Catalyst for selective catalytic reduction and preparation method therefor

Abstract

A catalyst for selective catalytic reduction is described. Cerium (III) sulfate (cerous sulfate) is bound to a support. The catalyst also includes vanadium oxide and cerium oxide.

Claims

1. A method for preparing a catalyst, the method consisting of: a) preparing a raw material catalyst, the raw material catalyst consisting essentially of a support material, vanadium oxide, antimony oxide, and cerium oxide, wherein the cerium oxide is cerium (IV) oxide, or a mixture of cerium (III) oxide and cerium (IV) oxide; b) heating the raw material catalyst to a temperature of 350 to 600 C. under air atmosphere; and c) treating the heated raw material catalyst with sulfur dioxide (SO.sub.2) to form cerium (III) sulfate on the surface of the support by reacting the cerium (IV) oxide of the heated raw material catalyst with the sulfur dioxide (SO.sub.2) and O.sub.2.

2. The method as claimed in claim 1, wherein in Step c), a concentration of sulfur dioxide at which the catalyst is treated is 50 to 1,000 ppm.

Description

BRIEF DESCRIPTION OF THE DRAWINGS

(1) FIG. 1 illustrates a process of denitrifying nitrogen oxides by a catalyst according to the present disclosure.

(2) FIGS. 2 to 8 illustrate the results according to Experimental Examples of the present disclosure.

DETAILED DESCRIPTION

(3) 1. Catalyst

(4) A catalyst of the present disclosure includes a support, vanadium oxide, and cerium oxide, and will be specifically described as follows.

(5) The support included in the catalyst of the present disclosure supports vanadium oxide as a catalyst active component. A material that may be used as the support is not particularly limited, but examples thereof include titanium oxide (TiO.sub.2), zirconium oxide (ZrO.sub.2), silicon dioxide (SiO.sub.2), tin dioxide (SnO.sub.2), alumina and composites thereof, and the like, and among them, titanium oxide (TiO.sub.2) is preferred.

(6) Cerium (III) sulfate (cerous sulfate) is bound to the support, and accordingly, the catalyst of the present disclosure including the same has excellent activity not only at a high temperature, but also at a low temperature, and the excellent activity will be described below. The cerium (III) sulfate is a salt to which a trivalent cerium ion (Ce.sup.3+) is bound, and is classified as a material different from cerium (IV) sulfate (ceric sulfate) to which a tetravalent cerium ion (Ce.sup.4+) is bound.

(7) The vanadium oxide included in the catalyst of the present disclosure is a catalyst active component. The vanadium oxides may be embodied as vanadium pentoxide (V.sub.2O.sub.5), vanadium dioxide (VO.sub.2), vanadium trioxide (V.sub.2O.sub.3), or vanadium monoxide (VO), and among them, the vanadium oxide included in the catalyst of the present disclosure is usually vanadium pentoxide.

(8) The cerium oxide included in the catalyst of the present disclosure is a cocatalyst which enhances the activity of the vanadium oxide which is a catalyst active component. Cerium oxides may be embodied as cerium (III) oxide (Ce.sub.2O.sub.3), or cerium (IV) oxide (CeO.sub.2), and the cerium oxide included in the catalyst of the present disclosure is the cerium (III) oxide and/or the cerium (IV) oxide.

(9) This catalyst of the present disclosure includes a support to which cerium (III) sulfate is bound, and thus has excellent activity not only at a high temperature, but also at a low temperature, and the excellent activity will be described with reference to FIG. 1 as follows.

(10) FIG. 1 schematically illustrates the process of denitrifying the nitrogen oxide by the catalyst of the present disclosure, which includes a support to which cerium (III) sulfate is bound. When cerium (III) sulfate is bound to the surface of a support as in the catalyst of the present disclosure, a denitrification rate (reduction rate) of nitrogen oxides at a low temperature may be increased as the activity of the catalyst is enhanced due to an increase in reaction acid sites of the catalyst. Further, cerium (III) sulfate bound to the surface of the support may suppress a poisoning substance ammonium bisulfate from being adsorbed, thereby minimizing the poisoning of the catalyst. In the present disclosure, the reaction acid site of the catalyst may be defined as a site where a reducing agent adsorbed on the surface of the catalyst reacts with nitrogen oxides to remove the nitrogen oxides.

(11) Meanwhile, the catalyst of the present disclosure may further include antimony oxide as a cocatalyst in consideration of the activity of the catalyst. Antimony oxides may be embodied as antimony trioxide (Sb.sub.2O.sub.3), antimony tetroxide (Sb.sub.2O.sub.4), or antimony pentoxide (Sb.sub.2O.sub.5), and among them, the antimony oxide included in the catalyst of the present disclosure is usually antimony trioxide (Sb.sub.2O.sub.3).

(12) This catalyst of the present disclosure may exhibit a denitrification efficiency of 90% or more when denitrifying nitrogen oxides at a low temperature, preferably 220 to 300 C., and more preferably 225 to 250 C. in the presence of a reducing agent (for example, ammonia).

(13) 2. Method for Preparing Catalyst

(14) In order to prepare the catalyst of the present disclosure described above, first, a raw material catalyst including a support, vanadium oxide, and cerium oxide is prepared. In this case, it is preferred that antimony oxide is further included in the raw material catalyst.

(15) Next, the prepared raw material catalyst is heated to a temperature of 350 to 600 C. Specifically, it is preferred that the raw material catalyst is heated to a temperature of 400 to 500 C., and the heating method is not particularly limited as long as the method is publicly known in the art.

(16) Finally, the heated raw material catalyst is treated with sulfur dioxide (SO.sub.2) to form cerium (III) sulfate on the surface of the support. That is, cerium (IV) oxide among the cerium oxides is reacted with sulfur dioxide to form cerium (III) sulfate. A reaction of forming the cerium (III) sulfate may be expressed as the following reaction formula.
2CeO.sub.2+3SO.sub.2+O.sub.2.fwdarw.Ce.sub.2(SO.sub.4).sub.3Reaction Formula

(17) Here, when the heated raw material catalyst is treated with sulfur dioxide (SO.sub.2), the concentration of sulfur dioxide (SO.sub.2) at which the raw material catalyst is treated is not particularly limited. However, a preferred technique includes that the raw material catalyst is treated with sulfur dioxide (SO.sub.2) at 50 to 100 ppm such that the formation of cerium (III) sulfate is facilitated.

(18) As described above, the catalyst of the present disclosure is prepared by a simple method for treating a raw material catalyst with sulfur dioxide (SO.sub.2) to modify the surface of the raw material catalyst. Therefore, when a catalyst is prepared by the preparation method of the present disclosure, it is possible to economically provide a catalyst having an excellent denitrification rate of nitrogen oxides not only at a high temperature, but also at a low temperature.

(19) Hereinafter, the present disclosure will be described in detail through Examples, but the following Examples and Experimental Examples only exemplify one form of the present disclosure, and the scope of the present disclosure is not limited by the following Examples and Experimental Examples.

Example 1

(20) A catalyst was prepared by heating a raw material catalyst, which is composed of 86 wt % of titanium oxide (support), 2 wt % of vanadium oxide (catalyst active component), 2 wt % of antimony oxide (cocatalyst), and 10 wt % of cerium oxide (cocatalyst), to 400 C. (10 C./min) under the air atmosphere. Then, the raw material catalyst was treated with sulfur dioxide at 500 ppm for 1 hour.

Example 2

(21) A catalyst was prepared in the same manner as in Example 1, except that the raw material catalyst was warmed to 500 C. before being treated with sulfur dioxide.

Comparative Example 1

(22) The raw material catalyst in Example 1 was applied as it was.

Comparative Example 2

(23) A catalyst was prepared in the same manner as in Example 1, except that the raw material catalyst was warmed to 180 C. before being treated with sulfur dioxide.

Comparative Example 3

(24) A catalyst was prepared in the same manner as in Example 1, except that the raw material catalyst was warmed to 300 C. before being treated with sulfur dioxide.

Experimental Example 1: Analysis of X-Ray Absorption Near Edge Structure (XANES) of Catalyst

(25) The beam line at the Pohang Accelerator Laboratory was used to absorb X-ray on the surfaces of the catalysts prepared in Examples 1 and 2 and Comparative Examples 1 to 3 and measure the electron shift movement variation (3d.fwdarw.4f orbital shift) of the surfaces. The total electron yield was obtained and is shown in FIG. 2.

(26) Referring to FIG. 2, it can be confirmed that for the catalysts in Examples 1 and 2 according to the present disclosure, the peak shift occurred from Ce.sup.4+ to Ce.sup.3+. It was concluded that the peak shift occurred because, as the catalyst was treated with sulfur dioxide, cerium (III) sulfate was formed on the surfaces of the catalysts in Examples 1 and 2, and that, as a result, the amount of Ce.sup.3+ was increased.

(27) Meanwhile, for the catalyst of Comparative Example 1, which was not treated with sulfur dioxide, and the catalysts of Comparative Examples 2 and 3, which were heated to 180 C. and 300 C., and then treated with sulfur dioxide, the peak shift did not occur. From the results, it can be seen that the catalyst temperature before the catalyst is treated with sulfur dioxide acts as an important factor in forming cerium (III) sulfate.

Experimental Example 2: Ce3+ XPS Analysis of Catalyst

(28) The Ce.sup.3+ ratios of the catalysts prepared in Example 2 and Comparative Example 1 were measured by using X-ray photoelectron spectroscopy (PHI 5800 ESCA), and the results are shown in FIG. 3.

(29) Referring to FIG. 3, it can be confirmed that the catalyst (Ce.sup.3+ ratio: 47.16%) in Example 2 according to the present disclosure has a higher Ce.sup.3+ ratio than the catalyst (Ce.sup.3+ ratio: 41.35%) in Comparative Example 1. This result appears to be because, as the catalyst was treated with sulfur dioxide, cerium (III) sulfate was formed on the surface of the catalyst in Example 2, increasing the amount of Ce.sup.3+.

Experimental Example 3: Measurement 1 of Denitrification Rate of Nitrogen Oxides

(30) The catalysts prepared in Examples 1 and 2 and Comparative Examples 1 and 3 were each loaded into a fixed-bed catalytic reactor, the denitrification rates of the catalysts depending on the temperature were measured by a gas analyzer. The results are shown in FIG. 4. In this case, the denitrification reaction conditions were as follows. Reducing agent: NH.sub.3 800 ppm Concentration of nitrogen oxides (NO.sub.x): 800 ppm Injection concentration of sulfur dioxide (SO.sub.2): 500 ppm, Injection of 3 vol % of oxygen (O.sub.2) and 6 vol % of water (H.sub.2O) Space Velocity (SV): 60,000 h.sup.1

(31) Referring to FIG. 4, it can be confirmed that the catalysts in Examples 1 and 2 according to the present disclosure had a better denitrification rate than those of the catalysts in Comparative Examples 1 and 3 at a low temperature (specifically 150 to 250 C.).

Experimental Example 4: Measurement 2 of Denitrification Rate of Nitrogen Oxides

(32) The catalysts prepared in Examples 1 and 2 and Comparative Example 3 were each loaded into a fixed-bed catalytic reactor, the denitrification rates of the catalysts at 225 C. over time were measured by a gas analyzer. The results are shown in FIG. 5. In this case, the denitrification reaction conditions were as follows. Reducing agent: NH.sub.3 800 ppm Concentration of Nitrogen Oxides (NO.sub.x): 800 ppm Injection concentration of sulfur dioxide (SO.sub.2): 500 ppm, Injection of 3 vol % of oxygen (O.sub.2) and 6 vol % of water (H.sub.2O) Space Velocity (SV): 60,000 h.sup.1

(33) Referring to FIG. 5, it can be seen that the catalysts in Examples 1 and 2 according to the present disclosure had a smaller decrease in denitrification rate of the catalyst over time than the catalyst in Comparative Example 3. The result supports a conclusion that, from the catalysts in Examples 1 and 2, production of poisoning substances was minimized compared to the catalyst in Comparative Example 3. As a result, the lifetime thereof is expected to improve.

Experimental Example 5: NH3 Analysis of Catalyst

(34) The catalysts prepared in Example 2 and Comparative Example 1 were each loaded into a TPD (Temperature Programmed Desorption) reactor, an NH.sub.3 gas was injected into the reactors at normal temperature for 1 hour to adsorb NH.sub.3 on the surfaces of the catalysts. Then the catalysts were purged to analyze the amount of NH.sub.3 desorbed depending on the temperature by means of a Mass analyzer. The results are shown in FIG. 6.

(35) Referring to FIG. 6, it can be seen that the catalyst in Example 2 according to the present disclosure had a higher amount of NH.sub.3 desorbed than the catalyst in Comparative Example 1. It was concluded from this result that the catalyst in Example 2 had a higher amount of NH.sub.3 adsorbed due to an increase in acid sites than that in Comparative Example 1, and the increase in amount of NH.sub.3 adsorbed resulted in an effect of improving the denitrification rate.

Experimental Example 6: NO Analysis of Catalyst

(36) The catalysts prepared in Example 2 and Comparative Example 1 were each loaded into a TPD (Temperature Programmed Desorption) reactor, an NO gas was injected into the reactors at normal temperature for 1 hour to adsorb NO on the surfaces of the catalysts. Then, the catalysts were purged to analyze the amount of NO desorbed and the amount of NO adsorbed in the catalyst to be oxidized into NO.sub.2 depending on the temperature by means of a Mass analyzer. The results are shown in FIG. 7.

(37) Referring to FIG. 7, it can be confirmed that the catalyst in Example 2 according to the present disclosure had a higher ratio of NO.sub.2 than the catalyst in Comparative Example 1. The increase in ratio of NO.sub.2 leads to an effect of improving the denitrification rate.

Experimental Example 7: FT-IR Analysis of Catalyst

(38) A diffuse reflectance infrared Fourier transform spectroscopy (DRIFTS) was filled with the catalysts in Example 2 and Comparative Example 1, respectively, and then NH.sub.3 was injected into the spectroscopy to analyze reaction acid sites (Brnsted and Lewis acid sites) on the surfaces of the catalysts. The results are shown in FIG. 8.

(39) Referring to FIG. 8, it can be confirmed that the catalyst in Example 2 according to the present disclosure had a more increased amount of reaction acid sites than the catalyst in Comparative Example 1. It is concluded that this result is because the amount of the reaction acid sites on the surface of the catalyst was increased by Ce.sup.3+ of cerium (III) sulfate bound to the catalyst surface (specifically, support surface) in Example 2.

(40) The catalyst according to the present disclosure has excellent catalytic activity at a low temperature because cerium (III) sulfate is bound to a support. Therefore, when nitrogen oxides are decomposed by applying the catalyst of the present disclosure, excellent denitrification efficiency may be obtained not only at a high temperature, but also at a low temperature. Further, production of poisoning substances may also be minimized.