Open Access Article
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Electric field-assisted NSR process for lean NOx reduction at low temperatures

Ayaka Shigemoto *a, Yuki Inoda a, Chihiro Ukai a, Takuma Higo a, Kohei Oka b and Yasushi Sekine *a
aDepartment of Applied Chemistry, Waseda University, 3-4-1, Okubo, Shinjuku, Tokyo, 169-8555, Japan. E-mail: ayaka.shigemoto@nifty.com; ysekine@waseda.jp
bIsuzu Central Research Center, Fujisawa, Kanagawa, Japan

Received 22nd October 2023 , Accepted 4th January 2024

First published on 4th January 2024


Abstract

Lean-burn engines are gaining attention for their lower CO2 emissions, higher thermal efficiency, and improved fuel economy compared to traditional combustion engines. However, they present some difficulty for reducing nitrogen oxides (NOx) because of residual oxygen. To address this difficulty, NOx storage reduction (NSR) system, which combines noble metals and NOx adsorbents, is developed as a viable approach. But it requires cyclic operation, which adversely affects fuel efficiency. A novel approach proposed in this work is electric field-assisted lean NOx reduction, which applies an electric field to the NSR catalyst during lean conditions. This innovation uses surplus vehicle electricity for exhaust purification, enhances hydrogen transfer, and improves NOx reduction, even at low temperatures. Tests with a 3 wt% Pt–16 wt% BaO/CeO2 catalyst demonstrate markedly higher NOx conversion to N2 (13.1% vs. 2.9% without an electric field). This process is effective with extended electric field exposure, doubling the conversion rate. Electric field-assisted lean NOx reduction, by improving NSR technology, can enhance NOx conversion efficiency, reduce emissions, and optimize fuel efficiency in lean-burn engines.


Lean-burn engines are attracting preference over stoichiometric combustion engines because of their lower CO2 emissions, higher thermal efficiency, and better fuel economy.1–3 However, classical three-way catalysts (TWCs) are ineffective at reducing nitrogen oxides (NOx) because of the presence of residual oxygen (O2) in the exhaust gases of lean burn engines. To overcome this difficulty, NOx storage reduction (NSR) technology has attracted attention as a viable approach to remove NOx from lean-burn engine exhaust.

Typical NSR catalysts combine noble metals (Pt, Pd, Rh) as active sites and alkali or alkaline earth metal oxides (Ba, K) as NOx storage sites.4–6 Conventional NSR catalysts work under cycling conditions. Under lean burn conditions, NO is oxidized by O2 and is stored on the NSR catalyst surface in the form of nitrate (NO3). In the following rich (oxygen-deprived) conditions, NOx released from the surface is reduced to nitrogen (N2) by reductants such as hydrogen (H2), carbon monoxide and hydrocarbons.7–9 However, conventional NSR technology requires complex cyclic operation with frequent switching between lean and rich states, resulting in unavoidably lower fuel efficiency.10,11

For this study, a new catalytic NSR process is proposed to reduce the adsorbed NOx and to improve engine efficiency using H2 in a lean burn state without switching to a rich combustion state after NOx adsorption. This new concept is designated as electric field-assisted lean NOx reduction, as an electric field is applied to the NSR catalyst during lean NOx reduction. With the introduction of this technology, surplus electricity in the vehicle is useful for exhaust gas purification, which is part of energy management. Furthermore, the application of an electric field activates the reduction function of the supplied H2 and simultaneously promotes hydrogen transfer. This effect promotes NOx reduction, even at low temperatures. Our earlier reports have described that application of an electric field to the reaction enhances hydrogen transfer at the surface of the support.12–15 In such heterogeneous catalysis under an electric field, the proton conductivity of the surface plays an important role, thereby enabling reaction pathways by collisions between H+ on the catalyst support and adsorbates on the supported metal. We have already established a purification technique that allows very high NO conversion and N2 selectivity, even at low temperatures, by the combination of catalyst and electric field.16,17 In this study, a novel NSR process using a Pt–BaO/CeO2 catalyst was shown to convert accumulated NOx to N2 efficiently, even at low temperatures of 423 K and under lean burn conditions.

Four NSR catalyst samples x wt% Pt–y wt% BaO/CeO2 (x[thin space (1/6-em)]:[thin space (1/6-em)]y = 3[thin space (1/6-em)]:[thin space (1/6-em)]16, 0.5[thin space (1/6-em)]:[thin space (1/6-em)]16, 3[thin space (1/6-em)]:[thin space (1/6-em)]8, 0.5[thin space (1/6-em)]:[thin space (1/6-em)]8) in powder form were obtained from Umicore Shokubai Japan Co., Ltd. Fig. S1 (ESI) shows the XRD patterns of four samples activated at 773 K for 30 min in 5% H2/Ar (100 SCCM total flow rate). Here, CeO2 was used as a support because, in the case of alumina and other materials, it is impossible to apply an electric field due to its insulating properties. Strong diffraction peaks attributed to CeO2 and BaCO3 were observed in all samples. In contrast, no diffraction for Pt and PtOx was observed. This observation suggests that Pt is highly dispersed and not sufficiently large to be detected by XRD. Table S1 (ESI) presents the results for the BET specific surface area and Pt particle size. Transmission electron microscopy (TEM) and HAADF images and EDX mapping of the four catalysts are exhibited in Fig. S2 (ESI).

Catalytic activity tests were conducted in a fixed flow type quartz reactor at atmospheric pressure as shown in Fig. S3 (ESI), and the procedure of activity tests is shown in Fig. S4 (ESI). An electric field was applied with a power supply via stainless steel electrodes, contacting the catalyst bed (amount of fixed catalyst was 250 mg) on the upper and bottom sides. The results are plotted as the average of the three values obtained from the Q-mass (BELMass; MicrotracBEL Corp.).

The NOx storage capacity of the four catalysts was measured at 573 K for 1 h with a continuous flow of 700 ppm NO and 8 vol% O2 (200 sccm total flow rate). Also, Fig. S5 and Table S2 (ESI) show that the 3 wt% Pt–16 wt% BaO/CeO2 catalyst has the highest NOx storage capacity of the four catalysts. As Fig. S2(a) (ESI) shows, Pt and Ba on the 3 wt% Pt–16 wt% BaO/CeO2 catalyst are highly dispersed on the CeO2 support. There is no aggregation of Pt and Ba compared to the other three catalysts, indicating that Pt and Ba are highly interacting on the 3 wt% Pt–16 wt% BaO/CeO2.

This result illustrates clearly that the NOx storage capacity depends on the states of both Pt and Ba, which is in agreement with earlier studies pointing out that Pt in contact with Ba or in proximity to Ba is likely to be responsible for the high NOx storage capacity.7,18

Lean NOx reduction tests with and without an electric field were performed on the 3 wt% Pt–16 wt% BaO/CeO2 catalyst with the highest NOx storage capacity: 0.2 vol% H2, 8 vol% O2 and 10 vol% H2O (200 sccm total flow rate) were flowed; the stored NOx was reduced at 423 K for 1 h (200 sccm total flow rate). For 3 wt% Pt–16 wt% BaO/CeO2 catalyst with and without the electric field, the conversion of stored NOx to N2 is presented in Fig. 1(a). For the catalytic reaction without the electric field, the conversion of NOx to N2 was only 2.9%. In contrast, when a 6-mA electric field was applied, high conversion of 13.1% was obtained even under lean burn conditions at the low temperature of 423 K. This result confirms that the electric field greatly promotes catalytic activity. In these tests, the catalyst bed temperature was directly measured using a thermocouple attached to the catalyst to confirm the effects of Joule heating induced by the applied direct current on the catalytic activity. Taking into account the Joule heating, lean NOx reduction test was conducted even at 573 K (i.e. higher temperature) without the electric field. The conversion of NOx to N2 was only 3.5% shown in Fig. S6 (ESI). Therefore, the high activity is not attributable to Joule heating. Furthermore, the distribution of nitrogen-containing species in the outlet gas of the 3 wt% Pt–16 wt% BaO/CeO2 catalyst during lean NOx reduction is shown in Fig. 1(b)–(d). N2, NO, and NO2 were detected as outlet gases, with no N2O detected. Regarding NH3 formation, quantitative analysis was not possible because NH3 was captured in the cold trap. However, the nitrogen balance demonstrated that NH3 production was negligible (ESI in Table S3 presents additional details). As presented in Fig. 1(c), the conversion of accumulated NOx to N2 increased linearly with the time course. By application of an electric field, the accumulated NOx was reduced continuously to N2. This reaction behaviour remained almost unchanged even when the electric field reduction time was doubled, resulting in the approximate doubling of NOx to N2 conversion from 13.1% to 29.1% (Fig. S7, ESI). These results indicate that the continuous reduction of accumulated NOx to N2 is enhanced by the application of an electric field, even in a lean atmosphere.


image file: d3cc05189g-f1.tif
Fig. 1 Lean NOx reduction over 3 wt% Pt–16 wt% BaO/CeO2 with/without the electric field (EF): (a) conversion of NOx to N2, (b) NOx and N2 production amounts during one hour, and (c) and (d) the distribution of nitrogen-containing species in the outlet gas (calculated on nitrogen-base).

In situ transmission infrared spectroscopy (TIRS) measurements were taken to investigate the behaviour of adsorbed NOx in the reduction reaction using a 3 wt% Pt–16 wt% BaO/CeO2 catalyst. The measurement procedure is shown in Fig. S8 (ESI). Fig. S9 (ESI) portrays the TIRS spectra of the surface species of the 3 wt% Pt–16 wt% BaO/CeO2 catalyst when 700 ppm NO and 8 vol% O2 were added, and when NOx was adsorbed at 573 K. The bands at 1040 and 1270 cm−1 are shown in the TIRS spectra of the 3 wt% Pt–16 wt% BaO/CeO2 catalyst. These bands are assigned respectively to monodentate and bidentate nitrates on the BaO phase.19–21 Then, after dosing with 0.2 vol% H2, 8 vol% O2 and 5 vol% H2O (100 sccm total flow rate) at 423 K in a 6-mA electric field, the absorbance of these bands assigned to nitrate decreased, as presented in Fig. 2. Fig. S10 (ESI) shows the TIRS spectra of 3 wt% Pt–16 wt% BaO/CeO2 at 423 K without an electric field. A comparison of the normalized area of nitrate species with and without an electric field shows a marked increase in the decomposition rate of nitrate monovalent in the presence of an electric field, as shown in Fig. S11 (ESI). This result shows good agreement with results obtained from the activity tests, indicating that greater removal of nitrate species from the surface is observed when an electric field is applied in a lean atmosphere.


image file: d3cc05189g-f2.tif
Fig. 2 Transmission infrared spectroscopy spectra during lean NOx reduction over 3 wt% Pt–16 wt% BaO/CeO2 with the electric field.

It is generally considered that NOx adsorbed at the Ba site is reduced to N2 and NO by H2 according to reactions (1) and (2).22–24

 
Ba(NO3)2 + 5H2 → N2 + BaO + 5H2O(1)
 
Ba(NO3)2 + 3H2 → 2NO + BaO + 3H2O(2)
Findings obtained from the NOx reduction reaction over 3 wt% Pt–16 wt% BaO/CeO2 catalyst with and without an electric field clarify that more H2 is consumed when the electric field is applied than when the field is not applied, as shown in Fig. S12 (ESI). Fig. 3 portrays the breakdown of H2 consumption during NOx reduction, as calculated based on the stoichiometric ratio of H2 to N2 and NO in reactions (1) and (2). The total consumption of H2 used to produce N2 and NO in the electric field is 0.102 mmol (pink and purple areas). This figure shows close agreement with the 0.107 mmol of extra H2 consumed during application of the electric field. This result suggests that the 3 wt% Pt–16 wt% BaO/CeO2 catalyst can use H2 to convert the accumulated NOx to N2 and NO, even in a lean atmosphere, by application of an electric field.


image file: d3cc05189g-f3.tif
Fig. 3 Breakdown of H2 consumption during lean NOx reduction over 3 wt% Pt–16 wt% BaO/CeO2 with and without the electric field.

Several studies have investigated the mechanisms of reduction of accumulated NOx. Reports of a few studies have included speculation that NOx accumulated as nitrate spills over to available Pt sites and that NO and N2 are released by the reductant, which has been termed reverse NOx spillover.25–28 Other reports have described that hydrogen spillover from Pt to the metal support occurs during the reduction of stored NOx with H2.25,26,29,30 The proposed mechanism involves the activation of H2 on Pt sites and the subsequent hydrogen spillover to nitrate ad-species on the storage component, mainly releasing NO. A possible scheme for NOx storage and lean NOx reduction on 3 wt% Pt–16 wt% BaO/CeO2 is portrayed in Fig. 4, together with the electric field. During NOx storage, NOx is stored as nitrate ad-species on the BaO phase. During lean NOx reduction, hydrogen is transferred from the Pt site to the storage component and reacts with the nitrate directly. Finally, the released NOx reaches the Pt site, where NOx is reduced to form N2 and NO.


image file: d3cc05189g-f4.tif
Fig. 4 Assumed reaction model for electric field-assisted lean NOx reduction over 3 wt% Pt–16 wt% BaO/CeO2.

We showed earlier that the application of an electric field actively promotes hydrogen spillover/migration at the surface of the support in the low temperature range.12–15 Indeed, we conducted lean NOx reduction tests with a physical mixture of 3 wt% Pt/CeO2 and 16 wt% Ba(NO3)2/CeO2 catalyst. A schematic image of this catalyst is shown in Fig. S13 (ESI). Fig. S14 (ESI) portrays the protocol for activity tests. The nitrates were reduced to form NO only when applying the electric field, as illustrated in Fig. S15 and Table S4 (ESI). These results clearly show that the nitrate decomposition occurs not only in close proximity to the Pt, but also further away from the Pt in the electric field. The NOx reduction reaction hardly proceeded without hydrogen during the lean NOx reduction in the electric field, indicating that the NOx reduction resulted from hydrogen spillover/migration due to the application of the electric field. Furthermore, to discuss the role of Pt for hydrogen spillover/migration, NOx reduction tests were performed in the electric field using only 16 wt% Ba(NO3)2/CeO2 catalyst without Pt. The amount of NOx reduced was lower compared to the physical mixture of 3 wt% Pt/CeO2 and 16 wt% Ba(NO3)2/CeO2 catalyst, indicating that Pt is essential for hydrogen spillover/migration in the electric field (ESI in Fig. S13–S15 and Table S4 presents additional details). An important role of the electric field in lean NOx reduction under an electric field at low temperatures is to facilitate the activation and transfer of hydrogen species. Therefore, even under lean burn conditions, stored NOx reduction can be achieved at the low temperature of 423 K.

The effect of applying an electric field to the catalyst for lean burn combustion, which has lower CO2 emissions, higher thermal efficiency and better fuel economy than conventional internal combustion engines, was investigated by application of an electric field to the catalyst with the aim of operating NOx storage and reduction (NSR) at lower temperatures. The proposed electric field-assisted lean NOx reduction improved NOx reduction at low temperatures using a small amount of excess electricity in (plug-in-) hybrid vehicles for exhaust purification and by promoting hydrogen transfer on the catalyst surface. The conversion of NOx to N2 was improved considerably when an electric field was applied using a 3 wt% Pt–16 wt% BaO/CeO2 catalyst. The catalyst surface was investigated using infrared spectroscopy and reaction mechanisms was proposed. At present, the application of an electric field causes the desorption of absorbed NO as well as its conversion to nitrogen, but as the NO desorbed in this process has an increased outlet concentration, overall purification can also be achieved by effectively combining catalytic processes. Further development of the system is anticipated.

The authors thank Mr Koki Saegusa (Waseda University) for his great assistance in the TIRS measurements. The experiment of TEM was performed at the Joint Research Center for Environmentally Conscious Technologies in Materials Science (Grant no. JPMXP0723833151) at ZAIKEN, Waseda University. The author acknowledges the NSR powder supports from Umicore Shokubai Japan Co., Ltd.

Conflicts of interest

The authors have no conflict of interest.

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Footnote

Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d3cc05189g

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