Published: 30 June 2023
1. Introduction
Over the past decade, the number of torrential rain events in Korea has increased approximately 1.5 times compared to the past, and the frequency of these events has increased six times [
1]. Increases in phenomena such as heavy rainfall are closely related to climate change. Compared to the past, the annual average temperature reached its peak in 2016, confirming that global warming is continuing [
2]. The main cause of these phenomena is air pollution caused by emissions of large amounts of substances such as fine dust, nitrogen oxides (NO
x), and carbon dioxide [
3]. More than 50% of total NO
x emissions are caused by automobiles. Thus, reducing automobile usage can lead to reduced NO
x emissions; however, that is almost impossible to achieve because of increasing numbers of advance automobiles. Therefore, the development of structures such as a NOx absorbing infrastructure is necessary for reducing NO
x emissions. Various studies have been conducted worldwide to reduce NO
x emissions, and one of the most widely used materials in the construction field is titanium dioxide (TiO
2) [
4]. TiO
2 is a photocatalytic material that can adsorb NO
x. To exploit this property, we sought to develop pervious concrete that can adsorb NO
x over a larger area.
Accordingly, as basic research for the development of photocatalytic pervious concrete to reduce NOx, this study aims to evaluate the basic physical properties of pervious concrete, such as porosity, permeability coefficient, and compressive strength. Moreover, we intend to conduct experiments on the NOx removal ratio to analyze the NOx reduction effect according to two types of photocatalysts, namely, TiO2 and spray-type.
2. Material and Methods
2.1. Materials
Type I (equivalent to Type I) Ordinary Portland cement, coarse aggregates with a maximum size of 10 mm, TiO
2, isopropyl alcohol (IPA) solution with a specific gravity of 0.79 was used. Properties of aggregates and TiO
2 are listed in
Table 1 and
Table 2, respectively.
2.2. Experimental Details
2.2.1. Mix Proportion
The mix proportions used in this study are listed in
Table 3. TiO
2 was incorporated by substituting 5% and 10% of cement weight.
2.2.2. Porosity Measurement Method
The porosity of the pervious concrete was measured using the porosity test method suggested by the Concrete Research Committee of the Japan Concrete Institute (JCI). Equations (1) and (2) are used to measure the total and continuous porosities, respectively.
where,
W1 is the weight of the specimen in water;
W2 is the weight of the specimen in an absolutely dry state; and
V is the specimen volume.
2.2.3. Permeability Coefficient-Measurement Method
Because the permeability coefficient of pervious concrete is more than 105 times larger than that of ordinary concrete, it is impossible to measure the permeability coefficient using the permeability method for ordinary concrete. Therefore, we measured the permeability coefficient according to ASTM C 1701 “Standard Method for Infiltration Rate of In Place Pervious Concrete” using Equation (3).
where,
I denotes the infiltrate in/h;
M denotes mass of infiltrated water (lb);
D denotes the inside diameter of the infiltration ring (in);
t denotes the time required for the measured amount of water to infiltrate the concrete (s); and k = 126,870 (constant).
2.2.4. Compressive Strength Measurement Method
Using a Φ100 × 200 mm cylindrical mold, the compressive strength was measured after 28 days according to KS F 2405.
2.2.5. NOx Removal Ratio Test Method
The NOx removal ratio test was conducted according to KS L ISO 22197-1. The test was conducted by supplying a mixed gas with a certain concentration of nitric oxide and high-purity air at a certain ratio, while emitting ultraviolet light to activate TiO2, which adsorbs NOx when exposed to light.
2.2.6. TiO2 vs. Spray-Type Photocatalyst Test Method
To compare the NO
x removal effect of pervious concrete using TiO
2, the specimens with dimensions of 100 mm × 100 mm × 400 mm, height, breadth and length, respectively, were used. A spray-type photocatalyst was sprayed on the pervious concrete to create a test specimen for comparison. A comparison of the NO
x removal ratios between the TiO
2-substituted and photocatalyst-sprayed specimens was conducted using the same process as the removal ratio test method described in
Section 2.2.5.
3. Experimental Results and Analysis
3.1. Basic Property Evaluation
Table 4 presents the experimental results for evaluating the basic properties, including the porosity, permeability coefficient, and compressive strength. The continuous porosity of all the variables was approximately 7%, and the permeability coefficients were similar.
3.2. NOx Removal Ratio Test Results
Table 5 presents the NO
x removal ratio and total porosity results. For the OPC without photocatalysts, the NO
x removal ratio was 0.2%, indicating almost no removal effect. However, the removal ratios for the 5% and 10% TiO
2 substitution samples were 49% and 37%, respectively, indicating excellent NO
x removal. The removal ratio was expected to increase as the TiO
2 substitution rate increased; however, the experimental results were inconsistent with this expectation.
4. Conclusions
This study evaluated the basic properties of pervious concrete, including porosity, permeability coefficient, and compressive strength, and conducted experiments on the NOx removal ratio by using TiO2 and spray-type photocatalysts. The conclusions are as follows.
According to the NOx removal ratio test results for pervious concrete with TiO2, the 5% substitution variable showed a better removal ratio than the 10% substitution variable. Thus, we conclude that the best NOx removal ratio can be achieved with an appropriate mix proportion of TiO2, rather than based on the amount of TiO2. Therefore, further experimental research on the optimal mixing proportion of TiO2 is necessary.
TiO2 was applied to pervious concrete with a large air-exposure area to increase the NOx removal ratio. However, pervious concrete formed a somewhat high porosity, which made it difficult to apply TiO2 to concrete structures such as road pavements and parking lot decks. Therefore, additional evaluations of the durability characteristics should be conducted along with evaluations of the mechanical performance because of the high porosity.
Author Contributions
Conceptualization, C.P. and S.K.; methodology, C.P., M.C., D.-J.K., U.-D.P., Y.-S.K., M.J. and S.K.; formal analysis, C.P. and S.K.; writing—original draft preparation, C.P., M.C., D.-J.K., U.-D.P., Y.-S.K., M.J. and S.K.; writing—review and editing, C.P. and S.K. All authors have read and agreed to the published version of the manuscript.
Funding
This work was supported by the National Research Foundation of Korea (NRF) grant funded by the Korea government (MSIT) (No.2021R1A2C201409713).
Institutional Review Board Statement
Not applicable.
Informed Consent Statement
Not applicable.
Data Availability Statement
Not applicable.
Conflicts of Interest
The authors declare no conflict of interest.
References
- Kim, Y.T.; Park, M.Y.; Kwon, H.H. Spatio-Temporal Summer Rainfall Pattern in 2020 from a Rainfall Frequency Perspective. Korean Soc. Disaster Secur. 2020, 13, 93–104. [Google Scholar]
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Table 1.
Physical properties of aggregates with a maximum size of 10 mm.
Table 1.
Physical properties of aggregates with a maximum size of 10 mm.
Aggregate Size | Specific Gravity | Absorption Rate | Fineness Modulus |
---|
10 mm | 2.6 | 1.9% | 5.9 |
Table 2.
Properties of TiO2 used.
Table 2.
Properties of TiO2 used.
Type | Specific Gravity | Content | Particle Size | Molecular Weight |
---|
anatase | 4.0 | 98.5% | 0.35–0.5 µm | 77.9 g |
Table 3.
Mix proportions used.
Table 3.
Mix proportions used.
Variable | W | C | TiO2 | G | 1 S/P |
---|
OPC | 108 | 360 | - | 1814 | 0.9 |
T5 | 342 | 18 | 1817 |
T10 | 324 | 36 | 1820 |
Table 4.
Results of basic property evaluation experiments.
Table 4.
Results of basic property evaluation experiments.
Variable | Compressive Strength (MPa) | Total Porosity (%) | Continuous Porosity (%) | Permeability Coefficient (cm/s) |
---|
OPC | 17 | 9.30 | 7.60 | 1.25 |
T5 | 18.3 | 9.00 | 7.02 | 1.22 |
T10 | 18.0 | 8.90 | 6.89 | 1.20 |
T5-IPA | 18.3 | 8.90 | 7.00 | 1.20 |
T10-IPA | 18.4 | 8.80 | 6.84 | 1.19 |
Table 5.
NOx removal ratio and total porosity.
Table 5.
NOx removal ratio and total porosity.
Variable | Total Porosity (%) | Removal Ratio (%) |
---|
OPC | 9.30 | 0.2 |
T5 | 9.00 | 49.0 |
T10 | 8.90 | 37.0 |
T5-IPA | 8.90 | 35.1 |
T10-IPA | 8.80 | 27.7 |
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