Effect of SiO2 addition on NH4HSO4 decomposition and SO2 poisoning over V2O5–MoO3/TiO2–CeO2 catalyst
Graphical abstract
Introduction
The selective catalytic reduction (SCR) technology is applied for NOx emission control in both stationary and mobile sources like power plants and vehicles (Busca et al., 1998). V2O5/TiO2 catalyst promoted by WO3 or MoO3 is widely commercialized due to high performance in de-NOx activity and N2 selectivity (Topsøe et al., 1995, Choo et al., 2003). However, the oxidation of SO2 to SO3 is inevitable over V2O5-based catalysts (Svachula et al., 1993, Du et al., 2018). It is generally believed that gaseous SO3 will unavoidably react with reductant NH3 and H2O vapor to generate NH4HSO4, which will accumulate on the SCR catalyst surface in low temperature. The deposition of NH4HSO4 leads to the block of pore structures and coverage of active sites, consequently resulting in the drop of denitration efficiency (Guo et al., 2009). Therefore, the issues that SO2 oxidation and NH4HSO4 deposition on catalysts surface are gaining increased concerned.
As we know, the oxidation of SO2 to SO3 and NH4HSO4 decomposition could be affected by the chemical composition of SCR catalyst (Zhu et al., 2000, Xiao et al., 2019). Kobayashi et al. (2005) pointed out that the mixed oxide of TiO2 and SiO2 as support for V2O5-based catalyst could noticeably decrease the SO2 catalytic oxidation. The addition of GeO2 could reduce SO2 oxidation over V2O5/TiO2 catalyst, as reported by Morikawa et al. (1981). Dunn et al., 1999, Dunn et al., 1999 believed that SO2 catalytic oxidation was irrelevant to the VO bonds and the V–O–V bridge of polymeric polyvanadium species but mainly related to the V–O-M bonds. Ji et al. (2016) held the view that the VO bond played a critical role in the adsorption and oxidation of SO2. Furthermore, for the purpose to promote the sulfur resistance of SCR catalysts, many researchers had focused on improving the SO2 resistance and reducing the decomposition temperature of NH4HSO4 by catalyst component modification. The addition of Fe in V–Ti oxide catalyst showed excellent SO2 tolerance, as proposed by Zhu et al. (2020). Ye et al. (2018) confirmed that the NH4HSO4 decomposition could be enhanced by Nb and Sb decoration. Huang et al. (2003) proved that carbon-based catalysts would make differences in the reactivity behavior of NH4HSO4 with NO in low temperature.
Recently, the promotion of CeO2 on SCR activity over V-based catalysts has been investigated in depth (Cheng et al., 2014). Due to the better redox properties and acid-base properties, the addition of CeO2 appeared to be promising for low temperature SCR catalysts (Xu et al., 2009, Peng et al., 2014, Peng et al., 2014). Nevertheless, the catalytic performance of catalysts containing CeO2 would be inhibited easily in the present of SO2 and H2O at temperature below 300°C (Zhang et al., 2015, Gao et al., 2010). And CeO2 could be directly sulfated by SO2 under oxidizing conditions (Kullgren et al., 2014). It has been assumed that surface Ce(SO4)2, which is the most stable cerium sulfate species, will generate after SO2 poisoning (Liu et al., 2012). Therefore, both NH4HSO4 and cerium sulfate species would form over catalysts surface after being treated in simulate flue gas conditions and the catalytic activity in low temperature was unrecoverable (Xu et al., 2018). Zhang et al., 2015, Gao et al., 2010 found that CeO2 could facilitate the NH4HSO4 decomposition over V2O5–MoO3/CeO2–TiO2 catalyst, while cerium sulfate species would generate in the process of decomposition and the accumulation of cerium sulfate would delay the release of SO2 to higher temperature. Therefore, it is imperative to lower the sulfates stability over CeO2-modified catalysts surface for industrial application.
It is widely agreed that the decoration of SiO2 in Ti–Ce mixed catalysts can enlarge the specific surface area, which is helpful for the active component to be dispersed well on the support (Peng et al., 2013, Fang et al., 2014), as well as for deposited NH4HSO4. Besides, the enlargement of specific surface area means increased active sites could be accessible, which may affect the interaction between NH4HSO4 and catalyst surface. However, the details of NH4HSO4 decomposition behavior over Ti–Ce mixed catalysts doped with SiO2, was seldom discussed. Moreover, as mentioned before, the addition of SiO2 to SCR catalysts could lower the SO2/SO3 conversion, and the SO2 tolerance properties of SiO2-doped catalyst were enhanced (Ye et al., 2019). It was found that SO2 preferentially connected with CeO2 as sulfate species over CeO2–TiO2–SiO2 catalyst after SO2 poisoning (Peng et al., 2017), but the role SiO2 played in the poison effect was unclear.
Based on the discussion above, in this work, SiO2 was doped into V2O5–MoO3/TiO2–CeO2 catalyst to investigate the decomposition behavior of deposited NH4HSO4 and SO2 poisoning effect. V2O5–MoO3/TiO2 was also taken into consideration as a comparison. The samples were characterized by X-ray diffraction (XRD), N2 adsorption-desorption, X-ray photoelectron spectroscopy (XPS), temperature-programmed methods. The effect of SO2 poisoning over catalysts were revealed by SO2 oxidation tests, thermogravimetry-differential thermogravimetry (TG-DTG) measurement, in situ diffused reflectance infrared Fourier transform spectroscopy (DRIFTS) and SO2 temperature-programmed desorption (TPD).
Section snippets
Catalyst preparation
TiO2, TiO2–CeO2 and TiO2–SiO2–CeO2 were prepared as support by co-precipitation method. A certain amount of neutral silica sol or cerium nitrate was completely dissolved in the titanium sulphate solution. Then ammonia solution was dropwisely added into the mixture until the pH arrived at 10 under vigorous stirring. Continuing to stir for 3 hr and aging for 24 hr, the precipitates were filtered and washed thoroughly with deionized water. Dried at 110°C overnight and calcined in air at 500°C for
XRD and N2-physisorption
XRD patterns are showed in Fig. 1. For all samples, only anatase TiO2 is detected (Joint Committee on Powder Diffraction Standards (JCPDS) card 21–1272). This result indicates that V2O5, MoO3 and NH4HSO4 are highly dispersed on the anatase TiO2 surface. The weak diffraction peaks presented in VMo/Ti–Ce and VMo/Ti–Si–Ce samples demonstrate that the doping of SiO2 and CeO2 destroy the anatase TiO2 crystal structure to some extent and form inherently amorphous structure (Gao et al., 2010a),
Conclusions
The effect of SiO2 doped as support component of VMo/Ti–Ce on NH4HSO4 decomposition, together with SO2 poisoning over catalysts tested, is studied in this research. The addition of SiO2 into VMo/Ti–Ce catalyst could significantly increase the specific surface area and affect the interaction between catalyst surface atoms before and after NH4HSO4 deposition. The doping of SiO2 has little effect on the denitration performance of VMo/Ti–Ce catalyst, but VMo/Ti–Si–Ce catalyst exhibits better
Conflict of interest statement
We declare that we have no financial and personal relationships with other people or organizations that can inappropriately influence our work, there is no professional or other personal interest of any nature or kind in any product, service and/or company that could be construed as influencing the position presented in, or the review of, the manuscript entitled, “Effect of SiO2 addition on NH4HSO4 decomposition and SO2 poisoning over V2O5–MoO3/TiO2–CeO2 catalyst”.
Acknowledgments
This work was supported by the National Natural Science Foundation of China (No. 51576039).
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