1. Introduction
Urban transit authorities worldwide are increasingly prioritizing the electrification of bus fleets to mitigate the environmental impacts of public transportation. The transportation sector is a major contributor to urban air pollution and greenhouse gas emissions, generating 15% of total CO
2 emissions [
1], and as such, replacing diesel buses with electric buses (EBs) can significantly reduce these emissions. Many cities and transit agencies across the globe have announced targets for transitioning to 100% EB fleets over the coming decades. Establishing sustainable cities through efficient public transportation is paramount [
2] to cater for the world’s urban population, which is projected to rise significantly by 2050 [
3], and sustainability goals. For instance, Dubai’s Roads & Transport Authority (RTA) has set a goal to fully electrify its public bus fleet by 2050, aligning with broader sustainability initiatives [
4]. Achieving such ambitious targets requires strategic long-term planning, as transit agencies must balance environmental objectives with financial and operational realities.
While the transition to EBs promises substantial benefits, it also presents several challenges that must be addressed in a comprehensive transition plan [
5,
6]. EBs have limited driving ranges compared to diesel buses, necessitating careful scheduling and charging strategies to maintain service levels. Developing a robust charging infrastructure is essential to support an electrified fleet whereby agencies must determine the number, type, and locations of chargers (e.g., depot vs. en-route fast chargers) to meet energy demands without causing excessive vehicle downtime. Moreover, large-scale electrification will introduce significant loads on the electrical grid, potentially requiring grid upgrades or smart charging management to avoid capacity issues [
7,
8]. These technical and operational hurdles occur in parallel with financial considerations. EBs typically have higher upfront costs than diesel buses, including vehicles and batteries, as well as infrastructure investments for charging stations. On the other hand, EBs promise lower fuel (energy) and maintenance costs over their lifetimes. Transit agencies often operate under tight budget constraints, so the capital expenditures for EBs and chargers must be planned alongside operating costs and revenues. Opportunities exist to offset costs where government subsidies can reduce purchase costs [
9], and transit authorities may consider modest fare increases given the improved service sustainability [
10,
11,
12]. Additionally, the societal and environmental benefits of electrification, such as improved air quality, curbed carbon emissions, and reduced noise levels, have economic value that can be monetized through incentive mechanisms (e.g., carbon trading) or considered as part of a broader cost–benefit setting.
Existing studies on bus fleet electrification have typically focused on specific subsets of these issues, such as optimizing charging infrastructure placement, establishing bus-to-route assignment given a fixed fleet composition, or minimizing vehicle and energy costs, in lieu of integrating all aspects into a single decision-making framework. In practice, the transition plan must be holistic, coordinating financial planning, technical requirements, operational considerations, and multi-stakeholder perspectives over a several-year planning horizon. A financial plan must include not only capital and operating costs but also potential revenue changes (e.g., fare policies) and budget limitations. Technical requirements involve selecting appropriate bus types (battery capacity, size) and charger technologies, as well as deciding where to deploy chargers (depots or opportunity charging at terminals). Operational factors include the characteristics of existing bus routes (length, frequency, passenger demand) and fleet utilization. A multi-stakeholder perspective needs to be incorporated as well, including government agencies that might provide subsidies or set electrification mandates, and utility companies that need to coordinate grid capacity and electricity supply for charging infrastructure. Finally, modeling elements such as the temporal dimension (planning over several periods or years) and fleet age dynamics (phasing out old buses and introducing new ones) are crucial for capturing long-term effects.
There is a pressing need for a scalable optimization framework that can simultaneously handle these diverse elements to guide EB fleet transition planning. To that end, this paper aims to develop a comprehensive multi-period mixed-integer linear programming (MILP) model that integrates all key transition planning elements. The specific objectives of the study are to:
- (1)
Identify and integrate the critical planning elements (financial, technical, operational, and stakeholder-related) influencing EB fleet transitions;
- (2)
Formulate a comprehensive optimization model that jointly optimizes fleet electrification schedules, charging infrastructure deployment, and operational allocation over a long-term horizon;
- (3)
Apply the model to a real-world case drawn from Dubai’s RTA and validate its effectiveness toward producing a feasible, cost-effective transition strategy;
- (4)
Analyze various scenarios to test the model’s robustness and derive practical insights on how changes in key input parameters impact the optimal transition plan.
The primary contribution of this work is a unified planning model for EB fleet transition that combines financial analysis, technology selection, strategic fleet deployment, infrastructure planning, and policy levers in one optimization framework. To the authors’ best knowledge, this level of integration exceeds that of prior studies, which have not concurrently addressed all these dimensions. Notably, this comprehensive integration is coupled with three specific advances. First, rather than relying on the fixed charger-to-bus ratios common in prior work, this work embraces an endogenous demand-linked energy aggregation approach at depots and terminals that determines the number, type, and placement of chargers from route energy demand. Second, the proposed model explicitly incorporates system feasibility constraints within the strategic planning framework, particularly dwell time availability and charging grid-capacity limits, ensuring that infrastructure deployment and fleet transitions remain consistent with physical and operational service requirements. Third, the proposed model adopts a profit-maximization-based objective that internalizes fare revenue, governmental subsidies, and monetized environmental and social externalities within the fleet transition decision-making process.
The UAE’s 2050 net-zero initiative [
4] provides an excellent case study that demonstrates how transit agencies can use the model to evaluate trade-offs. For example, the model can determine the cost of accelerating electrification versus the environmental benefits and can help strategize the timing of investments. The scenario analysis provides further insights into the sensitivity of the transition’s outcomes to critical factors, guiding agencies on what external support or operational adjustments have the greatest impact. Overall, this work offers a practically applicable yet methodologically rigorous decision support tool that would aid policymakers and transit authorities in planning the complex transition to EBs in an efficient and cost-effective manner.
The remainder of this paper is organized as follows.
Section 2 provides an overview of EB research, describes the transition planning elements in more detail and reviews the relevant modeling-based literature on EB transition planning, highlighting this paper’s unique contributions.
Section 3 presents the mathematical formulation of the optimization model and a detailed description of the problem context.
Section 4 provides the practical case study used for implementing the optimization model.
Section 5 presents the results of the base case along with a scenario-based assessment and a one-way sensitivity analysis validating the model’s effectiveness and practical relevance. Finally,
Section 6 presents concluding remarks, draws some managerial implications and outlines potential avenues for future work.
3. Model Formulation
This section presents the MILP model seeking to optimize the EB transition plan for urban transit authorities as depicted in
Figure 1. Consider a transition plan taking place over a planning horizon composed of
years, and let
represent all possible ages for a bus of type
. It is assumed that the transit authority makes replacement decisions at the beginning of each year, where age
corresponds to a new bus, and a bus of type
can operate until it reaches an age of
, at which point it must be salvaged. In order to address technical and infrastructure requirements, we introduce sets for bus types
and charging technologies
. Bus types encompass various fuel technologies, models, configurations, and sizes. Let
denote the subset of
types, with an example being EB 250 40, referring to a 40-foot electric bus with 250 kWh battery capacity. Charging technologies are primarily categorized into fast chargers
, which are used in terminals and are associated only with fast-charging electric buses FEB ⊆ B, and depot chargers
that support all types of EBs.
To realistically capture the complexities of EB operations, the model includes route-bus assignment with compatibility constraints. These constraints account for factors such as distance, battery capacity, energy consumption, dwell time, and load requirements. As indicated by [
13], using an aggregated approach to route assignment helps balance traceability and demand granularity. Let
denote the set of routes, where compatibility between routes and bus types is captured by a binary parameter
(1 if bus
of age
is eligible for route
in period
). Furthermore, suitable locations for charging infrastructure are identified by set
, which includes subsets
for depots and
for terminals. Building on the existing network,
represents the route–location relationship parameter (1 if connected, 0 otherwise). Electric utility constraints are modeled by grid capacity limitations
at every location. At the beginning of the planning horizon, the fleet consists of
buses of type
and age
, while the charging infrastructure comprises
chargers of type
at location
.
Financial planning encompasses various costs and revenue calculations associated with replacement decisions. These costs cover bus purchases, midlife refurbishments (such as engine or battery replacements), operations (including maintenance and energy), and charger purchase and maintenance. Environmental and social costs are integrated based on the work of [
9], capturing the negative externalities of diesel buses in terms of air pollution, noise, and climate change. These costs were estimated using established methodologies, including damage cost, avoidance cost, and replacement cost approaches, and are assigned to each bus type based on its fuel technology. The model also incorporates two government subsidies, including a one-time purchase subsidy,
, reducing initial bus purchase costs, and an annual operational subsidy
based on active buses of type
and age
. The annual budget
available for purchasing buses and charging infrastructure in period
may be increased by subsidies and salvage revenues. To account for the time value of money, let
be the periodic discount rate, and let V =
be the corresponding one-period discount factor. All cash flows gradually incurred over the course of a period, such as bus fare revenues or maintenance and energy costs, are assumed to be made at the beginning of the period. Thus, an amount incurred in period
will be discounted by
.
On the revenue side, the salvage value for retired buses of type and age in period represents the monetary return, influenced by transit authority policy (sell, scrap, or donate). Research also indicates a higher customer willingness to pay for EBs, leading to the bus fare for route when using bus type as a significant revenue source. As the fleet transitions to more EBs, annual bus fare revenue is expected to rise, contingent on factors such as the number of trips, passenger capacity and the route’s average load factor .
As detailed below, eight sets of decision variables are used in the model, seven of which are integers, and one is continuous. These include the number of buses and chargers purchased, salvaged, available and assigned, as well as the allocation of buses to routes and locations. Given that routes connect two terminals, the model allows for flexibility in distributing the number of buses across these terminals, which then influences the number of fast chargers required for EBs. The continuous variable estimates total daily energy demand at each route–location pair, depending on factors such as route distance , energy consumption , and battery capacity , which is then used to determine the required number of chargers. This approach directly addresses the shortcomings in existing studies that often rely on the oversimplified fixed charger-to-bus ratios.
A comprehensive list of all sets, parameters and decision variables used in the development of the mathematical model is included in
Appendix A. The model’s objective function and constraints are developed next.
The objective function maximizes the total discounted profit of the entire transition plan by incorporating all relevant revenues and costs. The overall structure builds on the formulation in [
13] by including internal bus costs such as purchase prices, midlife refurbishment expenses, ongoing maintenance and energy costs, charging infrastructure costs covering charger purchase, installation, and maintenance, and the salvage values of retired buses. It is then extended by incorporating the one-time subsidy that reduces initial purchase costs, the annual subsidy based on the number of operational buses, and the environmental and social cost terms related to air pollution, noise, and climate change as presented in [
9]. In addition to these elements, this work adds the revenue generated from bus fares to obtain the profit-based formulation. The profit objective is best interpreted not as commercial profit but as a net social benefit, or public-sector planning objective. Once fare revenue and monetized environmental and social externalities are internalized, it nets the agency’s costs against user-borne fares and society-borne externalities, and it reduces to cost minimization when the revenue and externality terms are switched off, as in the base case. Profit maximization was adopted deliberately so that revenue-side levers, fare adjustments (Scenario 6) and subsidy design (Scenario 7) could be assessed, which a pure cost-minimization framework cannot capture.
The following constraints represent standard practice for fleet assignment, availability, and aging throughout the planning horizon, based on the approach in [
13]. Constraint (1) ensures that the number of assigned buses matches the required amount over time. Constraint (2) stipulates that route assignments respect bus type and age compatibility, ensuring that only suitable buses operate on specific routes. Additionally, Constraint (3) states that all available buses of a given type and age during a specific period must be assigned to runs to prevent idle capacity. However, the model is flexible enough to accommodate overcapacity by adding dummy routes, ensuring there are sufficient spare buses available for emergencies or scheduled maintenance without incurring additional costs or generating revenue from them. Constraints (4) and (5) determine the availability of new buses of each type based on purchases made at the beginning of each period, including any already owned buses considered new for the first period. The model tracks fleet aging through Constraint (6), which updates the number of buses of each type and age annually, taking into account those that have been salvaged. Once buses reach the maximum age, Constraints (7) and (8) mandate that all buses, whether purchased or preowned, be automatically salvaged, and Constraint (9) ensures that the initial fleet composition accounts for buses already owned minus those salvaged at the start of the planning horizon.
To link buses to their respective locations and account for the resulting energy demand, this study introduces constraints that aggregate daily energy use at depots and terminals and ensure it stays within grid capacity limits. Constraints (10) and (11) assign buses to locations in each period by using
, a binary parameter that establishes the link between routes and their corresponding locations. However, since routes connect two terminals, this may lead to a varying distribution of energy demands, resulting in different grid capacity and fast charger requirements. Consequently, for terminals specified in Constraint (11), the model manages the assignments to ensure maximum utilization and cost-effectiveness. Constraint (12) calculates each depot’s total daily energy demand by combining the energy consumption of EBs that charge solely at the depot with the battery capacity of buses that utilize fast-charging at terminals and depot charging. Constraint (13) calculates each terminal’s total daily energy demand by determining the energy consumption of EBs using terminal fast chargers, subtracting the battery capacity that has already been charged at the depot. Constraint (14) ensures that the total daily energy demand does not exceed grid capacity limits at each location.
To coordinate the allocation of chargers at depots and terminals and meet the corresponding energy requirements, this study introduces constraints that establish the number, type, and assignment of chargers over time. Constraints (15) and (16) ensure that the number and type of chargers at each location (depot chargers at depots and fast chargers at terminals) are sufficient to meet energy demands. This is based on their charging rate and the available charging time, which is constant at depots but differs at terminals due to factors such as the number of trips and the dwell time of each route. Contrary to the assumption that fleet growth always requires more fast chargers, Constraint (16) leverages a strategic trade-off, where increasing the number of EBs can reduce the demand on terminal fast chargers by shifting the required energy supplement to cheaper, more available overnight depot charging. Constraint (17) yields feasible fast terminal charging schedules by limiting bus assignment per charger. By calculating the ratio of required charging duration to available operational hours, it determines the minimum number of chargers needed to serve buses during their dwell time, which aligns charging duration with the operational hours of routes connected to that terminal within which charging can be scheduled. Constraints (18) and (19) track the number of EB chargers over time. Constraint (20) prevents the reassignment of chargers to different locations.
Constraint (21) ensures that the electrification targets are satisfied. The model assumes that the targets dictate a minimum percentage of buses that should be electric each year. Constraint (22) states that the total purchasing funds available at the beginning of a period are the sum of the budget and salvage revenues from that period, along with any one-time subsidies and annual subsidies. Constraint (23) prevents the excessive accumulation of aging buses by setting a maximum allowable average bus age in the final period Tf. This ensures long-term fleet renewal and sustainability, while also mitigating the end-of-horizon effect, where the model assumes operations will cease at the final period and make decisions without considering any future operations. Finally, Constraints (24)–(30) define the non-negativity and integrality restrictions on the respective decision variables. In practice, this end-of-horizon effect is further mitigated by re-solving the model on a rolling-horizon basis, whereby the average age constraint acts as a terminal condition, and each re-optimization captures updated parameter values and any change in fleet requirements.
4. Case Study
To assess the performance and applicability of the proposed MILP model, a comprehensive experimental environment is configured, carefully sourcing and processing data to reflect real-world operations in Dubai’s bus network. The practical data, including route specifications, were obtained from Dubai’s official RTA sources. Additional parameters such as maintenance and energy costs were acquired from relevant studies in the literature (as detailed below). The MILP model for the base case and for the different variants of input parameters was solved to optimality via the CPLEX optimizer within reasonable computational time (as seen below) using commercial hardware (Intel Core i7-11800H processor, 16GB RAM). The use of Microsoft Excel facilitated the input and output data management, alongside the organization and analysis of scenario results. The base-case model comprises 286,681 decision variables and 294,760 constraints, and solution times are reported per scenario in the corresponding results tables.
The study adopted a 25-year planning horizon (2026–2050) in alignment with predetermined electrification targets [
4]. While emphasizing the importance of long-term planning, we also recognize the need for accurate and up-to-date data inputs, especially given the rapid advancements in EB technology. Therefore, to maintain the model’s relevance and effectiveness, it should be solved periodically whenever changes occur. The case study is bounded to 71 of the 77 RTA lines, a fixed 406-bus fleet, year-round operation, and a 10 min dwell assumption. When the model is re-solved periodically, an agency would refresh the timetables and route distances, load factors, grid-capacity limits, the battery-cost trajectory, energy and diesel prices, and the fare-response parameters. For reproducibility, the optimization model implementation (solved with CPLEX), the full input dataset, and the route-vehicle compatibility matrices are made available at
https://doi.org/10.5281/zenodo.20598731. An explanation of the acquired data for the base-case scenario is provided next.
Network and Route Data: The obtained data comprises detailed schedule and routing information for 71 of the RTA’s 77 urban bus lines directly from the Dubai RTA’s online timetable portal [
35]. Six low-volume or data-incomplete routes were consolidated to avoid distortions in demand estimation. For each route, we extracted the number of daily departures, average trip frequency, average trip duration, first-and-last service times, with the difference indicating operational hours (
), and nominal trip lengths. Geographic distances between stops were computed via a GIS tool, enabling precise calculation of per-trip energy requirements. Depot charging windows (i.e., the time during which buses are idle and available for charging) were inferred from non-operational hours, as reported in RTA depot operational manuals. Using this data, the number of required buses per route,
, was calculated using the formula
, where
indicates the smallest integer greater than or equal to
. We assumed that the dwell time is 10 min, which is sufficient for passengers to board and alight the bus. Consequently, we derived the daily and annual number of trips per bus (
and
), as well as the daily and annual distance traveled per bus (
and
), assuming year-round operation. Different bus fares (
) were allocated for each route, with longer routes assigned higher fares [
36]. Typically, higher-passenger-capacity buses are designated for routes with fewer stops, resulting in higher speeds. For bus size distribution, sources indicate allocations of 64% for standard models, 24% for articulated, and 12% for double-decker buses [
37].
Fleet and Vehicle Characteristics: The existing fleet consists of 406 Diesel buses with ages following a normal distribution, having a mean of 7 years and a standard deviation of 2 years, with zero EBs or charging installations initially deployed. Ten candidate vehicle configurations were selected, three diesel and seven electric variants, based on a combination of published technical specifications such as [
38] and manufacturer data [
39]. Electric variants differ by battery capacity (ranging from 250 kWh to 650 kWh), on-route charging capability (depot-only vs. depot + terminal fast-charging), and vehicle length. Compatibility matrices were constructed to ensure that each bus type could satisfy the minimal range requirements of every route under both peak and off-peak load factors. The fleet size is kept constant at 406 throughout the planning horizon. The specific bus types considered in this analysis include 40 ft standard and double-decker buses and 60 ft articulated diesel buses with specifications as indicated in
Table 3. The specifications of the EBs are summarized in
Table 4.
This constant fleet assumption is justified on two grounds. First, UAE’s population is roughly 10% nationals and 90% expatriates, and projected growth is concentrated in the national segment, whose public bus ridership is extremely low or nonexistent, rendering the ridership base served by the network relatively stable over the planning horizon. Second, as noted above, the model is intended to be re-solved on a rolling-horizon basis, allowing demand drift and any fleet-size adjustment to be absorbed at each re-optimization, whereas the explicit modeling of demand growth is left to future work.
The bus specifications detailed in
Table 3 and
Table 4 were gathered from various reliable sources. We based our figures on the recent work of [
9], which referenced median prices reported by [
38]. For EBs, costs are divided into battery and vehicle costs. Diesel bus and vehicle costs are assumed to remain constant throughout the planning period. However, Battery cost is projected to decline annually by 9%, driven by ongoing technological advancements. This decline begins with a baseline cost of 858 AED per kWh in year 0 (initial year), reflective of the 2017 figure of 1825 AED per kWh reported by [
40] and adjusted according to market projections from [
41]. Bus passenger capacity was obtained from [
39], with EB energy consumption figures. For diesel buses, fuel consumption data was sourced from [
42] for standard buses and from [
38] for both articulated and double-decker buses. It is noted that the assumed lifetime for diesel buses is 15 years [
41], while EBs are estimated to have a lifetime of 12 years [
18], reflecting the shorter battery life compared to diesel engines.
Environmental and social cost, subsidies, bus fare and load factor: The environmental and social costs for air pollution, noise, and climate change by bus type are presented in
Table 5, with values sourced from [
9], who cited [
43]. These costs reflect only the operational externalities and exclude life-cycle emissions associated with electricity generation for EBs or the production and disposal of the buses themselves. To establish a baseline, these costs were set to zero in the base-case scenario. Since the average load factor influences passenger demand, fare revenue, and related environmental and social costs, we calculated it to be 0.727. This value was based on the RTA’s reported 2023 ridership of 173.5 million passengers [
44] and the assumption that the selected routes in this study, representing 40% of the total, also constitute 40% of the demand. Although the load factor, along with subsidies, fares, and environmental and social costs, does not affect the base-case scenario, their individual impacts are evaluated in later scenarios. The environmental and social cost values are adopted from [
9], which draws on the European Commission external-cost handbook [
43], and are assigned by fuel technology. Therefore, their transferability to the UAE is approximate since the local grid mix, climate-driven health burden, and valuation parameters may shift the magnitudes. Consistent with [
9], these values capture operational (tailpipe and noise) externalities only and exclude upstream electricity generation emissions for EBs as well as battery production and disposal. Note that this treatment biases the comparison modestly in favor of EBs, and a more carbon-intensive grid would narrow but not reverse the gap. The load factor of 0.727 is a system average estimate derived from 2023 ridership under a proportional demand assumption where route-level load factors vary around this value and constitute a further source of uncertainty examined in the sensitivity analysis section.
Charger-related information: Two charger types are considered: a 100 kW depot charger (292,000 AED) and a 250 kW terminal fast charger (548,000 AED) [
41], with maintenance costs set at 1% of the purchase cost [
18].
Maintenance and energy cost: Building upon the methodology of [
13], total energy and maintenance costs for each bus type and age over the planning horizon were calculated based on the approximate annual distance of each route. For 60 ft diesel buses, maintenance costs were derived from a regression analysis using real transit agency data [
33], which modeled maintenance cost per mile as a function of vehicle age. Maintenance costs were assumed to be consistent across different bus sizes of the same type. For EBs, ref. [
45] estimated maintenance costs to be 20% to 60% lower than those of diesel buses. In this study, a midway value of 40% reduction in EB maintenance costs is adopted. Energy costs were calculated by multiplying the fuel or energy consumption of diesel and EBs by the route’s annual distance, using diesel and electricity prices of 2.77 AED per liter [
46] and 0.38 AED per kWh [
47], respectively. This facilitated the estimation of energy cost per unit distance for each bus type.
Electrification targets and discount rate: The electrification targets were established in accordance with the RTA’s strategic plan [
4], outlining the following progression: 10% electrification by 2030, 20% by 2035, 40% by 2040, 80% by 2045, and 100% by 2050. However, due to the identified incompatibility of certain routes with all considered EB types, the base-case scenario was adjusted to achieve 90% electrification by 2050. This adjustment reflects realistic operational constraints and will be further evaluated and refined in subsequent scenario analyses. Furthermore, a yearly discount rate of 3.4% accounts for the time value of money, reflecting regional economic considerations within the UAE [
48].
6. Concluding Remarks and Future Research Avenues
This study presented a comprehensive and data-driven optimization model to support transit authorities in planning a cost-effective and operationally feasible transition to EB fleets. We formulated a multi-period MILP model that jointly integrates key inherent transition planning elements, including financial planning, technical and infrastructure requirements, existing bus network operations, multiple stakeholder perspectives, and essential modeling elements (as seen in
Table 1). By combining these dimensions, the model better mimics real-world practices, fills a critical gap in the existing literature and offers a practical decision-support tool for transit agencies navigating the shift to zero-emission transport. Beyond this integration, the framework is distinguished by three specific advances: an endogenous, demand-linked determination of charger number, type, and placement in place of fixed charger-to-bus ratios; the explicit embedding of system-feasibility constraints, namely dwell time availability and grid-capacity limits; and a profit-maximization objective, which is interpreted as a net social benefit or public-sector planning objective, that internalizes fare revenue, government subsidies, and monetized environmental and social externalities. The scalability and practical relevance of the proposed model were illustrated via a case study of Dubai’s RTA, where the model generated an actionable transition plan that aligns financial prudence with operational feasibility. The optimized strategy includes a phased bus procurement schedule, prioritization of terminal-based fast-charging infrastructure, deployment of a mixed fleet tailored to route diversity, and a financing structure that evolves alongside battery cost declines and policy shifts. To assess the robustness of this plan, seven different realistic scenarios reflecting technological, economic, operational, and policy variations were developed. Collectively, the scenario analyses demonstrate the model’s capacity to quantify complex trade-offs among technology, policy, and operations. Rather than relying on a single solution, transit authorities can benefit from integrated, scenario-based planning frameworks that adapt to shifting market dynamics, stakeholder goals, and operational constraints, enabling them to design effective electrification roadmaps that balance financial performance, environmental objectives, and operational realities.
In particular, the results of the scenario analysis reveal that charging strategy and dwell time assumptions significantly influence both cost and feasibility. Scenarios with shorter dwell times and terminal-based fast-charging achieved full electrification with reduced infrastructure investment by enabling higher charger utilization and faster vehicle turnover. Furthermore, it turned out that technology choice plays a pivotal role. In range-constrained conditions, fast-charging standard EBs consistently offered better performance than depot-only models. However, as battery prices declined, the model favored more flexible fleet compositions, which demonstrates how cost trajectories can broaden viable options over time.
Policy-related scenarios illustrate that ambitious procurement mandates, such as transitioning to an EB-only fleet, can bring forward full electrification by a decade with minimal financial impact, provided that infrastructure expansion is coordinated. In contrast, scenarios characterized by specific time-phased electrification targets resulted in significant financial implications, highlighting the importance of maintaining flexibility in target-setting, budget allocations, and grid development timelines.
While the incorporation of environmental and social costs contributes a relatively small portion of total direct cost, it did trigger a shift in procurement timelines and technology choices. Notably, profit maximization emerged as a suitable planning objective, as it encompasses both cost savings and revenue generation and yields outcomes well-aligned with public benefit. Revenue-enhancing policies, such as modest EB-specific fare increases and carefully crafted subsidy structures, showed strong potential to improve financial outcomes and accelerate adoption, offering transit agencies an internally sustainable lever for funding cleaner fleets. Over time, as EB technology becomes more economically viable and electrification targets become more ambitious, the relative influence of subsidies diminishes. This highlights the importance of aligning policy support with the most financially sensitive phases of the transition. In this sense, the objective is best read as a net social benefit, or public-sector planning, objective rather than commercial profit, and the framework reduces to cost minimization when the revenue and externality terms are excluded.
For practitioners, these findings translate into several direct recommendations. One shall prioritize terminal-based fast-charging supported by adequate dwell time buffers, favor an all-electric procurement rule over rigid interim milestones, as this brings full electrification forward by roughly a decade at negligible additional cost, concentrate subsidies early through a declining-block design where their marginal impact is greatest, and either build flexibility into milestone dates or pre-allocate budget and accelerate grid development to avoid the cost premium associated with rigid targets.
Several future research avenues can further enhance the model’s applicability and depth. One priority is analyzing the interaction between bus requirements, dwell time, and route frequency, particularly as evolving passenger demand may influence fleet sizing and deployment strategies. Furthermore, moving beyond a one-to-one replacement logic toward network-wide optimization could reveal more efficient solutions. In addition, extending the model to account for a broader range of cost and revenue sources, along with the consideration of emerging technologies such as hydrogen fuel cell buses or alternate charging options such as battery swapping (see Fang et al. [
49]), would allow for a more holistic evaluation framework. Lastly, closing the loop by considering secondary uses of retired EB batteries and accounting for that as an integral part of the transition optimization framework stands out as a promising avenue for future research. Given that all results reported in this work above are deterministic, the framework could be extended to handle parameter uncertainty in electricity prices, battery cost, and ridership through two-stage stochastic programming or robust optimization, which stand out as a promising avenue for future research. Lastly, further priorities may consider extending the cost accounting to a full life-cycle basis that incorporates upstream electricity-generation emissions as well as battery production and disposal.