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Review

A Review of Thermal Energy Management of Diesel Exhaust after-Treatment Systems Technology and Efficiency Enhancement Approaches

by
Gang Wu
1,
Guoda Feng
1,
Yuelin Li
1,
Tao Ling
2,
Xuejun Peng
2,
Zhilai Su
2 and
Xiaohuan Zhao
3,*
1
College of Automotive and Mechanical Engineering, Changsha University of Science and Technology, Changsha 410114, China
2
China Railway Wuju Group First Engineering Co., Ltd., Changsha 410114, China
3
Energy and Electricity Research Center, International Energy College, Zhuhai Campus, Jinan University, Zhuhai 519070, China
*
Author to whom correspondence should be addressed.
Energies 2024, 17(3), 584; https://doi.org/10.3390/en17030584
Submission received: 22 December 2023 / Revised: 21 January 2024 / Accepted: 23 January 2024 / Published: 25 January 2024
(This article belongs to the Special Issue Advanced Thermal Management Technologies and Heat Transfer)

Abstract

:
The DOC (diesel oxidation catalyst), DPF (diesel particulate filter), SCR (selective catalytic reduction), and ASC (ammonia slip catalyst) are widely used in diesel exhaust after-treatment systems. The thermal management of after-treatment systems using DOC, DPF, SCR, and ASC were investigated to improve the efficiency of these devices. This paper aims to identify the challenges of this topic and seek novel methods to control the temperature. Insulation methods and catalysts decrease the energy required for thermal management, which improves the efficiency of thermal management. Thermal insulation decreases the heat loss of the exhaust gas, which can reduce the after-treatment light-off time. The DOC light-off time was reduced by 75% under adiabatic conditions. A 400 W microwave can heat the DPF to the soot oxidation temperature of 873 K at a regeneration time of 150 s. An SCR burner can decrease NOx emissions by 93.5%. Electrically heated catalysts can decrease CO, HC, and NOx emissions by 80%, 80%, and 66%, respectively. Phase-change materials can control the SCR temperature with a two-thirds reduction in NOx emissions. Pt-Pd application in the catalyst can decrease the CO light-off temperature to 113 °C. Approaches of catalysts can enhance the efficiency of the after-treatment systems and reduce the energy consumption of thermal management.

1. Introduction

Due to their efficiency and reliability [1,2], diesel engines are still widely used in transportation for the long term [3,4]. However, the hydrocarbon (HC), carbon monoxide (CO), nitrogen oxides (NOx), and particulate matter (PM) in the exhaust gas of diesel engines seriously threaten human health [5,6]. Governments have successively introduced emission regulations to limit the emissions of diesel engines [7,8]. To meet the emission regulations, diesel oxidation catalysts (DOCs) [9,10], diesel particulate filters (DPFs) [11,12], and selective catalytic reduction (SCR) [13,14] are widely used in diesel exhaust gas after-treatment systems. However, the efficiency of DOC, SCR, and DPF is closely related to temperature [15,16]. The emission is poor [17,18] at a low exhaust temperature [19,20], and DOC and SCR are at a low efficiency level [21,22]. The urea stops injecting when the temperature is below 200 °C [23,24]. A large amount of HC, CO, and NOx will be directly discharged into the atmosphere if the exhaust gas is not treated at this time. Due to the low temperature, PM cannot be eliminated, resulting in blockage in the DPF, which deteriorates the performance of the engine [25,26]. The substrate will melt, and the activity of the catalysts will decrease or even fail, if the temperature is too high [27,28]. Therefore, diesel after-treatment thermal management is crucial for the efficiency of the after-treatment system.
Bai et al. [29] reported that a 15–20% opening of the intake throttle valve could increase the exhaust temperature to more than 200 °C, and the NOx emission under the world harmonized transient cycle (WHTC) could be reduced by 41.5%. They have performed experiments under transient conditions that provide a reference for practical applications. Honardar et al. [30] investigated the effect of post injection timing on exhaust gas temperature and brake-specific fuel consumption (BSFC) on a 1.56 L diesel engine. The exhaust gas temperature increased from 260 °C to 300 °C and the BSFC deteriorated from 530 g/kWh to 620 g/kWh when the post injection timing was postponed from 130 °CA BTDC to −10 °CA BTDC. Brin et al. [31] increased exhaust gas temperature by more than 50 °C with a turbine bypass under the cold federal test procedure (FTP). Turbine bypass might be an optimal thermal management strategy. Salehi et al. [32] optimized the exhaust valve opening (EVO) timing, which reduced the SCR light-off time from 659 s to 500 s, but the fuel consumption increased by 4.1%. Kovacs et al. [33] retarded the intake valve closing timing by 50°, which caused a 20 °C increase in the exhaust temperature and 1.4% reduction in fuel consumption. This research provided a method, intake valve closing timing, that saved fuel and raised the exhaust temperature at the same time.
Hamedi et al. [34] investigated a double-layer exhaust pipe thermal insulation strategy via CFD. The result showed that the DOC inlet temperature increased by 12 °C and the emissions of CO and HC were both reduced by 17%. Burch et al. [35] led to a 52% and 29% reduction in total CO and HC emissions, respectively, via vacuum insulation and phase-change materials (PCMs). Excellent results have been obtained by combining phase-change materials and thermal insulation. Feng et al. [36] increased the SCR inlet temperature by 19.9 °C on average, and improved the NOx conversion efficiency up to 8.0%, with an electrically heated catalyst (EHC). Miao et al. [37] employed a 4.85 kW EH-SCR and a 5.4 kW EH-DOC to shorten the SCR light-off time by 62 s. The dual EHC system presented in that study significantly reduced SCR light-off time. Ma et al. [38] developed an afterburner to reduce the catalytic converter light-off time to below 20 s. Sharp et al. [39] studied the influence of the mini-burner on exhaust gas temperature and fuel consumption. The results showed that SCR reached 200 °C at around 200 s, 400 s faster than baseline, but the fuel consumption increased by 2.6%. They used the burner for SCR and significantly reduced the light-off time. Kurien et al. [40] reported that the DPF with a 400 W microwave achieved a soot light-off temperature of 873 K at a regeneration time of 150 s.
Various methods of diesel engine after-treatment thermal management are listed in this paper. The feature of the study is a focus on non-engine-based after-treatment thermal management technologies, describing thermal management control strategies in detail and summarizing the effects of the various thermal management strategies on exhaust temperature, emission concentrations, and fuel consumption. Some catalysts that help with thermal management are also mentioned. A summary of the relevant literature as well as an identification of deficiencies and challenges are both presented in this paper.

2. Composition and Work Principle of Diesel Engine after-Treatment Systems

As shown in Figure 1, a typical diesel after-treatment system consists of a DOC, DPF, SCR, and ASC (ammonia slip catalyst) [41].

2.1. DOC

The DOC is the first after-treatment device through which exhaust gas flows [42]. The working principle of the DOC is to oxidize the CO and HC in the exhaust gas [43,44]. The DOC also oxidizes NO to NO2 [45], which increases the ratio of NO2 in NOx. A high ratio of NO2 assists DPF regeneration [46] and improves NOx conversion in SCR [47]. The heat released by the oxidation reaction in the DOC increases the downstream temperature, which assists the DPF light-off [48]. The DOC consists of the shell, the shock-absorbing layer, the substrate, and the catalyst coating [49] (Figure 2a). The substrate of the DOC is a flow-through monolith with a catalyst coating [50] (Figure 2b).
The active components in the catalyst reduce the reaction activation energy and promote the oxidation reactions of CO, HC, and NO [51]. CO, HxCy (=HC) and NO enter the DOC, are adsorbed onto the catalyst coating, and react with CO2, NO2, and H2O as follows (reactions (R1)–(R3)) [52]:
C O + 1 2 O 2 C O 2
N O + 1 2 O 2 N O 2
H x C y + ( x 4 + y ) O 2 y C O 2 + x 2 H 2 O

2.2. DPF

The exhaust gas flows through the wall of the DPF, and then the PM is filtered, which is the working principle of the DPF [53]. The substrate of the wall-flow DPF has a wall-flow monolith, in that the ends of the channels in it are alternately plugged [50] (Figure 3a). The accumulation of PM leads to a back-pressure increase, which leads to a deterioration of the engine performance [54]. The process of removing PM is DPF regeneration. DPF regeneration is classified as active regeneration and passive regeneration [55,56]. Efficient oxidation of PM requires a certain high temperature [57]. Active regeneration is a method that actively injects energy to increase the DPF temperature to the soot light-off temperature. For example, engine-based heating measures [58,59] or microwave-regeneration-based [60,61] active regeneration include post injection in the DOC [62,63] and an extra heating device [64,65]. Passive regeneration includes NO2 oxidation-assisted regeneration [66,67], catalytic diesel particulate filters, (CDPFs) (Figure 3b) [68,69], etc., but requires no energy input. A lot of heat is released during the regeneration (Figure 3c) [70,71], which causes the DPF to age and deteriorates the efficiency of SCR at the downstream side of the DPF [72,73]. Therefore, thermal management is important during regeneration.

2.3. SCR and ASC

The role of SCR is to reduce NOx to nitrogen (N2) [27]. The exhaust gas contacts the reducing agent in the SCR, and the reducing agent catalytically reduces NOx to N2 (as shown in Figure 4). For reasons of safety and toxicity, an aqueous solution of urea (NH2CONH2) is the preferred selective reducing agent for SCR [76]. NH3 is produced via the hydrolysis of urea injected (reaction (R4)) by the urea solution injector upstream of the SCR [76]. The ASC is installed at the downstream side of the SCR and is used to react the unreacted NH3 [77,78]. The main reactions in SCR and ASC are as follows (reactions (R5)–(R13)) [79,80].
NH 2 CONH 2 + H 2 O 2 NH 3 + CO 2
4 N O + 4 N H 3 + O 2 4 N 2 + 6 H 2 O
2 N O 2 + 4 N H 3 + O 2 3 N 2 + 6 H 2 O
4 N H 3 + 2 N O + 2 N O 2 4 N 2 + 6 H 2 O
6 N O + 4 N H 3 5 N 2 + 6 H 2 O
6 N O 2 + 8 N H 3 7 N 2 + 12 H 2 O
2 N H 3 + 1.5 O 2 N 2 + H 2 O
2 N H 3 + 2 O 2 N 2 O + H 2 O
N H 3 + 1.5 O 2 N O + 1.5 H 2 O
N H 3 + 2 O 2 N O 2 + 1.5 H 2 O

3. After-Treatment Thermal Management Technology

3.1. Exhaust Gas Thermal Management

The high initial exhaust gas temperature can accelerate the after-treatment system to ignite without other heating devices. Taking the DOC as an example, achieving an increase in the initial exhaust temperature under low exhaust temperature conditions helps the DOC to start oxidizing CO and HC earlier, and the exothermic oxidation reaction further increases the temperature. As the engine load gradually increases, the exhaust gas temperature also increases further. Thus, the DOC ignites earlier. The effects of engine control technologies such as variable valve timing technology (VVT) [82,83], injection technology [84], variable geometry turbo technology (VGT) [85], etc. on the exhaust temperature, BSFC, and BTE are listed in Table 1. EEVO, intake throttle, exhaust throttle, and post injection technology can raise the exhaust temperature and reduce the thermal efficiency. VGT and IVC may be the ways to improve thermal efficiency and exhaust gas temperature and effectively solve the trade-off problem between thermal efficiency and exhaust gas temperature. Injection timing slightly affects the exhaust temperature but reduces the BSFC.
VVT is a technology that can adjust the open and close timing of the intake and exhaust valves based on engine operating conditions to run the engine in an optimized state [86,87]. Employing VVT also increases the exhaust gas temperature. Robert et al. [82] used a model to predict the effect of early exhaust valve opening (EEVO) on the exhaust gas temperature under a low load condition. The model predicted an approximate 30 °C–100 °C increase in turbine out temperature and a 5% reduction in BTE when the EVO was 90° before nominal. Basaran et al. [83] investigated the effect of early intake valve closing (EIVC) and late intake valve closing (LIVC) on exhaust temperatures. The result showed that both EIVC and LIVC increase the exhaust temperature. The exhaust temperature was higher than 250 °C when the valve timing was earlier than −25 °CA ATDC or later than 115 °CA ATDC. Fuel injection timing affects the heat release rate, and thus, it is related to exhaust temperature and engine thermal efficiency. Bai et al. [84] studied the impacts of the injection advance angle on exhaust temperature and fuel consumption through experiments. When the injection advance angle was postponed from −4 °CA to 7 °CA, the exhaust temperature increased from 225 °C to 253 °C, and the fuel consumption increased by 17 g/(kWh) at a condition of 1300 r/min and 300 N·m. In general, the main injection timing has little effect on exhaust temperature and fuel consumption. The results of the above papers were obtained under steady-state conditions and present us with the thermal management effect of VVT technology, but further transient experiments are needed for practical application.
To find ways to improve thermal efficiency and increase exhaust temperature, Wu et al. [85] studied the influence of intake throttle, exhaust throttle, post injection, and VGT on exhaust temperature and BTE. The exhaust gas temperature increased by 40 °C and 60 °C, and the BTE decreased by 1% and 2%, respectively, when the opening of the intake throttle valve and the exhaust throttle valve were sufficiently reduced (Figure 5a,b). The parameters of the post injection quantity and timing had significant effects on the exhaust temperature and thermal efficiency. When the timing was retarded from 30 °CA ATDC to 70 °CA ATDC, the exhaust temperature increased by 50 °C, and the BTE decreased by about 1% at a constant post injection quantity of 9 mg. When the post injection quantity increased from 3 mg to 15 mg, exhaust temperature increased by 50 °C, but the BTE decreased by 3% (Figure 5c,d). As shown in Figure 5e,f, the exhaust temperature increased by about 50 °C and the BTE increased by about 7% with the reduction in the VGT working capacity.

3.2. DOC Thermal Management

The conversion efficiency of the DOC is closely related to temperature because the catalytic activity of catalysts is positively correlated with temperature. Take the common Pt precious metal catalyst as an example. CO conversion reached 100% at a temperature of around 180 °C, while HC conversion reached 40% at a temperature of 270 °C [88]. Ho et al. [89] presented that CO conversion and C3H6 conversion reached 100% at a temperature of around 300 °C, but when the temperature was 150 °C, the CO conversion and C3H6 conversion were 20% and 0%, respectively. A lot of CO and HC will be released into the atmosphere without being treated at low temperatures. Therefore, rapid DOC light-off is crucial [90,91]. High-temperature exhaust gas has a significant effect on DOC light-off. As shown in Figure 6a, Grag et al. [92] increased the exhaust temperature from 195 °C to 255 °C by adjusting the intake valve closing timing. Chuan et al. [93] increased the exhaust temperature from 190 °C to 310 °C, which was higher than the DOC light-off temperature, via cylinder deactivation (CDA) at idle operation. Neely et al. [94] applied intake throttle technology to raise the turbocharger outlet temperature to 230 °C at the condition of 1200 rpm, 1.7 bar BMEP, and 25 °C coolant temperature. Francisco et al. [95] explored exhaust pipe thermal insulation to increase the DOC inlet temperature and accelerate DOC light-off. The adiabatic exhaust port (EP), exhaust manifold (EM), internal surface of the turbine volute (TI), and turbine external housing were simulated under the WTLC. The result is shown in Figure 6b. DOC light-off took 800 s without any insulation, while DOC light-off took only about 200 s when all parts were completely insulated. The exhaust manifold was the part that lost the most heat. The rapid DOC light-off also benefits from external heat sources such as burners and EHCs.
Zhao et al. [96] added a burner upstream of the DOC. The simulation calculation showed that it took 65 s for the 1.54 kg DOC substrate to reach a temperature of 300 °C at the condition of 79.2 kg/h exhaust flow rate and 25 °C initial temperature. In practical situations, the actual light-off time will increase due to the interference of factors such as heat transfer loss. Paolo et al. [97] employed an EHC to heat the DOC. The DOC employing EHC took about 220 s to reach the peak temperature in driving cycle conditions, and the temperature of the DOC could be maintained at more than 50% of the peak temperature through the on-off control of the electric heater.

3.3. DPF Thermal Management

The soot oxidation light-off temperature of the DPF is higher than the DOC light-off temperature [98,99]. Under the normal operation of diesel vehicles, the exhaust temperature (200–400 °C) cannot meet the continuous oxidation of O2/NO2 to the accumulated PM [100]. Even if the catalyst is applied, high temperatures are required. When the Printex-U load of 3.5 g/L was regenerated at 400 °C, the filtration efficiency of particles showed a value of 86.4% [101]. Tan et al. [102] increased the DOC outlet temperature to 550 °C via a late post injection technology, but raising the DPF inlet temperature in that way was accompanied by worsening fuel consumption [103]. The diesel vaporizer system was to introduce diesel into the DOC to intensify the oxidation heat release of the DOC [104], which enabled the DOC outlet temperature to reach 650 °C rapidly, with a fuel consumption reduction of 50%. Utilizing the HC tailpipe injection could reduce extra fuel consumption. The injection amount is calculated according to the target temperature via Equation (1). This formula is idealized, and its premise is that all fuel is fully oxidized by the DOC to heat the exhaust gas [105]:
m ˙ f u e l = m ˙ e x h a u s t × Δ T e x h a u s t × c p H
where m ˙ f u e l is the mass flow rate of fuel injection, kg/h; m ˙ e x h a u s t is the mass flow rate of the exhaust gas, kg/h; cp is the specific heat of the exhaust gas, kJ/kg/K; Δ T e x h a u s t is the difference between the target exhaust temperature and the incoming exhaust temperature, K; and H is the lower heating value of the diesel fuel, kJ/kg.
Microwaves rapidly heat the DPF to the soot light-off temperature. Kurien et al. [106] utilized microwaves to raise the maximum temperature of the substrate to 800 K and the average temperature to more than 600 K in a regeneration time of 180 s. In [40], the magnetron port power was considered. The DPF reached a soot oxidation temperature of 873 K in a regeneration time of 150 s with a power of 400 W. To minimize microwave energy consumption during DPF regeneration, E et al. [107] developed a microwave energy consumption optimization model and obtained an optimized microwave regeneration power and regeneration heating time. The microwave energy consumption of the four cases was reduced by 5.65%, 5.7%, 10.64%, and 14.64%, respectively. E et al. [108,109] optimized the rotary microwave regeneration performance and obtained a series of optimized regeneration parameter ranges. The optimal parameter ranges of the exhaust temperature, oxygen content, soot mass fraction, and microwave power were 600–750 K, 0.11–1.15, 0.06–0.08, and 800–1200 W, respectively.
Zhao et al. [110] proposed that the field synergy angle could be an index to optimize the temperature distribution of the DPF. Deng et al. [111] concluded that 20–30 g/s was the optimal exhaust mass flow range based on an analysis of the synergy between the vector field and the temperature gradient. Furthermore, wall melting and thermal stress damage could be avoided when the PM load was less than 5 g/L. As shown in Equation (2), the concept of a temperature uniformity coefficient was proposed [112]. The temperature uniformity coefficient describes the temperature distribution of the DPF more accurately. They found that an inlet velocity of 36 m/s and an inlet pressure of 0.08 Mpa were the optimal parameter values based on the formula.
R T U = 1 n j = 1 n T j T ¯ T ¯ 2
where T j is the temperature of a position in the wall-flow filter, K; T ¯ is the wall-flow filter’s average temperature under a certain condition, K; and R T U is the temperature uniformity coefficient.
Drop to idle (DTI) is a driving behavior in which the engine rapidly changes from a high-speed condition to an idle condition. The increase in oxygen content and the decrease in exhaust flow lead to an accumulation of heat in the DPF; thus, the temperature rises rapidly during DTI [113,114]. The peak temperature and temperature gradient are a concern. The substrate will crack and melt if the temperature gradient and the peak temperature are too high [115,116]. Wang et al. [117] increased the idle speed via EGR and intake throttling to reduce the oxygen concentration in the exhaust gas, which alleviated the intensity of the oxidation reaction. The presence of EGR and intake throttling reduced the peak temperature by 130 °C at an idle speed of 2200 rpm. Bai et al. [118] raised the idle speed from 700 rpm to 1100 rpm, which resulted in a decrease in the peak temperature from 820 °C to 632 °C and a reduction in the maximum temperature gradient from 30 °C/cm to 10 °C/cm. Tan et al. [119] investigated the effect of PM load, target regeneration temperature, and exhaust mass flow on DPF temperature distribution during DTI. The peak temperature and the maximum temperature gradient of the DPF increased by 17% and 48.6%, respectively, when the PM load was increased from 3.6 g/L to 5.6 h/L (Figure 7a). The increase in the target regeneration temperature from 575 °C to 625 °C was accompanied by a 10.5% increase in the peak temperature and a 15.9% increase in the maximum temperature gradient (Figure 7b). When the exhaust mass flow was increased from 40 g/s to 60 g/s, the peak temperature and the maximum temperature gradient were reduced by 7.75% and 48.17%, respectively (Figure 7c).

3.4. SCR Thermal Management

The catalyst in SCR requires a certain temperature range. An iron titanate catalyst showed good activity in a temperature window of 200–350 °C with the NOx conversion above 90% [120]. Nicolo et al. [121] adopted a strategy of VGT and fuel injection timing to advance SCR light-off by 600 s under the cold NEDC for the Euro 6 emission regulations. The fuel consumption of SCR increased by 7.39%. Sung et al. [122] proposed a plasma burner to heat the SCR during cold start conditions (Figure 8a). The SCR surface reached the light-off temperature of 200 °C in only 25 s with the 250 W plasma burner heated. Culbertson et al. [123] studied the impacts of different heating powers on SCR light-off time. SCR reached 200 °C at around 130 s via a 30 kW EHC under the cold FTP, more than 8 min faster than the No EHC case. The catalysts in the SCR have a high conversion efficiency within a specific temperature window [124,125]. SCR will hydrothermally age if exposed to high temperatures for a long time [126,127]. Therefore, the peak temperature of the SCR also needs to be considered. It can be solved using a logic block that was adopted to control the open and close of the burner in [128]. The burner turned off when the maximum set temperature was reached and turned on when it fell below the minimum set temperature. As shown in Figure 8b, the exhaust temperature rose rapidly to 250 °C, and the SCR inlet temperature fluctuated between 200 °C and 250 °C. This indicates that the burner heated up faster and its temperature was relatively stable.
Jiang et al. [129] adopted a PCM to control the temperature of the SCR. After completing the preheating procedure in the European transient cycling (ETC) with a target temperature of 563 K, the fluctuation in the exhaust gas temperature was limited within 30 K. The NOx conversion efficiency was over 90%, and the total NOx emission was reduced by about 2/3 (Figure 8c).

4. After-Treatment Systems Efficiency Enhancement Approaches

4.1. Burner

The burners installed at the upstream side of the catalysts heat the exhaust gas directly, which can effectively reduce the light-off time of the DOC. Alexander et al. [130] employed a burner in a 2 L engine after-treatment system. The emission of HC improved significantly when the preheat time was 0.5 s. When the preheat time was extended to about 20 s, the catalytic converter reached the light-off temperature before the engine turned on. Thomas et al. [131] added a microburner to the engine model. The burner turned on at 4 s under the cold FTP and worked at a constant fuel rate of 0.256 g/s until the end of the cycle. As shown in Figure 9a, the DOC inlet temperature reached 250 °C at 100 s. The late start of the ammonia spray is a limitation.
Two burner control strategies were proposed in [132], as shown in Figure 9b,c. The control strategy represented by the red line was preheating for 5 min after the engine turned on. The DPF outlet temperature was 200 °C as the threshold temperature. (The burner turned off once the temperature was reached.) The control strategy represented by the green line was preheating for 3 min after the engine turned on, which adopted 300 °C as the threshold temperature once, and then reduced the threshold temperature to 200 °C. The DOC and SCR light-off times were less than 50 s and 100 s, respectively, but the DOC temperature could not be maintained above 250 °C all the time. McCarthy et al. [133] utilized an identical two-tier control strategy for SCR. The SCR inlet temperature was maintained at more than 200 °C, and the emission of NOx deceased by 93.5%, but the CO2 emission increased by 9%.

4.2. EHC

EHC is an effective way to improve the efficiency of after-treatment systems. Augusto et al. [134] indicated that nonuniform distribution of the heat generated by the electrical heating device determined the formation of some hot spots inside the catalyst, which promoted the light-off of the reactions at the early cold start condition. Johannes et al. [135] adopted EHC in a hybrid vehicle, which significantly reduced NOx emission levels during urban and short-distance driving. Pfahl et al. [136] utilized a 1 kW EHC to warm up the DOC under the NEDC. An EHC deceased the DOC light-off time by 100 s, while the conversion rates of HC and CO increased by 20% and 60%, respectively. Pace et al. [137] reported that 60% less energy was required for the EHC to reach temperature levels similar to engine-based catalyst heating methods.
The EHC is a flexible device. Reasonable control strategies can optimize energy consumption, exhaust temperature, catalyst efficiency, and thermal damage to the catalyst. Gao et al. [138] presented two EHC control strategies and investigated their influence on energy consumption and emissions. As displayed in Figure 10a,b, strategy A meant that the EHC turned off when the engine stopped injecting fuel or the exhaust temperature was higher than the target temperature (Ttarget). Strategy B was that the EHC turned off only when the exhaust gas temperature was higher than the target temperature (Ttarget1) and when the engine stopped injecting fuel. A Ttarget2 less than or equal to Ttarget1 was set.
Strategy A significantly shortened the catalyst light-off time under the cold WLTC. The light-off times were 254 s and 256 s when the target temperature was set to 180 °C and 200 °C (A180 and A200), respectively. Compared with A180, A200 deteriorated the CO2 emission by about 18%, and reduced the CO, HC, and NOx emissions by about 48%, 35%, and 12%, respectively. Compared with the No EHC case, A200 decreased CO, HC, and NOx emissions by about 73%, 75%, and 62%, respectively, while the CO2 emissions increased by 7.64%. In strategy B, when Ttarget1 and Ttarget2 were both set to 200 °C (B200), the CO, HC, and NOx emissions were reduced by about 80%, 80%, and 66%, respectively, while the CO2 increased by 9.35% (as given in Figure 10c). In [139], a pulsating heating strategy with a pulse width of 30 s led to an approximate 70% and 24% reduction in the CO and HC emissions, respectively, under the NEDC. Compared with the typical heating strategy, the pulsating heating strategy increased the CO and HC conversion efficiency by 34% and 31%, respectively. NOX conversion was much lower than that of CO and HC due to the fact that SCR occurs at the end of the after-treatment system and hardly benefits from the heat of the EHC.
Before the engine is turned on, there is no airflow in the exhaust pipe; therefore, when the preheating strategy was adopted, the heat distribution in the after-treatment devices was uneven, and the downstream devices were insufficiently heated. To solve this problem, Bargman et al. [140] installed an air pump upstream of the after-treatment system and utilized the airflow to preheat the downstream after-treatment devices. The results showed that the emission of NOx was reduced by 51% in non-methane organic gas under the cold start condition. Hamedi et al. [139] proposed the method of combining EHC with post injection technology, which reduced the total emission of HC by 79% compared with employing the post injection technology individually. Kim et al. [141] combined EHC and HC injection. The 4.8 kW peak power was applied from the start-up, and then, an appropriate amount of HC injection was applied after 20 s when the EHC temperature reached 250 °C. SCR light-off time was within 100 s. Furthermore, the conversion efficiency of the SCR reached 90% during 100 s to 350 s during the cold FTP75. Matheaus et al. [142] studied the effects of EH combined with CDA on SCR emissions reduction and fuel consumption. Compared with CDA individually, EH (5 kW constant) combined with CDA decreased NOx emissions by 62.5%, and BSFC was increased by 5.7% under the cold FTP. Compared with EH alone, NOx emissions and BSFC decreased by 50% and 2%, respectively.
The coupling system of a thermoelectric generator and exhaust gas heater was investigated in [143]. Electric energy was generated by the temperature difference between the exhaust gas and cooling water to compensate for the energy consumption of the electric heater through the coupling system. Ximinis et al. [144] implemented a thermoelectric generator and EH coupling system in the after-treatment system of a diesel engine (Figure 11a). Employing a 5 kW EH powered by a thermoelectric generator alone, they were able to increase the SCR conversion efficiency by 55%.

4.3. Thermal Insulation

Thermal insulation improves catalyst performance by reducing exhaust heat loss during engine warm-up. Broatch et al. [145] simulated the effects of exhaust ports and exhaust manifolds under adiabatic conditions on engine efficiency and after-treatment systems. The exhaust gas temperature slightly increased, and the fuel consumption decreased by 0.5% under the WLTC. Rohil et al. [146] simulated a vacuum-insulated catalytic converter. CO and HC emissions decreased by 26% and 48%, respectively, at real-world driving conditions. Wang et al. [147] applied a layer of 6 mm insulation material to the exhaust pipe in a section between the turbine outlet and the DOC, which reduced NOx emission by 19.5% under the NRTC. Wang et al. [148] increased the in-cylinder temperature by 100–200 K via a thermal barrier coating, which indirectly increased the exhaust gas temperature. Luján et al. [149] investigated the effects of exhaust port insulation and turbocharger insulation on exhaust temperature and fuel consumption. Four cases of exhaust port insulation strategies are shown in Figure 11b. The inlet temperature followed a trend of 4 > 3 > 2 > 1, and the BSFC followed a trend of 1 > 2 ≈ 3 > 4. The thermal insulation strategy of the turbocharger affected insignificantly the inlet temperature of the after-treatment system and BSFC. Thermal insulation methods can improve exhaust temperatures, but they do not provide additional heat. Thus, thermal insulation methods cannot be used as a final solution.

4.4. PCMs and the Heat Recovery System

PCMs release or absorb a large amount of heat during phase change to heat or cool down [150,151]. PCMs can be used to recover waste heat and improve energy utilization. PCMs have been widely implemented in automobiles [152,153]. PCMs are implemented in the after-treatment system to recover heat under high load conditions and then release energy under low load conditions to improve catalyst performance.
Korin et al. [154] embedded a 3.8 kg PCM into the TWC. After the engine turned off, the TWC remained above the light-off temperature for 4 h, which benefited from the heat release of the PCM. If the engine turns on again within 4 h, the emission under cold start conditions will be improved, but the PCM will not work if the engine starts after 4 h. Gaiser et al. [155] adopted a PCM with a phase change temperature higher than the catalytic converter light-off temperature and installed a latent heat storage (LHS) device upstream of the catalytic converter to heat the exhaust gas using the fact that the temperature of the PCM in the LHS did not change when it melted. The catalyst inlet temperature reached 200 °C within 100 s and remained around 200 °C in the following 400 s under the cold start condition. Hamedi et al. [156] developed a thermal energy storage system (TES) based on a PCM to reduce cold start emissions (as shown in Figure 11c). Under the NEDC, the DOC equipped with TES reduced CO and HC emissions by 64% and 34%, respectively.
Jiang et al. [129] limited the temperature fluctuation of SCR to 30 K via PCM. Raznoshinskaia et al. [157] decreased the range of exhaust temperature vibrations by 73.1% with the ternary eutectic mixture of 7NaNO3/40NaNO2/53KNO3. PCMs are a potential way to stabilize the exhaust temperature. Dae et al. [158] developed an engine exhaust heat recovery system (EERS) equipped with secondary combustion. Exhaust gas temperatures increased from 200–350 °C to 350–550 °C due to the combustor, which was installed at the outlet of the exhaust manifold (Figure 11d). The EERS improved thermal efficiency up to 20–25% and decreased CO, NOx, and PM emissions by 80%, 35%, and 90%, respectively. Park et al. [159] adopted the heat storage system of a PCM for a 1.6 L diesel engine. The time to warm up the coolant to 95 °C was reduced by 40.5% under the NEDC, and fuel consumption was reduced by 2.71%. Gumus et al. [160] utilized PCMs to preheat the engine, which improved emissions during cold start. The HC and CO emissions deceased by 17.32% and 28.71%, respectively.
Figure 11. Structures of exhaust gas after-treatment devices and components in various studies. (a) Structure and energy flow of EGH-ATEG [144]. ① heating stage; ② recovery stage. (b) Representation of exhaust ports thermal insulation cases [149]. (c) PCM model geometry diagram [156]. (d) Schematic diagram of secondary combustor [158].
Figure 11. Structures of exhaust gas after-treatment devices and components in various studies. (a) Structure and energy flow of EGH-ATEG [144]. ① heating stage; ② recovery stage. (b) Representation of exhaust ports thermal insulation cases [149]. (c) PCM model geometry diagram [156]. (d) Schematic diagram of secondary combustor [158].
Energies 17 00584 g011
Table 2 is a summary of the reduction in exhaust emissions by the above after-treatment thermal management technologies.

4.5. VVT and Post Injection

Arnau et al. [161] investigated the effects of VVT on exhaust temperature, DOC light-off time, and fuel consumption. The combination of an advanced exhaust and a delayed intake obtained a 27 °C increase in DOC inlet temperature, 75 s reduction in DOC light-off time, and 6% deterioration in fuel consumption during the low-speed phase of the worldwide harmonized light vehicles test cycle. Wu et al. [85] combined thermal insulation, post injection, and VGT-RIVCT under cold WHTC to enable the SCR to reach 190 °C at 450 s, which could significantly reduce NOx emission. CDA is achieved by adjusting valve movement and stopping in-cylinder fuel injection. CDA is a technology to reduce fuel consumption [162,163]. The benefit is achieved in part-load operations when the BSFC is higher than in full-load operations [164]. CDA is also an effective method to increase the exhaust temperature [165,166]. Ramesh et al. [167] increased exhaust temperature by 60 °C and improved BTE up to 10% with a three-cylinder strategy at a condition of 800 rpm and 1.3 bar BMEP. A two-cylinder strategy increased the exhaust temperature by 120 °C and improved BTE up to 2%. Allen et al. [168] explored the performance of CDA to maintain warmth for the after-treatment system at an extended idle operation. The result showed that the turbine outlet temperature was maintained above 250 °C with a two-cylinder strategy.
Internal exhaust gas recirculation (IEGR) is achieved with both negative valve overlap (NVO) and reinduction [169]. Joshi et al. [170] confirmed that EEVO/NVO increased the exhaust temperature to more than 255 °C and decreased fuel consumption by 5.7%. Simultaneously, LEVO took the exhaust temperature to above 280 °C with no extra fuel consumption. Wang et al. [171] explored the effects of post injection timing on engine-out HC emission, exhaust temperature, and torque, as displayed in Figure 12a,b.
With the delay in the post injection timing, the exhaust temperature increased and then decreased. The later the post injection timing was, the less fuel participated in the combustion, which resulted in a deterioration in torque. The fuel consumption and the HC entering the exhaust pipe increased (Figure 12c), which intensified the reaction of the DOC and raised the DOC outlet temperature.
Huang et al. [172] developed a DPF temperature control strategy based on post injection. The control strategy calculated the quantity of post injection based on the target regeneration temperature and amended the quantity via feedback and feedforward compensation methods based on both the exhaust gas temperature and flow rate. As shown in Figure 13a,b, after the DPF inlet temperature reached the target regeneration temperature, its fluctuation was within 15 °C under different urban driving conditions, which proved the robustness of the control strategy.

4.6. Catalysts

Catalysts with high activity and thermal stability improved the efficiency of the after-treatment system and reduced the energy consumption of the thermal management. Pt-based catalysts are the most widely used catalysts in DOCs [173,174]. Kolli et al. [175] and Boubnov et al. [176] confirmed that Pt/Al2O3 had a high catalytic activity and a poor sulfur resistance. As shown in Figure 14a’, Liang et al. [177] loaded Pt on MnOx, which enhanced the catalytic activity of Pt. The conversions of CO, C3H6, and NOx are given in Figure 14b’–d’. Väliheikki et al. [178] and Gu et al. [179] adopted SiO2-ZrO2 and Ce-Zr-SO42- as supports to improve the sulfur resistance and stability of Pt-based catalysts.
The researchers reported that doping with other metals can enhance the performance of Pt-based catalysts. Liang et al. [180] added 2%wt tungsten trioxide (WO3) to Pt/SiO2-Al2O3, and the light-off temperature of HC and CO was reduced. Kim et al. [181] reported the relationship between the value of Pd/Pt and light-off temperature and the relationship between thermal stability and the value of Pd/Pt (Figure 15a). E et al. [16] indicated that the light-off temperature of the Pt-Pd catalyst was lowest when the Pd was approximately 70%. Huang et al. [182] doped the Pt/Ce-Zr-O catalyst with vanadium (V) (Figure 15b). The CO and HC light-off temperatures of 1Pt-1V/Ce-Zr-O were approximately 195 °C and 190 °C, respectively. Furthermore, the light-off temperature of HC was almost constant, and the light-off temperature of CO increased by 10 °C in an SO2 atmosphere for 70 h.
The researchers developed alloy catalysts that were better than conventional catalysts. Dong et al. [183] investigated a Pt (1.0 wt%)-Pd (0.5 wt%) alloy catalyst loaded on SiO2. The activity of the Pt-Pd alloy catalyst was higher than the conventional Pt-Pd catalyst. Franken et al. [184] confirmed that the Mn-Pt alloy catalyst is a sulfur-tolerant catalyst. The conversion of NOx deteriorated by 6% under the 300 ppm SO2 for 70 h, while the pure Pt/Al2O3 catalyst deactivated fully within the first 30 min. Ceria (CeO2) catalysts, which are rare-earth metal catalysts, are widely applied in automotive exhaust after-treatment systems [185,186]. Bueno-López et al. [187] reported that the temperature at which CeO2 reached 50% soot conversion rate was 525 °C. Ce-based catalysts can be doped with rare-earth metals [188,189], noble metals [190,191], transition metals [192,193], alkali metals [194,195], and alkaline earth metals [196]. Yang et al. [197] added Mn to improve the activity of soot oxidation and the thermal stability of Ce-based catalysts. The T10 of the 40% Mn-Ce catalyst was 475 °C, and the T90 was 565 °C. Stability of the 40% Mn-Ce decreased in the third cycle of the thermo-gravimetric analyzer experiment. Atribak et al. [198] revealed that doping zirconium (Zr) improved the thermal stability of Ce-based catalysts. Yang et al. [199] added lanthanum (La) to the CeO2-ZrO2 catalyst and tested the catalytic activity of soluble organics (SOs). The test result indicated that the catalyst was more active and had a slower aging rate after doping with La. Wu et al. [200] studied the catalytic activity of CeZrK/rGo with different doping ratios. The T50 of Ce5Zr1K1/rGO, Ce5Zr2K2/rGO, and Ce5Zr3K3/rGO for soot oxidation were 352 °C, 339 °C, and 358 °C, respectively (Figure 16).
Sarli et al. [201] added Ag to CeO2, which greatly enhanced the catalytic activity. The T10 of 12% Ag/CeO2 for soot oxidation was 240 °C, and the temperature at maximum conversion was 435 °C. At present, various transition metal catalysts have been investigated. Cheng et al. [202] investigated a series of V2O5/TiO2 catalysts to improve the catalytic performance of NH3-SCR. The results showed that the NO conversion efficiency was above 80% when the 5% V2O5/TiO2 supported on aluminate was at temperatures between 325 °C and 400 °C. Ding et al. [203] prepared the MFe2O4 (M = Cu, Mn, and Zr) (Figure 17a). As shown in Figure 17b,c, MnFe2O4 had the highest activity, and ZnFe2O4 had the highest N2 selectivity, at low temperatures. CuFe2O4 was a balanced catalyst, but its efficient reaction temperature range is narrow. In addition, the catalytic activity of CuFe2O4 decreased by 8% in SO2 atmosphere for about 2 h. Zhang et al. [204] reviewed Mn-based catalysts for NH3-SCR and summarized the advantages and disadvantages of MnOx. MnOx had a high low-temperature activity and played a decisive role in the SCR reaction but had poor thermal stability and a narrow reaction temperature window. It also had an insufficient reaction in the eutrophic environment and weak sulfur resistance.
To reduce the cost and enhance the activity and stability of the catalysts, Tang et al. [205] developed a LaKCoO3/γ-Al2O3/cordierite perovskite catalyst. The results showed the high activity and thermal stability of the LaKCoO3/γ-Al2O3/cordierite. The T10, T50, and T90 of the LaKCoO3/γ-Al2O3/cordierite catalyst for soot oxidation were 186.3 °C, 314.6 °C, and 390.0 °C, respectively.

5. Outlook for Future Research

5.1. Shortcomings of Current Technologies

The engine-based after-treatment management methods increase the exhaust temperature, and the high-temperature flowing exhaust gas heats the after-treatment devices, which can shorten the light-off time of the after-treatment system. These methods do not require additional devices and are relatively simple to implement. However, changing the engine parameters leads to fuel economy penalties. Techniques such as intake and exhaust throttling [85] or EVO timing technology [82] lead to worse combustion and a deterioration in BTE. CDA and IVC timing can increase exhaust temperature and improve fuel consumption [161,167]. The low-flow-rate strategies reduce the exhaust flow rate, and the exhaust gas has a longer contact time with the exhaust pipe, which leads to more heat dissipation to the atmosphere [83,168]. Fuel strategies such as post injection and hydrocarbon injection directly convert the chemical energy of fuel to thermal energy to increase the temperature of the after-treatment system [171,172]. Energy conversion efficiency is a problem that needs to be considered, and these fuel strategies lead to higher fuel consumption [85,171]. Post injection can also lead to oil dilution, affecting the life of the engine [102].
Technologies such as burners, EHCs, and microwave heating have proven to be effective thermal management measures that are flexible and easy to control, but the control strategy cannot coordinate the entire after-treatment system [131,138]. For example, when the burner and EHC are installed upstream of the after-treatment system, the heat produced has a relatively weak effect on the SCR downstream of the after-treatment system. The conversion rate of NOx is lower compared with HC and CO [131,138]. The DPF outlet temperature can be considered the SCR threshold temperature while ignoring the DOC [131,133].
The heat recovery system based on the PCM for the after-treatment system thermal management can solve the trade-off problem of exhaust gas temperature and carbon dioxide emission, but the PCMs are effective only when the engine is turned on again before the PCM heat is exhausted [156]. PCMs are a potential method to stabilize exhaust temperatures [157]. The thermoelectric generator recovers a part of the electric energy through the exhaust heat and compensates for the EHC. The thermoelectric generator increases the complexity of the after-treatment system, which can increase the back pressure [143,144].
Simulation research under adiabatic conditions has confirmed that the thermal insulation methods are able to shorten the light-off time of the after-treatment system, but the currently developed thermal insulation methods still have a certain gap in the adiabatic case. The developed catalysts have high activity at low temperatures [174,183]. The reaction temperature window is narrow for SCR [203,204]. The anti-deterioration performance is still a challenge (anti-sulfur, phosphorus, etc.) [49,204].

5.2. Outlook for Future Technologies

As described in the previous section, there are limitations in the separate technical methods, and multiple technologies need to be combined to improve the efficiency of after-treatment thermal management technology. Future technologies can be further explored from the following aspects:
(1)
To optimize CO2 emissions and exhaust temperatures, control strategies for the EHC and post injection coupled methods are investigated [137].
(2)
The active and passive thermal management technologies are combined [85,156].
(3)
Further control strategies for EHC [138,139], burners [132,133], and late post injection [168], based on the entire after-treatment system, are applied.
(4)
Materials are used with lower thermal conductivity and different insulation methods to approach adiabatic conditions [145,149] for better PCM development [156,157].
(5)
The inexpensive catalysts’ improvement is developed widely to explore catalysts with excellent degradation resistance [204,205].

6. Conclusions

Although combustion technology [206,207] and alternative fuels [208,209] are constantly improving, increasingly stringent emission regulations promote the development of advanced technologies in the after-treatment systems of internal combustion engines [210,211]. After-treatment systems still have the shortcoming that they require strict temperature conditions to efficiently convert pollutants [212,213]. At too low or too high a temperature, the after-treatment devices are at a low conversion efficiency level [214,215]. This thermal heat can be converted into electrical energy, as shown in the latest research [216,217]. The investigation of diesel after-treatment thermal management is summarized. After-treatment thermal management can improve the efficiency of after-treatment devices and reduce emissions, but the trade-off problem between thermal efficiency and exhaust gas temperature is still a challenge. The technical advantages and application potential of after-treatment thermal management are valuable to carry out in-depth research. The main conclusions of this study are as follows.
(1)
SCR burners can decrease NOx emissions by 93.5%. EHC can decrease CO, HC, and NOx emissions by 80%, 80%, and 66%, respectively. PCMs can control the temperature of SCR, resulting in a 2/3 reduction in NOx emissions.
(2)
Thermal insulation decreases the heat loss of the exhaust gas, which can reduce the after-treatment light-off time. DOC light-off time was reduced by 75% under adiabatic conditions. Microwave is an effective method for DPF regeneration. A 400 W microwave can heat the DPF to the soot oxidation temperature of 873 K at a regeneration time of 150 s.
(3)
Catalysts can enhance the efficiency of the after-treatment system and reduce the thermal management energy consumption. Pt-Pd application in the catalyst can decrease the CO light-off temperature to 113 °C. The LaKCoO3/γ-Al2O3/cordierite catalyst with a T50 of 314.6 °C for soot oxidation can reduce the regeneration target temperature.
(4)
The future research trends focus on integration of engine-based and non-engine-based thermal management methods, control strategies of EHCs, insulation methods with low thermal conductivity, catalysts with excellent degradation resistance, and the implementation of these thermal management methods under transient operating conditions.

Funding

This work is supported by the National Natural Science Foundation of China (Grant No. 51976016), the Young Scientists Fund of the National Natural Science Foundation of China (Grant No. 52106151), and the Natural Science Foundation of Hunan Province, China (Grant No. 2020JJ4616).

Conflicts of Interest

Authors Tao Ling, Xuejun Peng, Zhilai Su were employed by the company China Railway Wuju Group First Engineering Co., Ltd. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Nomenclature

Compounds
Al2O3Alumina
COCarbon monoxide
CO2Carbon dioxide
CeO2Cerium dioxide
HCHydrocarbon
H2OWater
MnOxManganese oxides
N2Nitrogen
NOxNitrogen oxides
NO2Nitrogen dioxide
NONitric oxide
N2ONitrous oxide
NH2CONH2Urea
NH3Ammonia gas
O2Oxygen
PMParticulate matter
SOsSoluble organics
SO42−Sulfate
SiO2Silicon dioxide
TiO2Titanium oxide
V2O5Vanadium oxide
WO3Tungsten oxide
ZrO2Zirconium dioxide
Abbreviations
ASCAmmonia slip catalyst
ATDCAfter top dead center
ATEGAutomotive thermoelectric generator
BMEPBrake mean effective pressure
BSFCBrake-specific fuel consumption
BTDCBefore top dead center
BTEBrake thermal efficiency
CACrank angle
CDACylinder deactivation
CFDComputational fluid dynamics
CDPFCatalytic diesel particulate filter
DOCDiesel oxidation catalyst
DPFDiesel particulate filter
DTIDrop to idle
EEHRSEngine exhaust heat recovery system
EEVOEarly exhaust valve opening
EGRExhaust gas recirculation
EGTExhaust gas temperature
EHCElectrically heated catalyst
EHElectric heating
EIVCEarly intake valve closing
EMExhaust manifold
EPExhaust port
ETCEuropean transient cycling
EVOExhaust valve opening
FTPFederal test procedure
FTP75Environmental Protection Agency Federal Test Procedure
IEGRInternal exhaust gas recirculation
IVCIntake valve closing
LEVOLate exhaust valve opening
LHSLatent heat storage
LIVCLate intake valve closing
LLCLow load cycle
NEDCNew European driving cycle
NRTCNon-road transient cycle
NVONegative valve overlap
PCMPhase-change material
RIVCTRetarded intake valve closing timing technology
RDPFRotary diesel particulate filter
SCRSelective catalytic reduction
SEMScanning electron microscopy
TEMTransmission electron microscopy
TESSThermal energy storage system
TIInternal surface of the turbine volute
TWCThree-way catalyst
VGTVariable geometry turbine
VVTVariable valve timing
WHTCWorld harmonized transient cycle
WLTCWorld light vehicle test cycle
Symbols
cpSpecific heat of the exhaust gas, kJ/kg/K
HLower heating value of the diesel fuel, kJ/kg
m ˙ exhaustMass flow rate of the exhaust gas, kg/h
RTUTemperature uniformity coefficient
ΔTexhaustDifference between target exhaust temperature and incoming exhaust temperature, K
TjTemperature of a position in the wall-flow filter, K
T ¯ The wall-flow filter’s average temperature under a certain condition, K

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Figure 1. Architecture of diesel engine exhaust after-treatment system.
Figure 1. Architecture of diesel engine exhaust after-treatment system.
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Figure 2. Structure diagram of catalyst carrier. (a) Schematic diagram of DOC structure [49]. (b) The structures of a flow-through monolith and a wall-flow monolith [50].
Figure 2. Structure diagram of catalyst carrier. (a) Schematic diagram of DOC structure [49]. (b) The structures of a flow-through monolith and a wall-flow monolith [50].
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Figure 3. Schematic of the DPF. (a) Side view of adjacent channels [74]. (b) Methods for catalytic coatings on the DPF [75]. (c) Temperature contour of soot combustion reaction [71].
Figure 3. Schematic of the DPF. (a) Side view of adjacent channels [74]. (b) Methods for catalytic coatings on the DPF [75]. (c) Temperature contour of soot combustion reaction [71].
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Figure 4. Principle illustration of urea-based SCR diesel engine after-treatment system [81].
Figure 4. Principle illustration of urea-based SCR diesel engine after-treatment system [81].
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Figure 5. Effects of different thermal management techniques on exhaust gas temperature and BTE [85]. (a) Relationship between throttle opening and exhaust gas temperature. (b) Relationship between throttle opening and BTE. (c) Effect of post injection on exhaust gas temperature. (d) Effect of post injection on BTE. (e) Effect of VGT on exhaust gas temperature. (f) Effect of VGT on BTE.
Figure 5. Effects of different thermal management techniques on exhaust gas temperature and BTE [85]. (a) Relationship between throttle opening and exhaust gas temperature. (b) Relationship between throttle opening and BTE. (c) Effect of post injection on exhaust gas temperature. (d) Effect of post injection on BTE. (e) Effect of VGT on exhaust gas temperature. (f) Effect of VGT on BTE.
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Figure 6. Data of exhaust temperature and DOC light-off time. (a) Exhaust gas temperatures along EIVC and LIVC sweeps at 1200 RPM, 2.5 bar BMEP [92]. (b) Time to reach the DOC light-off temperature [95].
Figure 6. Data of exhaust temperature and DOC light-off time. (a) Exhaust gas temperatures along EIVC and LIVC sweeps at 1200 RPM, 2.5 bar BMEP [92]. (b) Time to reach the DOC light-off temperature [95].
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Figure 7. Peak temperature and maximum temperature gradient [119]. (a) The peak temperature and maximum temperature gradient at different PM loads. (b) The peak temperature and maximum temperature gradient at different target regeneration temperatures. (c) The peak temperature and maximum temperature gradient at different mass flows.
Figure 7. Peak temperature and maximum temperature gradient [119]. (a) The peak temperature and maximum temperature gradient at different PM loads. (b) The peak temperature and maximum temperature gradient at different target regeneration temperatures. (c) The peak temperature and maximum temperature gradient at different mass flows.
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Figure 8. Figures and data of SCR thermal management. (a) Comparison of times to heat SCR mid-bed to 200 °C [122]. (b) SCR inlet temperature data [128]. (c) The total quantity of NOx elimination with an SCR system only and with an SCR system assisted by a temperature control system [129].
Figure 8. Figures and data of SCR thermal management. (a) Comparison of times to heat SCR mid-bed to 200 °C [122]. (b) SCR inlet temperature data [128]. (c) The total quantity of NOx elimination with an SCR system only and with an SCR system assisted by a temperature control system [129].
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Figure 9. Exhaust gas temperature during preheating and the cold-start FTP cycle. (a) Exhaust gas temperatures at various locations within an after-treatment system that includes an in-exhaust burner [131]. (b) DOC-in temperature during preheating and the cold-start FTP cycle [132]. (c) DPF-out temperature during preheating and the cold-start FTP cycle [132].
Figure 9. Exhaust gas temperature during preheating and the cold-start FTP cycle. (a) Exhaust gas temperatures at various locations within an after-treatment system that includes an in-exhaust burner [131]. (b) DOC-in temperature during preheating and the cold-start FTP cycle [132]. (c) DPF-out temperature during preheating and the cold-start FTP cycle [132].
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Figure 10. Two different EHC control strategies and a graph of emission data [138]. (a) Control strategy A. (b) Control strategy B. (c) Impact of control strategies on emissions.
Figure 10. Two different EHC control strategies and a graph of emission data [138]. (a) Control strategy A. (b) Control strategy B. (c) Impact of control strategies on emissions.
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Figure 12. Effects of post injection on torque and HC [171]. (a) Effects of post injection on EGT at different loads. (b) Effects of post injection on engine brake torque at different loads. (c) Effects of post injection on HC at different loads.
Figure 12. Effects of post injection on torque and HC [171]. (a) Effects of post injection on EGT at different loads. (b) Effects of post injection on engine brake torque at different loads. (c) Effects of post injection on HC at different loads.
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Figure 13. Test results of different conditions [172]. (a) Test results under urban driving conditions. (b) Test results under aggressive suburban driving conditions.
Figure 13. Test results of different conditions [172]. (a) Test results under urban driving conditions. (b) Test results under aggressive suburban driving conditions.
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Figure 14. Conversion of all catalysts (Rx, “x” represents the reaction temperature of manganese oxide reduction) [177]. (a’) TEM images of catalyst: (a) R200, (b) R250, (c) 300, and the corresponding particle size distribution is inserted as a histogram; (d) HRTEM image of R250. (b’) CO conversion of all catalysts. (c’) C3H6 conversion of all catalysts. (d’) NO conversion of all catalysts.
Figure 14. Conversion of all catalysts (Rx, “x” represents the reaction temperature of manganese oxide reduction) [177]. (a’) TEM images of catalyst: (a) R200, (b) R250, (c) 300, and the corresponding particle size distribution is inserted as a histogram; (d) HRTEM image of R250. (b’) CO conversion of all catalysts. (c’) C3H6 conversion of all catalysts. (d’) NO conversion of all catalysts.
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Figure 15. Catalytic activity or stability of each series of catalysts. (a) Pt to Pd ratio effect on Pt-based diesel oxidation catalysts [181]. (b) Catalytic activities of CO on the Pt-Pd alloy catalyst and the conventional Pt-Pd catalyst [16].
Figure 15. Catalytic activity or stability of each series of catalysts. (a) Pt to Pd ratio effect on Pt-based diesel oxidation catalysts [181]. (b) Catalytic activities of CO on the Pt-Pd alloy catalyst and the conventional Pt-Pd catalyst [16].
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Figure 16. SEM and TEM images of CeZrK/rGO catalysts ((a,c,e) are SEM images. (b,d,f) are TEM images.) [200].
Figure 16. SEM and TEM images of CeZrK/rGO catalysts ((a,c,e) are SEM images. (b,d,f) are TEM images.) [200].
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Figure 17. Data of MFe2O4 (M = Cu, Mn, and Zn) [200]. (a) SEM of CuFe2O4 (A), MnFe2O4 (B), and ZnFe2O4 (C); HRTEM of CuFe2O4 (DF), MnFe2O4 (GI), and ZnFe2O4 (JL) [203]. (b) NOg conversion vs. temperature (GHSV = 30,000 h−1). (c) N2 selectivity vs. temperature (GHSV = 30,000 h−1).
Figure 17. Data of MFe2O4 (M = Cu, Mn, and Zn) [200]. (a) SEM of CuFe2O4 (A), MnFe2O4 (B), and ZnFe2O4 (C); HRTEM of CuFe2O4 (DF), MnFe2O4 (GI), and ZnFe2O4 (JL) [203]. (b) NOg conversion vs. temperature (GHSV = 30,000 h−1). (c) N2 selectivity vs. temperature (GHSV = 30,000 h−1).
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Table 1. Increase or decrease in exhaust temperature, BTE, and BSFC via different thermal management methods.
Table 1. Increase or decrease in exhaust temperature, BTE, and BSFC via different thermal management methods.
Thermal Management MethodsTest ConditionsIncrease in Exhaust TemperatureEffect on BTE or BSFC
BTEBSFC
EEVO [82]Low-load90 °C↓5%N.A.
IVC [83]1200 rpm, 2.5 bar65 °CN.A.↑9.3%
Injection timing [84]1100 rpm, 100 N·m28 °CN.A.↓17 g/(kW·h)
Intake throttle [85]1300 rpm, 0.4 Mpa38 °C↓0.75%N.A.
Exhaust throttle [85]1300 rpm, 0.4 Mpa60 °C↓1.95%N.A.
Post injection technology [85]1300 rpm, 0.4 Mpa57 °C↓3%N.A.
VGT [85]1300 rpm, 0.4 Mpa50 °C↑7%N.A.
Table 2. Performance improvement of exhaust after-treatment systems by different technologies.
Table 2. Performance improvement of exhaust after-treatment systems by different technologies.
TechnologiesTest ConditionsEffect on Pollutants in Exhaust Gas
HCCOPMNOxCO2
Burner [131]LLCN.A.N.A.N.A.↓93.5%↑9%
EHC [138]Cold WLTC↓80%↓80%N.A.↓66%↑9.35%
EHC + CDA [142]Cold FTP compared with CDAN.A.N.A.N.A.↓12.5%↓0.7%
Insulation methods [146]Real-world driving↓48%↓26%N.A.N.A.N.A.
PCM-based TES [156]NEDC↓41.2%↓91.7%N.A.N.A.N.A.
EERS [158]Water flow of 20 L/min and a power generation of 9 kWN.A.↓80%↓90%↓35%N.A.
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Wu, G.; Feng, G.; Li, Y.; Ling, T.; Peng, X.; Su, Z.; Zhao, X. A Review of Thermal Energy Management of Diesel Exhaust after-Treatment Systems Technology and Efficiency Enhancement Approaches. Energies 2024, 17, 584. https://doi.org/10.3390/en17030584

AMA Style

Wu G, Feng G, Li Y, Ling T, Peng X, Su Z, Zhao X. A Review of Thermal Energy Management of Diesel Exhaust after-Treatment Systems Technology and Efficiency Enhancement Approaches. Energies. 2024; 17(3):584. https://doi.org/10.3390/en17030584

Chicago/Turabian Style

Wu, Gang, Guoda Feng, Yuelin Li, Tao Ling, Xuejun Peng, Zhilai Su, and Xiaohuan Zhao. 2024. "A Review of Thermal Energy Management of Diesel Exhaust after-Treatment Systems Technology and Efficiency Enhancement Approaches" Energies 17, no. 3: 584. https://doi.org/10.3390/en17030584

APA Style

Wu, G., Feng, G., Li, Y., Ling, T., Peng, X., Su, Z., & Zhao, X. (2024). A Review of Thermal Energy Management of Diesel Exhaust after-Treatment Systems Technology and Efficiency Enhancement Approaches. Energies, 17(3), 584. https://doi.org/10.3390/en17030584

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