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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2021, Vol. 15 Issue (2) : 30    https://doi.org/10.1007/s11783-020-1322-1
RESEARCH ARTICLE
Promotional effect of ion-exchanged K on the low-temperature hydrothermal stability of Cu/SAPO-34 and its synergic application with Fe/Beta catalysts
Chen Wang1,2, Jun Wang1, Jianqiang Wang1, Meiqing Shen1()
1. School of Chemical Engineering & Technology, Key Laboratory for Green Chemical Technology of State Education Ministry, Tianjin University, Tianjin 300072, China
2. School of Environment and Safety Engineering, North University of China, Taiyuan 030051, China
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Abstract

• K+ hinder the structural degradation of Cu/SAPO-34 under humid condition<100°C.

• K+ on Cu/SAPO-34 brings lower acidity and inferior SCR activity at high temperature.

• Fe/Beta was used to compensate the low activity of Cu/SAPO-34 at high temperature.

• The hybrid catalysts with KCu/SAPO-34 and Fe/Beta show a great potential for using.

K ions were introduced onto Cu/SAPO-34 catalysts via the ion-exchange process in order to improve their stability under low-temperature hydrothermal aging. The changes in structure and copper-species contents of these catalysts upon hydrothermal aging were probed in order to investigate their effects on selective catalytic reduction (SCR) activity. For the fresh Cu/SAPO-34 catalysts, K ions had little influence on the chabazite framework but effected their acidities by exchanging with acid sites. After hydrothermal aging, the structural integrity and amount of active sites decreased on pure Cu/SAPO-34. While the K-loaded catalysts showed improved chabazite structure, acidity, and active site conservation with increasing K loading. However, although the 0.7 wt% K catalyst maintained the same crystallinity, active site abundance, and low-temperature SCR activity as the fresh catalyst upon aging, an apparent decrease in SCR activity at high temperature was observed because of the inevitable decrease in the number of Brönsted acid sites. To compensate for the activity disadvantage of K-loaded Cu/SAPO-34 at high temperature, Fe/Beta catalysts were co-employed with K-loaded Cu/SAPO-34, and a wide active temperature window of SCR activity was obtained. Thus, our study reveals that a combined system comprising Fe/Beta and K-loaded Cu/SAPO-34 catalysts shows promise for the elimination of NOx in real-world applications.

Keywords Selective catalytic reduction      Cu/SAPO-34 catalyst      Ion-exchanged K      Low-temperature hydrothermal stability      Fe/Beta catalyst     
Corresponding Author(s): Meiqing Shen   
Issue Date: 08 September 2020
 Cite this article:   
Chen Wang,Jun Wang,Jianqiang Wang, et al. Promotional effect of ion-exchanged K on the low-temperature hydrothermal stability of Cu/SAPO-34 and its synergic application with Fe/Beta catalysts[J]. Front. Environ. Sci. Eng., 2021, 15(2): 30.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-020-1322-1
https://academic.hep.com.cn/fese/EN/Y2021/V15/I2/30
Samples’ name Specific surface area (m2/g) ?S(%)a)
F-Cu 504
H-Cu 340 32.5
K-1 501
H-K-1 410 18.2
K-2 501
H-K-2 442 11.8
K-3 504
H-K-3 475 5.8
Tab.1  Specific surface areas and K contents over pure and K loaded samples before and after low-temperature hydrothermal aging
Samples’ Name Cu contents (wt.%) K contents (wt.%)
F-Cu 3.13
K-1 3.08 0.37
K-2 2.94 0.54
K-3 2.76 0.72
Tab.2  Cu and K contents over pure and K loaded samples a)
Fig.1  (a) XRD pattern of pure and K contained catalysts before (solid line) and after (dash line) aging and (b) the relative crystallinity from XRD patterns.
Fig.2  The ex-situ DRIFTs results of pure and K loaded catalysts before (solid line) and after (dash line) hydrothermal aging. (a) units in absorbance and (b) Kubelka-Munk.
Fig.3  27Al (a), 31P (b) and 29Si (c) NMR results of pure and K contained catalysts before (solid line) and after (dash line) aging.
Fig.4  (a) NH3-TPD results of pure and K contained catalysts before (solid line) and after (dash line) aging; (b) the relative acidity from NH3-TPD results.
Fig.5  (a) The H2-TPR profiles and (b) qualitative data of pure and K contained catalysts before (solid line) and after (dash line) aging.
Fig.6  (a) The EPR results of pure and K contained catalysts before (solid line) and after (dash line) aging and (b) the quantitative results from EPR results.
Fig.7  NOx conversion during standard SCR reaction over pure and K contained catalysts before (solid line) and after (dash line) aging.
Fig.8  (a) The conservation of SCR activity as a function of Cu2+ preservation at 200°C; (b) The conservation of SCR activity as a function of acidity preservation at 200°C; (c) The conservation of SCR activity as a function of Cu2+ preservation at 500°C; (d) The conservation of SCR activity as a function of acidity preservation at 500°C.
Fig.9  Conversion of NOx during standard SCR reaction over the monolith catalysts.
Fig.10  Conversion of NOx during standard SCR reaction over hybrid catalysts.
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