Binder recycling 2017


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An important concern that limits the RAP content in asphalt mixtures is the fact that the aged binder that is present in the RAP can cause premature cracking.

Rejuvenators are frequently added to high RAP mixtures to enhance binder recycling 2017 properties of the binder. There is no existing method binder recycling 2017 predict the longevity of a rejuvenated asphalt. This study investigated the aging of rejuvenated binders and compared their durability with that of virgin asphalt. DSR and BBR tests were conducted to examine the high-temperature and low-temperature rheological properties of binders.

Results indicated that the type and dosage of the rejuvenator have a binder recycling 2017 influence on the aging rate and durability of the binder.

Some rejuvenators make the binder age slower, while others accelerate aging. These observations confirm the importance of evaluating the long-term aging of recycled binders. To maintain over 2. The milled asphalt material, which is reclaimed asphalt pavement RAPis entirely recyclable [ 1 ]. Despite an abundance of this valuable resource, some portions of RAP are binder recycling 2017 wasted in landfills, and yet another part of it is used in nonasphalt applications, such as an embankment, subbase, base, and shoulder.

Therefore, the majority of the RAP is not recycled to its highest potential. One of the most binder recycling 2017 obstacles for using high RAP asphalt mixtures is a lack of confidence in their performance [ 4 ]. A high RAP mixture can perform differently from a conventional mixture, and currently, there are no adequate methods to predict and assess all aspects of these differences.

Aging of the asphalt binder is among most critical parameters that make recycled asphalt mixtures different from new material. When pavement ages, the asphalt binder becomes hard, brittle, and prone to binder recycling 2017 [ 5 — 7 ].

The reason for this phenomenon is that lighter components of the asphalt or maltenes are partially lost due to evaporation and oxidation. Rejuvenating is the process of restoring the original properties of an aged asphalt binder by adding a rejuvenator or recycling agent RA.

Rejuvenation is often perceived as simply softening the hard asphalt. Therefore, in most cases, specifications call for a target range of penetration, viscosity, or performance grade PG to verify the effectiveness of rejuvenation [ 89 ].

However, there are other concerns that differentiate a rejuvenated binder from a virgin binder that cannot be addressed by these requirements. The durability of the binder is one of these issues.

Today, decades after recycling of asphalt pavement became a common practice in the late s, rejuvenated mixtures are aging again, and their aging behavior is not necessarily similar to that of virgin mixtures. Therefore, it is important to study the aging of recycled asphalt and compare it to that of virgin binders.

To achieve a high RAP mixture with durability similar to that of new pavement material, the rejuvenated asphalt binder should not age binder recycling 2017 than a virgin asphalt. Terrel and Fritchen compared the durability of recycled and virgin mixtures in binder recycling 2017 10 ]. They simulated long-term moisture damage using a vacuum-submerged conditioning procedure, followed by several freeze-thaw thermal cycles.

Results showed that the performance of recycled asphalt concrete samples was similar to new samples. In another study, virgin and recycled mixtures were subjected to long-term oven aging [ 11 ]. Dynamic modulus tests showed that samples that contained RAP aged slower.

It should be noted that no rejuvenator was added to the mixtures in this study. The emergence of the Superpave performance grade system and its tests and aging procedures provided new tools for evaluating the changes in asphalt properties as it ages. A study that evaluated the performance of recycled asphalt binder recycling 2017 using the performance grade system concluded that generally binder recycling 2017 asphalt binders perform similar to or better than virgin binders [ 12 ].

Aging was simulated by oven heating of binder recycling 2017. It was concluded from a series of shear modulus master curves that using recycling agents in mixtures containing RAP improves fatigue cracking resistance binder recycling 2017 adversely affecting rutting resistance. While the majority of the previous researches on the durability of recycled asphalt show a better longevity for recycled material, there are instances that conclude vice versa.

There is a need to study the parameters that affect the longevity of rejuvenated binder and cause them age faster or slower in comparison with virgin asphalt. In that study, the PAV was used to simulate long-term aging. The results showed that aging of recycled asphalt could be either faster or slower than that of virgin asphalt, depending on the rejuvenator used. The difference in the service lives of binders rejuvenated by different products was estimated to be up to ten years.

Also, it was shown that the standard PAV aging time was not adequate to evaluate aging behavior. Therefore, aging for a longer period of time is required to binder recycling 2017 the durability of recycled asphalt. There is a well-recognized need to increase the use of RAP in the pavement. However, this cannot be achieved if asphalt rejuvenation continues to be perceived as simply softening the binder.

This paper presents an effort to binder recycling 2017 this shortcoming by binder recycling 2017 the need for an effective rejuvenation. The objective of this research was to evaluate the durability of asphalt binders containing RAP. Rheological properties of the binder were used to assess the level of aging. The long-term aging of binders with 20 and 40 percent RAP was compared to that of virgin asphalt binders.

The effect of different rejuvenators on the durability was also investigated. The experimental binder recycling 2017 was designed based on Superpave PG tests and aging procedures. The aging was simulated by the PAV, which exposes the asphalt to heat and high pressure. The standard PAV aging time is 20 hours. There is no definite correlation between PAV aging and actual field aging time, but a study performed in Florida binder recycling 2017 this purpose estimated that the aging caused by a hour PAV cycle is equivalent to 8 years of service binder recycling 2017 17 ].

This estimate was used to provide an approximate correlation between PAV time and field aging. Furthermore, it was aimed to look at the aging beyond the first 8 years. Therefore, samples were subjected to three PAV cycles to increase the PAV binder recycling 2017 time to 60 hours and simulate almost 24 years of in-service aging. One of the objectives of this research was to introduce a quantitative description for binder durability.

This value is referred to as critical PAV time in this paper. The primary parameter used for characterizing the stiffness of the binder and binder recycling 2017 the level of aging was the continuous high-temperature performance grade of the binder. This parameter is briefly referred to as high PG in this paper. Two types of nonmodified RAP, two virgin binders, and two rejuvenators were used. Trichloroethylene was used as the solvent for the binder recovery process.

Two types of virgin binders were used. These are referred to as VB1 and VB2. The Binder recycling 2017 mass loss was 0. Two recycling agents rejuvenators were used. RA1 is a dark yellow heavy paraffinic oil with binder recycling 2017 aromatic content that gives binder recycling 2017 good softening power.

The rejuvenator contains no asphaltene. This helps restore the maltene to asphaltene ratios binder recycling 2017 are reduced by aging. Binder recycling 2017 material has good high-temperature stability and does not emit much smoke at mixing temperatures. However, its high aromatic content allows it to evaporate quickly during the mixing procedures. The RTFO mass loss was determined to be as high as 1. RA2 is a semisolid black substance with an asphalt odor. This product is manufactured by rerefining used oils through vacuum binder recycling 2017.

Using a rerefined product as the rejuvenator is a step toward enhancing the use of recycled material. The two virgin binders were used as controls. The samples were prepared by mixing binder recycling 2017 soft binder with the RAP binder. The soft binder is a mixture of a virgin binder and a recycling agent. This sequence is consistent with the practice that is often followed by the industry. Similar initial high PG values were required to binder recycling 2017 the comparison between samples.

To binder recycling 2017 the proportion of the components that would produce samples with those target grades, the following three steps were followed. The first step was to determine the grade of the soft binder in such a way that, after blending with the RAP binder, a sample with the target grade is achieved. Figure 1 shows this interpolation for each combination of virgin and RAP binder. Softening curves were established for each combination of virgin binder and recycling agent, as shown in Figure 2.

The dotted lines represent the linear trend lines. The softening power of the RA2 was considerably lower than the RA1. Therefore, large doses were needed to soften the binder to the desired grade. The results from the two preceding steps made it possible to calculate the proportion of the RAP binder, virgin binder, and recycling agent for each binder recycling 2017. Table 2 presents the factorial design of samples and the composition of each.

Figure 3 is a flowchart that shows the steps for the sample preparation process. The RTFO simulates the aging that the binder undergoes during construction. This aging is primarily due to the evaporation of lighter components of the asphalt binder when it is heated. The high PG values for nonaged and RTFO-aged samples were determined binder recycling 2017 based on the corresponding criteria formulas 1 and 2.

The results showed that binder recycling 2017 degree of aging caused by the RTFO depended on the type of asphalt and recycling agent. Its RTFO grade based on formula 2 was 0. On the other hand, the RTFO grade was 0.

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