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Zhang, L.;  Zhang, C.;  Zhang, Z.;  Wang, H.;  Wang, S. Tire Rubber and Its Degradation Behavior. Encyclopedia. Available online: https://encyclopedia.pub/entry/31693 (accessed on 19 April 2024).
Zhang L,  Zhang C,  Zhang Z,  Wang H,  Wang S. Tire Rubber and Its Degradation Behavior. Encyclopedia. Available at: https://encyclopedia.pub/entry/31693. Accessed April 19, 2024.
Zhang, Lu, Chuanping Zhang, Zhen Zhang, Hanbing Wang, Shifeng Wang. "Tire Rubber and Its Degradation Behavior" Encyclopedia, https://encyclopedia.pub/entry/31693 (accessed April 19, 2024).
Zhang, L.,  Zhang, C.,  Zhang, Z.,  Wang, H., & Wang, S. (2022, October 28). Tire Rubber and Its Degradation Behavior. In Encyclopedia. https://encyclopedia.pub/entry/31693
Zhang, Lu, et al. "Tire Rubber and Its Degradation Behavior." Encyclopedia. Web. 28 October, 2022.
Tire Rubber and Its Degradation Behavior
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This entry is adapted from the peer-reviewed paper 10.3390/polym14204429

The use of ground tire rubber (GTR) for modifying asphalt is very promising and is a sustainable development strategy. The addition of GTR to asphalt shows many improvements in the physical, chemical and mechanical properties of the rubber asphalt binder, such as enhanced stiffness, increased skid resistance, extended service life, mitigated fatigue cracking and so on.

devulcanized rubber rubberized asphalt colloidal structure

1. Introduction

One of the key challenges in waste management, especially in the disposal of end-of-life tires, has always been the task of monitoring in the 21st century [1]. The most widespread disposal methods for end-of-life tires are landfills and incineration [2], causing much environmental pollution due to the nonbiodegradability, flammability and chemical characteristic of scrap tires, such as the emission of toxic gases and other harmful substances [3][4]. On the other hand, scrap tires are mainly composed of vulcanized rubber, reinforcing filler and a variety of materials, which is not only an environmental pollutant but also a great economic loss. Therefore, recycling and reuse of these waste materials are of great significance considering the world is facing a lack of resources and a shortage of energy.
The use of ground tire rubber (GTR) for modifying asphalt is very promising and is a sustainable development strategy [5]. The addition of GTR to asphalt shows many improvements in the physical, chemical and mechanical properties of the rubber asphalt binder, such as enhanced stiffness, increased skid resistance, extended service life, mitigated fatigue cracking and so on [6][7][8]. However, the multiple cross-linking network structure of GTR leads to not only high energy consumption and pollution emissions but also results in the poor compatibility and bad stability of rubber asphalt. The above problems limit the efficient utilization and cause the unscientific application of rubber asphalt. In view of this, devulcanization or degradation of the cross-linking network is urgent for reutilization with high efficiency.
In order to obtain stable rubber asphalt with good performance, the compatibility between asphalt and rubber should be improved. Tire rubber is usually composed of cross-linked rubber, carbon black (CB), silica and so on [9]. Devulcanization or degradation destroys the cross-linked network and rubber body carbon chains to be short chains and other separated small substances such as CB. Most previous studies focused on the devulcanization of rubber and the reduced molecular weight of sol fraction (Table 1); less is reported about the decreased size of CB (from several micrometers to micro-nanometers, Figure 1A–C) with the increase in degradation degree [10][11]. These degraded substances are well dispersed in the asphalt, as shown in Figure 1D [12]. Therefore, deeply degraded rubber provides a new strategy for preparing rubberized asphalt from a different perspective.
Polymers 14 04429 g001
Figure 1. (A–C) SEM micrographs of carbon black obtained from (A–C) at different degraded temperatures of 260 °C, 280 °C and 300 °C  [10]; (D) TEM micrograph of degraded rubber in the asphalt [12]. Insert: The enlarged TEM micrograph.
Table 1. Molecular weight and its distribution of sol fraction [11].
Temperature/°C M¯¯¯¯n(104 g/mol) M¯¯¯¯w(104 g/mol) M¯¯¯¯w/M¯¯¯¯n
220 1.19 6.12 5.12
240 1.25 6.01 4.79
260 1.42 6.89 4.84
280 1.34 6.29 4.70
300 0.41 2.28 5.57
The DR mainly consisted of micro-nano CB, low molecular weight of sol fraction and inorganic substances, denoted as micro-nano rubber. The DR showed much better dispersibility and reinforcement compared with GTR, thus usually used for the modification of asphalt with high content. Therefore, the DR was more and more used as the potential alternative for asphalt in pavement, which significantly improved the anti-cracking and anti-aging performance [13][14][15]. Although DRMA demonstrates much improved properties compared with both base asphalt or GTR modified asphalt, the standardized applications of rubber asphalt have always been a challenge for the lack of a deep understanding of the mixing mechanism, especially on a colloidal scale.

2. Tire Rubber and Its Degradation Behavior

2.1. Chemical Composition of Tire Rubber

Tire rubber has a crucial role in many fields such as industry, agriculture and national defense. It is reported that the global tire output is about 1.5 billion each year and that of waste tires is more than 17 million tons each year. With the increased demand for tires in developing countries, the output of waste tires grows more rapidly. Due to the cross-linking and reinforcing network structure of waste tires, they are difficult to degrade under natural conditions, which results in a large accumulation. Serious “black pollution” formed by wasted rubber severely threatens the health and life of human beings.
Tires mainly consist of vulcanized rubber and a series of additives [16]. The composition of a typical tire is shown in Figure 2 (by weight). It is mainly composed of natural rubber (NR) which comprises about 40% of the weight of truck tire rubber, making the tire full of elasticity and durability even under heavy loads [17][18]. The proportion of NR has increased nowadays, possibly due to the expansion in the use of radial tires and heavy-duty tires. It should be pointed out that the properties of NR can largely affect the workability of materials. For example, the molecular weight and gel content of NR may affect compound viscosity and filler dispersion in rubber mixing. In addition, the tendency of NR to crystallize upon stretching, even before cross-linking, has contributed to the strength of uncured rubber compounds.
Polymers 14 04429 g002
Figure 2. The composition of the GTR from truck tire [16].
Adding fillers to NR can improve interfacial adhesion and promote uniform dispersion, thus enhancing a series of properties of products, including stiffness, hardness, wear resistance, etc. Nanostructured CB and silica (SiO2) have a large surface area, allowing them to be dispersed in the rubber on a microscale.
CB is a proven reinforcing filler and has been widely applied in rubber, due to the improvement of mechanical properties, aging resistance, etc. Ayippadath et al. reported a more than 10-fold increase in tensile strength for SBR after adding N330 CB filler [19]. However, CB from petroleum is non-renewable and contaminative; therefore, recycling and reusing CB are quite necessary [20]. Silica is another widely used reinforcing filler. Different from CB, it is independent of oil resources and shows great advantages in low rolling resistance [21]. Idrus et al. evaluated the functions SiO2 plays in vulcanized NR [22]. They proved that irregularly shaped silica with ultra-fine particle size can better improve torque values. Many other chemicals are also used in rubber, such as cross-linking agents, antioxidants, plasticizers, etc.[23].
Different tires have distinguishable compositions; even different parts of the whole tire are different. However, their basic formulations and main components do not vary much: 50% rubber and 30% filler, as far as researchers know.

2.2. Degradation Behavior of Tire Rubber

Due to the irreversible vulcanization of tire rubber, conventional GTR with three-dimensional chemical cross-linking is an insoluble and infusible thermoset material, making it difficult to recycle and reuse. Therefore, the reclamation of vulcanized rubbers is urgent.
Reclamation is a procedure where the vulcanized rubber is converted into a product that can be vulcanized, processed and mixed again by using thermal energy and chemicals. The mechanism of this process is devulcanization or degradation [24]. In degradation, the breakage of chemical bonds occurs in the network, such as the C-S bond and S-S bond, and the chains of rubber are shortened as a result. While for devulcanization, the C-S bond, S-S bond and C-C bond are all broken without the scission of the main chains of rubber. Once the reclamation is increased seriously, the CB will separate from the rubber, and lightly pyrolyzed tire rubber will occur.
Song et al. reported the sol fractions and core–shell CB nanoparticles (Figure 3) in the process of reactive extrusion or warm aging [25]. They also reported a heterogeneous degradation of covalently cross-linked networks of GTR to core–shell CB nanoparticles [26]. Li et al. achieved the separation of CB from GTR by melt-extrusion pyrolysis at 300 °C  [10]. Terminal blend technology can induce devulcanization and degradation of GTR at a high temperature of over 260 °C in asphalt but gives off a huge fume [11]. Seghar et al. summarized the previous works of rubber reclamation, desulfurization and regeneration for GTR in detail [18][27][28][29].
Polymers 14 04429 g003
Figure 3. (A) Sol fractions obtained from degraded rubber with types of soybean oil under 150 °C for 4 h; (B) TEM image of CB from RGTR100 [26].
Wang et al. developed a new method named “thermal-oxidative reclamation” for devulcanizing GTR (Figure 4) [30]. This environmentally friendly method induces the completed breakage of the cross-link and part breakage of the main chain, leading to a decreased molecular weight of the sol with high content. The CB with micro-nano size can be released from the network of GTR.
Polymers 14 04429 g004
Figure 4. Schematic diagram of the dynamic thermal-oxidative reclaiming process [30].
The DR produced by the light pyrolysis process mainly consists of CB, sol fraction and inorganic species such as ZnO, silica, ZnS and so on. The CB has a very thin layer of tightly bound rubber, resulting in a core–shell structure (Figure 5A) [25]. With a crystal morphology between graphene crystal and amorphous, CB is usually less than 10 μm in diameter. Importantly, many polar functional groups including hydroxyl (-OH), carboxyl (-COOH), and amino groups (-NH2) are exposed on the surface of CB (Figure 5B), which provides an active site for the chemical reaction with asphalt [31]. In addition, sol fraction shows a relatively low molecular weight and is expected to be an alternative to asphalt because of its asphalt-like properties (Figure 5C) [30]. The inorganic products mainly contain ZnO, silica and ZnS. Silica is mainly composed of SiO2, and it can be expressed as SiO2·nH2O. nH2O in the SiO2·nH2O formula exists in the form of isolated silanols, vicinal silanols and geminal silanols (Figure 5D) [32]. These hydroxyls in silanols provide the possibility of intermolecular chemical reaction with other species such as asphalt. Previous reports found that DR could significantly improve the crack resistance of asphalt, providing an important foundation for the application and analysis of rubber asphalt [33].
Polymers 14 04429 g005
Figure 5. Components of DR. (A) TEM micrographs of CB [25]; (B) surface chemistry of CB [31]; (C) surface chemistry of silica [30]; (D) chemical formula of low molecular sol fraction [32].

References

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Lu Zhang
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Chuanping Zhang
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Zhen Zhang
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Hanbing Wang
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Update Date: 01 Nov 2022
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