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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

Postal Subscription Code 80-969

2018 Impact Factor: 2.809

Front. Chem. Sci. Eng.    2023, Vol. 17 Issue (12) : 1973-1985    https://doi.org/10.1007/s11705-023-2364-2
RESEARCH ARTICLE
NO hydrogenation to NH3 over FeCu/TiO2 catalyst with improved activity
Dan Cui1, Yanqin Li1, Keke Pan1, Jinbao Liu1, Qiang Wang1, Minmin Liu1, Peng Cao1, Jianming Dan1, Bin Dai1, Feng Yu1,2()
1. Key Laboratory for Green Processing of Chemical Engineering of Xinjiang Bingtuan, School of Chemistry and Chemical Engineering, Shihezi University, Shihezi 832003, China
2. Carbon Neutralization and Environmental Catalytic Technology Laboratory, Bingtuan Industrial Technology Research Institute, Shihezi University, Shihezi 832003, China
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Abstract

Ammonia is crucial in industry and agriculture, but its production is hindered by environmental concerns and energy-intensive processes. Hence, developing an efficient and environmentally friendly catalyst is imperative. In this study, we employed a straightforward and efficient impregnation technique to create various Cu-doped catalysts. Notably, the optimized 10Fe-8Cu/TiO2 catalyst exhibited exceptional catalytic performance in converting NO to NH3, achieving an NO conversion rate exceeding 80% and an NH3 selectivity exceeding 98% at atmospheric pressure and 350 °C. We employed in situ diffuse reflectance Fourier transform infrared spectroscopy and conducted density functional theory calculations to investigate the intermediates and subsequent adsorption. Our findings unequivocally demonstrate that Cu doping enhances the rate-limiting hydrogenation step and lowers the energy barrier for NH3 desorption, thereby resulting in improved NO conversion and enhanced selectivity toward ammonia. This study presents a pioneering approach toward energy-efficient ammonia synthesis and recycling of nitrogen sources.

Keywords NO hydrogenation      synthetic ammonia      10Fe-xCu/TiO2      high selectivity     
Corresponding Author(s): Feng Yu   
Just Accepted Date: 13 September 2023   Online First Date: 19 October 2023    Issue Date: 30 November 2023
 Cite this article:   
Dan Cui,Yanqin Li,Keke Pan, et al. NO hydrogenation to NH3 over FeCu/TiO2 catalyst with improved activity[J]. Front. Chem. Sci. Eng., 2023, 17(12): 1973-1985.
 URL:  
https://academic.hep.com.cn/fcse/EN/10.1007/s11705-023-2364-2
https://academic.hep.com.cn/fcse/EN/Y2023/V17/I12/1973
Fig.1  (a) XRD spectra, (b) EPR spectra, (c) N2 adsorption-desorption isotherm, and (d) Barrett-Joyner-Halenda pore size distribution curve spectra for the catalysts.
SamplesBET surface area/(m2·g–1)Pore diameter/nmPore volume/ (cm3·g–1)
10Fe/TiO2140.23.140.13
10Fe-1Cu/ TiO2135.83.340.14
10Fe-3Cu/TiO2126.53.130.12
10Fe-5Cu/TiO2118.53.310.13
10Fe-8Cu/TiO2112.43.240.12
10Fe-10Cu/TiO2106.03.310.11
Tab.1  BET specific surface area, pore size and pore volume of the catalysts
Fig.2  TEM and HRTEM images of (a) 10Fe/TiO2, (b) 10Fe-1Cu/TiO2, (c) 10Fe-3Cu/TiO2, (d) 10Fe-5Cu/TiO2, (e) 10Fe-8Cu/TiO2, and (f) 10Fe-10Cu/TiO2 catalysts, and (g) the corresponding element mapping images (Cu, Fe, O, and Ti) of 10Fe-8Cu/TiO2.
SamplesSurface atomic species/%
Cu+/CuFe3+/FeOS/(OL + OS)
10Fe/TiO249.727.3
10Fe-1Cu/ TiO238.943.729.1
10Fe-3Cu/TiO239.745.235.7
10Fe-5Cu/TiO248.646.437.9
10Fe-8Cu/TiO249.751.247.8
10Fe-10Cu/TiO241.249.341.2
Tab.2  Surface atomic species on the surface of the catalysts
Fig.3  XPS spectra of (a) Fe 2p, (b) Cu 2p, (c) O1s, and (d) Ti 2p for the catalysts.
Fig.4  (a) H2-TPR and (b) NO-TPD curves of the catalysts.
Fig.5  (a) NO conversion, (b) NH3 selectivity, (c) NH3 concentration for the catalysts; (d) the stability test of 10Fe-8Cu/TiO2 catalyst at 350 °C (Inset: antipoisoning performance of the 10Fe-8Cu/TiO2 catalyst at 350 °C (5 vol % H2O, 100 ppm SO2). Reaction conditions: [NO] = 350 ppm, [H2] = 2000 ppm, balance N2, total flow rate: 100 mL·min–1, GHSV = 38000 h –1, catalyst: 0.2 g).
Fig.6  In situ DRIFTS of 10Fe-8Cu/TiO2 catalyst: (a) adsorption spectra of NO on the catalyst at different temperatures; (b) Co-adsorption spectra of NO + H2 at different temperatures.
Fig.7  PDOS of NO adsorbed on (a) 10Fe/TiO2 and (b) 10Fe-8Cu/TiO2 surfaces; (c, d) the corresponding charge differential density (The pink area represents the accumulation of electrons, and the blue area represents a loss of electrons).
Fig.8  PDOS of NH3 adsorbed on (a) 10Fe/TiO2 and (b) 10Fe-8Cu/TiO2 surfaces; (c, d) the corresponding charge differential density (The pink area represents the accumulation of electrons, and the blue area represents a loss of electrons).
Fig.9  Energy potential and molecular configuration changes of (a) the *NO → *N + *O dissociation process, (b) the *NO + H → *NOH hydrogenation process and (c) the *HNO → *NO + *H dissociation process on the surface of 10Fe/TiO2 (black) and 10Fe-8Cu/TiO2 (red) catalysts (The IS, TS and FS are shown in the figure. The numbers in the figure are in units of Angstroms).
Fig.10  Schematic showing the pathway of NO formation on the surface of 10Fe/TiO2 (black) and 10Fe-8Cu/TiO2 (red).
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