2.5.1. Possible Options
Mitigation measures to reduce the GHG emissions produced by road projects can be related to activities carried out during all phases of a road project life cycle, starting as early as the design stage. Thus, emissions can be reduced by either reducing the quantity associated with an activity, substituting an activity with another one that has a lower emission factor, or by altering both measures at the same time.
Several mitigation scenarios can be explored with the intent of reducing GHG emissions associated with road construction practices. These include increasing the use of recycled materials or increasing the use of regionally available materials. An increase in the use of recycled materials can be achieved by utilizing recycled construction waste in road projects or by using reclaimed asphalt. Similarly, increasing the use of regionally available materials is expected to reduce emission due to material transportation.
Emissions can also be reduced during the construction phase by using GGBFS in the concrete mix to reduce cement content, replacing hot-mix asphalt with warm-mix techniques, or reducing emissions associated with construction equipment [
14,
26]. The use of thinner pavement layers with improved materials such as asphalt with a high stiffness modulus in the base layer is also an option [
23]. This, in fact, will have a double positive effect, as it reduces the compaction effort, and thus the compaction time, while also reducing the quantity of material used. A third aspect of innovation is to optimize the use of available resources through construction management measures such as rational equipment and material usage, as well as optimal transport of construction vehicles and placement of road safety barriers.
During the traffic operation phase, several options to reduce GHG emissions can be explored. One scenario is to reduce traffic volume. This can be achieved by different means such as (i) increasing the market share of other transportation modes such as public and non-motorized transport, (ii) managing travel demand by adopting transport demand management strategies such as congestion pricing or taxing car owners, or (iii) promoting mixed land use development [
45,
46,
47,
48]. Another possible scenario is to alter traffic characteristics by increasing the proportion of (i) higher-efficiency vehicles (in terms of fuel consumption), (ii) vehicles powered by liquefied natural gas (LNG), and (iii) electrically powered vehicles. Such options can be promoted through incentive/subsidy programs and/or taxation on low-efficiency vehicles. Previous work has indicated that improving vehicle energy efficiency and adopting low carbon fuels are the strategies with the greatest potential for achieving high GHG reductions in the transportation sector [
48,
49].
GHG emissions can also be reduced during the operation phase through the use of solar power or light-emitting diode (LED) lights that replace conventional lamps. Another option would be to reduce water consumption for roadside-plant irrigation. This can be achieved by using plant species that require less water, using smart irrigation systems, or using soil amendment to increase soil water capacity.
While this paper focuses on exploring options to reduce GHG emissions produced during the road construction and traffic operation phases, emissions can also be reduced during other phases. For example, during the rehabilitation and the maintenance phases, emissions can be reduced by minimizing the use of imported material for rehabilitation and maintenance through the use of in-situ cold recycling or reclaimed asphalt pavement. Xiao et al. [
50] found that energy saving, GHG emission reduction, and cost-saving can be achieved through the implementation of reclaimed asphalt pavement. Meanwhile, adopting a proper maintenance program may also increase the service life of the road and consequently reduce the annually emitted GHGs over the life cycle of the project. Moreover, treatment of the road surface layers with rejuvenators may significantly increase the life span of a road [
23]. However, rejuvenators are not fully established and applied yet [
23], but as their use is developed further, their impact on reducing GHG emissions could be assessed more accurately.
2.5.2. Scenarios Selection
In this study, a number of scenarios with the potential to reduce GHG emissions in Abu Dhabi were selected and classified into two groups: those of relevance to municipalities and those of relevance to transport authorities. The first group includes road works during the construction phase as well as road lighting and irrigation during the road operation phase. The second group includes options for traffic management.
Although there is not yet a formalized procedure for the integration of GHG reduction in road projects in the UAE, there are initiatives such as those of “Estidama” and the Abu Dhabi Sustainable Roads Rating System (ADSRRS) that can be utilized as a guide for achieving this purpose. The Abu Dhabi Urban Planning Council (ADUPC) initiated Estidama (which means sustainability in Arabic) to transform the emirate into a model of sustainable urbanization and to endorse greener building standards. This initiative was designed to keep the physical, cultural, and traditional aspects of the region while applying sustainable measures. In addition to these features, Estidama has a unique rating system, called “the Pearl rating system”, specifically tailored to fit the conditions of Abu Dhabi. It gives guidance from design through construction to operation stages of a project, taking into consideration the environmental, social, cultural, and economic pillars of sustainability [
51]. On the other hand, the Abu Dhabi Department of Municipal Affairs identifies best practices for applying sustainable policies and measures to road projects through the ADSRRS, along with clarifying the appropriate guidelines to be followed. As the ADSRRS is an initial start in developing a comprehensive rating system for road projects, it can then be used over time to score performance in applying sustainable best practices to projects.
The selection of the explored scenarios was guided by the above sustainability initiatives and findings from the literature. The explored scenarios were also selected based on their potential adoption in Abu Dhabi in the short–medium term (i.e., within the coming 15 years). Thus, key factors in selecting some of the scenarios, whether they are available to use and apply, are not still in the research or development stage, and the extent to which a proposed scenario could be achieved within the short–medium term. For example, assuming total replacement of ICEVs with EVs may not be achievable in the coming decade since ICEVs are long-lived, there is a need for EV-related infrastructure, and EVs are not affordable by many. However, a lower EV adoption level of 10% may be possible.
Another guiding factor in the selection of the explored scenarios is related to the extent to which an activity contributes to GHG emissions. For example, results of the baseline cases showed that traffic movement during the operation phase contributes 80% to 97% of GHG emissions, while emissions during the construction phase account for only 1.8% to 6.5% of the total emissions of a road life cycle, and the rest of the emissions are mainly attributed to road lighting and plant irrigation [
16]. Thus, it is expected that a reduction of emissions from vehicular traffic would have a higher overall impact on GHG emission reduction as compared to reduction of emissions generated during road construction. Nonetheless, it is still worth devoting effort to assessing the impact of reducing emissions from road construction activities, as they can offer opportunities for recycling waste material, reducing used resources, and meeting future targets for emission reduction set by local authorities. In fact, road construction GHG emissions are growing rapidly due to major ongoing road programs aiming to support economic development [
52].
In total, fourteen scenarios were explored in this study. Five scenarios are related to the use of innovative techniques and approaches in road infrastructure construction. These five scenarios targeted road works (
Table 3) and were found to contribute the most to GHG emissions during the construction phase [
16]. Four scenarios are related to road lighting and water management during the operation phase, and the remaining five are related to traffic movement during the operation phase.
Table 4 lists the explored scenarios, while a detailed description of these scenarios is presented below.
Scenario S1 applies 15% of recycled asphalt. This percentage was adopted from Frigio et al. [
53], who suggested that this is the current upper limit for the use of recycled asphalt in pavement. In this case, the quantity and transportation of asphalt reported by Alzard et al. [
16] were reduced by 15%. For the reduced quantity, only GHG emissions related to transportation of material to the construction site were considered, since the effects of material extraction, processing, and removal have already been accounted for by another project (indirect emissions). Transportation of the reduced quantity was assumed to occur from Al Dhafra Industrial Facility in Abu Dhabi, which is almost 82 km away from Case 1 and 70 km from Cases 2 and 3.
Scenario S2 explores the option of using 50% recycled aggregate, which is the upper limit set by ADM. Similar to Scenario S1, the quantity of aggregate, as reported by Alzard et al. [
16], was reduced by 50%. For this reduced rate, only the transportation effect was considered, since material extraction and processing have already been considered by another project. Recycled aggregates were assumed to be brought from Al Dhafra Industrial Facility, whereas raw aggregates were brought from Al Fujairah Emirate with a roundtrip of 500–600 km from the project sites.
In Scenario S3, hot-mix asphalt used in the baseline case studies was replaced with warm-mix asphalt. As a result, the emission factor of processing asphalt was changed, but the transportation effect remained the same. According to Blankendaal et al. [
26], a 30% reduction in emissions is achieved by adopting warm-mix asphalt. Hence, the emission factor for asphalt processing was reduced by 30% when applying this scenario.
In Scenario S4, the PC used in the concrete mix used for structural purposes was replaced by a mix of 30% PC and 70% GGBFS. This was applied to Cases 1 and 3 but not to Case 2, since concrete mixtures used during the construction phase of Case 2 utilized GGBFS as a replacement of a portion of PC. According to Tait and Cheung [
29], the use of a concrete mix with 30% PC and 70% GGBFS would lead to a 60% reduction of GHG emissions. Thus, in applying this scenario, the emission factor associated with processing concrete used for structural purposes was reduced by 60%.
Scenario S5 is related to the use of asphalt with a high stiffness modulus in the base layer. Researchers found that this would reduce the layer thickness by 25% [
23]. Thus, by adopting this scenario, the quantity of the materials used for the base layer was reduced by 25%, resulting in lower emissions due to reduced material usage and transportation.
Scenarios S6 and S7 are related to better management of road lighting. In Scenario S6, conventional lamps currently used in the studied cases were replaced by LED lamps. Several studies reported that switching from conventional to LED lamps would reduce energy consumption by about 40% [
23,
54,
55]. Other studies reported an even higher energy reduction (60%) when specific conditions were satisfied [
56]. In exploring this scenario, the amount of fuel consumed to generate electricity for lighting was reduced by 40%.
Scenario S7 explores the option of replacing 25% of fuel-generated electricity for lighting with solar-generated energy. Road lighting is exclusively used at night, while solar power is exclusively produced during the day. This mismatch raises the need for energy storage facilities. Energy storage facilities often rely mainly on lithium-ion batteries. The production of lithium-ion batteries produces a significant amount of emissions. In addition, there is an efficiency problem associated with solar energy production. That is, only a fraction of the solar energy is converted into electricity. This creates a need for increased energy production capacity, which in turn translates into emissions related to significant solar panel production. Nonetheless, in this study, emission reduction related to the use of solar energy for road operation lighting was considered. Jungbluth et al. [
57] used Ecoinvent and found that photovoltaic (PV) electricity emission rates for different countries range from 0.046 to 0.084 kg CO
2e/kWh. In this study, the upper value was used as a conservative estimate of the rate of emissions associated with the use of solar-powered PV panels in Abu Dhabi, since almost 100% of the power produced in the UAE is produced by fossil fuels, more specifically, natural gas. As such, the emission factor associated with 25% of fuel-generated electricity was reduced from 1.0389 kg CO
2e/kWh [
58] for the baseline conditions to 0.084 kg CO
2e/kWh.
Scenarios S8 and S9 are related to water usage in road irrigation. Scenario S8 assumes a reduction of 20% in water consumption for irrigation due to the adoption of water conservation initiatives. GHG emission calculations for the baseline conditions were carried out assuming that 75% of the water used in road landscape irrigation is TSE while the remaining 25% is desalinated water [
16]. The proposed reduction was applied to the amount of desalinated water (EF = 0.02158 kg CO
2e/L [
59]) used, since it has a higher environmental impact than that of TSE (EF = 0.0001475 kg CO
2e/L [
44]). On the other hand, Scenario S9 assumes full utilization of TSE for the irrigation of green landscapes.
Scenarios S10–S14 were selected to investigate the possibility of reducing emissions from traffic operations by changing the traffic characteristics of passenger cars. In Scenario S10, the passenger car traffic was reduced by 10%. This scenario is straightforward, and entails reducing the number of each type of passenger cars (two-seater, mini-compact, subcompact, compact, mid-size, full-size, small station wagon, and mid-size station wagon) by 10%. In a similar manner, in Scenario S11, 10% of the passenger cars were replaced by more fuel-efficient ones, in terms of fuel consumption rate. For example, a 2014 model station wagon with a fuel consumption rate of 0.0799 L fuel/km was replaced by a value of 0.0716 L fuel/km for the 2018 model, thus reducing the amount of fuel consumed per kilometer travelled. In Scenario S12, 20% of the passenger cars that originally operated by gasoline were replaced by passenger cars that use LNG. Since LNG has a lower emission factor (1.436 kg CO2e/L) compared to gasoline (2.384 kg CO2e/L), a drop in emissions due to applying this scenario would be expected.
Scenario S13 was selected to investigate the impact of replacing ICEVs with BEVs on emission reduction. It was assumed that a 10% replacement would occur. However, it was expected that this 10% replacement would occur within the passenger car vehicle class only, as this is the only vehicle class in which BEVs have been adopted on a meaningful scale due to battery and cost issues [
60]. Although replacing 10% of the internal combustion engine (ICE) passenger cars with battery electric (BE) passenger cars might seem to be a low adoption rate, it is much higher than the current global adoption rate of only 1% [
61]. Furthermore, it is important to consider barriers that have the potential to prevent a larger-scale shift from ICEVs to BEVs in Abu Dhabi in the medium term. For example, gasoline prices in Abu Dhabi are significantly lower than those in many European countries, BEVs have a higher purchase cost relative to ICEVs [
62], and gasoline vehicles are long-lived [
63]. Thus, unless the Abu Dhabi government adopts policies to incentivize BEV uptake [
64], these barriers may prevent ICEV owners from switching to BEVs at a faster pace.
Different passenger cars have different fuel efficiency levels. In addition, Abu Dhabi’s hot weather may lower BEVs’ efficiency levels [
65] and, therefore, lower driving ranges as well as emission reduction levels. S13 was modelled based on electricity consumption levels pertaining to one of the most largely sold electric vehicles, the Nissan Leaf. As such, a city-based consumption of 0.111 kWh/km was assigned to Case 1 (Al Rahba City), while a consumption of 0.144 kWh/km was assigned to Cases 2 and 3 (Al Salam Street and Corniche Road) [
66]. Fuel efficiency levels (in L fuel/km) of ICE passenger cars, light trucks, and heavy trucks were determined as a weighted average based on vehicle models included in the traffic counts provided by ADM. As such, the fuel efficiency of ICE passenger cars, light trucks, and heavy trucks for Case 1 was 0.1179, 0.1536, and 0.35, respectively. Fuel efficiency of ICE passenger cars, light trucks, and heavy trucks for Case 2 was 0.1036, 0.1366, and 0.30, respectively. Fuel efficiency of ICE passenger cars, light trucks, and heavy trucks for Case 3 was 0.1013, 0.1536, and 0.35, respectively.
In S13, the average emissions estimation method was utilized to determine the amount of carbon emitted by the power sector. Though output from the average emissions estimation method might not be as accurate as output from the marginal emissions method (depending on factors such as energy mix and electricity consumption timing), the adoption of the average emissions method may be a reasonable approach in the context of power systems where the dispatchable energy is generated from one source [
67]. In Abu Dhabi, 85% and 13% of the electricity are currently produced by combined-cycle and open-cycle natural gas power plants, respectively. The remaining 2% is produced by solar energy [
68,
69]. Heat rates of thermal plants as well as carbon emission factors for natural gas fuel were obtained from Elshurafa and Peerbocus [
70].
Finally, an alternative scenario to S13 (S14), based on Abu Dhabi’s 2035 planned energy mix and a higher BEV adoption rate, is also discussed. This futuristic scenario was based on (i) a future energy mix consisting of 26%, 34%, and 40% of solar, gas, and nuclear energy, respectively [
68,
69] and (ii) increased replacement of ICE passenger cars with BE passenger cars from 10% to 30%. To model this scenario, a few assumptions had to be made. First, the solar energy would be consumed during the daytime. This would not only eliminate the need for energy storage facilities, but it would also simplify the distribution of electricity consumed by BEVs per energy source. Second, future power grid capacity could accommodate additional electricity demand from BEV charging [
71]. Third, BEVs would be charged during off-peak times (i.e., late at night and early in the morning) only under a controlled scenario [
72]. This assumption would eliminate the need to determine BEV electricity consumption based on random charging times (though this would be a more realistic scenario once Abu Dhabi has proper BEV-related infrastructure in place). Thus, assuming that BEVs would be charged during off-peak times only and that solar energy would be consumed during the daytime, BEVs would consume electricity produced either by natural gas or nuclear power. Finally, since it is expected that 26%, 34%, and 40% of the electricity consumed in Abu Dhabi by 2035 will be produced by solar energy, natural gas, and nuclear energy, respectively, 54.05% and 45.95% of the electricity consumed by BEVs during off-peak times would be produced by nuclear energy and natural gas, respectively. Considering that power companies would prioritize operating their plants with lower operating costs first (i.e., nuclear as opposed to gas power plants), it would be reasonable to assume that nuclear energy would produce the baseload power and, therefore, the electricity consumed by BEVs would come from dispatchable power produced by gas power plants. The implications of this alternative scenario are discussed in
Section 3.3.2. Altering any of the assumptions previously described would surely change emission reductions. For example, previous research has shown that BEV charging times may have an impact on the effectiveness of BEVs on reducing system-wide carbon emissions, depending on the energy mix used to power the grid [
35].
It is important to stress that this study focused solely on tailpipe emissions and that it was not the purpose of this study to investigate life-cycle emissions. Therefore, this study rather focused on the local (i.e., within the boundaries of each one of the three case studies analyzed) emission reduction impact that the replacement of a portion of ICE passenger cars with BE passenger cars would have. This is an important consideration, since previous studies have shown that a large portion of the emissions associated with BEVs are produced upstream (e.g., during battery production) [
36]. These upstream emissions may likely be even more significant when the effect of extreme temperature is considered [
65]. That is, in environments in which extremely high temperatures are the norm (as is the case in Abu Dhabi during most of the year), the expected lifetime of the batteries may be reduced. Therefore, it is likely that the emission reduction presented in this paper is larger than what it would have been had upstream emissions produced during the battery manufacturing phase (coupled with extreme weather impact during the vehicle operation phase) been considered. Another point to stress is that the assumption made in this study that nuclear power will be the source of electricity for 40% of Abu Dhabi’s electricity in the future is merely based on Abu Dhabi’s already-announced future energy mix plans [
68]. Nuclear power currently produces 10% of the world’s energy [
73] and is a carbon-free energy source, which, due to its non-intermittent nature, can be effective in reducing carbon emissions. However, nuclear power usage results in the generation of nuclear waste, which can remain radioactive for a long time and, therefore, may threaten the safety of human lives and the environment. Methods intended to safely handle nuclear waste have been implemented for some time now, but some of these methods have been seen as not only unsafe, but also as short-term oriented [
74,
75]