A sensitivity analysis on the application of the Joule heating strategy on the designed POCS is carried out. Then, the selected operating conditions are applied to simulate the response of an after-treatment system equipped with EHC–POCS and to evaluate the computed abatement performances with respect to the reference exhaust line.
4.2.1. Electrical Heating Sensitivity Analysis
The results obtained according to the different applied potential differences are presented. A visualization of the simulated domains’ temperature and voltage fields is reported in
Figure 11, referring to the simulation end-time of the 38 V potential difference. The shown distributions prove the goodness of the designed electrical circuit, resulting in the significant heating of the struts region only. The struts’ average temperature profile all over the simulated time range is reported in
Figure 12. The applied boundary condition significantly influences the Joule heating power that is produced as the electrical current flows through the silicon carbide struts, as reported in
Table 7.
Given the expected interaction in the first phases of a cold start between the exhaust gases and the POCS, a potential difference higher than
V is required: the identified maximum average temperature is slightly higher than 500 K and no beneficial effects in the cold start abatement efficiencies are expected below the highlighted temperature. However, the associated supplied electrical power would exceed 500 W for a single duct; the application of such a structure in all the exhaust manifolds could significantly affect the vehicle battery’s operational life. In addition, the maximum temperature that characterizes the POCS struts after the simulated five seconds could exceed the material limit temperature. The maximum values for each investigated condition are reported in
Figure 13. Nonetheless, the interaction between the cold exhaust gases and the struts could limit the achieved maximum temperatures, ensuring that the material limits are respected. For this reason, the formulated heating strategy is modified and a total of six seconds of electrical heating are applied for the cold start assessment simulations. Even though the overall supplied electrical power could be critical for a real exhaust line application, the
V operating condition was selected for the cold start assessment. As such, the maximum capability of the EHC–POCS could be investigated.
4.2.2. Exhaust Line Equipped with EHC–POCS Assessment
The results related to the application of the EHC–POCS as a pre-catalyst are reported. In particular, the obtained data of two different scenarios (with and without the designed structure) are analyzed in order to evaluate the application of the EHC–POCS and the resulting beneficial effects in terms of ATS performances. The EHC operating conditions are selected to exploit the electrical heating sensitivity analysis:
V for a total of six seconds. At first, the heat transfer phenomena occurring in the first portion of a single exhaust manifolds are investigated in case the EHC–POCS is equipped in the exhaust line. To carry out a consistent comparison, the thermal response of the same first portion of the exhaust manifold is simulated excluding the presence of the designed structure. The analysis of the obtained temperature profile at the outlet of the considered geometry provides a clear understanding of the effects related to the electrical heating application and to the fluid–POCS heat transfer phenomena. In particular, the outlet temperature profiles computed through the two different simulations, superimposed over the inlet temperature trend, are shown in
Figure 14.
The heating strategy is effective in increasing the temperature of the fluid flow. In particular, the achieved temperatures are such that the catalytic reactions are active in the first seconds of the cold start, which are commonly referred to as the most critical phases and are responsible for most of the pollutants emissions. As soon as the electrical heating is deactivated, the thermal inertia of the EHC–POCS is such that part of the fluid enthalpy is employed to heat up the designed structure. Two seconds after the deactivation, the EHC–POCS structure is responsible for lower outlet temperatures than what can be observed for the case without POCS. To account for the effectiveness of the obtained pre-catalyst behavior, the pollutants’ percentage abatements are computed and their profiles all over the simulated time-range are presented in
Figure 15. Considerable pollutant abatement is achieved three seconds after the engine cold start, which is approximately 20% for all the considered pollutants.
After the initial activation of the catalytic reactions, the pollutant abatement increase is slowed down around the time instant corresponding to 5 s: the maximum exhaust gas mass flow is being discharged while the gas temperatures are still below the characteristic reactions’ light-off values. As a consequence, even though the electrical power is continuously being supplied, the local maximum temperatures are slightly reduced. As time advances and the inlet fluid temperatures increase, the pre-catalyst is more and more effective. The final CO, NO and HC percentage abatements are approximately 45, 40, and 32%. The analyzed data prove the effectiveness of the pre-catalyst, resulting in higher fluid temperatures during the initial phases of the cold start and a considerable reduction in the pollutant emissions prior to the standard ATS devices. A visualization of the HC pollutants concentration and fluid temperature distributions for different selected time instants is presented in
Figure 16. A minimum temperature threshold equal to 500 K is employed in order to identify the domain portions where the catalytic activity is expected. From a qualitative point of view, it is possible to appreciate how the electrical power supply is effective in increasing the fluid temperature which grows as the radial distance from the POCS decreases (
Figure 16a,b). Once the heating strategy is over, the fluid temperature distribution is ruled by the imposed inlet profile (
Figure 16c,d). In addition, the pollutant abatement due to the washcoat-induced catalytic activity corresponding to the struts walls can be appreciated.
The proposed results are employed as boundary conditions for the exhaust line simulations. As such, the beneficial effects of the EHC–POCS equipment can be investigated, both in terms of the increase in the catalysts’ temperature and the pollutant abatement prior the ATS devices. An evaluation of the thermal transient of the first catalyst is presented in
Figure 17. In particular, the surface average temperature of four different sections are analyzed over the simulated time-range. The selected axial coordinates for which such an evaluation is carried out corresponds to the inlet, 25 mm after the inlet, mid, and outlet coordinates.
The electrical heating phase results in a significant spur of the heating of the first portion of the CAT1. After five seconds, the temperature of the inlet section for the ATS configuration equipped with the EHC–POCS is 100 K higher than what can be observed for the reference case. However, once the electrical heating strategy is over, the presence of the EHC–POCS induces a heat loss that becomes significant as the exhaust gas temperatures increase: the initial spur is gradually recovered until the heat transfer between the exhaust gases and the designed POCS results in an overall cooling of the fluid flow. In particular, the inlet section temperature profile of the reference case overcomes the profile of the ATS equipped with the EHC–POCS after eight seconds, while the 25 mm and mid-sections after eleven and sixteen seconds, respectively.
The improved heating of the first portion of the CAT1 catalyst can be additionally analyzed by evaluating the temperature fields of the device for the two different configurations. In particular, the distribution of a slice of the temperature fields for two selected time intervals is presented in
Figure 18, referring to half and to the end of the applied electrical heating strategy.
However, the exhaust gas mass flow rates and the pre-defined voltage boundary conditions are such that the overall energy contribution that is provided to the catalytic substrate is limited. In addition, the EHC–POCS structures are located in the initial portion of the exhaust manifolds: before reaching the standard catalyst, the heated fluid flow exchanges a significant amount of wall heat power with the exhaust manifolds. As a consequence, at the end of the heating strategy, only a small portion of the ATS device was significantly heated up. As the exhaust gas flow rates and temperatures increase, the induced heat transfer between the hot gases and the designed POCS are responsible for a significant reduction in the first catalyst temperature with respect to the reference case. The temperature field distributions of the first catalyst at the simulation end-time is reported in
Figure 19 for both of the ATS configurations analyzed. In particular, different regions featured by a temperature difference of 100 K have been highlighted through the identification of temperature iso-lines.
Only the thermal transient of the first catalyst was investigated, while the second substrate was not considered. The simulated operating conditions are such that no relevant effects affect the thermal response of the second catalyst. Indeed, at the simulation end-time, the outlet temperature of the CAT1 increased by approximately 50 K only under the assigned initial conditions. The thermally related effects discussed herein are strongly coupled to the obtained pollutants’ conversions. In particular, the percentage abatement profiles of the three considered pollutants are reported in
Figure 20.
The heating strategy and the pre-catalyst behavior achieved through the EHC–POCS are effective in inducing significant pollutant conversions. Even in the first phases of the cold start, the abatement of the three pollutants resulted in 25% due to the combination of the POCS pre-catalyst behavior and a modest spur of the CAT1 light-off. When the maximum exhaust gas mass flow rate was discharged, the abatement efficiency was slightly affected, while it was promoted as the inlet exhaust gases temperature increases. In addition, the tail-pipe pollutants’ cumulative emissions are evaluated for both the configurations under investigation, which are the ATS equipped with the EHC–POCS and the base exhaust line. The reductions induced by the POCS structure are reported in
Table 8. The presented values show how the EHC–POCS behavior as a pre-catalyst is effective in reducing the pollutants’ emissions in the first phases of a cold start.
However, the heat losses associated with the late exhaust gases and EHC–POCS interaction result in a reduction in the fluid temperatures prior the first catalytic device. As a consequence, the chemical reactions characterized by a high activation energy could be penalized. For most of the simulated time-range, the reference exhaust line provides a lower conversion efficiency than what can be obtained by exploiting the EHC–POCS. Towards the end of the simulation, the previously addressed thermal inertia effects are such that the maximum temperatures of the first catalyst are lower than those of the reference case and a lower HC abatement is obtained (
Figure 20). This aspect is detrimental for the abatement of the C3H8 chemical species, whose reaction rate strongly depends on the temperature. The percentage abatement of the two considered hydrocarbons is reported in
Figure 21, highlighting the appointed phenomena: towards the end of the simulation, the C3H8 conversions in the reference case are higher than in the POCS case results.