1. Introduction
A large number of waste tires are generated worldwide every year [
1]. Tires are not biodegradable, the necessary periods for degradation are too long to be considered practically feasible. Therefore, the development of other new uses has been the focus of numerous studies. Many researchers [
2,
3,
4,
5,
6] have suggested promising options to for this rubber, such as (1) creation of mixtures of rubber, asphalt, and cement; (2) generation of fuel; and (3) reuse. In Taiwan, scrap tires have been used as a fuel for cement kilns and as feedstock for making carbon black. Rubber has a high capital investment, and while using tires as a fuel is technically feasible, it is not very economically or environmentally attractive [
7,
8].
It is well known that crumb rubber can be used as an additive to form a cement matrix composite known as rubcrete. Rubcrete has the ability to absorb a large amount of energy under compressive and tensile loads [
9,
10,
11,
12], so it is recommended for use in circumstances where vibration damping is required, such as in shock absorbers or sound barriers in highway construction, and as an earthquake shock-wave absorber in buildings [
9,
10,
13].
Because rubcrete is a useful material, many studies have focused on modifying crumb rubber to improve it as a concrete additive. However, because the hydrophobic crumb rubber does not distribute well in the hydrated cement and it does not bond firmly with the cement hydrate, rubcrete has a lower mechanical strength than concrete [
14,
15,
16,
17,
18,
19,
20]. To promote the use of rubcrete, the mechanical strength of rubcrete needs to be improved [
1].
Lee et al. [
15] suggested that the loss of mechanical strength may be improved by a proper surface treatment of the crumb rubber. Segre and Joekes [
21,
22] suggested that rubber particles with rough surfaces may have improved bonding with the cement matrix. Chou et al. [
23] showed that an NaOH treatment enhanced the adhesion of tire rubber particles to the cement paste. Thus, the mechanical properties of rubcrete with the NaOH-treated rubber crumbs were improved over those of the rubcrete with the as-received crumb rubber. Siddique and Naik [
3,
24] gave a detailed review on this topic.
To improve the compressive strength of rubcrete [
25,
26], most studies have tried to modify the surface properties of the rubber particles for enhanced adhesion to calcium silicate hydrate (C–S–H) colloidal probes. Chou et al. [
24] showed that the adsorption of waste organic sulfur compounds on the rubber surface could enhance the hydrophilicity of the rubber and was helpful in improving the intermolecular interactions between the rubber and C–S–H. Chou et al. [
27] also prepared mortars with partially oxidized crumb rubber and found that the compressive strength of the rubberized mortars increased 10% in comparison with that of the controlled mortar.
They suggested that the presence of sulfur compounds on the surface of the treated rubber may increase the strength of the rubberized mortars with the partially oxidized crumb rubber.
In this study, to prevent any effect from sand, rubberized cement pastes (instead of mortars) were prepared to understand the effects of partial oxidation on the bonds between C–S–H moieties and the treated crumb rubber. The crumb rubber was partially oxidized to enhance its hydrophilicity. Reactions were conducted in a batch reactor under various reaction conditions. The functional groups on the surfaces of the treated crumb rubber were observed via Fourier transform infrared spectroscopy (FT-IR). The contact angles of water drops on the rubber surface were measured statically. The intermolecular interactions between the rubber and the C–S–H were measured with an atomic force microscope (AFM). Cement pastes with the treated crumb rubber and the as-received crumb rubber were prepared to observe the distribution of the crumb rubber within the cement hydrate.
2. Materials and Methods
Crumb rubber (styrene-butadiene rubber (SBR) + natural rubber) used in this study was supplied by the Chih Cheng Rubber Factory Co. LTD, Taiwan. The crumb rubber was screened to a particle size range of 300– 600 μm for use in the cement-matrix composite (
Figure 1).
To prepare the rubber specimens for measurements of the intermolecular forces, rubber sheets (10 mm × 10 mm × 0.1 mm) were cleaned with acetone and distilled water to remove any possible contaminants on the surface. The surface roughness of the rubber specimen was observed by AFM (JPK, Axiovert 200, Berlin, Germany). To measure the intermolecular forces, a colloidal probe with C–S–H was prepared according to the method proposed by Plassard et al. [
28]. Both types of rubber samples were treated by partial oxidation using the same reaction conditions. The temperature within the reactor was controlled by an electrical heating system. The flow rates of air and nitrogen were controlled and recorded to determine the air/nitrogen ratio. There were three air/nitrogen ratios: 1/0, 1/4, and 0/1. The temperatures were kept at 200 °C or 250 °C. The gas flow rate was 100 ± 10 mL/min for 30 min. The gas flows were then stopped and the temperature was raised to the desired level.
Figure 2 shows the batch reactor used in this study to partially oxidize crumb rubber [
27].
The change in surface functional groups of the crumb rubber was observed using FT-IR (Shimadzu FTIR-8400, Japan). The instrument “Goniometer” (Sindatek Model 100SB) was used to measure the contact angle of the rubber.
Pastes with a crumb rubber level of 5% by weight were tested. The first type of Portland cement was used in this study. Specimens were prepared with a cubic molder (5 cm × 5 cm × 5 cm) to facilitate the physical testing and with water/cement 0.35 (
Figure 3).
The fracture surfaces of hardened paste fragments obtained from the compressive test were observed with SEM (Hitachi SU8010, Japan) and FT-IR. The measurement of compressive strength of specimens was conducted according to ASTM standards methods, C109. Specimens aged 7 days, 14 days, 28 days, and 56 days were tested. For statistical analysis, 6 samples were used for each test. Specimens were indicated by C0, UR5, and TR5 for identification. Among them, C0 was a pure cement paste, UR5 was a paste having 5% by weight of the as-received crumb rubber, and TR5 was a paste having 5% by weight of the treated crumb rubber.
3. Results
3.1. TGA Analysis of Crumb Rubber
The as-received crumb was analyzed by thermogravimetric analysis (TGA) under both nitrogen and air ambient to understand its characteristics to determine the reaction temperature. The results are shown in
Figure 4. The first weight loss under N
2 flow, between 200 and 300 °C [
29] was attributed to the volatilization of processing oil or other low boiling-point components. The next mass loss observed in the N
2 flow, which has a maximum rate at 350 °C, was due to the decomposition of natural rubber (NR). Since the crumb rubber used in this study contained fillers (such as carbon black and inorganic fillers), and the fillers had little mass loss at high temperature, the residue of the crumb rubber was therefore greater than that of NR. In the air, oxygen reacted with carbon black, so the residue of the crumb rubber in nitrogen was greater than that in the air (
Figure 4).
Under both conditions, the two curves crossed at 350 °C. This is consistent with the results from several references [
29,
30,
31,
32]. In our experiments, we maintained the temperature of the reactor at 200 °C, and 250 °C individually to prevent from over-cracking.
3.2. FT-IR Spectra of Crumb Rubber
Figure 5 shows the IR spectra of the crumb rubber treated under various reaction conditions. Where 200 and 250 are reaction temperatures (Celsius), and R represents the air/nitrogen flow ratio (R1: air/nitrogen flow = 1/0, R2: air/nitrogen = 1/4, and R3: air/nitrogen flow = 0/1). UR is the as-received rubber. The absorption in the region from 1000–1100 cm
−1 corresponds to the stretching absorption of the two S–O bonds in the R–SO
2–R functional groups [
33]. The region from 960– 980 cm
−1 corresponds to the S=O bond stretching absorption of the R–SO–R functionalities [
33]. The region from 2800–3100 cm
−1 corresponds to a C–H (sp
3) stretching adsorption [
33].
By treating the crumb rubber with partial oxidation, some of the R–S–R groups on the surface of the crumb rubber were oxidized to R–SO2–R, and R–SO–R. The production of S–O bonds on the surface of the rubber made the treated material more hydrophilic than the as-received rubber.
The area of the sp
3 hydrocarbon bond (C–H) stretching absorption and the area of the SO
2 and S–O (SOx) stretching absorption were integrated individually. The ratio of the SOx to C–H (sp
3) areas in the IR spectrum was chosen as an index to evaluate the performance of the reaction, as shown in Equation (1).
The area ratios (area of SOx/area of C–H) were calculated for the various tested air/nitrogen ratios and are listed in
Table 1.
Table 1 shows that air/nitrogen = 1/4 (R2) was the optimal gas flow ratio at both tested temperatures (200 °C and 250 °C). As depicted in
Figure 3, the sulfur on the surface of the rubber could be oxidized to SOx. This might be caused by oxidation of the sulfur atoms on the surface of the crumb rubber when the oxygen content present is sufficient. However, when the oxygen content is increased at high temperature, excessive oxidation of the sulfur atoms induced thermal cracking of the crumb rubber and reduced the area ratio. Chou et al. [
27] suggested that the partial oxidation reaction should be conducted at or below 250 °C with an oxygen/nitrogen ratio of 0.04 or less. Based on this result, an air/nitrogen gas flow of 1/4 was chosen for the subsequent experiments.
3.3. Effect of Partial Oxidation on the Wettability of Rubber Surfaces and the Intermolecular Forces
The surface morphology of the rubber is shown in
Figure 6. The treated rubber particles have a rougher, rippled surface, which could improve bonding with the cement matrix as described by Segre and Joekes [
21,
22].
It is well-known that rubber is a hydrophobic polymer and hydration products of cement are hydrophilic inorganic materials. The hydrophobic materials have a large contact angle and low wettability. The main interaction forces between the hydrophilic and hydrophobic materials are van der Waals forces, which are very weak. With the low interaction forces between C–S–H (the most important product of cement hydration) and rubber, the compressive strength of the cement-matrix composite containing crumb rubber will be much less than that of cement-matrix composite without crumb rubber.
3.4. Contact Angles
Results of contact angle measurements are presented in
Figure 7. The treated rubber has a lower contact angle than that of the as-received rubber. It was apparent that the partial oxidation treatment reduced the contact angle and, thus, enhanced the hydrophilicity of the rubber surface. It has been previously shown that enhanced hydrophilicity of the rubber surface increases the local water availability for the hydration of cement [
23]. An increase in the water availability can prevent local imperfections in the hydration of the cement by the addition of heterogeneous rubber particles.
3.5. The C–S–H Colloidal Probe
Figure 8 shows a colloidal C–S–H probe, and
Figure 8a shows the original probe for comparison. The colloidal C–S–H probe grew at the apex of the probe, as shown in
Figure 8b.
3.6. Intermolecular Interactions
The intermolecular interactions between the C–S–H colloidal probe and the rubber were measured via AFM, as-received rubber showed the smallest forces (
Figure 9a). Furthermore, the rubber treated by partial oxidation clearly had stronger interactions with the C–S–H than the as-received rubber while the typical force-distance relationship is shown in
Figure 9. The force distributions of the rubbers treated under various reaction conditions is shown in
Figure 10. It was clear that the rubber treated at 250 °C displayed the largest intermolecular forces, and the as-received rubber showed the smallest forces.
3.7. The SEM Image of the Rubber and Cement
Pastes with crumb rubber were observed with SEM to understand the effects of partial oxidation on the hydration of the cement. There are many kinds of cement crystal, such as calcium hydroxide (C–H), calcium monosulfoaluminate (AFm), ettringite (Aft), and calcium silicate hydrate (C–S–H) which are more representative. The SEM images are shown in
Figure 11. These SEM images show that the calcium silicate hydrate (C–S–H) on the treated rubber is much more than the C–S–H on the as-received rubber. This proves that partial oxidation contributes to the formation of C–S–H on the rubber surface.
3.8. The Compressive Strength
The compressive strengths of the various hardened cement pastes are shown in
Figure 12, where C0 represents the pure cement paste, UR5 is the cement paste with 5 wt% of the as-received crumb rubber, and TR5 is the paste with 5 wt% of the treated crumb rubber. The compressive strength of the hardened paste with the as-received crumb rubber decreased as much as 45% in comparison to that of the pure hardened paste (56 days). The compressive strength of the pure hardened cement paste is consistent with that of previous reports [
34,
35]. However, the compressive strength of the hardened paste with the treated crumb rubber was reduced by only 17% to 18%. The partial oxidation treatment induces the formation of hydrophilic function groups on the surface of rubber (as depicted in the IR spectra
Figure 5) and therefore increases the hydrophilicity of the surface of the rubber, and the contact angle of water on the surface of the rubber decreases. It implies that the hydrophilic fresh cement paste can be spread well on the surface of the treated rubber and the hydrophilic C–S–H can also adhere firmly to the hydrophilic surface of the treated rubber. The mechanical strengths of this cement-based composite are therefore improved. These experimental results provide evidence that partial oxidation is an effective method to improve the properties of waste crumb rubber as an additive in cement-based composites.
4. Conclusions
The addition of rubber materials to cement mixtures decreases the physical properties of the concrete. To combat this challenge and achieve improved physical properties, partial oxidation of the rubber surface was performed in this study. The rubber treated by partial oxidation had enhanced hydrophilicity, which increased the intermolecular interactions between the rubber and a colloidal C–S–H probe, and in turn, increased the local water availability for the hydration of the cement. This increase in the water availability prevents local imperfections in the hydration of the cement on the addition of heterogeneous rubber particles. Thus, the modification of rubber surfaces via a partial oxidation reaction is a simple, economically viable process to improve the performance of rubber-concrete composites.
Author Contributions
M.-T.L. designed the experiments; C.-Y.C. performed the experiments; M.-T.L. and C.-Y.C. analyzed the data; and M.-T.L. and C.-Y.C. wrote the paper.
Funding
All New Chemical Engineering Consultants Company.
Acknowledgments
All New Chemical Engineering Consultants Company, Chun-Nan Lin, and Jau-Hung Chen are acknowledged.
Conflicts of Interest
The authors declare no conflict of interests.
References
- Li, Z.; Li, F.; Li, J.S.L. Properties of concrete incorporating rubber tyre particles. Mag. Concr. Res. 1998, 50, 297–304. [Google Scholar] [CrossRef]
- Fang, Y.; Zhan, M.; Wang, Y. The status of recycling of waste rubber. Mater. Des. 2001, 22, 123–128. [Google Scholar] [CrossRef]
- Siddique, R.; Naik, T.R. Properties of concrete containing scrap-tire rubber--an overview. Waste Manag. 2004, 24, 563–569. [Google Scholar] [CrossRef] [PubMed]
- Youssf, O.; ElGawady, M.A.; Mills, J.E.; Ma, X. An experimental investigation of crumb rubber concrete confined by fibre reinforced polymer tubes. Constr. Build. Mater. 2014, 53, 522–532. [Google Scholar] [CrossRef]
- Mendis, A.S.M.; Al-Deen, S.; Ashraf, M. Behaviour of similar strength crumbed rubber concrete (crc) mixes with different mix proportions. Constr. Build. Mater. 2017, 137, 354–366. [Google Scholar] [CrossRef]
- Xie, J.-H.; Guo, Y.-C.; Liu, L.-S.; Xie, Z.-H. Compressive and flexural behaviours of a new steel-fibre-reinforced recycled aggregate concrete with crumb rubber. Constr. Build. Mater. 2015, 79, 263–272. [Google Scholar] [CrossRef]
- Guo, S.; Dai, Q.; Si, R.; Sun, X.; Lu, C. Evaluation of properties and performance of rubber-modified concrete for recycling of waste scrap tire. J. Clean. Prod. 2017, 148, 681–689. [Google Scholar] [CrossRef]
- Onuaguluchi, O.; Panesar, D.K. Hardened properties of concrete mixtures containing pre-coated crumb rubber and silica fume. J. Clean. Prod. 2014, 82, 125–131. [Google Scholar] [CrossRef]
- Topçu, L.B.; Avcular, N. Analysis of rubberized concrete as a composite material. Cem. Concr. Res. 1997, 27, 1135–1139. [Google Scholar] [CrossRef]
- Avcular, N.; Topçu, I. Collision behaviours of rubberized concrete. Cem. Concr. Res. 1997, 27, 1893–1898. [Google Scholar]
- Li, G.; Garrick, G.; Eggers, J.; Abadie, C.; Stubblefield, M.A.; Pang, S.-S. Waste tire fiber modified concrete. Compos. Part B: Eng. 2004, 35, 305–312. [Google Scholar] [CrossRef]
- Topçu, I.B.; Bilir, T. Analysis of rubberized concrete as a three-phase composite material. J. Compos. Mater. 2009, 43, 1251–1263. [Google Scholar] [CrossRef]
- Fattuhi, N.I.; Clark, L.A. Cement-based materials containing shredded scrap truck tyre rubber. Constr. Build. Mater. 1996, 10, 229–236. [Google Scholar] [CrossRef]
- Eldin, N.N.; Senouci, A.B. Observations on rubberized concrete behavior. Cem. Concr. Aggreg. 1993, 15, 74–84. [Google Scholar]
- Lee, B.I.; Burnett, L.; Miller, T.; Postage, B.; Cuneo, J. Tyre rubber/cement matrix composites. J. Mater. Sci. Lett. 1993, 12, 967–968. [Google Scholar] [CrossRef]
- Topçu, İ.B. Assessment of the brittleness index of rubberized concretes. Cem. Concr. Res. 1997, 27, 177–183. [Google Scholar] [CrossRef]
- Toutanji, H.A. The use of rubber tire particles in concrete to replace mineral aggregates. Cem. Concr. Compos. 1996, 18, 135–139. [Google Scholar] [CrossRef]
- Hernández-Olivares, F.; Barluenga, G.; Bollati, M.; Witoszek, B. Static and dynamic behaviour of recycled tyre rubber-filled concrete. Cem. Concr. Res. 2002, 32, 1587–1596. [Google Scholar] [CrossRef]
- Hernández-Olivares, F.; Barluenga, G. Fire performance of recycled rubber-filled high-strength concrete. Cem. Concr. Res. 2004, 34, 109–117. [Google Scholar] [CrossRef]
- Oikonomou, N.; Mavridou, S. Improvement of chloride ion penetration resistance in cement mortars modified with rubber from worn automobile tires. Cem. Concr. Compos. 2009, 31, 403–407. [Google Scholar] [CrossRef]
- Segre, N.; Joekes, I. Use of tire rubber particles as addition to cement paste. Cem. Concr. Res. 2000, 30, 1421–1425. [Google Scholar] [CrossRef]
- Segre, N.; Monteiro, P.J.; Sposito, G. Surface characterization of recycled tire rubber to be used in cement paste matrix. J. Colloid Interface Sci. 2002, 248, 521–523. [Google Scholar] [CrossRef] [PubMed]
- Chou, L.H.; Lu, C.K.; Chang, J.R.; Lee, M.T. Use of waste rubber as concrete additive. Waste Manag. Res. 2007, 25, 68–76. [Google Scholar] [CrossRef]
- Chou, L.H.; Lin, C.N.; Lu, C.K.; Lee, C.H.; Lee, M.T. Improving rubber concrete by waste organic sulfur compounds. Waste Manag. Res. 2010, 28, 29–35. [Google Scholar] [CrossRef] [PubMed]
- Youssf, O.; Mills, J.E.; Hassanli, R. Assessment of the mechanical performance of crumb rubber concrete. Constr. Build. Mater. 2016, 125, 175–183. [Google Scholar] [CrossRef]
- Aliabdo, A.A.; Abd Elmoaty, A.E.M.; AbdElbaset, M.M. Utilization of waste rubber in non-structural applications. Constr. Build. Mater. 2015, 91, 195–207. [Google Scholar] [CrossRef]
- Chou, L.-H.; Yang, C.-K.; Lee, M.-T.; Shu, C.-C. Effects of partial oxidation of crumb rubber on properties of rubberized mortar. Compos. Part B: Eng. 2010, 41, 613–616. [Google Scholar] [CrossRef]
- Plassard, C.; Lesniewska, E.; Pochard, I.; Nonat, A. Nanoscale experimental investigation of particle interactions at the origin of the cohesion of cement. Langmuir 2005, 21, 7263–7270. [Google Scholar] [CrossRef]
- Fernández-Berridi, M.J.; González, N.; Mugica, A.; Bernicot, C. Pyrolysis-ftir and tga techniques as tools in the characterization of blends of natural rubber and sbr. Thermochim. Acta 2006, 444, 65–70. [Google Scholar] [CrossRef]
- Kaminsky, W.; Mennerich, C.; Zhang, Z. Feedstock recycling of synthetic and natural rubber by pyrolysis in a fluidized bed. J. Anal. Appl. Pyrolysis 2009, 85, 334–337. [Google Scholar] [CrossRef]
- Kaminsky, W.; Mennerich, C. Pyrolysis of synthetic tire rubber in a fluidised-bed reactor to yield 1,3-butadiene, styrene and carbon black. J. Anal. Appl. Pyrolysis 2001, 58–59, 803–811. [Google Scholar] [CrossRef]
- Miguel, G.S.; Fowler, G.D.; Sollars, C.J. Pyrolysis of tire rubber: Porosity and adsorption characteristics of the pyrolytic chars. Ind. Eng. Chem. Res. 1998, 37, 2430–2435. [Google Scholar] [CrossRef]
- Yang, Z.; Shi, X.; Creighton, A.T.; Peterson, M.M. Effect of styrene–butadiene rubber latex on the chloride permeability and microstructure of portland cement mortar. Constr. Build. Mater. 2009, 23, 2283–2290. [Google Scholar] [CrossRef]
- Poon, C.S.; Kou, S.C.; Lam, L. Compressive strength, chloride diffusivity and pore structure of high performance metakaolin and silica fume concrete. Constr. Build. Mater. 2006, 20, 858–865. [Google Scholar] [CrossRef]
- Chindaprasirt, P.; Jaturapitakkul, C.; Sinsiri, T. Effect of fly ash fineness on compressive strength and pore size of blended cement paste. Cem. Concr. Compos. 2005, 27, 425–428. [Google Scholar] [CrossRef]
© 2019 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (http://creativecommons.org/licenses/by/4.0/).