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Investigations of SO 2 poisoning and thermal aging mechanisms for Pt/BaO/Al 2 O 3 lean NO x trap catalysts D. H. Kim 1 , Y.-H. Chin 1 , G. Muntean 1 , C.H.F. Peden 1* , R. Stafford 2 , J. Stang 2 , A. Yezeretz 2 , W. Epling 2 , N. Currier 2 , H.-Y. Chen 3 , H. Hess 3 , O. Kresnawahjuesa 3 , D. Lafyatis 3 1 Pacific Northwest National Laboratory, Richland, WA 99352, USA, 2 Cummins, Inc., Columbus, IN 47201, USA, 3 Johnson Matthey Catalysts, Wayne, PA 19087, USA *[email protected] Introduction The lean NO x trap (LNT) (also known as NO x adsorber) technology is based upon the concept of storing NO x as solid nitrates in a ‘storage material’ (commonly BaO) during a lean-burn cycle, and then reducing the stored nitrates to N 2 during fuel-rich cycle over precious-metal components of the LNT. Although this technology has been recognized as particularly promising for meeting stringent NO x emission standards for diesel vehicles, deactivation of the LNTs due to poisoning by SO 2 and/or thermal aging remain significant technical challenges for implementation. Under operating conditions, low levels of SO 2 in the exhaust cumulatively deposit onto the barium sites, gradually converting these sites into BaSO 4 [1]. Because the formation of BaSO 4 is thermodynamically favored over other barium phases, this process is irreversible at the operating temperature [2], causing severe activity losses in the NO x storage-reduction function. In order to retransform BaSO 4 into BaCO 3 and/or BaO, a high temperature treatment of the NO x storage material is required. However, under high temperatures where the desulfation process occurs, sintering of Pt metal and undesirable formation of BaAl 2 O 4 take place. Thus, there is a trade-off in regenerating activity by removing the sulfur species while, on the other hand, potentially decreasing it due to thermal deactivation. Furthermore, it becomes difficult to distinguish what is responsible for deactivation in this case. This study is focused on the identification and the understanding of the important degradation mechanism(s) of the Pt/BaO/Al 2 O 3 materials used in LNTs due to the effects of high temperature operation and sulfur poisoning. In particular, a new reaction protocol enables us to de-couple the two degradation processes, and then correlate changes in physicochemical properties and the performance of these LNT materials. Experimental Pt/BaO/Al 2 O 3 samples were supplied by Johnson Matthey. LNT performance was evaluated in a fixed bed reactor operated under continuous lean-rich cycling. NO x conversion was defined as the ratio of the amount of NO x uptake to the amount of inlet NO x during a lean cycle for 4 min and 30 min, prior to a 1 min rich cycle. Reactants consisted of a continual flow of NO, CO 2 , and H 2 O, balanced with He and SO 2 , if necessary, with either rich (C 3 H 6 , CO and H 2 ) or lean (O 2 ) gases added. Catalyst characterization techniques such as XRD, XPS, IR, TEM/EDS, and TPD/TPRX were utilized to probe changes in the physicochemical properties of the catalyst samples under simulated deactivating conditions or after reaction. Specifically, H 2 TPRX, NO 2 TPD and XPS methods were used extensively to quantify the levels, speciation and distribution of sulfur on the LNT material as a function of exposure time. Results and Discussion Thermal aging gave rise to the formation of a BaAl 2 O 4 phase and a dramatic increase in the size of Pt metal particles, based on XRD and TEM studies. Fig. 1(a) shows the NO x conversion as a function of temperature for the Pt/BaO/Al 2 O 3 samples calcined at 500 °C for 3 hrs (as-calcined) and at 900 °C for 10 hrs (900 °C). Compared with an as-calcined sample, which exhibits high activities over a wide range of temperatures between 300 °C and 450 °C, the 900 °C sample displays a dramatic decrease in activity. Fig. 1(b) shows the NO x conversion after being lightly sulfated. The 1 st run indicates little, if any, change in the conversion. However, a 2 nd measurement of the performance, performed after completing a first set of runs to 450 °C, reveals a significant decrease in activity, perhaps caused by a redistribution of sulfur species during the reaction. 250 300 350 400 450 500 0 20 40 60 80 100 (a) conversion (4 min) conversion (30 min) open symbol: 900 o C NOx conversion (%) Temperature ( o C) 250 300 350 400 450 500 0 20 40 60 80 100 (b) conversion (4 min) conversion (30 min) open symbol: 2nd run NOx conversion (%) Temperature ( o C) Fig. 1(a) NO x conversion over Pt/BaO/Al 2 O 3 catalysts. Solid symbols and open ones indicate the as-calcined and 900 °C treated samples, respectively. Fig. 1(b) NO x conversion over lightly sulfated Pt/BaO/Al 2 O 3 catalysts for a 1 st run (solid symbols) and 2 nd run (open symbols). Depending on the degree of sulfation, sulfur species are present in a combination of both easily desorbed (weakly bound) and strongly bound forms, both most likely in the form of sulfates, as evidenced by H 2 TPRX and XPS. NO 2 TPD and reaction results show that the relative concentration of each sulfate species differently affects the NO x adsorption/desorption chemistry and eventually the NO x storage-reduction function. After reaction in the presence or absence of SO 2 , the catalyst was treated at higher temperature, followed by a 2 nd evaluation of the activity without SO 2 . Comparison of the activities with/without SO 2 and before/after the heat treatment allowed us to estimate the contribution to the activity changes from the two potential sources of deactivation. In addition, post-reaction analysis gave important clues to understand the deactivation process in detail. Significance By decoupling the effects of de-sulfation and thermal aging, material property changes are correlated with loss of performance, providing information on deactivation mechanisms. References 1. P. Engström, A. Amberntsson, M. Skoglundh, E. Fridell, G. Smedler, Appl. Catal. B 22 (1999) L241. 2. L. Lietti, P. Forzatti, I. Nova, E. Tronconi, J. Catal. 204 (2001) 175.

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Investigations of SO2 poisoning and thermal aging mechanisms for Pt/BaO/Al2O3 lean NOx trap catalysts

D. H. Kim1, Y.-H. Chin1, G. Muntean1, C.H.F. Peden1*, R. Stafford2, J. Stang2, A. Yezeretz2,

W. Epling2, N. Currier2, H.-Y. Chen3, H. Hess3, O. Kresnawahjuesa3, D. Lafyatis3 1Pacific Northwest National Laboratory, Richland, WA 99352, USA, 2Cummins, Inc.,

Columbus, IN 47201, USA, 3Johnson Matthey Catalysts, Wayne, PA 19087, USA *[email protected]

Introduction

The lean NOx trap (LNT) (also known as NOx adsorber) technology is based upon the concept of storing NOx as solid nitrates in a ‘storage material’ (commonly BaO) during a lean-burn cycle, and then reducing the stored nitrates to N2 during fuel-rich cycle over precious-metal components of the LNT. Although this technology has been recognized as particularly promising for meeting stringent NOx emission standards for diesel vehicles, deactivation of the LNTs due to poisoning by SO2 and/or thermal aging remain significant technical challenges for implementation. Under operating conditions, low levels of SO2 in the exhaust cumulatively deposit onto the barium sites, gradually converting these sites into BaSO4 [1]. Because the formation of BaSO4 is thermodynamically favored over other barium phases, this process is irreversible at the operating temperature [2], causing severe activity losses in the NOx storage-reduction function. In order to retransform BaSO4 into BaCO3 and/or BaO, a high temperature treatment of the NOx storage material is required. However, under high temperatures where the desulfation process occurs, sintering of Pt metal and undesirable formation of BaAl2O4 take place. Thus, there is a trade-off in regenerating activity by removing the sulfur species while, on the other hand, potentially decreasing it due to thermal deactivation. Furthermore, it becomes difficult to distinguish what is responsible for deactivation in this case.

This study is focused on the identification and the understanding of the important degradation mechanism(s) of the Pt/BaO/Al2O3 materials used in LNTs due to the effects of high temperature operation and sulfur poisoning. In particular, a new reaction protocol enables us to de-couple the two degradation processes, and then correlate changes in physicochemical properties and the performance of these LNT materials. Experimental

Pt/BaO/Al2O3 samples were supplied by Johnson Matthey. LNT performance was evaluated in a fixed bed reactor operated under continuous lean-rich cycling. NOx conversion was defined as the ratio of the amount of NOx uptake to the amount of inlet NOx during a lean cycle for 4 min and 30 min, prior to a 1 min rich cycle. Reactants consisted of a continual flow of NO, CO2, and H2O, balanced with He and SO2, if necessary, with either rich (C3H6, CO and H2) or lean (O2) gases added. Catalyst characterization techniques such as XRD, XPS, IR, TEM/EDS, and TPD/TPRX were utilized to probe changes in the physicochemical properties of the catalyst samples under simulated deactivating conditions or after reaction. Specifically, H2 TPRX, NO2 TPD and XPS methods were used extensively to quantify the levels, speciation and distribution of sulfur on the LNT material as a function of exposure time.

Results and Discussion

Thermal aging gave rise to the formation of a BaAl2O4 phase and a dramatic increase in the size of Pt metal particles, based on XRD and TEM studies. Fig. 1(a) shows the NOx conversion as a function of temperature for the Pt/BaO/Al2O3 samples calcined at 500 °C for 3 hrs (as-calcined) and at 900 °C for 10 hrs (900 °C). Compared with an as-calcined sample, which exhibits high activities over a wide range of temperatures between 300 °C and 450 °C, the 900 °C sample displays a dramatic decrease in activity. Fig. 1(b) shows the NOx conversion after being lightly sulfated. The 1st run indicates little, if any, change in the conversion. However, a 2nd measurement of the performance, performed after completing a first set of runs to 450 °C, reveals a significant decrease in activity, perhaps caused by a redistribution of sulfur species during the reaction.

250 300 350 400 450 5000

20

40

60

80

100 (a) conversion (4 min) conversion (30 min)

open symbol: 900 oC

NO

x co

nver

sion

(%)

Temperature (oC)250 300 350 400 450 500

0

20

40

60

80

100 (b)

conversion (4 min) conversion (30 min)

open symbol: 2nd run

NO

x co

nver

sion

(%)

Temperature (oC)

Fig. 1(a) NOx conversion over Pt/BaO/Al2O3 catalysts. Solid symbols and open ones indicate the as-calcined and 900 °C treated samples, respectively. Fig. 1(b) NOx conversion over lightly sulfated Pt/BaO/Al2O3 catalysts for a 1st run (solid symbols) and 2nd run (open symbols).

Depending on the degree of sulfation, sulfur species are present in a combination of both easily desorbed (weakly bound) and strongly bound forms, both most likely in the form of sulfates, as evidenced by H2 TPRX and XPS. NO2 TPD and reaction results show that the relative concentration of each sulfate species differently affects the NOx adsorption/desorption chemistry and eventually the NOx storage-reduction function. After reaction in the presence or absence of SO2, the catalyst was treated at higher temperature, followed by a 2nd evaluation of the activity without SO2. Comparison of the activities with/without SO2 and before/after the heat treatment allowed us to estimate the contribution to the activity changes from the two potential sources of deactivation. In addition, post-reaction analysis gave important clues to understand the deactivation process in detail. Significance By decoupling the effects of de-sulfation and thermal aging, material property changes are correlated with loss of performance, providing information on deactivation mechanisms. References 1. P. Engström, A. Amberntsson, M. Skoglundh, E. Fridell, G. Smedler, Appl. Catal. B 22 (1999) L241. 2. L. Lietti, P. Forzatti, I. Nova, E. Tronconi, J. Catal. 204 (2001) 175.