Sustainable Asphalt Mixtures: A Review of Recycling and Low-Temperature Technologies for an Integrated Sustainability Assessment
Abstract
1. Introduction
2. Methodology
2.1. Literature Search Strategy
2.2. Screening and Selection Criteria
2.3. Data Synthesis and Thematic Organisation
3. Conceptual and Technological Framework for Sustainable Asphalt Mixtures
3.1. Environmental and Technical Challenges of Conventional Asphalt Mixtures
3.2. Recycled and Waste-Derived Materials in Asphalt Mixtures
- Reclaimed asphalt (RA): Derived from milled pavement layers, RA enables the partial substitution of both aggregates and binder, substantially reducing the demand for virgin materials [23,24,25]. When rejuvenation and binder blending are appropriately managed, high-RA mixtures can be feasible; however, binder ageing and feedstock variability remain practical challenges.
- Steel slag aggregates (SSA): As a byproduct of the steel industry, SSA offers high hardness and angularity, which can enhance aggregate interlock and potentially improve pavement durability. Nevertheless, excessive replacement levels may negatively affect workability and volumetric stability due to the high density and rough particle morphology of slag aggregates [26,27].
- Recycled concrete aggregates (RCA): RCA from construction and demolition waste can be effectively incorporated at moderate replacement levels. At higher contents, its porous and angular structure tends to increase binder demand, requiring careful gradation control and mix design adjustments [28].
3.3. Low-Temperature Production Technologies
3.4. Synergistic Integration of Recycling and Temperature-Reduction Strategies
4. Mechanical Performance and Economic Assessment of Sustainable Asphalt Mixtures
4.1. Mechanical Performance of Asphalt Mixtures with Recycled Materials
4.2. Mechanical Behaviour of Low-Temperature Asphalt Mixtures
4.3. Combined Effect of Recycling and Temperature Reduction: Experimental Evidence and Cost Analysis
5. Environmental and Life-Cycle Assessment of Sustainable Asphalt Mixtures
5.1. LCA Framework and General Applications in Sustainable Asphalt Mixtures
5.2. Environmental Performance of Asphalt Mixtures with Recycled Materials
5.3. Environmental Performance of Low-Temperature Asphalt Technologies
5.4. Environmental Assessment of Combined Recycling and Temperature-Reduction Strategies
5.5. Integrated Summary of LCA Results
6. Discussion: Toward an Integrated Sustainability Assessment Perspective
7. Conclusions
- Recycling strategies and low-temperature production technologies represent two major and complementary pathways towards more sustainable asphalt pavement systems. Reclaimed asphalt, recycled concrete aggregates, and steel slag can maintain—and in many cases enhance—mechanical performance while reducing reliance on virgin aggregates and binders. In parallel, warm-, half-warm-, and cold-mix technologies can reduce production energy demand and associated greenhouse gas emissions, while also offering potential production-stage cost savings under favourable conditions.
- The most significant sustainability gains are generally achieved when recycling and temperature-reduction approaches are combined. Integrated solutions can simultaneously reduce raw-material consumption, production-related environmental burdens, and, in many cases, initial production costs, while preserving key performance requirements such as stiffness, rutting resistance, fatigue behaviour, and long-term durability when mixture design is properly optimised.
- The sustainability benefits of the reviewed solutions are strongly conditioned by material variability, binder demand, curing behaviour, construction quality control, and methodological assumptions. These factors may substantially influence the practical performance, environmental interpretation, and economic viability of the reviewed solutions, particularly at high recycled contents or very low production temperatures.
8. Future Research Directions and Implementation Challenges
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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| Approach/ Technology | Core Mechanism | Typical Benefits | Main Limitations | Representative References |
|---|---|---|---|---|
| Reclaimed asphalt (RA) | Partial replacement of virgin aggregates and binder through reclaimed pavement material | Reduced demand for raw material. Improved circularity. Potential cost savings. | Aged binder variability. Incomplete blending. Moisture sensitivity at high RA contents. | [23,24,25] |
| Steel slag aggregates (SSA) | Industrial byproduct replacing coarse aggregates. | High angularity improves aggregate interlock. Potential durability enhancement. | High density affects workability. Volumetric instability at high replacement levels. | [26,27] |
| Recycled concrete aggregates (RCA) | Aggregate substitution using construction and demolition waste. | Supports circular economy. Reduces quarrying impacts. | Increased binder demand due to porosity. Variability in gradation and structure. | [28] |
| Warm-mix asphalt (WMA) | Additive-enabled viscosity reduction or improved wettability (110–140 °C). | Lower production fuel use. Improved compaction. Reduced emissions. | Additive dependency. Potential rutting or moisture issues, depending on additive chemistry and dosage. | [29,33] |
| Half-warm-mix asphalt (HWMA) | Foamed or emulsified bitumen technologies (60–100 °C). | Substantial production-phase energy and emissions reductions. | Compaction sensitivity. Moisture control requirements. Narrow construction window. | [34,35,36] |
| Cold-mix asphalt (CMA) | Ambient-temperature production without aggregate heating (<30 °C). | Largest production energy savings. Suitable for low-volume roads and as a base layer. | Slow curing. Lower early-age strength. Dependence on emulsion-based binders. | [37,38] |
| Integrated approaches (recycling + temperature reduction) | Synergistic combination of recycled materials with low-temperature asphalt systems. | Combined reduction of material- and process-related impacts. Enhanced circularity. | Requires optimised rejuvenation, compaction control, and standardised protocols. | [5,13,15,43] |
| Mixture Type/Strategy | Mechanical Findings | * Economic Implications | Key Insights and Limitations |
|---|---|---|---|
| RA mixtures | Comparable or improved stiffness and rutting resistance at moderate RA contents (20–50%); high RA may increase brittleness if blending is incomplete. | Material and production cost reductions through reduced virgin binder and aggregate demand (~14–34%). | Requires effective rejuvenation and control of binder ageing. Variability at high RA contents. |
| RCA mixtures | Adequate Marshall stability at moderate replacement levels (≈30–50%). Performance declines at higher dosages due to porosity and binder demand. | Moderate economic feasibility depending on treatment and binder requirements. | Strong dosage dependence. Higher absorption affects volumetrics and durability. |
| SSA mixtures | Increased stiffness, rutting resistance, and fatigue improvement due to angularity and interlock. | Pavement-level savings (~14–20%) are possible under favourable sourcing conditions. | Workability and compaction challenges at high contents. Transport distance is critical. |
| WMA mixtures | Mechanical performance is generally comparable to HMA, with improved workability and compaction. | Reduced production costs driven by lower mixing temperatures and fuel demand (energy savings reported ~20–75%). | Performance is sensitive to additive chemistry and dosage. Moisture and rutting effects must be controlled. |
| HWMA mixtures | Comparable stiffness and fatigue behaviour to HMA under optimised compaction and curing. | Production cost reductions up to ~50% reported in favourable cases. | Narrow construction window. Limited large-scale field validation. |
| CMA mixtures | Adequate stiffness and fatigue resistance for base and sub-base applications when stabilised with foamed/emulsified binders. | Cost effective in rehabilitation contexts, with reported savings up to ~60%. | Slow curing and lower early strength limit use in high-traffic surface layers. |
| Integrated solutions | Balanced stiffness, rutting and fatigue performance when recycling and temperature reduction are jointly optimised. | Consistent production-phase savings reported (commonly ~20–60%) due to reduced fuel and virgin material demand. | Requires optimised rejuvenation, temperature control, and compaction procedures for reliable field performance. |
| Strategy/ System | Typical Economic Tendency | Nature of Economic Evidence | Main Limitations for LCA–LCCA Integration | Practical Interpretation |
|---|---|---|---|---|
| RA incorporation | Frequent material and production cost savings, especially at moderate RA contents. | Mostly material/production cost studies; limited project-level and life-cycle evidence. | Sensitive to blending assumptions, durability, transport distance, and binder demand. | Attractive where RA is locally available and durability is maintained. |
| RCA incorporation | Moderate or mixed cost effectiveness. | Limited and heterogeneous evidence, often influenced by higher binder demand. | Higher absorption and binder demand may offset initial savings; life-cycle evidence remains limited. | More favourable at moderate replacement levels and under controlled sourcing and mix design conditions. |
| SSA incorporation | Potentially favourable under local sourcing conditions. | Case-specific studies combining cost, performance, and transport considerations. | Transport distance strongly affects viability; benefits remain context dependent. | Economically promising when haul distances are short and mechanical advantages are effectively used. |
| WMA technologies | Lower production costs due to reduced fuel and energy demand. | Mainly production-stage evidence; fewer full LCCA-based comparisons. | Additive cost, durability assumptions, and plant conditions may alter life-cycle outcomes. | Initial savings are often clear, but full economic advantage depends on long-term performance and local conditions. |
| HWMA technologies | Favourable production- stage savings reported in selected cases. | Limited but promising evidence, often based on laboratory or pilot-scale applications. | Compaction, curing, and limited field validation constrain robust life-cycle interpretation. | Promising option, but stronger field-based LCCA evidence is still needed. |
| CMA/CRM technologies | Often associated with strong cost advantages in rehabilitation and base-layer applications. | Project-level and rehabilitation case studies are more common than for other low-temperature systems. | Service life, curing conditions, and maintenance frequency strongly affect full life-cycle interpretation. | Particularly attractive in rehabilitation contexts, but long-term value depends on durability in service. |
| Integrated technologies | Strong potential for combined economic and environmental gains. | Heterogeneous evidence mixing production-cost, project-scale, LCA, and occasional LCCA studies. | Comparability is limited by differing cost scopes, system boundaries, and durability assumptions. | Best interpreted through an integrated assessment that combines cost, durability, and environmental outcomes. |
| Strategy/ System | * Energy Reduction | * GHG Reduction | Main Drivers/ Sensitivities | Limitations/ Research Gaps |
|---|---|---|---|---|
| RA incorporation | ~20–30% | ~15–35% | Avoided virgin aggregate extraction. Reduced virgin binder demand. Blending and rejuvenation assumptions. | Strong sensitivity to transport distances. Uncertainty in binder blending/allocation modelling. |
| RCA incorporation | ~5–20% | ~5–20% | Aggregate substitution at low replacement levels. Local availability. | Increased binder demand due to porosity may offset benefits at higher RCA contents. |
| SSA incorporation | ~5–15% | ~1–15% | Avoided quarrying. Industrial by-product recovery. Reduced extraction burdens. | Transport dominates environmental performance. Density effects and variability in mixture-specific binder demand. |
| WMA technologies | ~15–35% | ~20–40% | Reduced heating fuel consumption. Additive type and plant efficiency. Reduced binder ageing. | The environmental footprint depends on assumptions about additive production and durability. |
| HWMA technologies | ~50–60% | ~60–70% | Substantial temperature reduction. Limited oxidation. Lower production energy demand. | Limited large-scale field datasets. Compaction sensitivity and moisture control requirements. |
| CMA technologies | ~56–90% | ~40–60% | Near-elimination of aggregate heating. High reuse of existing pavement materials. | Curing time, emulsion formulation, and application layer strongly influence net benefits. |
| Integrated technologies | ~30–90% | ~40–70% | Synergistic combination of avoided virgin materials and reduced-temperature manufacturing. | High variability due to methodological inconsistencies (system boundaries, allocation rules, blending assumptions). |
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Moura, C.F.N.; Silva, H.M.R.D.; Oliveira, J.R.M. Sustainable Asphalt Mixtures: A Review of Recycling and Low-Temperature Technologies for an Integrated Sustainability Assessment. Infrastructures 2026, 11, 139. https://doi.org/10.3390/infrastructures11040139
Moura CFN, Silva HMRD, Oliveira JRM. Sustainable Asphalt Mixtures: A Review of Recycling and Low-Temperature Technologies for an Integrated Sustainability Assessment. Infrastructures. 2026; 11(4):139. https://doi.org/10.3390/infrastructures11040139
Chicago/Turabian StyleMoura, Caroline F. N., Hugo M. R. D. Silva, and Joel R. M. Oliveira. 2026. "Sustainable Asphalt Mixtures: A Review of Recycling and Low-Temperature Technologies for an Integrated Sustainability Assessment" Infrastructures 11, no. 4: 139. https://doi.org/10.3390/infrastructures11040139
APA StyleMoura, C. F. N., Silva, H. M. R. D., & Oliveira, J. R. M. (2026). Sustainable Asphalt Mixtures: A Review of Recycling and Low-Temperature Technologies for an Integrated Sustainability Assessment. Infrastructures, 11(4), 139. https://doi.org/10.3390/infrastructures11040139

