solution is then combined with a construction material such as concrete or gypsum and allowed to dry. This method results in nanoparticles that are uniform in size and shape, thereby increasing the photocatalytic efficiency of the construction material.
The sol-gel technique boasts a significant benefit in its cost-effectiveness, as well as its capacity to maintain precise control over the chemical composition of its products by employing a low reaction temperature. Furthermore, the sol-gel method yields nanoparticles that are uniform in both size and shape, thereby intensifying the photocatalytic activity of the building material. Nonetheless, this method is relatively slow and may produce nanoparticles that lack stability [43].
It is worth noting that the sol-gel method can be used as a forming material in the manufacture of ceramics and can be used as an intermediate between metal oxide films in a variety of applications. Although the sol-gel method is a cost effective way of producing nanoparticles of uniform size and shape that can enhance the photocatalytic activity of building materials, it is a relatively slow process and the resulting nanoparticles can have low stability.

4.2. Hydrothermal Method

The hydrothermal method involves the synthesis of TiO2 nanoparticles in an aqueous solution under high pressure and temperature. In this method, the precursor solution is placed in a sealed vessel and heated to a high temperature, which promotes the formation of nanoparticles. The resulting nanoparticles are then mixed with the building material and allowed to dry. The advantage of the hydrothermal method is that it produces nanoparticles with a high surface area, which enhances the photocatalytic activity of the building material.
The hydrothermal method is one of the most commonly used methods for the synthesis of TiO2 nanostructures. It has several advantages over other methods, such as appropriate crystallization temperatures, environmental friendliness, controlled reaction conditions, low energy consumption and low cost. Hydrothermal synthesis is a simple and effective method for the synthesis of TiO2 nanostructures. It involves the use of alkali solutions such as lithium hydroxide, sodium hydroxide and potassium hydroxide as solvents [44]. The concentration of the base solution used has an effect on the crystallinity, agglomeration ratio, particle size and specific surface area of the resulting TiO2 phase [44]. NaOH is the most commonly used solvent in material preparation techniques [45]. However, the use of other alkali solutions (e.g. KOH) has been shown to affect the morphology and crystal structure of TiO2 nanostructures obtained by hydrothermal methods [45]. The use of different TiO2 precursors as non-homogeneous photocatalysts can also affect the morphology of TiO2 nanostructures obtained by hydrothermal methods [46]. The photocatalytic performance of the synthesised TiO2 products at different NaOH concentrations was evaluated by the toxic NOx gas removal efficiency. The nanostructured TiO2 samples prepared at higher NaOH concentrations showed higher nitrogen removal efficiency than the TiO2-P25 precursor [47]. In summary, the hydrothermal method is an effective way to synthesise TiO2 nanoparticles with high specific surface area, enhancing the photocatalytic activity of the building materials. The use of different alkali solutions and TiO2 precursor pairs can both affect the morphology and crystal structure of the materials. This affects the efficiency of TiO2-based building materials in degrading pollutants.

4.3. Spray-Drying Method

The spray-drying method involves the synthesis of TiO2 nanoparticles by spraying a TiO2 precursor solution into a hot drying chamber. The hot air evaporates the solvent, leaving behind the nanoparticles, which are then collected and mixed with the building material. This method has several advantages:
  • Production of nanoparticles with a narrow size distribution to enhance the photocatalytic activity of building materials.
  • An efficient and scalable method for producing nanoparticles with a uniform distribution.
  • Allows the phase composition, crystal size and surface area of nanoparticles to be adjusted.
Although spray drying is an efficient and scalable method for the synthesis of TiO2 nanoparticles, it has a number of limitations. One of the main disadvantages is that the method is highly dependent on the nature of the parent ion solution, such as its viscosity, surface tension and concentration. If the precursor solution is not properly formulated, the resulting nanoparticles may be of poor quality or not form at all [48]. In addition, the method requires a large amount of energy to operate, which can increase production costs.
In conclusion, the preparation of TiO2 photocatalytic building materials involves the selection of appropriate nanoparticles, the preparation of the building materials, and the incorporation of the nanoparticles into the materials. Various methods have been reported in the literature for the preparation of TiO2 photocatalytic building materials, including sol-gel, hydrothermal, and spray-drying methods. These methods produce nanoparticles with different properties, which can affect the photocatalytic activity of the building materials. Therefore, the selection of an appropriate method depends on the specific requirements of the application.

4.4. Anodic Oxidation Method

The anodic oxidation technique represents an innovative method to generate photocatalytic building materials with TiO2. This approach entails electrochemically oxidizing titanium metal or alloy in an electrolyte solution, which forms a porous TiO2 layer on the surface. This resulting layer of TiO2 can serve as a coating for a diverse range of construction materials, including but not limited to steel, aluminum, and glass. As a result of this method, TiO2 nanoparticles are produced, which possess high porosity and surface area, as well as a morphology and crystallinity that can be adjusted, ultimately enhancing the photocatalytic efficacy of the building material [49].
The anodic oxidation method presents certain advantages over alternative techniques, including a straightforward and eco-friendly process, direct formation of TiO2 on the substrate without any binder, and a robust adhesion and durability of the coating. Nevertheless, this method is not without challenges, such as the necessity for high-quality titanium metal or alloy as the anode material, the complexity of maintaining uniformity and thickness of the TiO2 layer, and the potential corrosion of the substrate by the electrolyte solution [50].

4.5. Microwave-Assisted Method

The microwave-assisted method is a modern technique for synthesizing TiO2 nanoparticles and integrating them into construction materials. This approach employs microwave radiation to heat and activate the titanium precursor and solvent in an enclosed vessel, producing TiO2 nanoparticles. These particles are subsequently blended with a construction material such as cement or ceramic and cured under suitable conditions. The outcome of this method is TiO2 nanoparticles with a high level of crystallinity and purity, as well as a narrow size distribution and a spherical shape, ultimately enhancing the photocatalytic efficacy of the construction material [51].
The microwave-assisted method has several benefits over the other methods, such as a rapid and homogeneous heating process, a low energy consumption and environmental impact, and a facile control over the reaction parameters and product properties. However, this method also has some limitations, such as the requirement of special equipment and microwave-absorbing materials, the possible formation of hot spots and thermal gradients in the reaction vessel, and the difficulty in scaling up for industrial applications.

5. Strategies for Improve TiO2 Photocatalytic Efficiency

TiO2 which is low-cost and environmentally friendly is a vital and widely used photocatalyst for preparing photocatalytic building materials. Although the great majority of photocatalytic building materials use TiO2, there are three main problems must be addressed: (1) tendency to rapidly aggregation in a suspension, owning to the diameters of TiO2 particles is relatively small, considerably decreasing its effective surface area and catalytic efficiency, and the photocatalytic oxidation reaction rate of TiO2 was restricted owing to its poor adsorptive power; (2) the wide band gap (>3.0 eV) of TiO2 restricts its utilization of visible light in the solar spectrum; (3) the high recombination rate of the electron-hole pair in TiO2 restricts its photocatalytic ability.
To broaden the optical response wavelength of TiO2-based photocatalysts, enhance the photocatalytic efficiency of TiO2-based photocatalyst. According to present studies about TiO2-based photocatalysts, this section mainly reviewed the strategies which focus on addressing the problem of TiO2 aggregation and broadening the light wavelength response and improving the photocatalytic performance of TiO2 to provide a reliable basis for the future development of TiO2-based photocatalyst and promote the large-scale industrial application of photocatalytic technology.

5.1. Strategies for REDUCING aggregation of TiO2

TiO2 nanoparticles within smaller particle diameter size have a high specific surface area and more active site could accelerated photocatalytic reaction rate of TiO2-based photocatalysts [52]. However, for its relatively small diameter size TiO2 is prone to aggregation in the suspension caused the photocatalytic efficiency was rapidly reduced [53]. Therefore, researchers anchored TiO2 to various supporting materials, such as activated carbon [54], clay [53] and silicon [12] to reduce TiO2 aggregation in the reactivation process and improve its adsorption capacity and photocatalytic efficiency. Among these nanoparticles, silica (SiO2) is a common component in building materials within high chemical stability and low cost, it is a promising candidate to preparing TiO2-based nanocomposites [12]. Elena Ghedini et al. [55] synthetized an environmentally friendly and readily-available TiO2-SiO2 photocatalyst which with high surface area by using an incipient wetness impregnation method, they found that ethylbenzene could be degraded by TiO2-SiO2 photocatalyst under ultraviolet excitation. Their research indicated that multifunctional TiO2-SiO2 photocatalyst is expected to combine with building materials to improve air or indoor pollution. Zhou et al. [56] using sol-gel method synthesized TiO2-SiO2 based photocatalyst within high specific surface area and high adsorption capacity. They found that TiO2-SiO2 based photocatalyst could effectively degrade toluene with UV irradition indicated that SiO2 as a carrier combined with TiO2 porous photocatalyst has high adsorption capacity could promote the subsequent photocatalytic reaction and produce a positive synergistic effect.
As shown in Figure 3, Chen et al. [57] successfully synthesized the FAS12-loaded UV-responsive microcapsules by Pickering emulsion polymerization, which were easily dispersed into waterborne polysiloxane latex. The microcapsule could realize the superhydrophobicity of aluminum plate, sheet, glass, polypropylene, wood and other materials by spraying the microcapsule on the surface of these materials, owning to the microcapsule ruptured under UV irradition and then released FAS12.
In addition to inhibiting TiO2 agglomeration, SiO2 can also regulate the crystallization of TiO2 during high-temperature calcination [58]. It is well known that the crystalline structure of TiO2 will affect its catalytic properties. According to report [59], anatase has highest photoactivity than other crystalline structure of TiO2 owning to its admirable specific surface area. Silica can regulate the crystallization of amorphous TiO2 layer into anatase nanocrystal and limited the growth size of anskite grain during high temperature calcination process [58]. However, mostly TiO2/SiO2 nanocomposites can only achieve photocatalytic reaction under UV irradition, which limited their further applications in building industry. Therefore, the combination of weak visible light induced TiO2 based photocatalyst with metal elements to effectively use the whole solar light may be a drastically promising way. Zhao et al. [60] successfully synthesized TiO2/SiO2/Ag ternary composite aerogel with highly porous structures by a facile sol–gel method combined with a supercritical drying technique. They found that the addition of Ag particles effectively decreased the recombination of photo-electrons and holes and enhanced visible-light photocatalytic activity of TiO2/SiO2/Ag ternary composite. Nadeem Raza et al. [61] reported a Ag-doped nanocomposite with low band-gap energy of 2.5 eV, it exhibited an excellent photocatalytic performance for organic dye degradation under solar-light irradition. However, the high cost and aggregation of noble-metal materials on the TiO2 greatly obstacles its industrial application.
In order to obtain a TiO2-based visible-light photocatalysts which with high adsorption ability and excellent photocatalytic efficiency. Researchers have attempted to combine nanocarbon materials with TiO2, particularly, carbon nanotubes (CNTs) as a typical one-dimensional nanostructure have been receiving much attention in the preparation of new photocatalytic materials owning to their electrical, chemical properties and mechanical [62]. According to report [63], TiO2 deposited on the surface of carbon nanotubes can effectively improve the light absorption efficiency of photocatalysts, due to the light shines into the TiO2 hollow tubes and nanosheets, it will bounce back and forth many times and will eventually be absorbed, thus improving the photon capture efficiency. Nguyen et al [64]. Synthesized nanohybrids TiO2/CNTs materials though hydrolysis method, and compared with pure TiO2 or CNTs nanohybrids TiO2/CNTs materials exhibited better photocatalytic performance for methylene blue degradation. Wang et al. [65] found that the combination of TiO2 and CNTs could minimize the recombination of photogenerated electrons and holes.
In addition to carbon nanotubes, graphene is also a common carbon-based carrier which make TiO2 nanoparticles evenly distributed in the liquid and increase the separation and transmission of electron-hole pairs in the TiO2 [52]. According to report [66], the rGO-based TiO2 composite improve TiO2's photocatalytic capability owning to rGO could retard the electron-hole pair recombination. Similarly, Xue et al. [67] verified that graphene can significantly enhance the photogenic electron-hole pair separation and transport and reduce the reunion. Although those nanocomposites have more potential development than pure TiO2 for application, the incorporation of TiO2 in carbon material mesopore volume, drastically reduce the specific surface area of the carbon material result to adsorption inability of pollutants. In addition, carbon materials mostly powder state, no magnetic powder carbon material based-TiO2 material is not conducive to recycling, thus limiting its application in industry [68]. Presently, there are not many practical applications of carbon-based TiO2 nanocomposites, and mostly carbon-based TiO2 nanocomposites are still in the fundamental development stage. Therefore, the development of carbon-based TiO2 with high photocatalytic efficiency is still highly challenging.

5.2. Strategies for Improving the Photocatalytic Efficiency of TiO2

Anchoring TiO2 to silica, carbon nanotubes, graphene and other carriers can reduce TiO2 agglomeration. However, the specific surface area of carriers were partially covered by TiO2 cause the photocatalytic efficiencies of carriers decreased [69]. Therefore, in order to obtain nanocomposites with high photocatalytic efficiencies, researchers used metal elements (Fe3+, Cu2+, Pt+, etc.) or non-metallic elements (S/ N/B, etc.) to modify TiO2 to obtain metal elements/ non-metallic-doped nanocomposites. Previous studies reported that metal atoms doping onto TiO2 can drastically enhance the efficiency of TiO2 and broaden its excitation band. Fe as a commonly metal element in the environment with low-cost and environmental friendly is a better potential candidates for modified TiO2 compared with other metal element dopants [70]. Liu et al. [71] synthesized a visible-light-driven TiO2 with Fe(III) doped. they found that the visible-light absorption ability of Fe(III)-doped TiO2 is better than that of pure TiO2 and the high quantum efficiency of Fe(III)-doped TiO2 is maintained by the surface-grafted Fe(III) ions.
Liu et al. [72] developed a novel TiO2 photocatalyst, which can be achieved by visible light, by coupling Ti(IV) and Fe(III) nanoclusters on the surface of TiO2. The photodegradation mechanism of the novel photocatalyst as sown in Figure 4, they pointed that the holes and electrons were generated under visible light irradition, Ti(IV) nanoclusters on the surface of TiO2 would accumulate photogenerated holes and Cu(II) and Fe(III) nanoclusters would accumulate photogenerated electrons, thus, tardily recombination of photogenerated electron-hole pairs improve its solar energy conversion efficiency.
Although transitional metal modified TiO2 can be activated by visible light irradition, the quantum efficiencies of modified TiO2 catalysts under visible light irradition are still unsatisfactory. [72] What is more, transition metal elements modified TiO2 usually exhibited poor thermal stability and vulnerable to light corrosion. Contrastly, nonmetal decoration can create a narrower band gap in TiO2 as electron donor or acceptor and improve the visible light absorption capability of the modified TiO2, which is much more successful than metal decoration. Due to the small ionization energy and stability of nitrogen and comparable atomic size to that of oxygen [73], nitrogen incorporation for improving photocatalytic efficiency of TiO2 is more appropriate than other nonmetals. Chen et al. [74] synthesized N-doped TiO2 and immobilized it above the surface of asphalt road to evaluate its photodegradation ability for vehicle emissions. they found that N-doped TiO2 asphalt road exhibited higher vehicle emissions photodegradation efficiency under visible-light irradition than that of pure TiO2 asphalt road demonstrated that the N-doped TiO2 would provide a valuable channel for the preparation of photocatalytic asphalt road materials with high visible light induced photocatalytic activity. Jun et al. [75] reported N-doped TiO2 by pyrolysising the co-precipitation of tri-thiocyanuric acid with TiO2 under 500℃. the results suggested that nitrogen doping into the lattice in TiO2 can successfully reduce the band gap energy by changing the band structure, enhancing the absorption capacity of the visible light and accelerating the superoxide radical formation. Giacomo Barolo et al. [76] found that N-doped TiO2 exhibited moderately photocatalytic active under visible light. The synergistic action of the visible light (about 400 nm) and the near-infrared light allows the photocatalytic material to form surface electrons and surface holes to a lower extent.
Although N-doped TiO2 exhibited visible-light photocatalytic ability, researchers claimed that there are some thorny problems with N-doped TiO2 limited its practical application: 1. the doping nitrogen concentration is rather low; 2. N doped into the lattice of TiO2 would generates more oxygen vacancies than that of pure TiO2, these defects promoting the recombination of photogenerated electron-hole pair; 3. the stability of N-doped TiO2 is usually unsatisfactory [77]. In order to separate the photogenerated electrons and holes of TiO2, the method of co-doping of TiO2 with two different ions to resisting the recombination of photogenerated electron-hole pair has aroused wide concern. Vaiano et al. [78] found that the band gap of Fe and N co-doped TiO2 become narrow and the modified TiO2 had a significant photodegradation capability for Acid Orange 7 azo dye under visible-light irradition. The decolorization and mineralization of Acid Orange 7 azo dye achieve 90 and 83% under LEDs light irradition with 60 min, respectively. Li et al. [79] reported that Fe and N co-doped TiO2/GF exhibited better photocatalytic efficiency than that of single doped with Fe-TiO2/GF and N-TiO2/GF suggested that N and Fe could synergistically modify the structure of TiO2 and inhibit the recombination of photogenerated electron-hole pairs.
As shown in Figure 5, Liu et al. [80] synthesized a Fe and N co-doped carbon nanosheets composite by in-situ self-template strategy. They found that Fe-N-CNS composites exhibited excellent ORR activity, high selectivity and admirable stability.
Hayati et al. [81] successfully deposited N and Fe elements on the surface of the functionalized single-walled carbon nanotubes, the nanocomposites could completely photodegraded sulfathiazole under ultrasonic irradition at pH: 7.0, and it exhibited an excellent removal rate of real wastewater's COD and TOD indicated that the novel photocatalyst has an excellent photocatalytic efficiency for decontamination of recalcitrant compounds and pharmaceutical wastewater. However, the photocatalytic performance of most photocatalysts is unsatisfactory for industry application. Therefore, it is still a challenging to develop TiO2-based photocatalysts with high specific surface area, low charge recombination, superior photocatalytic activity and excellent stability.

6. Application Status and Future Prospects of TiO2-Based Building Materials

Numerous practical applications have demonstrated the feasibility of integrating photocatalytic technology with building materials to achieve pollution and carbon reduction in buildings. In the preceding chapters, we discussed the preparation methods of photocatalytic building materials and the modification strategies of TiO2 to enhance the photocatalytc performance of TiO2-based building materials. In this chapter, we discussed some practical examples of photocatalytic building materials to further analyze the effectiveness and critical factors that influence the application of modified functional materials. Lastly, we discuss the limitations and future trends of photocatalytic construction in practice, aiming to deepen understanding of photocatalytic construction materials and provide a reference for the subsequent development of photocatalytic functional building materials.

6.1. Application Status and Key Influencing Factors of Photocatalytic Building Materials

After obtaining good results from laboratory-scale tests, the photocatalytic building materials have been used in practical applications, including office buildings, museums and transportation infrastructures. Table 2 lists a number of demonstration projects using photocatalytic building materials. These materials have been employed in different countries such as China, Berlin, and the Netherlands, and have proven to be durable and effective through long-term field testing. For instance, the Toledo Specialist Hospital in Mexico City has employed tiles coated with TiO2, produced by Elegant Decoration, a construction company based in Berlin. The photocatalytic façade was found to be effective in reducing pollution levels in the surrounding air, as confirmed by long-term field tests. Similarly, the Jubilee Church in Rome, Italy, features a TiO2 coating on its façade, which has been shown to break down harmful pollutants like NOx and VOCs into harmless compounds, while retaining the white appearance of the church and preventing the growth of vegetation. In addition, a segment of the north toll station of Nanjing Yangtze River Bridge, China, which spans an area of approximately 6000 m2 and is situated in heavily polluted areas, employed loaded nano TiO2 photocatalytic material. Researchers monitored pollutant levels in buildings within a few months and determined that the removal efficiency of NOx exceeded 80%.
Despite the encouraging treatment outcomes of these demonstration projects, there are critical issues that must be addressed in the practical application of photocatalytic building materials. The first issue concerns the stability of the building's photocatalytic function. During the use of photocatalytic building materials, the material structure itself is insufficiently stable, leading to the deactivation of building materials. Moreover, during the degradation process of air pollutants, a significant number of intermediate products, such as VOCs by-products or airborne dust, accumulate on the surfaces of photocatalytic building materials, resulting in catalyst contamination and consequently, negatively impacting the building's photocatalytic function. Furthermore, the impact and quantification of production by-products have scarcely been reported. The environmental impact of the intermediate by-products produced during the degradation of pollutants in photocatalytic buildings remains unknown, and further research is needed to gain a deeper understanding of the impact of photocatalytic buildings on the environment.
In practice, photocatalytic building materials need to take into account a variety of factors, such as the catalyst, the installation environment and the building structure, to ensure that the photocatalytic building can operate in a stable and efficient manner. Therefore, photocatalytic building materials need to be selected from catalysts with high activity and stability, and their structures and morphologies need to be optimised to improve the degradation efficiency and stability of photocatalytic materials. To avoid the accumulation of intermediates and by-products, multifunctional catalysts, such as composites of TiO2 with other catalysts, can be tried to improve the catalytic activity and selectivity. Secondly, photocatalytic building materials need to be installed in a suitable environment to ensure their effective absorption of light and exposure in air. The location of the installation in the building, such as light openings, vents and walls, can also have a significant impact on the effectiveness of photocatalytic materials. When installing photocatalytic building materials, the reaction rate and light intensity of the material needs to be considered in order to achieve optimum degradation at the time and under the conditions of contact between the pollutant and the light. Finally, it is worth noting that photocatalytic building materials need to be matched to the structure of the building to ensure their effective application. The properties of photocatalytic building materials, such as light transmission, mechanical strength and durability, need to be taken into account during the building design phase. The coating and veneer materials on the building surface also need to be coordinated with the photocatalytic materials to ensure their degradation and aesthetics.

6.2. Future Perspective and Related Problem Discussions

In the future, the application of photocatalytic building materials in air pollution prevention is highly promising, as environmental protection awareness increases and technology advances. As urbanization accelerates, urban air pollution poses a significant threat to public health and quality of life. Therefore, using photocatalytic building materials in urban construction and planning can effectively enhance air quality. However, researchers are still exploring more efficient and stable photocatalytic building materials for better application in air pollution prevention and control. Both the government and enterprises should promote and apply photocatalytic building materials widely to maximize their environmental benefits. To better apply photocatalytic building materials in the real environment, the following technical challenges must be overcome:
  • Stability of photocatalytic materials: The stability of photocatalytic materials is critical in practical applications. It is important to study the stability of these materials, which undergo prolonged exposure to light and environmental factors, to improve their lifetime. Some factors that may affect the stability of photocatalytic materials include humidity, temperature, pH, pollutants, and microorganisms. Moreover, the photocatalytic materials may also degrade the substrates or binders that they are attached to, resulting in a reduction of mechanical strength and durability [82]. Therefore, developing strategies to enhance the stability of photocatalytic materials and their substrates or binders is necessary for their long-term performance.
  • Photocatalytic reaction rate: The photocatalytic reaction rate is a key issue that affects the practical application of photocatalytic building materials. It is necessary to ensure that the reaction rate is fast enough to effectively degrade harmful substances in the air. Therefore, exploring different photocatalytic reaction mechanisms is necessary to increase the reaction rate. Some factors that may influence the reaction rate include light intensity, wavelength, catalyst loading, surface area, morphology, crystallinity, doping, and co-catalysts [4]. Moreover, the reaction rate may also depend on the type and concentration of pollutants, as well as the presence of other substances that may interfere with the photocatalysis [4]. Therefore, optimizing these factors to enhance the reaction rate is essential for achieving high efficiency and selectivity of photocatalysis.
  • Selectivity of photocatalytic materials: The selectivity of photocatalytic materials refers to their ability to selectively oxidize or reduce specific pollutants in the presence of other substances [83]. Selectivity is important for achieving high efficiency and avoiding unwanted by-products or secondary pollution. However, most photocatalytic materials have low selectivity and tend to react with various organic and inorganic compounds in the air [84]. This may lead to a decrease in photocatalytic activity and an increase in energy consumption. Therefore, designing and modifying photocatalytic materials with high selectivity for target pollutants is a key challenge for their application in air pollution control.
  • Economics of photocatalytic materials: The economics of photocatalytic materials involves the cost-effectiveness and feasibility of their production and application. The cost of photocatalytic materials depends on several factors, such as the type and amount of raw materials, the synthesis method, the fabrication process, the scale-up potential, and the maintenance cost. The benefits of photocatalytic materials depend on their performance, durability, environmental impact, and social acceptance [58]. Therefore, evaluating and optimizing the economics of photocatalytic materials is essential for their widespread adoption and implementation in air pollution prevention.

7. Conclusions and Future Perspectives

This paper reviewed recent progress in the photodegradation of atmospheric pollutants through TiO2-based building materials and discussed the photodegradation mechanism of VOCs, NOx and SOx by photocatalyst under light irradition. Lots of researches confirmed the ability of photocatalytic technology in the decomposition of gaseous pollutants. Particularly, the photodegradation efficiency of low concentrations pollutants is acceptable. Furthermore, we discussed the strategies to improve TiO2 aggregation and broaden its visible light absorption capability in application, including synthesize composite nanomaterials with silica dioxide, carbon nanotubes, graphene and other materials to reduce TiO2 agglomeration, and the methods of modifying TiO2 with metal or non-metallic elements to improve TiO2 photocatalytic ability and visible light absorption. At present, based on TiO2 photocatalyst researches have made greatly progress, however, the catalytic efficiency of TiO2-based building materials under the visible light irradition in practical application is still fall flat. What is more, the generation path of by-products is unclear, there are no general evaluation criteria, limited simulation tools, the durability of photocatalysts is unknown, and photocatalytic building materials are far from widely commercial applications. To accelerate the commercialization process, there is ample need for conducting more basic research work to overcome the shortcomings of the existing catalysts. We suggested that recent priority research should focus on developing new photocatalysts which have excellent pollutants removal efficiency under solar-light irradition and without or less low toxicity byproduct, excellent compatibility with building materials and improve its service life. This review provides a reference for optimizing existing methods and exploring new strategies, aiming to design better building materials which with photocatalytic capability to achieve efficient air purification function.

Author Contributions

All authors verify their contribution to the current review article as follows: Design, study conception, and supervision of the whole article is done by Yuanchen Wei and Yongqing Zhang; data collection is done by Xiaoyu Bai, Hong Meng, Que Wu; analysis and interpretation of results by Xiaoyu Bai, Hong Meng and Que Wu;; manuscript preparation and proofreading by Xiaoyu Bai, Hong Meng, Yuanchen Wei and Yongqing Zhang.

Funding

This work was financially supported by the National Key Research and Development Program of China (2016YFC0400708), Guangdong Basic and Applied Basic Research Foundation, China (2019A1515011761) and the Foundation of Longhua District Bureau of Public Works of Shenzhen Municipality, Shenzhen, China.

Conflicts of Interest

There are no conflict to declare.

References

  1. Jason, K.M.; et al. The emerging risk of exposure to air pollution on cognitive decline and Alzheimer's disease—Evidence from epidemiological and animal studies. Biomed. J. 2018, 41, 141–162. [Google Scholar]
  2. Stanaszek-Tomal, E. Anti-Smog Building and Civil Engineering Structures. Processes 2021, 9, 1446. [Google Scholar] [CrossRef]
  3. Majbauddin, A.; Onishi, K.; Otani, S.; et al. Association between Asian Dust-Borne Air Pollutants and Daily Symptoms on Healthy Subjects: A Web-Based Pilot Study in Yonago, Japan. J. Environ. Public Health 2016, 2016, 1–6. [Google Scholar] [CrossRef]
  4. He, F.; Jeon, W.; Choi, W. Photocatalytic air purification mimicking the self-cleaning process of the atmosphere. Nat. Commun. 2021, 12, 2528. [Google Scholar] [CrossRef]
  5. Saputera, W.H.; Amri, A.F.; Daiyan, R.; et al. Photocatalytic Technology for Palm Oil Mill Effluent (POME) Wastewater Treatment: Current Progress and Future Perspective. Materials 2021, 14, 2846. [Google Scholar] [CrossRef]
  6. Al-Nuaim, M.A.; Alwasiti, A.A.; Shnain, Z.Y. The photocatalytic process in the treatment of polluted water. Chem Zvesti 2023, 77, 677–701. [Google Scholar] [CrossRef]
  7. Chen, J.; Poon, C.-S. Photocatalytic construction and building materials: From fundamentals to applications. Build. Environ. 2009, 44, 1899–1906. [Google Scholar] [CrossRef]
  8. Jenny, S.D.; et al. Understanding TiO2 Photocatalysis: Mechanisms and Materials. Chem. Rev. 2014, 114, 9919–9986. [Google Scholar]
  9. Gopalan, A.I.; et al. Recent Progress in the Abatement of Hazardous Pollutants Using Photocatalytic TiO2-Based Building Materials. Nanomaterials 2020, 10, 1854. [Google Scholar] [CrossRef] [PubMed]
  10. Wang, D.H.; et al. One-step hydrothermal synthesis of N-doped TiO2/C nanocomposites with high visible light photocatalytic activity. Nanoscale 2012, 4, 576–584. [Google Scholar] [CrossRef]
  11. Alonso-Tellez, A.; et al. Comparison of Hombikat UV100 and P25 TiO2 performance in gas-phase photocatalytic oxidation reactions. J. Photochem. Photobiol. A Chem. 2012, 250, 58–65. [Google Scholar] [CrossRef]
  12. Resende, S.F.; Nunes, E.H.M.; Houmard, M.; et al. Simple sol-gel process to obtain silica-coated anatase particles with enhanced TiO2-SiO2 interfacial area. J. Colloid Interface Sci. 2014, 433, 211–217. [Google Scholar] [CrossRef] [PubMed]
  13. Dhanasekar, M.; et al. Ambient light antimicrobial activity of reduced graphene oxide supported metal doped TiO2 nanoparticles and their PVA based polymer nanocomposite films. Mater. Res. Bull. 2018, 97, 238–243. [Google Scholar] [CrossRef]
  14. Yuan, T.; Yao, W. Preparation and Properties of g-C3N4-TiO2 Cement-Based Materials Supported by Recycled Concrete Powder. Catalysts 2023, 13, 312. [Google Scholar] [CrossRef]
  15. Fang, Y.; et al. Preparation and Properties of Magnesium Cement-Based Photocatalytic Materials. Catalysts 2022, 12, 420. [Google Scholar] [CrossRef]
  16. Domínguez-Espíndola, R.B.; et al. A critical review on advances in TiO2-based photocatalytic systems for CO2 reduction. Appl. Therm. Eng. 2022, 216, 119009. [Google Scholar] [CrossRef]
  17. Kumer, A.; Chakma, U. Developing the amazing photocatalyst of ZnAg2GeSe4, ZnAg2Ge0.93Fe0.07Se4 and ZnAg2Ge0.86Fe0.14Se4 through the computational explorations by four DFT functionals. Heliyon 2021, 7, e07467. [Google Scholar] [CrossRef]
  18. Zhong, L.; Haghighat, F. Photocatalytic air cleaners and materials technologies—Abilities and limitations. Build. Environ. 2015, 91, 191–203. [Google Scholar] [CrossRef]
  19. Almaie, S.; Vatanpour, V.; Rasoulifard, M.H.; et al. Volatile organic compounds (VOCs) removal by photocatalysts: A review. Chemosphere 2022, 306, 135655. [Google Scholar] [CrossRef]
  20. Olivier, J.G.J.; Bouwman, A.F.; Van der Hoek, K.W.; et al. Global air emission inventories for anthropogenic sources of NOx, NH3 and N2O in 1990. Environ. Pollut. 1998, 102, 135–148. [Google Scholar] [CrossRef]
  21. Jin, Y.; Wang, D.; Zhang, W. Effects of substrates on N2O emissions in an anaerobic ammonium oxidation (anammox) reactor. Springerplus 2016, 5, 741. [Google Scholar] [CrossRef] [PubMed]
  22. Razavi, Z.; et al. Adsorption and photocatalytic removal of SO2 using natural and synthetic zeolites-supported TiO2 in a solar parabolic trough collector. J. Clean. Prod. 2021, 310, 127376. [Google Scholar] [CrossRef]
  23. Mendoza, J.A.; et al. Photocatalytic performance of TiO2 and WO3/TiO2 nanoparticles coated on urban green infrastructure materials in removing nitrogen oxide. Int. J. Environ. Sci. Technol. 2017, 15, 581–592. [Google Scholar] [CrossRef]
  24. Chen, D.; et al. Photocatalytic degradation of organic pollutants using TiO2-based photocatalysts: A review. J. Clean. Prod. 2020, 268, 121725. [Google Scholar] [CrossRef]
  25. Yousefi, A.; Allahverdi, A. Effective dispersion of nano-TiO2 powder for enhancement of photocatalytic properties in cement mixes. Constr. Build. Mater. 2013, 41, 224–230. [Google Scholar] [CrossRef]
  26. Nguyen-Phan, T.-D.; Shin, E.W. Morphological effect of TiO2 catalysts on photocatalytic degradation of methylene blue. J. Ind. Eng. Chem. 2011, 17, 397–400. [Google Scholar] [CrossRef]
  27. Igenepo John, K.; et al. Unravelling the effect of crystal dislocation density and microstrain of TiO2 nanoparticles on tetracycline removal performance. Chem. Phys. Lett. 2021, 776, 138725. [Google Scholar] [CrossRef]
  28. Liu, C.; et al. Applications and Advances in TiO2 Based Photocatalytic Building Materials. J. Phys. Conf. Ser. 2021, 2011, 012049. [Google Scholar] [CrossRef]
  29. Cárdenas, C.; et al. Functionalized building materials: Photocatalytic abatement of NOx by cement pastes blended with TiO2 nanoparticles. Constr. Build. Mater. 2012, 36, 820–825. [Google Scholar] [CrossRef]
  30. Poon, C.S.; Cheung, E. NO removal efficiency of photocatalytic paving blocks prepared with recycled materials. Constr. Build. Mater. 2007, 21, 1746–1753. [Google Scholar] [CrossRef]
  31. Demeestere, K.; et al. Heterogeneous photocatalytic removal of toluene from air on building materials enriched with TiO2. Build. Environ. 2008, 43, 406–414. [Google Scholar] [CrossRef]
  32. Hüsken, G.; Hunger, M.; Brouwers, H.J.H. Experimental study of photocatalytic concrete products for air purification. Build. Environ. 2009, 44, 2463–2474. [Google Scholar] [CrossRef]
  33. Chen, J.; Kou, S.-C.; Poon, C.-S. Photocatalytic cement-based materials: Comparison of nitrogen oxides and toluene removal potentials and evaluation of self-cleaning performance. Build. Environ. 2011, 46, 1827–1833. [Google Scholar] [CrossRef]
  34. Aïssa, A.H.; et al. Characterization and photocatalytic performance in air of cementitious materials containing TiO2. Case study of formaldehyde removal. Appl. Catal. B Environ. 2011, 107, 1–8. [Google Scholar] [CrossRef]
  35. Pirola, C.; et al. Photocatalytic coatings for building industry: Study of 1 year of activity in the NO x degradation. J. Coat. Technol. Res. 2011, 9, 453–458. [Google Scholar] [CrossRef]
  36. Karapati, S.; et al. TiO2 functionalization for efficient NOx removal in photoactive cement. Appl. Surf. Sci. 2014, 319, 29–36. [Google Scholar] [CrossRef]
  37. Pérez-Nicolás, M.; et al. Photocatalytic NOx abatement by calcium aluminate cements modified with TiO2, Improved NO2 conversion. Cem. Concr. Res. 2015, 70, 67–76. [Google Scholar] [CrossRef]
  38. Guo, M.-Z.; Ling, T.-C.; Poon, C.S. Photocatalytic NO x degradation of concrete surface layers intermixed and spray-coated with nano-TiO2 : Influence of experimental factors. Cem. Concr. Compos. 2017, 83, 279–289. [Google Scholar] [CrossRef]
  39. Pérez-Nicolás, M.; et al. Atmospheric NOx removal: Study of cement mortars with iron- and vanadium-doped TiO2 as visible light–sensitive photocatalysts. Constr. Build. Mater. 2017, 149, 257–271. [Google Scholar] [CrossRef]
  40. Seo, D.; Yun, T.S. NOx removal rate of photocatalytic cementitious materials with TiO2 in wet condition. Build. Environ. 2017, 112, 233–240. [Google Scholar] [CrossRef]
  41. Zouzelka, R.; Rathousky, J. Photocatalytic abatement of NOx pollutants in the air using commercial functional coating with porous morphology. Appl. Catal. B Environ. 2017, 217, 466–476. [Google Scholar] [CrossRef]
  42. Guo, M.-Z.; Poon, C.S. Superior photocatalytic NOx removal of cementitious materials prepared with white cement over ordinary Portland cement and the underlying mechanisms. Cem. Concr. Compos. 2018, 90, 42–49. [Google Scholar] [CrossRef]
  43. Macwan, D.P.; Dave, P.N.; Chaturvedi, S. A review on nano-TiO2 sol-gel type syntheses and its applications. J. Mater. Sci. 2011, 46, 3669–3686. [Google Scholar] [CrossRef]
  44. Zanganeh, S.; et al. Hydrothermal synthesis and characterization of TiO2 nanostructures using LiOH as a solvent. Adv. Powder Technol. 2011, 22, 336–339. [Google Scholar] [CrossRef]
  45. Keerthana, B.G.T.; et al. Hydrothermal synthesis and characterization of TiO2 nanostructures prepared using different solvents. Mater. Lett. 2018, 220, 20–23. [Google Scholar] [CrossRef]
  46. Payan, A.; Fattahi, M.; Roozbehani, B. Synthesis, characterization and evaluations of TiO2 nanostructures prepared from different titania precursors for photocatalytic degradation of 4-chlorophenol in aqueous solution. J. Environ. Health Sci. Eng. 2018, 16, 41–54. [Google Scholar] [CrossRef] [PubMed]
  47. Huang, L.; et al. Hydrothermal synthesis of different TiO2 nanostructures: Structure, growth and gas sensor properties. J. Mater. Sci. Mater. Electron. 2012, 23, 2024–2029. [Google Scholar] [CrossRef]
  48. Carne-Sanchez, A.; et al. A spray-drying strategy for synthesis of nanoscale metal-organic frameworks and their assembly into hollow superstructures. Nat. Chem. 2013, 5, 203–211. [Google Scholar] [CrossRef]
  49. Mizukoshi, Y.; Masahashi, N. Fabrication of a TiO2 photocatalyst by anodic oxidation of Ti in an acetic acid electrolyte. Surf. Coat. Technol. 2014, 240, 226–232. [Google Scholar] [CrossRef]
  50. Lai, L.; et al. Enhanced adhesive strength between SU-8 photoresist and titanium substrate by an improved anodic oxidation method for high aspect-ratio microstructures. J. Micromech. Microeng. 2019, 29, 047002. [Google Scholar] [CrossRef]
  51. Falk, G.S.; et al. Microwave-assisted synthesis of TiO2 nanoparticles: Photocatalytic activity of powders and thin films. J. Nanoparticle Res. 2018, 20, 23. [Google Scholar] [CrossRef]
  52. Chen, J.; et al. Recent progress in enhancing photocatalytic efficiency of TiO2 -based materials. Appl. Catal. A Gen. 2015, 495, 131–140. [Google Scholar] [CrossRef]
  53. Liao, C.; Wu, Q.; Teng, S.; et al. Nanocomposite gels via in-situ photoinitiation and disassembly of TiO2-Clay composites with polymers applied as UV protective films. ACS Appl. Mater. Interfaces 2014, 6, 1350–1360. [Google Scholar] [CrossRef] [PubMed]
  54. Ibusuki, T.; Takeuchi, K. Removal of low concentration nitrogen oxides through photoassisted heterogeneous catalysis—Science Direct. J. Mol. Catal. 1994, 88, 93–102. [Google Scholar] [CrossRef]
  55. Ghedini, E.; et al. Multifunctional and Environmentally Friendly TiO2-SiO2 Mesoporous Materials for Sustainable Green Buildings. Molecules 2019, 24, 4226. [Google Scholar] [CrossRef]
  56. Zou, L.; et al. Removal of VOCs by photocatalysis process using adsorption enhanced TiO2–SiO2 catalyst. Chem. Eng. Process. Process Intensif. 2006, 45, 959–964. [Google Scholar] [CrossRef]
  57. Chen, K.; et al. Fabrication of All-Water-Based Self-Repairing Superhydrophobic Coatings Based on UV-Responsive Microcapsules. Adv. Funct. Mater. 2015, 25, 1035–1041. [Google Scholar] [CrossRef]
  58. Joo, J.B.; et al. Mesoporous Anatase Titania Hollow Nanostructures though Silica-Protected Calcination. Adv. Funct. Mater. 2012, 22, 166–174. [Google Scholar] [CrossRef]
  59. Yang, C.C.; et al. Using C-doped TiO2 Nanoparticles as a Novel Sonosensitizer for Cancer Treatment. Antioxidants 2020, 9, 880. [Google Scholar] [CrossRef] [PubMed]
  60. Zhao, X.; Zhang, J.; Yi, X.; Liu, B.; Zhang, J.; Yi, X. Mesoporous TiO2/SiO2/Ag ternary composite aerogels for high photocatalysis. New J. Chem. 2019, 43, 6234–6241. [Google Scholar] [CrossRef]
  61. Nadeem Raza, W.R.; Gul, H.; Azam, M.; Lee, J.; Vikrant, K.; Kim, K.-H. Solar-light-active silver phosphate/titanium dioxide/silica heterostructures for photocatalytic removal of organic dye. J. Clean. Prod. 2020, 254, 120031. [Google Scholar] [CrossRef]
  62. Zhang, W.; et al. Micro/nano-bubble assisted synthesis of Au/TiO2@CNTs composite photocatalyst for photocatalytic degradation of gaseous styrene and its enhanced catalytic mechanism. Environ. Sci. Nano 2019, 6, 948–958. [Google Scholar] [CrossRef]
  63. Liang, Z.; et al. Full solar spectrum photocatalytic oxygen evolution by carbon-coated TiO2 hierarchical nanotubes. Appl. Catal. B Environ. 2019, 243, 711–720. [Google Scholar] [CrossRef]
  64. Nguyen, K.C.; Ngoc, M.; Nguyen, M.V. Enhanced photocatalytic activity of nanohybrids TiO2 /CNTs materials. Mater. Lett. 2016, 165, 247–251. [Google Scholar] [CrossRef]
  65. Wang, S.G.; et al. Photocatalytic properties of TiO2/cnts films with different morphology on stainless steel substrates. Nano 2014, 9, 1450003. [Google Scholar] [CrossRef]
  66. Olana, M.H.; et al. Citrus sinensis and Musa acuminata Peel Waste Extract Mediated Synthesis of TiO2/rGO Nanocomposites for Photocatalytic Degradation of Methylene Blue under Visible Light Irradiation. Bioinorg. Chem. Appl. 2022, 2022, 5978707. [Google Scholar] [CrossRef] [PubMed]
  67. Pan, X.; Zhao, Y.; Liu, S.; et al. Comparing Graphene-TiO2 Nanowire and Graphene-TiO2 Nanoparticle Composite Photocatalysts. ACS Appl. Mater. Interfaces 2012, 4, 3944. [Google Scholar] [CrossRef] [PubMed]
  68. Tang, Y.; Luo, S.; Teng, Y.; et al. Efficient removal of herbicide 2,4-dichloropheNOxyacetic acid from water using Ag/reduced graphene oxide co-decorated TiO2 nanotube arrays. J. Hazard. Mater. 2012, 241–242, 323–330. [Google Scholar] [CrossRef]
  69. Dong, W.; et al. Synchronous role of coupled adsorption and photocatalytic oxidation on ordered mesoporous anatase TiO2–SiO2 nanocomposites generating excellent degradation activity of RhB dye. Appl. Catal. B Environ. 2010, 95, 197–207. [Google Scholar] [CrossRef]
  70. Dholam, R.; et al. Hydrogen production by photocatalytic water-splitting using Cr- or Fe-doped TiO2 composite thin films photocatalyst. Int. J. Hydrogen Energy 2009, 34, 5337–5346. [Google Scholar] [CrossRef]
  71. Liu, M.; Qiu, X.; Miyauchi, M.; et al. Energy-level matching of Fe(III) ions grafted at surface and doped in bulk for efficient visible-light photocatalysts. J. Am. Chem. Soc. 2013, 135, 10064. [Google Scholar] [CrossRef] [PubMed]
  72. Min Liu, R.I.M.N.; Qiu, X.; Atarashi, D.; Sakai, E.; Nosaka, Y.; Hashimoto, K.; Miyauchi, M. Enhanced Photoactivity with Nanocluster-Grafted Titanium Dioxide Photocatalysts. ACS NANO 2014, 8, 7229–7238. [Google Scholar]
  73. Preethi, L.K.; Antony, R.P.; Mathews, T.; et al. A Study on Doped Heterojunctions in TiO2 Nanotubes: An Efficient Photocatalyst for Solar Water Splitting. Sci. Rep. 2017, 7, 14314. [Google Scholar] [CrossRef]
  74. Chen, M.; et al. Photocatalytic Oxidation of NOx under Visible Light on Asphalt-Pavement Surface. J. Mater. Civ. Eng. 2017, 29. [Google Scholar] [CrossRef]
  75. Khan, T.; et al. Synthesis of N-Doped TiO2 for Efficient Photocatalytic Degradation of Atmospheric NOx. Catalysts 2021, 11, 109. [Google Scholar] [CrossRef]
  76. Barolo, G.; et al. Mechanism of the Photoactivity under Visible Light of N-Doped Titanium Dioxide. Charge Carriers Migration in Irradiated N-TiO2 Investigated by Electron Paramagnetic Resonance. J. Phys. Chem. C 2012, 116, 20887–20894. [Google Scholar] [CrossRef]
  77. Zhang, Y.W.; Xing, M.; Leghari, S.A.K. ; Sajjad, S, Development of modified N doped TiO2 photocatalyst with metals, nonmetals and metal oxides. Energy Environ. Sci. 2010, 3, 715–726. [Google Scholar] [CrossRef]
  78. Mancuso, A.; et al. Enhanced visible-light-driven photodegradation of Acid Orange 7 azo dye in aqueous solution using Fe-N co-doped TiO2. Arab. J. Chem. 2020, 13, 8347–8360. [Google Scholar] [CrossRef]
  79. Weerasinghe, R.; et al. Study on the effect of Fe and N co-doped supported TiO2/GF photocatalytic oxidation of nitrobenzene wastewater. E3S Web Conf. 2021, 237, 01036. [Google Scholar]
  80. Liua, Y.; Zhu, S.; Li, D. TiN nanoparticles hybridized with Fe, N co-doped carbon nanosheets composites as highly efficient electrocatalyst for oxygen reduction reaction. Chem. Eng. J. 2020, 400, 125968. [Google Scholar] [CrossRef]
  81. Hayati, F.; Isari, A.A.; Moradi, S.; Kakavandi, B. LED-assisted sonocatalysis of sulfathiazole and pharmaceutical wastewater using N,Fe co-doped TiO2@SWCNT: Optimization, performance and reaction mechanism studies. J. Water Process Eng. 2020, 38, 101693. [Google Scholar] [CrossRef]
  82. Chew, M.Y.L.; Conejos, S.; Law, J.S.L. Green maintainability design criteria for nanostructured titanium dioxide (TiO2) façade coatings. Int. J. Build. Pathol. Adapt. 2017, 35, 139–158. [Google Scholar] [CrossRef]
  83. Tsukamoto, D.; et al. Selective photocatalytic oxidation of alcohols to aldehydes in water by TiO2 partially coated with WO3. Chemistry 2011, 17, 9816–9824. [Google Scholar] [CrossRef]
  84. Pastor, A.; et al. ZnO on rice husk: A sustainable photocatalyst for urban air purification. Chem. Eng. J. 2019, 368, 659–667. [Google Scholar] [CrossRef]
Preprints 82770 g001
Figure 1. Basic principle of Photocatalytic oxidation for the removal of organic pollutants [18].
Figure 1. Basic principle of Photocatalytic oxidation for the removal of organic pollutants [18].
Preprints 82770 g001
Preprints 82770 g002
Figure 2. (a) Photocatalytic disinfection mechanism of bacteria and (b) viruses [23].
Figure 2. (a) Photocatalytic disinfection mechanism of bacteria and (b) viruses [23].
Preprints 82770 g002
Preprints 82770 g003
Figure 3. Schematic illustration of the preparation of all-water-based self-repairing superhydrophobic coatings based on U-capsules [57].
Figure 3. Schematic illustration of the preparation of all-water-based self-repairing superhydrophobic coatings based on U-capsules [57].
Preprints 82770 g003
Preprints 82770 g004
Figure 4. The photodegradation mechanism of the novel photocatalyst. Reprinted with permission from Ref. [72]
Figure 4. The photodegradation mechanism of the novel photocatalyst. Reprinted with permission from Ref. [72]
Preprints 82770 g004
Preprints 82770 g005
Figure 5. The preparation process of TiN/Fe-N-CNS catalyst [80] .
Figure 5. The preparation process of TiN/Fe-N-CNS catalyst [80] .
Preprints 82770 g005
Table 1. Selected research literature on air pollutant removal by TiO2-based building materials.
Table 1. Selected research literature on air pollutant removal by TiO2-based building materials.
Building material Method Light source Efficiency Reference/Year
cement mortar Mixing with cement mortar UV The degradation rate of NOx can reach 40.0% [32]2009
cement mortar Mix with mortar (2 and 5 wt%) UV NO (400 ppb) removal rate: 90 μ mol/（m2⋅h）； Toluene (200ppb) removal: 100% [33]2011
ceramic tiles Photocatalyst brushing on the top surface of tiles UV Toluene (17-35 ppbv) removal rate up to 512 μ g/（m2⋅h） [31]2008
cement mortar Mix with mortar (1-10% wt%) UV Formaldehyde (20 ppm) removal rate up to 65% [34]2011
portland cement Mix with cement slurry (0.5-5 wt%.) UV NOx (1 ppmv) removal amount:120 μmol/m2, 65 h [29]2012
Wall paint and plaster Mixing with 2 wt% TiO2 UV NOx (400 ppb) conversion range ranges from 80% of 50 days samples to 30% of 1 year samples [35]2011
cement mortar Mixed cement (0.5-2.5wt%) Simulated sunlight The removal rate of NO (1 ppm) can reach 15% [36]2014
cement mortar Mixing with cement mortar UV The degradation efficiency of NOx (1000 ppb) can reach 60.4% [37]2015
cement mortar Combine photocatalytic materials with building materials using mixing and spraying methods respectively UV NO (1000 ppb) removal condition: Material for spraying method: 220 μ Mol/(m2 Å h), mixed material: 80 μ mol/ （m2.h） [38]2017
cement mortar Mix with cement mortar (0.5~2.5 wt%) UVSunlightVisible light The highest conversion rates of NO (500 ppb) are 38% (P25), 15% (P25), and 5.5% (Fe TiO2 and V-TiO2), respectively [39]2017
cement mortar Mixing with cement mortar (1-10wt%) UV NO (1ppm) removal rate: 72% [40]2017
Concrete and gypsum Coating deposited on the .test concrete wall Sunlight Efficient removal of NOx from polluted air. [41]2017
White cement (WC) and ordinary Portland cement paste Mixed cement slurry (2-5wt%) UV NO (1000ppb) removal condition: OPC is 380 μ Mol/(m2. h) and WC at 500 μ mol/（m2⋅h） [42]2018
Table 2. The application of TiO2 in a building facade or roof.
Table 2. The application of TiO2 in a building facade or roof.
Building Name Location Building Materical Benefits Difficulties
Palazzo Italia Milan, Italy TiO2-based photocatalytic coating on façade Purifies air, reduces carbon emissions, energy-efficient design, use of renewable energy sources Cost of installation and maintenance
Jubilee Church Rome, Italy TiO2-coated façade Reduces air pollution, improves air quality by breaking down harmful pollutants Limited effectiveness in high-traffic areas
Palazzo Lombardia Milan, Italy TiO2-coated façade Purifies air, reduces energy consumption by reflecting sunlight and reducing need for air conditioning Cost of installation and maintenance
Bullitt Center Seattle, USA TiO2-coated roof Purifies air, reduces air pollution by breaking down harmful pollutants Limited effectiveness in high-traffic areas
Denby Dale Passivhaus Yorkshire, UK TiO2-coated façade Purifies air, reduces air pollution, reduces energy consumption for heating and cooling Cost of installation and maintenance
Edificio Malecon Mexico City, Mexico TiO2-coated façade Reduces air pollution, improves air quality, self-cleaning properties, reduces energy consumption Cost of installation and maintenance
Haze-Free Tower Beijing, China TiO2-coated façade Reduces air pollution, improves air quality, enhances aesthetics, self-cleaning properties Limited effectiveness in high-traffic areas
Queen's Building Bristol, UK TiO2-coated façade Purifies air, reduces air pollution, self-cleaning properties Limited effectiveness in shaded areas
Nanjing Green Lighthouse Nanjing, China TiO2-coated façade Purifies air, reduces energy consumption, improves air quality, self-cleaning properties Cost of installation and maintenance
LaFargeHolcim Headquarters Switzerland TiO2-coated façade Reduces air pollution, self-cleaning properties, improves energy efficiency Limited effectiveness in high-pollution areas
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.
Copyright: This open access article is published under a Creative Commons CC BY 4.0 license, which permit the free download, distribution, and reuse, provided that the author and preprint are cited in any reuse.
Prerpints.org logo

Preprints.org is a free preprint server supported by MDPI in Basel, Switzerland.

facebook logotwitter logolinkedin logo
MDPI Initiatives
Important Links
Subscribe

Disclaimer

Terms of Use

Privacy Policy

© 2024 MDPI (Basel, Switzerland) unless otherwise stated