1. Introduction
Nowadays fossil fuels are still the main worldwide energy resource (almost 80%) and global energy consumption is expected to increase by about 33% by 2050 [
1,
2]. Moreover, the amount of readily available fossil fuels, such as natural gas and petroleum, is estimated to decrease quickly in the next 50 years. At the same time, combustion of fossil fuels is regarded as the main contributor to air pollution and GHG (greenhouse gas) emissions [
3,
4]. In this regard, air pollutants produced by the road transport sector (such as carbon monoxide (CO), nitrogen oxides (NO
X), unburned hydrocarbons (HC), and particulate matter (PM)) are increasing meaningly worldwide and affecting the air quality in urban contexts with noteworthy negative effects on human health. In fact, recently, nearly 20% of worldwide GHG emissions are the result of the increasing number of circulating diesel and petrol cars [
5].
For these reasons, nowadays, nations worldwide are sturdily supporting research activity towards hybrid electric propulsion and renewable fuels both to decrease dependency on fossil fuels and to reduce dangerous air pollutants. In addition, in the last decades, severe national regulations have been applied to emissions from the road transport sector to improve air quality state in urban areas, hence reducing negative impacts on human health [
6].
In this context, in recent years, two-wheeled vehicles have taken on a growing main role in private mobility with a direct effect on the urban air quality of European countries. Realistically, the percentage contribution of emissions from motorcycles and mopeds to the whole air pollution will rise in the next few years if no corrective measures are assumed. Two-wheeled vehicles, in effect, are widely used as a means of urban transport in the chief European cities, in which they represent a significant share of motorized vehicles. In recent years, in fact, two-wheelers accounted for around 32 million vehicles in the EU-28, then being about 8% of the whole vehicle fleet [
5]. In Italy, for instance, traffic congestion and parking difficulties affect the actual alternatives for urban transportation mobility to the point that the percentage contribution of motorcycles and mopeds to the total passenger mobility fleet is higher than 20% [
6,
7].
For all these reasons, nations worldwide must strive to develop both cleaner alternative fuels from renewable sources and hybrid electric propulsion to decrease the demand for fossil fuels and to decrease dangerous air pollutant emissions from two-wheelers [
8]. This is precisely the purpose of this analytical-experimental investigation: to propose hybrid electric propulsion for motorcycle application to reduce engine-out emissions in urban contexts. However, to the best of the authors’ knowledge, little is known in scientific literature about hybrid electric propulsion for motorcycle application in ordinary working conditions. As a promising alternative for urban transportation mobility, at present, numerical-experimental assessments of the hybrid propulsion in SI engines for new generation motorcycles are lacking, and the emission performance at part-load operation has yet to be defined.
In a previous experimental investigation [
9], emissions of regulated pollutants were detected in the exhaust of a motorcycle belonging to the Euro-3 legislative category, equipped with a four-stroke SI engine (displacement of 280 cm
3) and a three-way catalytic converter. Since exhaust emissions and fuel consumption are very sensitive to variations in vehicles’ instantaneous speed and acceleration, in this research, new experimental results are used to recognize the kinematic parameters that cause higher HC and CO emissions. The hybrid electric propulsion is then proposed in this paper to reduce exhaust emissions in particular driving conditions which include high levels of acceleration with resultant fast, steep increase in engine speed. In such phases, in fact, an enrichment of the air/fuel mixture is generally needed which affects the conversion efficiency of the three-way catalyst. Then, the power requirements and the grade of electrical assistance in specific driving situations are estimated by a procedure based on both the measured exhaust emissions and the kinematic parameters of the driving dynamics collected during the experimental tests. Lastly, an environmental analysis is performed to predict a comparison between the tested thermal motorcycle and the proposed hybrid motorcycle, so estimating the share of saved CO and HC emissions. The results attained in this research can help to guide the existing research in emissions-reduction systems in motorised two-wheelers.
2. Experimental Tests: Vehicle and Emission Performance
A last generation motorcycle, equipped with a four-stroke SI engine (displacement of 280 cm
3), was tested for a previous experimental investigation [
9] in the laboratories of National Research Council (Naples, Italy). The vehicle under investigation, which belongs to the Euro-3 legislative category, is represented on the test bench in
Figure 1 and the main technical characteristics are summarized in
Table 1. For this motorcycle, an accurate tuning of air/fuel mixture was reached through an electronic fuel injection system and a closed-loop exhaust after-treatment control system. As specified in
Table 1, the technologies adopted on this vehicle to meet the latest emissive standards are a carbon canister and a three-way catalytic converter.
This motorcycle was tested on a two-wheeler chassis dynamometer (AVL Zollner 20″—single roller) which is designed to simulate road load resistance (comprising vehicle inertia) and to measure the engine-out emissions during the tests. During dynamic speed cycles, the exhaust gases are diluted with ambient air by adopting a Constant Volume Sampling with the Critical Flow Venturi (AVL CFV-CVS) unit. Subsequently, the diluted exhaust gases pass through a dilution tunnel to reach steady flow conditions. A fraction of diluted exhaust gases is sampled downstream of the dilution tunnel to measure continuously the concentration of CO and HC at 1 Hz by an exhaust gas analysis system (AVL AMA 4000) [
9]. In more detail, CO and HC concentrations were measured by a non-dispersive infrared analyser (NDIR) and a flame ionization detector analyser (FID), respectively, which offer a precision of ±2%. Before being tested, these measuring instruments were also calibrated daily with zero gas. The gases utilized in the calibration of these analysers were nitric oxide, CO, carbon dioxide and propane, which were mixed with pure nitrogen. In addition, the background pollutant concentrations of indoor air were evaluated by subtracting them from the test results.
In the experimental campaign performed for the purpose of the present study, CO and HC instantaneous emissions (shown in
Figure 2 and
Figure 3, respectively) were measured during the UDC (Urban Driving Cycle) that is the Type Approval driving cycle according to the procedures laid down in the last Directives. Such figures also report the pertinent real speed profile. Several aspects must be considered to explain these results, which must be regarded as closely related: the kinematic characteristics of the different driving patterns (especially the acceleration phases with the related enrichment of air/fuel mixture), the light-off temperature and the conversion efficiency of the catalyst, and the additional mixture enrichment during the engine warm-up.
In these figures, first, it is evident that the instantaneous CO and HC emissions reach sudden and very high peaks during driving dynamics characterized by high levels of acceleration. In more detail, to ensure these operating situations, the electronic control unit bypasses the lambda sensor control and fixes a very rich air/fuel mixture which is sometimes outside the optimum efficiency range of the three-way catalyst, thus implying a significant increase in HC and CO emissions (open loop operating conditions). Indeed, the highest levels of CO and HC engine-out emissions were detected when rapid changes in vehicle speed are required. This is attributable not only to the three-way catalyst efficiency of this motorcycle, but also to imperfect combustion processes in specific driving conditions with a rapid, steep rise in engine speed that is no longer balanced by the catalyst [
10,
11]. Thus, not only does the required rich air/fuel ratio produce high levels of CO and HC exhaust emissions but the mechanism of controlling them is limited too.
In this regard,
Figure 4 shows the air/fuel equivalent ratio λ, which is calculated during the UDC driving cycle according to the compositions of the measured exhaust emissions of CO, CO
2, HC and O
2. The λ ratio periodically fluctuates around the stoichiometric value as the fuel flow is varied and, under specific driving conditions that include several acceleration phases, a rich air/fuel mixture is fixed to be provided to the combustion process, which accounts for the higher HC and CO exhaust emissions of the tested vehicle [
12,
13]. In effect, in
Figure 4, it is shown that during the hot phase (after around 200 s), the equivalent ratio λ is only stoichiometric on average over time, while at high engine speeds and loads, and during acceleration phases, it decreases broadly from one time to the next. Hence, an enrichment of the air/fuel ratio is required in such driving conditions which affects the conversion efficiency of the catalyst, so producing higher emission levels [
14].
The width of the optimum range of air/fuel ratios near stoichiometric, for the best conversion efficiencies of CO, HC and NO
X, is very thin, about 0.1 air/fuel ratios (7 × 10
−3 in equivalence ratio units) but, generally, it also depends on mileage use and catalyst formulation [
15]. However, for an efficient closed-loop electronic control system, holding the air/fuel ratio accurately on the fixed stoichiometric value is also not an easy expectation.
In
Figure 4 it is also evident that, during the cold phase of this motorcycle, the engine operates using a rich mixture in the cylinder to help overcome the poor mixing of the inlet charge because of fuel vaporization being slow and the cylinder walls being cold. Clearly, increasing the fuel flow to provide an easily combustible fuel-rich mixture increases the CO and HC emissions because of there being too much fuel present to attain regular and complete combustion. Therefore, until such an enrichment is removed and the temperature of the exhaust emissions is higher than the light-off temperature of the catalyst, HC and CO engine-out emissions remain very high.
To better analyze the HC and CO emission results shown in the previous figures, the kinematic characteristics of the different driving patterns will be examined in the following paragraphs. Indeed, for a constant level of average speed, high values of acceleration involve a rise in energy request for the execution of the specific driving pattern, with resultant enrichment of the air/fuel ratio.
3. Analytical Evaluation of Power Requirements
The power requirements in several typical riding situations can be estimated by a procedure based on the experimental kinematic parameters that characterize the driving dynamics collected during the UDC test cycle. The whole power (
Ptotal) requested to move the motorcycle and the rider can be assessed as the sum of four terms: the power required to exceed the air strength (
Pdrag), the power needed to overtake the hill (
Phill), the power necessary to overcome rolling resistance (
Pfriction) and the power needed to exceed vehicle inertia (
Pacc) [
16]. The calculations to assess these power requirements (expressed in kW) are shown in Equations (1)–(5).
In these equations,
A [m
2] and
m [kg] are the frontal area and the total weight (motorcycle and driver), respectively,
Cd [-] is the drag coefficient,
δ [kg/m
3] is the density of air,
G is the slope grade,
Rc is the rolling coefficient and, lastly,
v [m/s] and
a [m/s
2] are the vehicle speed and acceleration, respectively. Clearly, for the vehicle under examination, all these values are well known.
In
Figure 5, the whole power requirements of the motorcycle under examination on the UDC driving cycle are estimated by using Equations (1)–(4) and the real speed–time profile (already reported in the previous
Figure 2 and
Figure 3). Clearly, since the motorcycle was tested on a two-wheeler chassis dynamometer, the power
Phill needed to overtake the hill is not evaluated in these numerical simulations. Instead, regarding the power
Pacc required to overcome the vehicle inertia during the acceleration phases of the UDC driving cycle, the kinematic parameters of the pertinent driving dynamics were considered and analyzed in detail. In general, for a constant level of average speed, high values of acceleration involve a rise in power request for the execution of the considered driving dynamics.
Thus, the driving dynamics of the UDC test cycle, which are assumed to cover various driving situations existing on urban roads, are analyzed by employing the collected real speed–time profiles. First, these online speed–time sequences were described with several kinematic factors to clearly differentiate its driving behaviour. Then, several driving situations were identified through a kinematic parameter that describes the driving behavior well in an urban context. This parameter is the product “
v·a” of the instantaneous values of speed
v and acceleration
a, computed for
a > 0 and expressed in m
2/s
3 (W/kg). Indeed, since this parameter characterizes (in Equation (3)) the tractive power
Pacc per unit mass needed in order to overtake the vehicle’s inertia during the acceleration phases, it is strictly linked to the exhaust emissions and fuel consumption of the vehicle under investigation [
16].
Table 2 shows the time-averaged levels of
Pdrag,
Pfriction and
Pacc which are estimated according to the above-stated classification and by using the measured kinematic parameters of the UDC driving cycle collected during the experimental tests. The global energy request for the tested motorcycle on the whole UDC driving cycle is also shown in the same table, where
Pmax represents the peak level of global power requirement (shown in
Figure 4).
4. Electrical Assistance on the Motorcycle: Modelling and Results
In this section, hybrid electric propulsion is proposed to reduce CO and HC exhaust emissions of the tested motorcycle in particular driving conditions that include high levels of acceleration, with resultant fast, steep increase in engine speed. In such phases, as exposed above, an enrichment of the air/fuel mixture is generally needed which affects the catalyst-conversion efficiency.
In the previous
Figure 5, peak levels of power requirements correspond to driving dynamics with high levels of acceleration, which involve a growth in the tractive power per unit mass necessary to overtake the vehicle inertia of the motorcycle. As exposed above, these high levels of power requirement during the acceleration phases are accountable for CO and HC over-emissions from the thermal engine.
A minimally invasive solution to reduce the environmental impact of this vehicle is to install an electric motor directly on the wheel hub, which can assist the thermal engine during transient phases, i.e., during acceleration phases. To choose the correct motor size, it is necessary to make some preliminary assessments, including evaluation of the maximum torque during transient acceleration, the wheel’s angular speed, and the nominal supply voltage of the electric motor [
17,
18]
Starting from the power required for the acceleration phases
Pacc and the angular speed
n, the acceleration torque
Tacc (which represents the acceleration mechanical load) can be obtained by adopting Equation (6). Once the wheel radius
r is fixed, the angular speed
n can be clearly evaluated in Equation (7), where
v is the linear speed of the motorcycle (reported in green line in
Figure 2 and
Figure 3). The angular speed
n and the acceleration torque
Tacc during the UDC driving cycle are displayed in
Figure 6.
Moreover, for the purpose of this research, a PM (permanent magnet) BLDC motor was selected with a supply voltage of 72 Vdc, a maximum supply current of 150 A, and 160 Nm of continuous torque. Subsequently, the selected PM BLDC motor was modelled with a suite of Matlab/Simulink scripts and subroutines, as shown in
Figure 7, where the DC machine model is described through the second principle of dynamics for a rotating body (Equation (8)).
In such an equation,
is the angular motor speed,
is the electromechanical torque, where
,
and
represent the motor inertia, the viscous friction coefficient and the Coulomb friction torque, respectively. In more detail, in this Matlab Simulink model, the mechanical acceleration torque
is the DC Motor input, whereas the motor control consists of a PI controller, in which the experimental angular speed
n and the simulated one are compared. Subsequently, the PI controller modulates the DC motor supply voltage and, consequently, the current
Ia supplied to the motor. The electromechanical torque
delivered by the BLDC motor is proportional to the armature current
, as shown by Equation (9), where
is a constant [
19].
The sizing of the energy storage system must satisfy several electrical and mechanical constraints. With regard to electrical features, the battery pack must guarantee the following conditions: the minimal energy storage to ensure the execution of the UDC driving cycle, DC-link voltage values compatible with the chosen BLDC motor and, lastly, discharging C-rate values able to provide the necessary power during the supply phase. On the other hand, concerning mechanical constraints, the maximum battery weight and requirement space cannot be neglected. For the selected BLDC motor, a lithium-ion battery storage has been modelled with a 72 Vdc nominal voltage and 27.2 Ah nominal capacity.
The battery voltage
Vbatt has been modelled using the Simulink Battery block. This block implements a generic dynamic model that represents the most popular types of rechargeable battery [
19]. In this study, a lithium-ion pack battery has been modelled, neglecting the battery aging effect. This battery was realized with 144 single cells, arranging 18 series and 8 parallel, each with a nominal voltage of
V and a max capacity of
Ah. The discharge model has been described through Equation (10), where
represents the discharging current,
is the filtered current value,
is the battery capacity, and
is the current time integral plus the initial battery charge [
18]. Moreover, in
Table 3, the most important parameters
,
, , A and
considered in this model have been shown. These parameters, known for single cells, have been recalculated by battery model code to obtain the good parameters able to describe the battery pack discharge behaviour shown in
Figure 8, composed of series and parallel combinations of cells.
In this research, an initial full State of Charge (SoC) of the battery was assumed (namely
). The SoC after 1200 s, which is the duration of the UDC driving cycle, is equal to
, as shown in
Figure 9a. This means that, for the selected battery pack (which has a nominal capacity of 27.2 Ah and nominal tension of 72 Vdc), approximately 11.8% of the whole charge is consumed after the execution of one repetition of the UDC cycle.
In other words, approximately 211 Wh of battery energy is consumed in one test repetition. Therefore, considering a full battery discharge and never going below 20% of the SoC, up to around 6.4 repetitions of the UDC driving cycle can be guaranteed, which correspond to an autonomy of about 44.8 km. The chosen battery must also be able to supply high current for a short time, with a maximum discharge C-rate equal to 4, as clearly shown in
Figure 9b. Moreover, the battery current supplied to the motor is always below 110 A, as shown in
Figure 9c, in accordance with the limits set by the BLDC motor manufacturer.
Lastly, in this research, an environmental analysis was performed to compare the tested thermal motorcycle with a similar one, that has the same technical characteristics of the tested vehicle and is equipped with an electric motor directly installed on the wheel hub (that is the configuration proposed in this research). Since this environmental analysis was performed under the same driving conditions of the selected UDC driving cycle, it is possible to estimate the share of CO and HC emissions that could be saved utilizing a hybrid motorcycle instead of a conventional thermal motorcycle.
Then, if the hybrid motorcycle was used, the share of saved CO and HC emissions on the distance travelled of 44.8 km (corresponding to the autonomy of the battery) was estimated starting from the experimental values of CO and HC emissions measured on the conventional motorcycle (shown in
Figure 1 and
Figure 2, respectively). The main results of this environmental analysis are reported in
Table 4. Clearly, as exposed in detail above, the autonomy of around 44.8 km has been calculated from the number of test repetitions of the UDC driving cycle which can be assured considering a full battery discharge when never going below 20% of the SoC.
It is important to highlight that the simulation results shown in
Table 4 for the hybrid motorcycle were obtained when the electric propulsion assists the thermal engine during specific driving dynamics characterized by high levels of acceleration (as already assumed in this research), so reducing the relevant high peaks of CO and HC exhaust emissions. In fact, high levels of power requirement during the acceleration phases of the UDC cycle (as shown in the previous section) are accountable for CO and HC over-emissions of the conventional motorcycle.
As can be clearly derived in relation to the results of
Table 4, the electricity production needed to recharge the batteries of the hybrid motorcycle becomes a source of exhaust emissions. Clearly, various production systems for electricity produce emissions of a mixture of pollutants which depend on the produced electrical energy. In upcoming research, the authors will investigate this specific aspect, also evaluating the pollutants related to the European and Italian Electricity mix.