Sage Journals: Discover world-class research

Abstract

To reduce diesel emissions while permitting the passive regeneration of the diesel particulate filter (DPF) at low temperatures, we developed three after-treatment DPF devices. These devices consisted of a ceramic body that was either bare or loaded with the catalysts CeO₂ (DPF-CeO₂) or Ce_0.5Mn_0.5O₂ (DPF-Ce_0.5Mn_0.5O₂). The effects of these units on soot, NO_x, CO, and hydrocarbon emissions were assessed. On average, the DPF-Ce_0.5Mn_0.5O₂ device outperformed the DPF-CeO₂ device. In addition, increasing the engine load was found to raise the exhaust temperature while increasing the soot oxidation efficiency and reducing soot emissions. The maximum soot removal percentages of the DPF-CeO₂ and DPF-Ce_0.5Mn_0.5O₂ were 37.6% and 55.1%, respectively, under B100 working conditions. The extent of NO_x removal also gradually increased as the load increased, and the average removal percentages were 8.6% and 15.0%, respectively. Both catalytic devices lowered CO emissions to a much greater extent than the bare DPF, with average removals of 45.8% and 55.6%, respectively, while the average hydrocarbon oxidation values were 39.1% and 50.9%, respectively. Notably, the hydrocarbon emissions were almost zero after Ce_1-xMn_xO₂ catalysis under C100 working conditions.

Keywords

Diesel engine emissions cerium base catalyst influence rule catalytic mechanism

Introduction

The primary harmful emissions from diesel engines are particulate matter (PM) and NO_x, for which there is a trade-off relationship such that both cannot be decreased using internal purification methods alone.^1–4 Consequently, diesel emissions control technology has become an important field of research. Diesel particulate filters (DPFs) are currently the primary means of reducing PM emissions and can provide particulate collection efficiencies in excess of 90%. However, this is purely a physical method of collecting PM and does not actually eliminate the particulates themselves, meaning that the DPF is subject to clogging. For this reason, there is an urgent demand for techniques to regenerate DPFs, especially passive systems. The passive regeneration technologies developed to date have employed chemical catalysis to reduce the activation energy associated with the oxidation of particulates, thus lowering the PM ignition temperature such that the particulates can be oxidized at the temperature of the diesel engine exhaust.^5–8 Combining a DPF with an appropriate catalyst can also reduce NO_x in the exhaust, and thus achieve the goal of simultaneously reducing PM and NO_x. Consequently, selecting catalysts that exhibit a high level of activity is the key to optimizing passive regeneration technology.

Rare-earth-based catalysts have unique physiochemical properties because of their extremely abundant electronic energy-level structures. Among the rare earth oxides, ceric oxide (CeO₂) has received considerable attention as a potential catalyst^9–17 because of its special crystal structure, and because it is inexpensive and can readily and reversibly transition between Ce³⁺ and Ce⁴⁺. CeO₂ can catalyze the oxidation of soot and also convert CO, hydrocarbons (HC_S), and NO_x in exhaust to CO₂, H₂O, and N₂, respectively.^18–20 In addition, CeO₂ can serve as an oxygen buffer by rapidly storing oxygen when it is present in high concentrations in the exhaust and rapidly releasing it when the oxygen concentration is low. This characteristic can improve the catalytic activity and prolong the useable lifetime of the oxide.^21–24 Gong et al.²³ established a model for a DPF catalytic regeneration system incorporating a Ce-based catalyst that allowed the regeneration performance to be predicted at various exhaust temperatures. The results indicated that a Ce catalyst should reduce the initial temperature required for the particulate oxidation reaction and also improve performance. Liu et al.²⁵ studied the effect of CeO₂ on the oxidation of carbon black particles using X-ray diffraction, scanning electron microscopy, and image processing techniques. Their work demonstrated that CeO₂ has desirable oxygen-storage/oxygen-release properties, high catalytic activity, and stability during the carbon black oxidation process. Daturi et al.²⁶ used H₂ to reduce the CeO₂ surface, and the resulting high concentration of surface oxygen vacancies was found to degrade NO_x without the use of a reducing agent. Moreover, analyses using infrared spectroscopy and mass spectrometry determined that the NO_x degradation activity was closely related to the concentration of oxygen vacancies on the CeO₂ surface.

In the present study, the performance of a specially designed catalytic DPF (CDPF) device was assessed, based on the removal of pollutants from the exhaust of a 4DB1-40 diesel engine. Both CeO₂ and Ce_0.5Mn_0.5O₂ were selected for use in this system based on their high catalytic activities, and a wall-flow honeycomb ceramic filter was used as the support for these materials by coating the ceramic with the catalysts via an impregnation method.^27,28 The CDPF units were installed in the diesel exhaust system to carry out an experimental study. Trials were also performed using a blank DPF without the catalyst coating for comparison purposes, and the effects of the two catalysts (CeO₂ and Ce_0.5Mn_0.5O₂) on carbon, NO_x, CO, and HC emissions were investigated. The potential disadvantages of this new device were assessed, and possible improvements were identified, with the aim of demonstrating new concepts for DPF catalytic regeneration technology.

Experimental

Experimental apparatus

The test engine was a four-cylinder, turbocharged, intercooled, electronic control common-rail diesel engine, for which the primary technical parameters are provided in Table 1. No changes were made to the original structure or operating parameters of the diesel engine before the experiment, and only the original after-treatment device was uninstalled.

Table 1.

Specifications of the test engine.

Item	Specification
Type	4-cylinder, in-line, turbocharged and intercooled
Bore × stroke (mm)	105 × 118
Combustion chamber type	Direct injection ω type
Compression ratio	17.5
Displacement (L)	4.09
Max. torque/speed (Nm/r/min)	400/1500
Rated power/speed (kW/r/min)	95/2600
Max. injection pressure (MPa)	160
Fuel injection system	Electronic controlled high pressure common-rail

A schematic diagram of the test bench is shown in Figure 1. In this apparatus, sampling tubes were installed at the front and rear of the DPF to monitor the pollutant concentrations and allow assessments of the effect of the DPF on NO_x, CO, HC, soot, and PM emissions. During these trials, a CAC250 electric dynamometer was used to control the revolution rate and torque of the engine, and the speed and torque measurement accuracies were 0.05% and 0.1%, respectively. An FC2005 monitoring system was utilized to measure the performance indexes of the engine (power, torque, revolution rate, fuel consumption, soot output, flow, and temperature) in real-time with a high level of precision. The emissions data were automatically and simultaneously recorded. Gaseous pollutants, such as NO_x, HCs, and CO, were determined using a Horiba MEXA-7200D emission analyzer. Among these, NO_x was analyzed via a chemiluminiscence method, while CO was detected using non-dispersive infrared spectroscopy and HCs were monitored using a flame ionization detector. The measurement accuracies for NO_x, HCs, and CO were 2 ppm, 2 ppm, and 1 ppm, respectively. The fuel consumption rate was measured using a 735 S instantaneous fuel consumption meter (AVL Co.), with a measurement accuracy of 0.12%. The air intake flow was determined with a Sensyflow FMT700 -P mass flow meter. The soot output was measured using a 415 S filter-type smoke meter, with a measurement accuracy of 0.01 FSN.

Figure 1.

Schematic diagram of the engine test apparatus.

Experimental DPF device

Because of the significant exhaust output from a diesel engine and the high strength required of filter materials, honeycomb carriers are typically used to ensure sufficiently low resistance to flow together with the appropriate level of strength. A cordierite ceramic was used as the support in this study, and the physical parameters of this material are summarized in Table 2. Typically, the preparation of the sizing agent is an important step in fabricating such ceramics, and the compatibility and stability of this agent must be considered, because these factors directly affect the eventual catalytic performance. The primary components of the sizing agent used in these experiments were pseudoboehmite, acetic acid, and γ-Al₂O₃. Stoichiometric quantities of pseudoboehmite, acetic acid, and deionized water were initially weighed out and mixed to form a suspension to enhance the specific surface areas of the catalysts. Subsequently, the catalysts were loaded onto the DPF using an impregnation method, after which the impregnated DPF was heated.

Table 2.

Physical properties of the cordierite support.

Physical parameters	Parameter values
Diameter (mm)	144
Length (mm)	152
Hole density (CPSI)	200
Porosity	39%

Experimental program

The European steady-state test cycle (ESC), which has been in effect in the European Union since 2001, includes a test cycle for the Euro III standard and above that includes 13 operating conditions (four load rates at A, B, and C rotational rates and idle). In the present study, these test procedures were initially employed to derive the external characteristic curve of the diesel test engine. During these trials, the throttle position was fixed at 100% and the rotational rate of the engine (as controlled by an electric dynamometer) was increased from 800 to 2800 r/min. The resulting curves showed that the A, B, and C rotational rates were 1787, 2230, and 2673 r/min, respectively, while the corresponding loads were 25%, 50%, 75%, and 100% and the engine idle speed was 800 r/min. In this work, the ESC13 procedure was used to provide the operating parameters, in conjunction with the specific operating sequence and times provided in Table 3.

Table 3.

Thirteen operating conditions of the ESC cycle.

Working condition number	Rotational speed(r/min)	Torque (Nm)	Weighting factor	Time (min)
1 (Idle)	800	0	0.15	4
2 (A100)	1787	351	0.08	2
3 (B50)	2230	175	0.10	2
4 (B75)	2230	263	0.10	2
5 (A50)	1787	176	0.05	2
6 (A75)	1787	263	0.05	2
7 (A25)	1787	88	0.05	2
8 (B100)	2230	351	0.09	2
9 (B25)	2230	88	0.10	2
10 (C100)	2673	319	0.08	2
11 (C25)	2673	80	0.05	2
12 (C75)	2673	239	0.05	2
13 (C50)	2673	159	0.05	2

ESC: European steady-state test cycle.

Three after-treatment devices were assessed: a DPF ceramic support loaded with the CeO₂ catalyst (DPF-CeO₂), a DPF loaded with the Ce_0.5Mn_0.5O₂ catalyst (DPF-Ce_0.5Mn_0.5O₂), and a bare ceramic with no catalyst. The soot, NO_x, HC, and CO emissions obtained with each of these systems were determined under the ESC13 working conditions and compared to explore the effects of the catalysts on pollutant removal.

Direct, continuous sampling of the exhaust after preheating was performed under each set of operating conditions during the test cycle and the average values were calculated. This exhaust gas sampling, as well as measurements of the engine exhaust flow and power, were performed in real-time during operation of the engine, and the resulting data were weighted. Gaseous pollutants were monitored during the last 30 s of each distinct set of working conditions, and the average concentrations of NO_x, HC, and CO emissions associated with each set of conditions are reported. Soot emissions were also measured under the ESC13 working conditions. Throughout the test process, the flow of exhaust particulates was diluted with compressed air and the particulates were collected on filter paper. The sampling time under each set of working conditions was a weighting coefficient of each 0.01 for 4 s.

Results and discussion

Exhaust temperatures and oxygen levels during the ESC cycle

Both the exhaust temperature and oxygen concentration are critical factors determining the effectiveness of the after-treatment device. In this work, trials were performed using the same engine conditions with the various DPF permutations to compare the effects of the different catalysts. Figure 2(a) and (b) shows the oxygen concentrations and exhaust temperatures at the entry to the DPF during the ESC13 test cycle. It is evident from Figure 2(a) that the oxygen concentration in the exhaust decreased as the engine load was increased and increased (although to a lesser extent) with the revolution rate. The maximum oxygen concentration of 18.58% was obtained under idling conditions. This occurred because the fuel feed increases along with the load such that the air–fuel ratio in the combustion chamber of the cylinder decreases and oxygen consumption increases. Because the fuel feed is lowest while idling, the highest oxygen surplus is present.

Figure 2.

O₂ concentrations and exhaust temperatures during the ESC test cycle: (a) O₂ concentration; (b) exhaust temperature.

Figure 2(b) demonstrates that the diesel exhaust temperature increased with both the load and the revolution rate, with values of 489°C, 544°C, and 571°C for a full load at revolution rates A, B, and C, respectively. This correlation is attributed to increases in the fuel feed at higher loads, which raise the thermal energy output during the combustion process. In addition, at a constant load, increasing the revolution rate will increase the number of work cycles per unit time and the gas flow field in the cylinder, leading to more intense combustion that raises the exhaust temperature.

Effect of Ce_1-xMn_xO₂ on diesel engine emissions

Effect of Ce_1-xMn_xO₂ on soot emissions

The stability and properties of slurry are directly related to the performance of catalyst. The main components of the paste used in this study were pseudo-thin bauxite, acetic acid, and γ-Al₂O₃. Three DPF supports were coated with the same slurry such that changes in the emission concentrations were primarily caused by the catalytic activity of the CeO₂ or Ce_1-xMn_xO₂. Figure 3 summarizes the soot emissions from the diesel engine downstream of the three DPF after-treatment devices during the ESC test cycle. The soot emissions after the various DPF devices all show a similar trend: the emissions increase along with both the load and the revolution rate and are lowest while idling. Under the same working conditions, the Ce_0.5Mn_0.5O₂ removed soot more efficiently than the CeO₂, presumably because the Mn-loaded nano-CeO₂ possessed superior catalytic activity and a wider temperature window, and so more effectively promoted soot oxidation. Under a 25% load at rotational rates A, B, and C, the catalysts do not exhibit a suitable level of activity because of the low exhaust temperatures, and so the after-treatment soot emissions of all three DPF units are basically the same. The exhaust temperature increased along with the load, which in turn enhanced the activity of the Ce_1-xMn_xO₂ and the soot oxidation efficiency to reduce soot emissions. Typically, the optimal soot removal by catalysis is achieved under B100 working conditions, and the soot removal efficiencies of the CeO₂ and Ce_0.5Mn_0.5O₂ under these conditions were found to be 37.6% and 55.1%, respectively. This greater efficiency is due to the higher exhaust temperature produced under B100 working conditions as being higher than the exhaust temperature under A100 conditions. The higher temperature increases the catalytic activity, improves the oxidation efficiency of soot, and reduces the emission of soot. However, the revolution rate associated with the B100 conditions is lower than that under C100 conditions, meaning that the exhaust will flow through the DPF over a longer time span, which could also promote the catalytic oxidation of soot particles.

Figure 3.

Smoke emissions during the ESC test cycle after the DPF.

Effect of Ce_1-xMn_xO₂ on NO_x emissions

Figure 4 compares the NO_x emissions in the diesel exhaust after passing through the three after-treatment devices (DPF, DPF-CeO₂, and DPF-Ce_0.5Mn_0.5O₂) under the 13 working conditions. These data show that compared with the blank DPF, the NO_x emissions under each set of working conditions were decreased to varying degrees by the Ce_1-xMn_xO₂ catalyst. The removal efficiency increased with increases in the load, and the performance of the Ce_0.5Mn_0.5O₂ was also higher than that of the CeO₂. Removal efficiencies were 2.1% and 8.9% at a 25% load and rotational rate A for CeO₂ and Ce_0.5Mn_0.5O₂, respectively, and 21.2% and 37.1%, respectively, at a 100% load. The blank DPF showed poor performance because it had no catalyst. In addition, a greater concentration of PM would presumably be gathered with increases in the load and the temperature would also increase, both of which are conducive to the removal of NO_x. The NO_x removal efficiency of the Ce_1-xMn_xO₂ tended to plateau at a 25% load at each revolution rate because the low temperatures under these conditions did not promote the reactions of PM and NO_x. Notably, the temperature was only 180°C under idling conditions, which is below the catalyst activation temperature, and so there was no NO_x removal effect. By contrast, the temperature under C100 working conditions was higher than the optimal catalyst activation temperature, resulting in a lower NO_x removal efficiency than at revolution rates A and B.

Figure 4.

NO_x emissions during the ESC test cycle after the DPF.

The NO_x emission concentrations obtained from all three DPF units increased with increases in load when the revolution rate was held constant. This effect can be attributed to increases in the average effective pressure, flame temperature, and average temperature in the cylinder as the load increases, all of which are associated with higher NO_x emissions. At the same load, faster revolution rates provided lower NO_x emissions. When the diesel engine combustion system is unchanged, the injection advance angle is fixed. At higher rotational speeds, the physical mixing time of the oil bundle and the air is shorter. Less mixture is formed during the combustion delay period, and the premix heat release rate is lower, so less NO_x is created. In other words, higher engine speed leads to shorter reaction time or residence time at high temperature, causing the level of NO_x emissions to decreases with engine speed.²⁹ The average NO_x removal efficiencies of the CeO₂ and Ce_0.5Mn_0.5O₂ were determined to be 8.6% and 15.0% under the ESC13 working conditions. These data are consistent with (although not identical to) the results obtained from catalytic activity simulations.^30,31

Effect of Ce_1-xMn_xO₂ on CO emissions

CO is the primary intermediate product during the combustion of diesel fuel and is at least partly converted to CO₂ in the cylinder. This transformation proceeds via the following reaction.

CO + OH \to C O_{2} + H

(1)

In the case of oxygen-enriched combustion, the CO level in the exhaust will increase with increases in the stoichiometric excess of fuel. However, during the combustion of a dilute fuel mixture, the production of CO will remain essentially unchanged with changes in the equivalence ratio. Typically, if R represents the carbon hydroxyl, the reaction that generates CO during the combustion of a hydrocarbon can be expressed as below.

RH \to R \to R O_{2} \to RCHO \to RCO \to CO

(2)

Thus, the primary source of CO during combustion is the pyrolysis and oxidation of RCO to form CO.

Figure 5 compares the CO emissions after the exhaust has passed through the three after-treatment devices (DPF, DPF-CeO₂, and DPF-Ce_0.5Mn_0.5O₂) under all 13 working conditions. The CO emissions after the DPF-CeO₂ and DPF-Ce_0.5Mn_0.5O₂ were significantly lower than the value obtained using the bare DPF, indicating that both catalysts had an effect. The catalytic efficiency of the Ce_1-xMn_xO₂ was greater than 93% at a 100% load at each revolution rate, while the oxidation efficiency was almost 100% under the C100 working conditions, giving close to zero CO emissions. In comparison, under idling and low load conditions, the exhaust temperatures were below the activation temperatures for the catalysts, which led to low CO oxidation efficiencies. The average catalytic efficiencies of the CeO₂ and Ce_0.5Mn_0.5O₂ for CO oxidation were 45.8% and 55.6%, respectively, under the ESC13 working conditions. This is attributed to an increase in the number of oxygen vacancies that promote CO oxidation in the Ce_0.5Mn_0.5O₂. The addition of Mn likely increases the concentration of lattice defects in the CeO₂, which is conducive to the formation of oxygen species and so contributes to oxygen adsorption, migration, and transformation. As a result, the CO oxidation efficiency is markedly improved.

Figure 5.

CO emissions during the ESC test cycle after the DPF.

Effect of Ce_1-xMn_xO₂ on HC emissions

Figure 6 compares the HC emissions after the three after-treatment devices (DPF, DPF-CeO₂, and DPF-Ce_0.5Mn_0.5O₂) under the ESC13 working conditions. The HC emissions obtained from all three devices decreased as the load increased at all revolution rates, and the HC emissions were highest under idling conditions. This occurred because a low load produces a very dilute mixture in the cylinder such that the combustion becomes less intense and extremely low temperatures are present in the cylinder. Under such conditions, there is also a weak mixture in the vicinity of the injection site, meaning that the fuel is not completely combusted, which is the primary source of unburned HCs. Therefore, the HC emissions from a diesel engine under idling and low load working conditions are higher than those at high loads. The data in this figure also demonstrate that the Ce_1-xMn_xO₂ significantly lowered the HC emissions. Typically, the catalytic efficiencies of the CeO₂ and Ce_0.5Mn_0.5O₂ with regard to HC reduction were 92.3% and 98.7%, respectively, under the C100 working conditions, due to the extremely high exhaust temperatures during these trials. Importantly, almost zero HC emissions were observed after Ce_1-xMn_xO₂ catalysis. In addition, the average HC oxidation efficiencies of the CeO₂ and Ce_0.5Mn_0.5O₂ under the ESC13 working conditions were 39.1% and 50.9%, respectively. The improved performance of the latter is primarily attributed to changes in lattice defects and a higher concentration of oxygen species following the addition of Mn to the original CeO₂, indicating that lattice oxygen is also directly related to the catalytic activity. These results also demonstrate that the presence of oxygen species enhances HC oxidation efficiency. Specifically, the activity of the original oxide was increased by approximately 50% after Mn doping.

Figure 6.

HC emissions during the ESC test cycle after the DPF.

Emission characteristics

Soot is typically formed as a result of the thermal decomposition of fuel at high temperatures under oxygen-deficient conditions. The transition of Ce from the CeO₂ (+4) valence state to the Ce₂O₃ (+3) state occurs via a relatively low-energy process. Thus, CeO₂ can provide the oxygen necessary for the reduction of soot while being converted to Ce₂O₃ as in equation (3).³⁰ While acting as an oxidation catalyst, CeO₂ also lowers the activation temperature for carbon combustion and thus enhances soot oxidation and promotes complete combustion.

4 Ce O_{2} + C (soot) \to 2 C e_{2} O_{3} + C O_{2}

(3)

Because of its high thermal stability, the Ce₂O₃ formed while reacting with the soot remains active after being generated in the initial combustion process and is subsequently reoxidized to CeO₂ through the reduction of NO,³¹ via the reaction in equation (4).³¹ Emissions of NO are also thus at least partly inhibited as the CeO₂ is regenerated.

2 C e_{2} O_{3} + 2 NO \to 4 Ce O_{2} + N_{2}

(4)

As shown in Figure 5, increased CO emissions were observed when using the blank DPF. When using this device, there was insufficient oxygen to convert all the carbon into CO₂, with the result that some of the fuel did not fully combust and CO was generated as an intermediate product during combustion. However, because of its useful oxygen storage and release capabilities, the Ce_1-xMn_xO₂ can act as an oxygen buffer and provide oxygen to promote the conversion of CO to CO₂. The corresponding reaction is presented in equation (5).

2 Ce O_{2} + CO \to C e_{2} O_{3} + C O_{2}

(5)

Cerium ions can lower the energy barrier associated with breaking H—C bonds and so accelerate high temperature dehydrogenation reactions. The corresponding reaction is presented in equation (6).

(2 x + y) Ce O_{2} + C_{x} H_{y} \to x + y / 2 C e_{2} O_{3} + x / 2 C O_{2} + y / 2 H_{2} O

(6)

The catalytic mechanism of the Ce_1-xMn_xO₂ is illustrated in Figure 7, which shows that the presence of cerium oxide enhances oxygen mobility during the reaction cycle. In addition, smaller particle sizes facilitate the migration of oxygen from the interiors of nano-crystallites to their surfaces. The interactions in Ce-Mn oxides can be regarded as a transition of lattice oxygen (O_latt) and chemisorbed oxygen (O_ads) to active O* on the active sites of the catalyst surface, which favors the soot oxidation process. During the redox cycle, the Ce⁴⁺/Ce³⁺ redox couple permits oxygen storage, because the CeO₂ acts as an oxygen buffer by storing/releasing oxygen species in association with the couple. This, in turn, facilitates the mobility of oxygen in the redox cycle. In addition, partial doping with Mn inhibits the growth of catalyst grains and increases the specific surface area of the catalyst. The concentration of lattice defects in Ce_1-xMn_xO₂ increases and oxygen species are formed more abundantly after Mn enters CeO₂, because these defects are conducive to the adsorption, migration, and transformation of oxygen. Moreover, the concentration of lattice oxygen, which has a strong adsorption and activation effect, increases with increasing Mn doping concentration.

Figure 7.

A schematic summarizing the catalytic effect of Ce_1-xMn_xO₂.

Conclusion

In this study, both CeO₂ and Ce_1-xMn_xO₂ catalysts were loaded onto DPF supports. The abilities of these materials to simultaneously catalyze the removal of soot, NO_x, CO, and HCs from diesel exhaust were examined and several conclusions were drawn.

First, the soot removal efficiency of the Ce_0.5Mn_0.5O₂ was superior to that of the CeO₂ under the same working conditions. The diesel exhaust temperature increased with the load, which enhanced the Ce_1-xMn_xO₂ activity and therefore the soot oxidation efficiency, thus reducing soot emissions. The highest degree of soot removal was achieved under B100 working conditions. The purification efficiencies of the CeO₂ and Ce_0.5Mn_0.5O₂ under these conditions were 37.6% and 55.1%, respectively.

Second, the Ce_1-xMn_xO₂ catalyst caused varying degrees of reduction in NO_x emissions (depending on the working conditions) compared with the results obtained using the blank DPF. The NO_x removal efficiency increased with the load, and the Ce_0.5Mn_0.5O₂ catalyst outperformed the CeO₂ catalyst. The average NO_x removal percentages exhibited by the CeO₂ and Ce_0.5Mn_0.5O₂ were 8.6% and 15.0%, respectively, under the ESC13 working conditions.

Third, the average catalytic efficiency of the Ce_0.5Mn_0.5O₂ for CO elimination was higher than that of the CeO₂ under the ESC13 working conditions, with the two materials showing average efficiencies of 45.8% and 55.6%, respectively. Finally, the HC removal percentages obtained from the CeO₂ and Ce_0.5Mn_0.5O₂ were 92.3% and 98.7%, respectively, under the C100 working conditions because of the extremely high exhaust temperatures associated with those conditions. Importantly, almost zero HC emissions were obtained when using the Ce_1-xMn_xO₂. The average HC oxidation efficiencies of the CeO₂ and Ce_0.5Mn_0.5O₂ under the ESC13 working conditions were 39.1% and 50.9%, respectively.

Footnotes

Acknowledgements

The authors acknowledge support from the University Natural Science Research Project in Jiangsu Province (19KJD470003) and Research Foundation of NIIT (YK18-04-04, YK18-04-03).

Handling Editor: David Chalet

Declaration of conflicting interests

The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.

Funding

The author(s) received no financial support for the research, authorship, and/or publication of this article.

ORCID iD

He Huang

References

Sivakumar

Shanmugasundaram

Rameshkumar

Effects of pongamia methyl esters and its blends on a diesel engine performance, combustion, and emission characteristics. Environ Prog Sustain 2017; 36: 269–276.

Mehregan

Moghiman

Effects of nano-additives on pollutants emission and engine performance in a urea-SCR equipped diesel engine fueled with blended-biodiesel. Fuel 2018; 222: 402–406.

Heywood

JB.

Internal combustion engine fundamentals. New York: McGraw-Hill, Inc., 1988.

Niaki

SRA

Mahdavi

Mouallem

, et al. Experimental and simulation investigation of effect of biodiesel-diesel blend on performance, combustion, and emission characteristics of a diesel engine. Environ Prog Sustain 2018; 37: 1540–1550.

May

Corinne

Alain

, et al. Oxidation of carbon by CeO2: effect of the contact between carbon and catalyst particles. Fuel 2008; 87: 740–750.

Mihai

Stenfeldt

Olsson

The effect of changing the gas composition on soot oxidation over DPF and SCR-coated filters. Catal Today 2018; 360: 243–250.

Hou

Lei

Zhang

, et al. Ethanol dry reforming for syngas production over Ir/CeO2 catalyst. J Rare Earth 2015; 33: 42–46.

Liu

Sun

Liu

, et al. Ce-based fuel borne catalyst enhancing regenerative effect of diesel particulate filter. Trans Chin Soc Agric Eng 2016; 32: 112–117.

Ryou

Lee

, et al. Low temperature NO adsorption over hydrothermally aged Pd/CeO2 for cold start application. Catal Today 2018; 307: 93–101.

10.

LWang

, et al. Ceria-terbia solid solution nanobelts with high catalytic activities for CO oxidation. Chem Commun 2009; 48: 7557–7559.

11.

Sugiura

Ozawa

Suda

, et al. Development of innovative three-way catalysts containing ceria-zirconia solid solutions with high oxygen storage/release capacity. Bull Chem Soc Jpn 2005; 78: 752–767.

12.

Shi

Liu

Yang

, et al. Evaluation of cordierite-ceria composite ceramic with oxygen storage capacity. J Eur Ceram Soc 2002; 22: 1251–1256.

13.

Ivanova

Homola

Bryukvin

, et al. Catalytic performance of Ag2O and Ag doped CeO2 prepared by atomic layer deposition for diesel soot oxidation. Coatings 2018; 8: 237–252.

14.

Aneggi

Boaro

Litenburg

, et al. Insights into the redox properties of ceria-based oxides and their implications in catalysis. J Alloy Compd 2006; 408–412: 1096–1102.

15.

Dutta

Waghmare

Baidya

, et al. Origin of enhanced reducibility/oxygen storage capacity of Ce1-xTixO2 compared to CeO2 or TiO2. Chem Mater 2006; 18: 3249–3256.

16.

Jiaqiang

Zhang

Chen

, et al. Performance and emission evaluation of a marine diesel engine fueled by water biodiesel-diesel emulsion blends with a fuel additive of a cerium oxide nanoparticle. Energ Convers Manage 2018; 169: 194–205.

17.

Mai

Sun

Zhang

, et al. Shape-selective synthesis and oxygen storage behavior of ceria nanopolyhedra, nanorods, and nanocubes. J Phys Chem B 2005; 109: 24380–24385.

18.

Overbury

SH.

Surface structure dependence of selective oxidation of ethanol on faceted CeO2 nanocrystals. J Catal 2013; 306: 164–176.

19.

Singh

Subramanian

Juneja

, et al. Investigating the effect of fuel cetane number, oxygen content, fuel density, and engine operating variables on NOx emissions of a heavy duty diesel engine. Environ Prog Sustain 2017; 36: 214–221.

20.

Mianzarasvand

Shirneshan

Afrand

Effect of electrically heated catalytic converter on emission characteristic of a motorcycle engine in cold-start conditions: CFD simulation and kinetic study. Appl Therm Eng 2017; 127: 453–464.

21.

Chen

Zhang

Chen

, et al. Influence of exhaust temperature and catalytic substrate properties on diesel exhaust. Trans Chin Soc Agric Eng 2012; 30: 42–49.

22.

Wang

The first principles study on the mechanism of rare earth and transition metalcatalytic materials in environmental catalysis. J East China Univ Sci Tech 2012; 15: 48–55.

23.

Gong

Long

Cai

, et al. Study on diesel particulate filter catalytic regenerating with ceria-based additive. Trans CSISE 2011; 29: 515–519.

24.

Lin

Zhu

, et al. Surface reactive species on MnOx(0.4)-CeO2 catalysts towards soot oxidation assisted with pulse dielectric barrier discharge. J Rare Earth 2014; 33: 153–158.

25.

Liu

, et al. Soot oxidation over CeO2 and Ag/CeO2: factors determining the catalyst activity and stability during reaction. J Catal 2016; 337: 188–198.

26.

Daturi

Bion

Saussey

, et al. Evidence of a lacunar mechanism for deNOx activity in ceria-based catalysts. Phys Chem Chem Phys 2001; 3: 252–255.

27.

Sajith

Sobhan

Peterson

GP.

Experimental investigations on the effects of cerium oxide nanoparticle fuel additives on biodiesel. Adv Mech Eng 2010; 2: 144–148.

28.

Mori

Miyauchi

Kuwahara

, et al. Shape effect of MnOx-decorated CeO2 catalyst in diesel soot oxidation. B Chem Soc Jpn 2017; 90: 556–564.

29.

Chen

Xie

, et al. NOx emission of biodiesel compared to diesel: higher or lower? Appl Therm Eng 2018; 137: 584–593.

30.

Huang

Liu

Sun

, et al. Study on the simultaneous reduction of diesel engine soot and NO with nano-CeO2 catalyst. RSC Adv 2016; 6: 102028–102034.

31.

Huang

Liu

Sun

, et al. Effects of Mn-doped ceria oxygen-storage material on oxidation activity of diesel soot. RSC Adv 2017; 7: 7406–7412.

Study on the effect of Ce 1-x Mn x O 2 catalyst on improving diesel emission performance

Abstract

Keywords

Introduction

Experimental

Experimental apparatus

Experimental DPF device

Experimental program

Results and discussion

Exhaust temperatures and oxygen levels during the ESC cycle

Effect of Ce1-xMnxO2 on diesel engine emissions

Effect of Ce1-xMnxO2 on soot emissions

Effect of Ce1-xMnxO2 on NOx emissions

Effect of Ce1-xMnxO2 on CO emissions

Effect of Ce1-xMnxO2 on HC emissions

Emission characteristics

Conclusion

Footnotes

Acknowledgements

Declaration of conflicting interests

Funding

ORCID iD

References

Effect of Ce_1-xMn_xO₂ on diesel engine emissions

Effect of Ce_1-xMn_xO₂ on soot emissions

Effect of Ce_1-xMn_xO₂ on NO_x emissions

Effect of Ce_1-xMn_xO₂ on CO emissions

Effect of Ce_1-xMn_xO₂ on HC emissions