Shaojun Liu1,2,3, Peidong Ji1, Dong Ye1, Ruiyang Qu1, Chenghang Zheng1, Xiang Gao 1

State Key Laboratory of Clean Energy Utilization, Zhejiang University, Hangzhou 310027, China
School of Energy and Power, Jiangsu University of Science and Technology, Zhenjiang 212003, China
Key Laboratory of Low-grade Energy Utilization Technologies and Systems (Chongqing University), Ministry of Education of China, Chongqing University, Chongqing 400044, China

Received: July 24, 2018
Revised: November 12, 2018
Accepted: December 11, 2018

Download Citation: ||  

Cite this article:

Liu, S., Ji, P., Ye, D., Qu, R., Zheng, C. and Gao, X. (2019). Regeneration of Potassium Poisoned Catalysts for the Selective Catalytic Reduction of NO with NH3. Aerosol Air Qual. Res. 19: 649-656.


  • The effect of K on SCR activity and the regeneration of catalyst were investigated.
  • Surface K species were removed in acid washing, and occupied acidic sites released.
  • Extra active components were added for CeO2 doping.
  • Poisoned catalysts were washed with H2SO4 solution and then doped with 5 wt.% CeO2.


In this study, we investigated the effect of potassium on the activity and regeneration of potassium-poisoned SCR catalysts. With the addition of potassium species, the NO conversion rate of the catalysts continuously decreased. After washing the poisoned catalysts with an H2SO4 solution or doping them with CeO2, the activity of the catalysts was improved to different extents. Acid washing almost completely removed the surface potassium species, freeing acidic sites to adsorb NH3, but it also potentially removed some of the active components, such as vanadia. CeO2 doping, on the other hand, added active components. Combining these two methods, the poisoned catalysts were washed with an H2SO4 solution and then doped with 5 wt.% CeO2. It was found that the level of activity could be restored to that of a fresh catalyst, and a conversion rate of over 90% was observed for NO between 300°C and 450°C, as the added CeO2 compensated for the active components lost during SCR reactions. Consequently, the above hybrid method shows high potential for regenerating commercial SCR catalysts.

Keywords: Selective catalytic reduction; Potassium; Deactivation; Regeneration; Ceria.


The selective catalytic reduction (SCR) of NOx with NH3 has been regarded as an effective method to control NOx emissions from stationary and mobile sources (Busca et al., 1998). The commercial SCR catalysts consist of TiO2 as support and V2O5-WO3 or V2O5-MoO3 as active components. They are shaped into honeycomb matrix because of the advantages such as low pressure drop, high geometric surface area, and resistance to deposition of dust (Lei et al., 2009).

The (co-)firing of biomass is a significant way to reduce the net CO2 emissions. However, high levels of alkali and alkaline earth metals, especially potassium, are present in the fly ash of the biomass fired systems. And potassium has been demonstrated to do harm to the SCR catalysts (Kamata et al., 1999; Moradi et al., 2003; Zheng et al., 2004, 2005; Due-Hansen et al., 2007; Castellino et al., 2009; Klimczak et al., 2010). Doping with alkali and alkaline earth metals results in a strong catalyst deactivation and the poisoning effect of alkali and alkaline earth metals is related to their basicity. The order is listed as K > Na > Ca > Mg (Klimczak et al., 2010). It is concluded that potassium preferentially coordinates to the Brønsted acid sites, which are responsible for the ammonia adsorption, thus decreasing their number and strength of the Brønsted acid sites. As a result, catalyst activity would be adversely affected. A deactivation of about 1% per day was found over monolith catalysts, which were exposed in a high-dust flue gas produced from straw-fired grate boiler (Zheng et al., 2005).

The cost of the catalysts is a major part of the total expense in an SCR system. Hence, it is important and necessary to regenerate the catalysts (Du et al., 2018; Wang et al., 2018a, b). Regeneration by washing with water followed by sulfation was not an optimal regeneration method due to the insufficient removal of the poison (Zheng et al., 2004). Washing with sulfuric acid can remove potassium accumulated on the surface and recover the catalytic activity (Khodayari and Odenbrand, 2001a, b; Zheng et al., 2004). However, active components such as vanadium and tungsten can also be removed through washing with sulfuric acid. So, it is necessary to compensate the loss of the active components. Recently, ceria-based catalysts have been investigated for SCR reactions because of the high oxygen storage capacity and excellent redox properties of CeO2 (Li et al., 2012; Hu et al., 2017; Huang et al., 2017; Jiang et al., 2017; Li et al., 2017; Yao et al., 2017; Chen et al., 2018; Jiang et al., 2018). We could also add ceria on the catalyst to compensate the loss of the active components.

In this work, potassium ions were doped on the commercial V2O5-WO3/TiO2 catalysts to simulate the poison effect. Then, a study of the regeneration of K-poisoned catalysts was presented. Specifically, loading different amount of ceria on the deactivated catalysts with or without sulfuric acid and deionized water washing have been investigated to show the commercial potential of ceria-involved regeneration method. 



The commercial honeycomb-type catalysts used in this investigation were obtained from RAGA Technology Co., Ltd. The catalysts contained about 1% V2O5 and 5% WO3 as active phase doped on a TiO2 support. The catalyst had a wall thickness of 1 mm and a channel pitch of 6 mm. The catalysts were cut into 25 mm × 20 mm × 20 mm blocks for poisoning of potassium and regeneration method tests.

ion of Catalysts

The catalysts doped with potassium were prepared by wet-impregnation method with aqueous solutions of KNO3. The prepared monolithic catalysts were immersed into 25 mL aqueous solutions with different concentration of KNO3. Then the samples were first dried at 110°C overnight and then calcined at 500°C for 5 h in a muffle furnace to form potassium oxide.

Regeneration of Deactivated Catalysts

Several blocks of deactivated catalysts (25 mm long monolithic segment) were washed in 1000 mL 0.5 M sulfuric acid (SA) solution for 120 min and then washed in 1000 mL deionized water for 15 min. In some cases, different concentrations of sulfuric acid (0.05 M, 0.1 M, 0.3 M, 0.5 M, 0.7 M) were used to optimize the washing process. The washing process was under continuous stirring. The temperature of the washing solution was kept at 50°C. After washing, different contents of CeO2 were loaded on the catalysts using the same method as potassium doping. Another regeneration method was that CeO2 was added on the deactivated catalysts without washing process. The catalysts were donated as xK-ySA-zCeO2. x represents the loading of potassium element (wt.%), y represents the concentration of SA (sulfuric acid) used for catalysts washing (M) and z represents the loading of CeO2 (wt.%) on the catalysts.


The activity tests for the reduction of NO by NH3 were carried out in a fixed bed quartz micro-reactor (inner diameter: 4 mm) with 0.2 g catalyst power of 250–380 µm in diameter. The feed gas mixture contained 1000 ppm NO, 1000 ppm NH3, 5 vol.% O2 and N2 as the balance gas. The total flow rate of the feed gas was 1000 mL min–1 and the GHSV was 183,000 h–1. The catalytic reaction was carried out with temperature ranging from 150°C to 450°C. The concentrations of NO and N2O before and after reaction were measured by an FTIR gas analyzer, the Gasmet DX4000. The NO conversion is defined a


where NOin and NOout stand for the NO concentration at the inlet and outlet, respectively.

Catalyst Characterization

The specific surface area and the textural properties (i.e., pore volume and average pore diameter) were measured by N2 adsorption and desorption experiments at liquid nitrogen temperature (–196°C) with Autosorb-1-C instrument (Quantachrome Instrument Corp.). The specific surface area was calculated by the Brunauer-Emmett-Teller (BET) method while the average pore diameter was calculated from the surface area and BET pore volume.

The X-ray diffraction (XRD) patterns were collected using a Panalytical X’pert Pro diffractometer equipped with Cu Ka radiation. The X-ray tube was operated at 40 kV and 40 mA.

The chemical composition of catalyst samples was analyzed by inductively coupled plasma-mass spectroscopy (ICP-MS; 7500a, Agilent) after the catalysts dissolved completely.

NH3-TPD tests were carried out on an AutoChem 2920 instrument provided by Micromeritics Corporation. NH3 signal was detected using a Hiden QIC20 mass spectrum instrument. 0.2 g catalyst powder was pretreated in He at 500°C for 30 min. After that, the sample was cooled to 100°C and exposed to a gas mixture of 5% NH3 in He for 30 min. Then the sample was flushed with pure He until signal was stabilized. The sample was then heated up to 700°C at a rate of 10°C min–1.

H2-TPR was also carried out in a quartz-tube reactor. 0.10 g catalyst powder was pre-treated at 200°C in N2 for 30 min. After that, the sample was cooled to room temperature and then heated to 700°C at a rate of 10°C min1 in a gas mixture of 5 vol.% H2 and Ar. The consumption of H2 was detected by a thermal conductivity detector (TCD).


Activity and Selectivity

Effect of Potassium Poisoning

Fig. 1 shows the activity of the fresh and potassium-loaded catalysts. For the fresh catalyst, the NO conversion increased as the temperature increased, which almost reached 100% at 350°C. Given that potassium was introduced, the NO conversion decreased. With the increase in the doping amount of potassium, catalyst activity continuously decreased. When the potassium loading amount reached 1%, the NO conversion of the catalyst was always below 30%. This is consistent with the result of Chen et al. (2011).

Fig. 1. NO conversion of the catalysts poisoned with different K loading amounts.Fig. 1. NO conversion of the catalysts poisoned with different K loading amounts.

Effect of Acid Washing

To regenerate the poisoned catalyst, the first step is to remove the accumulated K. Sulfuric acid was used as detergent combined with fresh water rinsing after the process. Different concentrations of sulfuric acid solutions were chosen and effect on NO conversion is depicted in Fig. 2. It is clear that with concentrated acid, poisoned catalyst is easily recovered, approaching its initial state. However, this effect was gradually weakened when the concentration increased from 0.05 M to 0.5 M. Specially, no obvious difference was observed for the catalysts treated with 0.5 M and 0.7 M H2SO4. As a result, 0.5 M H2SO4 was used in later section for acid washing. Moreover, the washing process also contributed to loss of active components, such as V and W. The negative effect of acid washing is shown in Fig. S1 in supporting information. The effect of washing time was also evaluated. It is evident that using diluted acid and short time could remove most of K and reduce the loss of V. However, as shown in Fig. 2, the diluted acid washing couldn’t totally recover the activity of the catalyst. On the other hand, after 2 h washing with 0.5 M H2SO4, 40% V of the catalyst was dissolved into the solution, resulting in the reduction of the activity, especially in lower temperatures (< 350°C). For this reason, it is necessary to load active components to compensate the loss.

Fig. 2. NO conversion of the catalysts regenerated with different concentrations of H2SO4 solution.Fig. 2. NO conversion of the catalysts regenerated with different concentrations of H2SO4 solution.

Effect of CeO2 Loading

The NO conversion of the K-poisoned and regenerated catalysts is presented in Fig. 3. The direct loading of 10% CeO2 to the deactivated catalyst could improve the activity, which was, however, much lower than that of the fresh catalyst. This is because potassium still remained on the catalyst and exerted a negative effect on the catalyst. Thus, removing potassium species constituted the first step to recover the activity of the deactivated catalyst. After washing with H2SO4 solution, an obvious enhancement in the high-temperature activity could be obtained, while the activity below 300°C remained almost unchanged. It should be noted that the activity of the regenerated catalyst washed with H2SO4 solution was still lower than that of the fresh one. That might be due to the loss of active components during the H2SO4 solution washing process. Therefore, various amounts of CeO2 were added to the deactivated catalysts after treatment by 0.5 M H2SO4 and deionized water. The NO conversion of 0.5K-0.5SA-3CeO2 catalyst is almost the same as that of the 0.5K-10CeO2 catalysts below 300°C. With temperature increasing, 0.5K-0.5SA-3CeO2 catalyst exhibited a better activity than that of 0.5K-10CeO2 catalyst. When the loading amount of CeO2 exceeded 5 wt.%, the activity of the regenerated catalysts almost restored to the level of the fresh one. Thus, it seems that washing with 0.5 M sulfuric acid solution and deionized water and then doping with 5 wt.% CeO2 is a good method to regenerate the K-poisoned catalysts.

Fig. 3. NO conversion of the catalysts regenerated with different cerium loading amounts.Fig. 3. NO conversion of the catalysts regenerated with different cerium loading amounts.

In order to investigate the adaptability of this regeneration method, catalyst with a higher potassium loading amount were chosen and tested. As illustrated in Fig. 4, it can be concluded that the amount of potassium had no obvious effect on the activity of the regenerated catalysts in the investigated range and the activity of the regenerated catalysts is almost the same as that of the fresh one. This indicated that 0.5 M H2SO4 and deionized water treatment could remove potassium species that interacted with the active sites, and 5 wt.% CeO2 additives could supply extra active sites to some extent.

Fig. 4. Effect of K content on the catalysts regenerated by washing and CeO2 modification.Fig. 4. Effect of K content on the catalysts regenerated by washing and CeO2 modification.

Selectivity of Regenerated Catalysts

In addition to NO conversion, N2O formation is also an important parameter to evaluate catalyst performance. Fig. 5 displays N2O formation in the SCR reactions. For the fresh and regenerated catalysts, the N2O concentration were fairly low (< 5 ppm) below 350°C. As the temperature increased, N2O concentration of the fresh catalyst rapidly increased up to 47 ppm at 450°C, while the N2O formation of the regenerated catalysts stayed below 17 ppm, suggesting a better selectivity than the fresh one. This phenomenon could be explained by the reduction of V and the addition of Ce, confirmed by Fig. S1 and Table 1. Since V2O5 has a strong ability to oxidize NH3 into N2O at higher temperatures (Chen et al., 2009), decrease of V2O5 could weaken this side reaction and improve the selectivity of SCR reaction.

Fig. 5. N2O formation of the catalysts regenerated by washing and CeO2 modification.Fig. 5. N2O formation of the catalysts regenerated by washing and CeO2 modification.

Table 1. Chemical composition, BET surface area, total pore volume, and average pore diameter of different samples.

Characterization of the Catalysts

Chemical Composition and BET Analysis

Table 1 shows the ICP-MS and BET results of the fresh and regenerated catalysts. It seems that no obvious variations could be observed in these catalysts, partly ruling out the possibility that physical properties mainly determined the activity of the catalysts. Instead, the variations in the chemical properties including acidity and redox constituted the main reason for enhanced activity of the catalysts after regeneration.

The ICP-MS results showed that the washing process could drastically remove potassium species over catalyst surface. At the same time, vanadia, as the active component, was also removed by a third with the content of tungsten remaining almost unchanged after the washing process.

Additionally, the measured Ce content was lower than the calculated value. This meant that there was loss of Ce during impregnation process.

XRD Analysis

XRD patterns of the series catalysts are shown in Fig. 6. All the catalysts presented anatase TiO2 phase with the absence of V2O5 and WO3 crystallites, indicating that V2O5 and WO3 were amorphous in structure on the TiO2 support (Lisi et al., 2004; Kustov et al., 2005; Zhang et al., 2009). Given the addition of 3% CeO2, no cubic CeO2 phase could be detect. This result indicated that ceria were highly dispersed and existed as an amorphous state. Further increasing the CeO2 loading amount to 5% or more, cubic CeO2 phase began to be observed, suggesting that CeO2 loading was beyond the theoretical monolayer coverage on the TiO2 support.

Fig. 6. XRD patterns of the (a) fresh; (b) 0.5K; (c) 0.5K-0.5SA; (d) 0.5K-10CeO2; (e) 0.5K-0.5SA-3CeO2; (f) 0.5K-0.5SA-5CeO2; (g) 0.5K-0.5SA-10CeO2.Fig. 6. XRD patterns of the (a) fresh; (b) 0.5K; (c) 0.5K-0.5SA; (d) 0.5K-10CeO2; (e) 0.5K-0.5SA-3CeO2; (f) 0.5K-0.5SA-5CeO2; (g) 0.5K-0.5SA-10CeO2.


According to previous studies, acidity plays an important role in the SCR reactions, since the first step is the adsorption of NH3 on the surface acidic sites of catalyst (Busca et al., 1998; Forzatti, 2001; Ye et al., 2018). NH3-TPD tests were carried out to investigate surface acidity of the series samples, and the results of which are illustrated in Fig. 7. The 0.5K and 0.5K-10CeO2 catalysts had several NH3 desorption peaks in the temperature region of 100–350°C, while the other catalysts possessed broad desorption peaks between 100°C and 450°C. The peaks near 170°C (Peak I) could be assigned to the desorption of physisorbed NH3, and the peaks around 270°C (Peak II) were attributed to NH3 on weakly acidic sites, while the peaks centering at 610°C (Peak III) linked to the strongly acidic sites (Guan et al., 2011; Li et al., 2012; Li et al., 2017; Yao et al., 2017). The quantity analysis of NH3-TPD is summarized in Table 2. For the 0.5K and 0.5K-10CeO2 catalysts, the presence of potassium caused the reduction of Peak II, which correlated with acidic sites, responsible for SCR activity (Forzatti, 2001). After washing process, abundant acidic sites were present, and NH3 could be adsorbed on the catalyst surface, reacting with NO. Besides, doping CeO2 could also in part enhance the acidity of the catalysts, which made 0.5K-0.5SA-5CeO2 catalyst had the same activity with the fresh one (Shi et al., 2017). That is consistent with SCR activity results in Fig. 3. Note that after washing and CeO2 modification, Peak I increased almost up to two times while Peak II reached about 80% of that of the fresh catalyst. It may be related to promoted SCR activity at low temperatures and inhibited NH3 oxidation at high temperatures.

Fig. 7. NH3-TPD curves of the (a) fresh; (b) 0.5K; (c) 0.5K-0.5SA; (d) 0.5K-10CeO2; (e) 0.5K-0.5SA-3CeO2; (f) 0.5K-0.5SA-5CeO2; (g) 0.5K-0.5SA-10CeO2.Fig. 7. NH3-TPD curves of the (a) fresh; (b) 0.5K; (c) 0.5K-0.5SA; (d) 0.5K-10CeO2; (e) 0.5K-0.5SA-3CeO2; (f) 0.5K-0.5SA-5CeO2; (g) 0.5K-0.5SA-10CeO2.

Table 2. Quantitative analysis of NH3-TPD and H2-TPR over the samples*.


The redox properties of the catalysts play an important role in the catalytic cycle of the SCR reactions (Topsoe, 1994; Topsoe et al., 1995; Putluru et al., 2009; Wang et al., 2018). The H2-TPR profiles and quantity analysis are shown in Fig. 8 and Table 2, respectively. The fresh catalyst showed a reduction peak located at 500°C, while the 0.5K sample presented a peak at 523°C. These peaks could be explained by the reduction of V5+ to V3+ (Tang et al., 2010; Chen et al., 2011; Guan et al., 2011). And it should be noted that the reduction peak shifted to higher temperatures after doping potassium, which is consistent with the results of Chen et al. (2011), showing that potassium doping exerted a negative effect on the catalyst redox properties. After H2SO4 washing process, a reduction peak at 485°C came out. This meant that washing with sulfuric acid solution and deionized water could remove potassium species and recover the redox ability of the catalysts. The reduction peaks shifted to higher temperature with the increasing loading amount of CeO2. Moreover, the adding of CeO2 slightly increased the consumption of H2, compared to 0.5K-0.5SA. This indicated that loading more Ce had a negative effect on the catalyst reducibility. Besides, XPS results shown in Fig. S2 confirmed that no obvious change in chemical state of V, W and Ti after acid washing or CeO2 modification. Combined with aforementioned results, it implied that improved SCR activity after acid washing and CeO2 adding could be ascribed to optimized acidic sites, which facilitate the low temperature SCR activity and inhibit high temperature NH3 oxidation.

Fig. 8. H2-TPR profiles of the (a) fresh; (b) 0.5K; (c) 0.5K-0.5SA; (d) 0.5K-10CeO2; (e) 0.5K-0.5SA-3CeO2; (f) 0.5K-0.5SA-5CeO2; (g) 0.5K-0.5SA-10CeO2.Fig. 8. H2-TPR profiles of the (a) fresh; (b) 0.5K; (c) 0.5K-0.5SA; (d) 0.5K-10CeO2; (e) 0.5K-0.5SA-3CeO2; (f) 0.5K-0.5SA-5CeO2; (g) 0.5K-0.5SA-10CeO2.


In this study, a new SCR catalyst regeneration method has been developed. Some conclusions are listed below.

  1. Potassium doping had a negative effect on the activity of the catalysts. The increase in the potassium loading amount continuously decreased the NO conversion rate of the catalysts. After washing the catalysts with an H2SO4 solution and deionized water, the SCR activity was partially restored. The further addition of CeO2 caused the regenerated catalysts to exhibit almost as much activity as the fresh ones.
  2. After washing the catalysts with an H2SO4 solution and deionized water, the potassium species were almost completely removed, benefical to NH3 adsorption. CeO2 was then added to compensate for the lost active species. These factors were primarily responsible for the recovery of the catalyst activity after regeneration. 


This work is supported by the National Key Research and Development Program of China (No. 2018YFC0213400), National Science Foundation of China (No. U1609212 and No. 51306079), and Open Fund of Key Laboratory of Ministry of Education of China (No. LLEUTS-201507).


Reference to any companies or specific commercial products does not constitute.

Don't forget to share this article 


Subscribe to our Newsletter 

Aerosol and Air Quality Research has published over 2,000 peer-reviewed articles. Enter your email address to receive latest updates and research articles to your inbox every second week.

Latest coronavirus research from Aerosol and Air Quality Research

2018 Impact Factor: 2.735

5-Year Impact Factor: 2.827

SCImago Journal & Country Rank

Aerosol and Air Quality Research (AAQR) is an independently-run non-profit journal, promotes submissions of high-quality research, and strives to be one of the leading aerosol and air quality open-access journals in the world.