Short communicationComparative study on sulfur poisoning of V2O5-Sb2O3/TiO2 and V2O5-WO3/TiO2 monolithic catalysts for low-temperature NH3-SCR
Graphic abstract
V2O5-Sb2O3/TiO2 monolithic NH3-SCR catalyst shows higher sulfur tolerance at 250 °C than the commercial V2O5-WO3/TiO2 mainly due to lower deposition of NH4HSO4.
Introduction
The nitrogen oxides (NOx) emitted from stationary and mobile source are important pollutants, which resulting in photochemical smog, acid rain, ozone depletion and greenhouse effects [1]. Among the developed deNOx technologies, the selective catalytic reduction of NO with NH3 (NH3-SCR) is an efficient method to remove NOx, and V2O5-WO3/TiO2 (VWTi) is a widely used catalyst for decades owing to its stability and high catalytic activity at 300–400 °C [2], [3]. The SCR unit is usually located upstream of the desulfurized and particulate control devices because the commercial catalyst is usually used in 350–400 °C. However, high concentrations of ash and SO2 could damage and deactivate the monolithic catalyst. When the SCR unit is located after cleaning and desulfurization with a lower reaction temperature, there is a strong need to develop low-temperature SCR catalysts, especially for flue gases from industry boilers and ship diesel engines [1]. Several V-free catalysts, including Mn- [4], [5], Cu- [6] and Ce-based catalysts [7], [8], have been widely researched for their catalytic performances at low temperatures (< 300 °C). However, the poor resistance to SO2 of those catalysts limits their application in industries [2], [9]. Nowadays, V-based catalysts with relative high loading of V2O5 are still a preferable choice for SO2-containing exhaust purification at low temperatures [10].
The predominant factor for sulfur poisoning varies at different temperatures. For NH3-SCR at high temperatures, sulfation of active metals is generally responsible for deactivation of catalysts. However, NH4HSO4 deposition on the catalysts surface is reported as the primary cause for the NH3-SCR deactivation at low temperatures in practical applications. The SO2 in sulfurous fuels can be oxidized into SO3, which further reacts with NH3 in stream to form NH4HSO4 [11]. Magnusson et al. [12] found that in the presence of both H2O and SO2, the V2O5-WO3/TiO2 monolithic catalyst did not show any signs of deactivation at temperatures above 300 °C, but at a lower temperature (250 °C) the catalytic performance for NOx reaction decreased with time. They ascribed such a decline to the formation of ammonium sulfate salts at low temperatures, which could cover parts of the active sites on the catalyst surface. Xi et al. [13] reported that the main deactivation reason at low temperature was physical poisoning by the formation of NH4HSO4, cutting off the NH3-SCR reaction, rather than the poisoning of active species. Therefore, one of the primary goals for industrialization is to develop low-temperature NH3-SCR catalysts with low NH4HSO4 deposition.
Recently, antimony (Sb) has attracted increasing attention for its good performance in the modification of V2O5/TiO2 catalyst. Phil et al. [14], [15] reported that Sb2O3 (2 wt.%) contained V2O5/TiO2 catalyst showed better NH3-SCR performance than other promoter (B, P and Cu) contained catalysts. Besides, the addition of Sb on Mn/TiO2 catalyst increased the low-temperature NH3-SCR activity by improving the reducibility and generating strong Lewis acid sites for NH3 desorption [16]. Meanwhile, the existence of Sb on Mn/TiO2 catalyst also exhibited high Na-resistance. In this study, V2O5 (2.7 wt.%)-Sb2O3 (2.0 wt.%)/TiO2 (V2.7Sb2Ti) and V2O5 (2.7 wt.%)-WO3 (4.0 wt.%)/TiO2 (V2.7W4Ti) monolithic catalysts were prepared. The V2.7Sb2Ti catalyst presented superior NH3-SCR activity and strong SO2 resistance, which could be a competitive catalyst for practical application, especially in high SO2 containing exhausts at low temperatures.
Section snippets
Catalyst synthesis
The V2.7Sb2Ti and V2.7W4Ti monolithic catalysts were prepared by an impregnation method. The V2.7Sb2Ti catalyst (the weight ratio of V2O5:Sb2O3:TiO2 = 2.7:2:95.3) was prepared by impregnating TiO2 power (DT51) in an aqueous solution of antimony acetate (0.5 mol L− 1) and ammonium metavanadate (1.1 mol L− 1). After stirring for 3 h, the solution was titrated with 15 wt.% ammonia hydroxide until the pH reached 9. After filtration, the resulting precipitates were dried in air for 24 h. The catalyst was
Results and discussion
Fig. 1a showed the NH3-SCR activities of V2.7Sb2Ti and V2.7W4Ti monolithic catalysts from 175 to 400 °C. The V2.7Sb2Ti exhibited higher NOx conversion within the whole temperature range. More importantly, it demonstrated a wide operation window with over 90% NOx conversion obtained from 225 to 375 °C, and even at 175 °C, 58% NOx conversion could be achieved. In contrast, the V2.7W4T only afforded an operation window from 275 to 350 °C with 90% NOx conversion. However, the NOx activities of the
Conclusions
Compared with V2O5-WO3/TiO2, V2O5-Sb2O3/TiO2 monolithic catalyst showed a broader temperature window (with exceeding 90% NOx conversion at 225–375 °C) and higher SO2 resistance at 250 °C. The deactivation of the catalysts at low temperatures was caused mainly by the deposition of NH4HSO4 on the catalyst surface. Lower SO2 oxidation to SO3 and higher reactivity of NH4HSO4 with NO led to a much lower accumulation of NH4HSO4 on the Sb2O3-modified catalyst and hereby better NH3-SCR performance in the
Acknowledgment
The authors gratefully acknowledge the financial support received from projects of the Ministry of Science and Technology of the People's Republic of China (Nos. 2015AA034603 and 2016YFC0205200) and Science and Technology Department of Zhejiang Province, PR China (No. 2015C31015).
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