Abstract

This work is aimed to study the possibility of recycling plastic waste (polypropylene (PP)) as aggregate instead of sand in the manufacturing of mortar or concrete. For this, an experimental study was carried out to evaluate the influence of nano-SiO2 and recycled PP plastic particles' content on physical, mechanical, and shrinkage properties and microstructure of the mortars with recycled PP plastic particles. The sand is substituted with the recycled PP plastic particles at dosages (0%, 20%, 40%, and 60% by volume of the sand). The nano-SiO2 content is 5% by weight of cement. The physical (porosity, water absorption, and density), mechanical (compressive and flexural strength) and shrinkage properties of the mortars were evaluated, and a complementary study on microstructure of the interface between cementitious matrix and PP plastic particles was made. The measurements of physical and mechanical properties showed that PP-filled mortar had lower density and better toughness (higher ratio of flexural strength to compressive strength). However, the compressive strength and flexural strength of PP-filled mortar is reduced, and the porosity, water absorption, autogenous shrinkage, and dry shrinkage increased as compared to normal cement mortar. The addition of nano-SiO2 reduced the porosity, water absorption, and drying shrinkage of PP-filled mortar and effectively improved the mechanical properties, but increased its autogenous shrinkage. A microscopic study of the interfacial zone (plastic-binder) has shown that there is poor adhesion between PP plastic particles and cement paste. From this work, it is found that recycled PP plastic waste has a great potential to be a construction material. It can be used as partial replacement of natural aggregates instead.

1. Introduction

Plastic, a common macromolecule compound, is widely used in all walks of life for its excellent properties of low density, high durability, high impact resistance, and easy processing [1]. According to statistics, the global plastic production in 2017 is nearly 350 million tons [2], and the annual output is growing steadily. China is not only a big producer of plastics, but also a big consumer of plastics. Its total plastic consumption accounts for about a quarter of the world, and has become the largest plastic consumer in the world [3]. Plastics offer many benefits to the society, but unfortunately also drawbacks. For a long time, the main treatment methods of plastic waste in various countries are landfill, incineration, and transportation to other countries. Due to the very low biodegradability of plastic waste [46], landfill will make it exist in the soil for a long time, increasing the burden of land resources, while incineration of plastic waste will produce polycyclic aromatic hydrocarbons, carbon monoxide, and other harmful substances, thereby seriously contaminating the environment. Under the background of global resource shortage, recycling plastic waste can reduce resource waste, avoid environmental pollution, and achieve sustainable development. However, the status of recycling plastic waste is not satisfactory. Even in the developed countries, it is difficult to have a high recycling rate of plastic waste in the areas where infrastructure construction is relatively perfect. For instance, the recycling rate of plastic waste is below 40% in almost all European countries [7]. In 2012, the total amount of plastic waste in municipal solid waste was 31.7 million tons in the United States, only 8.8% of which was recycled [8]. Therefore, how to treat plastic waste efficiently and improve the recycling rate is a difficult problem to be solved urgently.

At present, a promising method of recycling plastic waste is to grind it into recycled plastic particles and mix them into concrete or mortar instead of original building materials [57, 9, 10]. In this way, not only plastic waste can be effectively utilized, but also the environment can be protected, and thus good economic and social benefits can be achieved.

In the past ten years, many researchers have studied the application of plastic waste particles in concrete or mortar. Albano et al. [11] mixed recycled polyethylene terephthalate (PET) into concrete instead of original fine aggregates to study its mechanical behavior. The results indicated that PET-filled concrete showed a decrease in compressive strength, splitting tensile strength, modulus of elasticity, and ultrasonic pulse velocity; however, the water absorption increased when volume proportion and particle size of PET increased. Ismail and Al-Hashmi [12] used plastic waste of fabriform shapes as a partial replacement for sand and found that the results showed a tendency for compressive strength and flexural strength values of plastic waste concrete mixtures to decrease below the plain mixtures by increasing the plastic waste ratio. When plastic waste ratio in concrete was 20%, the flexural strength at 28 days curing age was 30.5% lower than that of the reference concrete. Liang et al. [13] put recycled PP plastic powder into concrete substituting part of fine aggregates, and the results showed that the higher the substitution rate of PP plastic powder, the lower the compressive strength, and the cube compressive strength of PP-filled concrete was 26.2% lower than reference concrete at 20% of substitution of PP plastic particles. Frigione [14] substituted the 5% by weight of fine aggregate (natural sand) in concrete with an equal weight of PET aggregates manufactured from the waste unwashed PET bottles (WPET). It was found that the WPET concrete displayed similar workability characteristics, compressive strength, and splitting tensile strength slightly lower than the reference concrete. It can be seen that the addition of plastic waste particles has a negative impact on the mechanical properties of concrete or mortar. However, it can improve the ductility of concrete or mortar because plastic has certain elasticity. For example, Rebeiz and Craft [15] incorporated plastic waste particles into asphalt concrete and found that the incorporation of plastic waste particles can increase the toughness of asphalt concrete and reduce the occurrence of cracks. Liu et al. [16] put recycled ABS/PC plastic particles into normal concrete to make a plastic modified concrete, and found that the ductility of the modified concrete was improved. Foti [17] made PET bottles into fibers and mixed them into concrete. The results showed that the average tensile strength of the fiber-reinforced concrete is very high, indicating that the ductility of concrete can be improved by adding PET fibers. Hannawi et al. [18] replaced partial natural aggregates by polycarbonate (PC) and PET waste in mortar, and found that the calculated flexural toughness factors increased significantly with increasing volume fraction of PET and PC aggregates. Kou et al. [19] replaced river sand with polyvinyl chloride (PVC) plastic waste granules in percentages of 0%, 5%, 15%, and 30% by volume in concrete. It was found that the concrete prepared with partial replacement by PVC was lighter, more ductile, and had lower drying shrinkage and higher resistance to chloride ion penetration.

The plastic-filled concrete or mortar shows a decrease in compressive strength compared to normal concrete, which limits the application of plastic waste in concrete or mortar. As one of the three emerging technologies in the 21st century, nanotechnology has developed rapidly and is widely used in various industries, including construction industry. Previous studies have shown that the unique size effect of nanomaterials can improve the microstructure of the interfacial transition zone (ITZ) between hardened cement paste and aggregates, and the strength of concrete is increased [2024]. Therefore, the mechanical properties of plastic-filled concrete can be improved by adding nanomaterials. Hasan-Nattaj and Nematzadeh [25] found that the introduction of nano-SiO2 in the fiber-reinforced concrete improved the elastic modulus due to an increase in the compactness of the cement paste bond with aggregates. The experiments of Nazari and Riahi [26] showed that the strength and water permeability of the specimens have been improved by adding SiO2 nanoparticles in the cement paste up to 4.0 wt.%. Zhao and Liu [27] found that the introduction of nano-SiO2 in rubber-recycled concrete amazingly improved the microstructure of rubber-recycled concrete, and the mechanical properties of rubber-recycled concrete are significantly improved. Jo et al. [28] experimentally studied the properties of cement mortars with nano-SiO2. The results showed that nanoscale SiO2 behaved not only as filler to improve mortar cement microstructure, but also as a promoter of pozzolanic reaction.

Polypropylene (PP) plastic is one of the most commonly used consumer plastics, which is widely used in food packaging industry. The PP plastic waste can be ground into particles and applied in concrete or mortar, which can prevent the environmental contamination caused by plastic waste and realize recycling plastic waste. Based on the above research results, the purpose of this paper is to study the possibility of recycling plastic waste as aggregate partially instead of sand in the mortar or concrete, the effects of recycled PP plastic particles content and nano-SiO2 on physical, mechanical, and shrinkage properties of mortar, and to analyze the microcharacteristics of PP-filled mortar with nano-SiO2 by scanning electron microscopy (SEM). The research results can provide references for the application of plastic waste and nanotechnology in concrete or mortar.

2. Materials and Methods

2.1. Materials Used

The materials used in this work were Portland cement, sand, a polycarboxylate-based superplasticizer, nano-SiO2 and recycled PP plastic particles. The Portland cement was purchased from Huainan Shunyue Cement Co., Ltd (China), whose strength grade was 42.5 MPa, density was 3120 kg/m3, and specific surface area was 1.447 m2/g. The chemical composition of the cement is shown in Table 1. The sand was obtained from local sources with fineness modulus of 2.6 and apparent density of 2650 kg/m3. The superplasticizer was produced by Shanxi Qinfen Building Materials Co., Ltd (China), whose water reduction rate was 30%. The nano-SiO2 (content ≥99.5%, powder, particle size ≈ 30 ± 5 nm and specific surface area is 200 m2/g) was produced by Shanghai Keyan Industrial Co., Ltd. The recycled PP plastic particles were purchased from Zhejiang Yuyao Fengli Plastic Co., Ltd (China), which were short columns with lengths from 2 mm to 3.5 mm, elastic modulus of 0.97 GPa, water capacity of less than 0.4%, and relative density of 0.89∼0.92 g/cm3 as shown in Figure 1.

2.2. Mix Design and Processing of Mortars

The mix proportions of mortars are shown in Table 2. The content of the superplasticizer was the percentage of the weight of the cementitious materials. The dosage of superplasticizer was controlled in order to avoid the floating phenomenon of recycled PP plastic particles due to its light density. The plastic particles were added into mortars replacing 0%, 20%, 40%, and 60% sand by volume. The nano-SiO2 content was the 5% by weight of cement. Brief procedure for mortar processing was as follows: (1) put the nanoparticles, cement, and sand in the mixing pot and mix for 2 min, (2) add water and superplasticizer into the mixing pot slowly, and mix for additional 3 min, and (3) add the recycled PP plastic particles into the mixing pot and mix for additional 3 min. During the mixing process, the flowability and workability of the mortar mixtures were kept consistent by adjusting the dosage of the superplasticizer. When this mixing process was finished, the recycled PP plastic particles and nano-SiO2 were homogeneously distributed throughout the mortar.

2.3. Physical Properties Test of Mortar Specimens

The dry weight D, suspended weight S, and saturated weight W of test mortar specimens at day 28 were measured according to ASTM C20-00 [29]. Brief procedure for physical properties test of mortar specimens was as follows: (1) dry the test mortar specimens in an oven at 105°C to constant weight and weigh the dry weight D, (2) place the test mortar specimens in distilled water, boil for 2 hours, and weigh the suspended weight S of each test specimen after boiling and cooling for a minimum of 12 hours and while suspended in water, and (3) blot each specimen lightly with a moistened smooth linen or cotton cloth to remove all drops of water from the surface and determine the saturated weight W. The apparent porosity P, the water absorption A, apparent specific gravity T, and bulk density B are, respectively, calculated according to formulas (1)∼(4):(1)Apparent porosity:(2)Water absorption:(3)Apparent specific gravity:(4)Bulk density:

2.4. Flexural and Compressive Strength Test

The flexural and compressive strength of mortar specimens were determined according to ASTM C348-18 [30] and ASTM C349-18 [31] by molding 24 prism specimens with 40 by 40 by 160 mm, as shown in Figure 2. The mortar specimens were removed from the molds after curing for 24 h in a standard curing box at a temperature of (23 ± 1)°C and a relative humidity of more than 95%. Then, immerse the specimens in saturated lime water for 3 d, 7 d, or 28 d.

2.5. Autogenous Shrinkage

According to ASTM C1698-09 [32], the autogenous shrinkage strain of mortar specimens were measured. The fresh mixture was slowly poured into the corrugated mold during vibration, and then placed on the corrugated plastic support rack. During the tests, maintain the surrounding air temperature at 23.0 ± 1.0°C. At the time of final setting tfs, the first length was measured. The autogenous strain of the specimen at time t, expressed as μm/m, is calculated with the following formula:where is the length of the specimen at time t.

2.6. Dry Shrinkage

According to ASTM C596-18 [33], the dry shrinkage of mortar specimens with 20 by 20 by 280 mm was determined. Moist cure the specimens in the molds in the standard curing box for 24 h. Then, remove the specimens from the molds and cure in lime-saturated water for 48 h. At the age of 72 h, remove the specimens from water, wipe with damp cloth, and immediately obtain a length comparator reading for each specimen. Then, place the specimens in air storage with temperature of (23 ± 1)°C and relative humidity of (50 ± 3)%. Obtain a length comparator reading for each specimen after 1, 2, 3, 4, 5, 6, 7, 14, 21, and 28 days of air storage. Drying shrinkage is calculated by equation,where is the length of the sample at the measuring time, and is the initial length of the sample at the age of 72 h.

2.7. Microscopic Test

When curing time up to 28 days, crush the PP-filled mortar specimens into small pieces with a size of about 8 by 8 by 5 mm, and polish them by a polishing machine, and then dry them in a vacuum drying oven for 48 hours. Fix the dried mortar pieces on a circular platform with a diameter of about 5 cm with double-sided adhesive tape and apply a proper amount of conductive tape to both sides of the mortar pieces, and then remove their surface debris with the ear wash balls. Then, spray the mortar pieces containing paste and plastic with metal coating by magnetron sputtering in magnetron ion diffractometer (MSP-2S), 120 seconds on the front and 30 seconds on the sides. Finally, the microstructures were studied by scanning electron microscopy (HITACHI S3400). In this experiment, the specimens were placed in the center of the scanning electron microscope, and the bonding interface between the recycled PP plastic particles and the cement paste was observed.

All parameters above are explained with mean and standard deviation (SD) values.

3. Results and Discussion

3.1. Physical Properties

The effect of the recycled PP plastic particles' content on physical properties (apparent porosity, water absorption, apparent specific gravity, and bulk density) of the PP-filled mortar after 28 d curing age is shown in Figure 3. The apparent porosity and water absorption have increased considerably for all mortar specimens with the increase of the content of replacement of sand by recycled PP plastic particles. The apparent specific gravity and bulk density have decreased with the increase of recycled PP plastic ratio. For example, compared to PP0, the apparent porosity and water absorption of PP6 increased by 72.02% and 117.02%, respectively, while the apparent specific gravity and bulk density decreased by 15.71% and 20.52%, respectively. The decrease in density of mortars can be attributed to the fact that the density of recycled plastic is lower than that of sand [34]. The images shown in Figure 4 clearly show the good distribution of recycled PP plastic particles in the mortar mixes and there is no phenomenon that PP plastic particles are floating due to their light weight. It should also be noted this distribution has favored to obtain a lightweight mortar [5]. Comparing the curves of PP and PN in Figure 3, it is found that the physical properties of mortar specimens were improved after adding nano-SiO2. For example, compared to PP6, the apparent porosity and water absorption of PN6 were reduced by 24.61% and 24.67%, respectively, and the apparent specific gravity increased by 4.38%, while the bulk density only increased by 0.17%. This shows that the addition of nano-SiO2 can improve the pore structure of plastic mortars, reduce the porosity and water absorption [35, 36], make them more compact, and thus improve the bulk density of plastic mortar.

3.2. Mechanical Properties
3.2.1. Compressive Strength

Test compressive strength results are shown in Figure 5. The compressive strength of PP-filled mortars decreased with increase in plastic waste content at all curing times. Compared to control mixes PP0, the compressive strength of PP2, PP4, and PP6 decreased by 15.19%, 38.98%, and 53.53%, respectively, at day 28, which shows that the compressive strength of PP-filled mortars has an approximate linear reduction relationship with the dosage. The reduction in the compressive strength of PP-filled mortars might be due to either a very poor bond strength between the cement paste and the surface of the recycled PP plastic particles or the low strength of this recycled PP plastic particles and or the hydrophobic nature of plastic waste, which can inhibit cement hydration reaction by restricting water movement. The plastic has smaller elastic modulus [37], and its ability to transfer stresses is poor, playing the role of ‘porosity’. The fracture section after the compression test is shown in Figure 6. The grooves left by the recycled PP plastic particles peeling off from cement paste can be clearly seen in Figure 6, which shows the low bond strength between the surface of the recycled PP plastic particles and the cement paste.

Therefore, improving the compressive strength of plastic mortar or concrete is the key to the application of plastic waste in mortar or concrete. When 5% nano-SiO2 was added to the mortars, the compressive strength of the mortars was obviously improved. The compressive strength of PN0, PN2, PN4, and PN6 increased by 20.38%, 15.87%, 36.36%, and 10.66%, respectively, compared to PP0, PP2, PP4, and PP6 at day 7. This is due to the physical properties of nano-SiO2. The nano-SiO2 particle size is very small, which can be used as a physical filler to make the interface between the aggregates and cement paste more compact. At the same time, the nano-SiO2 has high activity. Nano-SiO2 can react with Ca(OH)2 in the interfacial transition zone between the aggregates and cement paste to form C-S-H gel [26], which can enhance the structure of the interfacial transition zone and thus increase the compressive strength of plastic mortar.

3.2.2. Flexural Strength

The results of the flexural strength of mortar specimens have been given in Figure 7. According to these results, the flexural strength of mortar specimens decreased with the increase in PP plastic particles content. Compared to control mixes PP0, the flexural strength of PP2, PP4, and PP6 decreased by 9.70%, 31.08%, and 43.04%, respectively, at the age of day 28. This is due to the low resistance of the plastic waste [5]. When nano-SiO2 was added, the flexural strength of mortar specimens was bigger than that of mortar specimens without nano-SiO2. For example, compared to PP0, PP2, PP4, and PP6, the flexural strength of PN0, PN2, PN4, and PN6 increased by 12.38%, 12.77%, 16.93%, and 3.96%, respectively, at day 28. Therefore, the addition of nano-SiO2 can compensate for the negative impact on the flexural strength of mortar specimens to a certain extent because of the use of plastic waste as sand-substitution aggregate, which will promote the application of plastic waste in mortar or concrete.

3.2.3. Flexural-Compressive Ratio

The flexural-compressive ratio of mortar specimens as function of the recycled PP plastic particles content is shown in Figure 8. According these results, the flexural-compressive ratio of plastic mortar increased with the increase in recycled PP plastic particles content. Compared to the control mixes PP0, the flexural-compressive ratio of PP2, PP4, and PP6 increased by 6.47%, 12.95%, and 22.57%, respectively, at day 28. This shows that recycled PP plastic particles can effectively improve the toughness of mortar because the flexural-compressive ratio can reflect the toughness of concrete or mortar, and the greater the flexural-compressive ratio, the better the toughness of concrete [38]. The results of PN, adding nano-SiO2, are consistent with and are slightly higher than those of PP without nano-SiO2. This is due to that adding nano-SiO2 can improve mortar structure and increase its strength. The strength of PP-filled mortar is less than that of the control normal mortar; however, PP-filled mortar has better toughness, which has potential application in construction and buildings with toughness requirements.

For the mortar specimens with 20–60% of substitution of recycled PP plastic particles by volume of the sand, the compressive strength at day 28 decreased by between 15.19% and 53.53%, and the flexural strength decreased by between 9.70% and 43.04%. Therefore, if there is a requirement for the strength of the concrete or mortar, it is suggested that the substitution ratio of plastic waste should be controlled within 20% by volume of the sand. When conditions permit, a certain amount of nano-SiO2 can be added into the concrete or mortar to increase its strength and toughness. For non-load-bearing structures without too high strength requirements or buildings with toughness requirements, the amount of recycled PP plastic particles can be increased appropriately.

3.3. Autogenous Shrinkage

The results of the autogenous shrinkage of mortar specimens as function of curing time are shown in Figure 9.

According to the results, the autogenous shrinkage of mortar specimens increased slightly with increase in the recycled PP plastic particles content. Compared to PP0, the autogenous shrinkage of PP2, PP4, and PP6 increased by 7.39%, 18.75%, and 27.08%, respectively, at day 28. This can be attributed to the facts that the addition of PP plastic particles results in the mortar specimens less compact, and the elastic modulus of plastic particles is smaller than that of natural aggregates [37], while the autogenous shrinkage of mortar increases with the decrease of elastic modulus of aggregates [39]. Moreover, with the increase of recycled PP plastic particles content, the porosity of PP-filled mortar increases gradually, and its stiffness decreases gradually, which will result in the increase of deformation and autogenous shrinkage.

It can also be seen from Figure 9 that the incorporation of nano-SiO2 had a great influence on the autogenous shrinkage deformation of plastic mortar. At day 28, compared to PP0, PP2, PP4, and PP6, the autogenous shrinkage of PN0, PN2, PN4, and PN6 groups increased by 46.59%, 74.43%, 73.21%, and 115.35%, respectively. This observation was already verified by Guo et al. [40]. Nano-SiO2 can refine the pore size distribution in the plastic mortar [41], which leads to an increase of capillary tension and a corresponding increase of autogenous shrinkage. At the same time, the larger specific surface area of nano-SiO2 [25, 42] leads to the rapid combination of nano-SiO2 and the mixed water in the mortar, which further aggravates the water shortage between the pores of the cement paste, reduces the relative humidity inside the cement paste, and increases the autogenous shrinkage.

3.4. Drying Shrinkage

The drying shrinkage curves of plastic mortar are shown in Figure 10.

Similar to autogenous shrinkage, the drying shrinkage of mortars increased with the increase in recycled PP plastic particles' content. Compared to PP0, the drying shrinkage of PP2, PP4, and PP6 increased by 12.06%, 22.06%, and 34.49%, respectively, at day 28. The reason is that with the increase of recycled PP plastic particles' content, the internal porosity of mortars increases gradually, and free water and capillary water in mortar are easier to evaporate [43], and the drying shrinkage deformation is greater. It can also be seen from Figure 10 that the drying shrinkage deformation of plastic mortar can be decreased by adding nano-SiO2. Compared to PP0, PP2, PP4, and PP6, the drying shrinkage of PN0, PN2, PN4, and PN6 decreased by 6.06%, 6.11%, 11.48%, and 5.48%, respectively, at day 28. This may be because the microfilling effect of nano-SiO2 can reduce the content of capillary pores in plastic mortar, and the shrinkage of plastic mortar is usually caused by water loss of capillary pores. The refinement pore size of nano-SiO2 can increase the difficulty of moisture migration and reduce the shrinkage of plastic mortar [44]. In addition, in cement hydration process, nano-SiO2 consumes a large amount of CH to form dense C-S-H, resulting the plastic mortar’s microstructure more compact and firm, and more resistant to shrinkage deformation due to water dispersion loss [45]. The results of this study are consistent with the results of studies by Li and Yao [45], Güneyisi et al. [46], and Du and Pang [47]. Furthermore, the drying shrinkage of plastic mortar was larger than its autogenous shrinkage whether nano-SiO2 was added or not, which is related to the drying shrinkage mechanism. Drying shrinkage is the result of the combined action of volume shrinkage and internal autogenous shrinkage caused by the loss or migration of pore water in concrete in the air.

3.5. Microstructural Study

The SEM of PP0, PN0, PP6, and PN6 at curing age of 28 days is shown in Figure 11, which magnifies the microstructure 350 times and 3000 times. It is observed in Figure 11(a) that there are some obvious cracks and voids at the interface between sand and cement paste. Compared to PN0, the structure of PP0 is less dense, and PP0 has more porosity and wider cracks. By contrast, it is observed in Figure 11(b) that the structure of PN0 is more compact with fewer cracks. This is due to the size effect of the nano-SiO2, which can fill into the pores between sand and cement paste, make the structure denser, and improve the strength of mortar. The poor adhesion between the plastic and the cement paste is clearly observed in Figure 11(c). Compared to PP0, PP6 has more porosity and wider cracks, and the structure of PP0 is less dense. And, it is noticeable that the recycled PP plastic particles can be manually and easily pulled out from the matrix at the fracture section of the mortar specimens, which is consistent with the results of SEM. Figure 11(d) shows that the structure of PP-filled mortar with nano-SiO2 is denser with relatively good adhesion between the plastic and cement paste. Compared to PP0 and PP6, the PN0 and PN6 become more compact and uniform due to the filling effect of the nano-SiO2, and then improved strength can be achieved.

4. Conclusions

This paper has presented the results of a systematic study on the influence of nano-SiO2 and recycled PP plastic particles' content on physical, mechanical, and shrinkage properties of mortar. From the results obtained from this study, the following conclusions can be drawn:(i)This plastic waste type can be used successfully as aggregate instead of sand in mortar.(ii)With the increase in the replacement ratio of sand by recycled PP plastic particles:(1)The apparent porosity and water absorption of plastic mortar increase,(2)The apparent specific gravity, bulk density, compressive strength, and flexural strength decrease,(3)The toughness is improved because the flexural-compressive ratio increases, and(4)The autogenous shrinkage and dry shrinkage increase.(iii)The addition of nano-SiO2 reduces the porosity, water absorption, and drying shrinkage of plastic mortar, increases its density and flexural-compressive ratio, and effectively improves the compressive and flexural strength of plastic mortar. However, the addition of nano-SiO2 also increases the autogenous shrinkage of plastic mortar. Therefore, when using nano-SiO2 to enhance the mechanical properties of plastic mortar, the adverse effect on autogenous shrinkage strain of plastic mortar should be considered.(iv)The results of SEM show that there is a poor adhesion between recycled PP plastic particles and cement paste. Nano-SiO2 can make the interface structure between cement paste and aggregates (natural aggregate and PP plastic aggregate) more compact, thus improving the mechanical properties of plastic mortar.

Data Availability

The data used to support the findings of this study are available from the corresponding author upon request.

Conflicts of Interest

The authors declare no conflicts of interest.

Acknowledgments

This work was funded by the National Natural Science Foundation of China (Project No. 41440018, 41977236, and 41672278) and the National Natural Science Foundation of China Overseas and Hong Kong-Macao Scholar Cooperative Research Foundation (Project No. 51728201).