Combination of a Zeolite-Based SCR Catalyst with a Manganese-Based SCR Catalyst in the Bypass
20200332691 ยท 2020-10-22
Inventors
- Nicola Soeger (Nidderau, DE)
- Andrea DE TONI (Hanau, DE)
- Fei Wen (Kahl am Main, DE)
- Stephan Malmberg (Frankfurt, DE)
Cpc classification
F01N13/087
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N2560/06
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N2610/10
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N3/2066
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N2370/04
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N3/208
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N3/2053
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N3/035
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F01N2900/1404
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
International classification
Abstract
The invention relates to an exhaust-gas aftertreatment system for selective catalytic reduction with a plurality of SCR catalytic converters, which exhaust-gas aftertreatment system is able to reduce NOx in a large temperature range and can store SOx. The invention further relates to a method for treating an exhaust gas flow, in which method the exhaust-gas aftertreatment system according to the invention is used. The system comprises a high-temperature SCR catalyst for temperature ranges between 250 C. and 750 C. and a low-temperature SCR catalyst arranged downstream thereof for temperature ranges between 60 C. and less than 250 C. There is a reductant supply system directly upstream of the high-temperature SCR catalyst. The high-temperature SCR catalyst is designed to reduce NOx in exhaust gas that has a temperature above a temperature threshold value and to store SOx in the temperature range below the threshold value. The low-temperature SCR catalyst reduces NOx in the temperature range below the threshold value. In each case, the exhaust gas flows through the high-temperature SCR catalyst. An exhaust-gas bypass valve or flow control valve is arranged directly upstream of the low-temperature SCR catalyst. If the temperature of the exhaust gas is greater than or equal to the temperature threshold value, the exhaust gas is completely conducted past the low-temperature SCR catalyst. The high-temperature SCR catalyst advantageously contains a molecular sieve as a catalytically active layer, and the catalytically active layer of the low-temperature SCR catalyst is preferably a manganese-containing mixed oxide.
Claims
1. An exhaust gas aftertreatment system coupled to an internal combustion engine in such a way that it receives the exhaust gas flow, comprising a selective catalytic reduction catalyst for medium to high temperature ranges (HT-SCR), wherein the medium temperature range comprises temperatures of 250 C. to less than 450 C. and the high temperature range comprises temperatures of 450 C. to 750 C., which catalyst is designed both to reduce NOx in an exhaust gas having a temperature above a temperature threshold value, and to store the SOx contained in the exhaust gas across the temperature range of the exhaust gas, which is below a temperature threshold value, a reductant supply system arranged directly upstream of the HT-SCR, a low-temperature SCR (TT-SCR) arranged downstream of the HT-SCR, wherein the low temperature range comprises temperatures of 60 C. to less than 250 C., and wherein the TT-SCR is designed to reduce NOx in an exhaust gas having a temperature below a temperature threshold value, a temperature sensor arranged directly downstream of the HT-SCR and measuring the temperature of the exhaust gas flow exiting such HT-SCR, an exhaust gas bypass and/or flow control valve designed to conduct the exhaust gas flow in its entirety past the TT-SCR if such exhaust gas flow has a temperature greater than or equal to a temperature threshold value, wherein the exhaust gas bypass and/or flow control valve is arranged directly upstream of the TT-SCR.
2. The exhaust gas aftertreatment system according to claim 1, wherein the HT-SCR is present in the form of a catalytically active layer on a carrier substrate, wherein the catalytically active layer is a molecular sieve selected from an aluminosilicate having a SAR of 5-50 and a silicon aluminum phosphate (SAPO) having an (Al+P)/Si value of 4-15 is selected, wherein the molecular sieve contains 1-10% by weight of a transition metal selected from Fe, Cu, and mixtures thereof, calculated as Fe.sub.2O.sub.3 and CuO respectively, based on the total weight of the molecular sieve, and wherein the molecular sieve contains alkali metal and alkaline earth metal cations selected from Li, Na, K, Rb, Cs, Mg, Ca, Sr, Ba, and mixtures thereof in a total amount of 1% by weight, calculated in the form of the pure metals and based on the total weight of the molecular sieve, and wherein the molecular sieve contains the metals Co, Mn, Cr, Zr and Ni in a total amount of 1% by weight, calculated in the form of the pure metals and based on the total weight of the molecular sieve.
3. The exhaust gas aftertreatment system according to claim 2, wherein the molecular sieve is selected from small-pore zeolites having a maximum pore size of eight tetrahedral atoms and beta zeolite.
4. The exhaust gas aftertreatment system according to claim 2, wherein the molecular sieve is an Fe BEA having a SAR of 10 to 35, an alkali metal content of 0 to 0.7% by weight, calculated as pure metals, and an Fe content of 3 to 9% by weight, calculated as Fe.sub.2O.sub.3, wherein the alkali metal and Fe contents are each based on the total weight of the zeolite.
5. The exhaust gas aftertreatment system according to claim 2, wherein the molecular sieve is a Cu CHA having a SAR of 10 to 35, an alkali metal content of 0 to 0.7% by weight, calculated as pure metals, and a Cu content of 1 to 7% by weight, calculated as CuO, wherein the alkali metal and Cu contents are each based on the total weight of the zeolite.
6. The exhaust gas aftertreatment system according to claim 1, wherein the TT-SCR is a monolithic flow-through substrate with a manganese-containing coating as catalytically active layer.
7. The exhaust gas aftertreatment system according to claim 6, wherein the manganese-containing coating is a manganese-containing mixed oxide selected from mixed oxides of the general formula Mn.sub.aMe.sub.1-aO.sub.b, where Me is one or more elements from the group Fe, Co, Ni, Cu, Zr, Nb, Mo, W, Ag, Sn, Ce, Pr, La, Nd, Ti and Y and where a=0.02-0.98 and b=1.0-2.5, mixed oxides of the general formula Mn.sub.wCe.sub.xMe.sub.1-w-xO.sub.y, where Me is one or more elements from the group Fe, Co, Ni, Cu, Zr, Nb, Mo, W, Ag, Sn, Pr, La, Nd, Ti and Y and where w=0.02-0.98, x=0.02-0.98 and y=1.0-2.5, spinels of the general formula MnMe.sub.2O.sub.4 or MeMn.sub.2O.sub.4, where Me is Fe, Al, Cr, Co, Cu or Ti.
8. The exhaust gas aftertreatment system according to claim 1, and further comprising a second reductant supply system arranged directly upstream of the TT-SCR.
9. The exhaust gas aftertreatment system according to claim 1, wherein the reductant supply system contains a) a reductant source, b) a reductant pump, and c) a reductant dispenser or a reductant injector.
10. The exhaust gas aftertreatment system according to claim 1, wherein an oxidation catalyst is located directly upstream of the reductant supply system located directly upstream of the HT-SCR.
11. The exhaust gas aftertreatment system according to claim 9, wherein a second HT-SCR is located between the HT-SCR and the temperature sensor.
12. The exhaust gas aftertreatment system according to claim 9, wherein a catalytically coated diesel particulate filter (CDPF) is located between the oxidation catalyst and the reductant supply system.
13. The exhaust gas aftertreatment system according to claim 9, wherein one or more HT-SCRs are arranged upstream of the oxidation catalyst and the reductant supply system is located directly upstream of the the HT-SCR that is closest to the internal combustion engine.
14. The exhaust gas aftertreatment system according to claim 1, wherein an ammonia slip catalyst is arranged downstream of the TT-SCR.
15. A method for treating an exhaust gas flow, comprising: providing an exhaust gas aftertreatment system comprising an SCR catalyst for medium to high temperatures (HT-SCR), a low-temperature SCR (TT-SCR) arranged downstream of the SCR for medium to high temperatures, a temperature sensor arranged directly downstream of the HT-SCR and an exhaust gas bypass and/or flow control valve arranged directly upstream of the low-temperature SCR, wherein the SCR catalyst for medium to high temperatures, wherein the medium temperature range comprises temperatures of 250 C. to less than 450 C. and the high temperature range comprising temperatures of 450 C. to 750 C., is designed both a) to reduce NOx in an exhaust gas having a temperature above a temperature threshold value, and b) to store the SOx contained in the exhaust gas across the temperature range of the exhaust gas which is below a temperature threshold value, and the low-temperature SCR is designed to reduce NOx in an exhaust gas having a temperature below a temperature threshold value, wherein the low temperature range comprises temperatures of 60 C. to less than 250 C., and wherein the temperature sensor measures the temperature of the exhaust gas flow exiting the HT-SCR, and wherein the exhaust gas bypass and/or flow control valve is designed to conduct the exhaust gas flow in its entirety past the low-temperature SCR, if such exhaust gas flow has a temperature greater than or equal to a temperature threshold value, storing the SOx contained in the exhaust gas in the HT-SCR, reducing NOx in an exhaust gas flow with the low-temperature SCR catalyst, if a temperature of the exhaust gas flow is within a low temperature range; conducting the exhaust gas stream in its entirety past the low-temperature SCR, if such exhaust gas flow has a temperature greater than or equal to a temperature threshold value, and reducing NOx in an exhaust gas flow with the SCR catalyst for normal to high temperatures, if the temperature of the exhaust gas flow is within a normal to high temperature range.
Description
[0125]
[0126] In the embodiment according to
[0127]
[0128]
[0129]
[0130]
[0131]
[0132]
[0133]
[0134] The valve position according to
T.sub.actualT.sub.min<T.sub.Thd
T.sub.actualR.sub.min<T.sub.Thd
[0135] In this case. [0136] T.sub.actual=actual temperature of the HT-SCR [0137] T.sub.min=minimum operating temperature of the HT-SCR [0138] T.sub.Thd=temperature threshold value
[0139] As long as the actual temperature, i.e., the factual temperature of the HT-SCR, is below the temperature threshold value, the exhaust gas is conducted through the TT-SCR after exiting the HT-SCR, regardless of whether or not the minimum operating temperature of the HT-SCR has already been reached.
[0140]
T.sub.actual>T.sub.minT.sub.Thd
[0141] As soon as the temperature of the HT-SCR is greater than its minimum operating temperature and is greater than or equal to the temperature threshold value, the bypass valve is closed. After exiting the HT-SCR, the exhaust gas flow is then conducted past the TT-SCR.
[0142] If a flow valve or a combination of exhaust gas bypass and flow valve is exclusively used, conditions between 0% and 100% opening of the flow valve can be described by the condition
T.sub.actual>T.sub.min<T.sub.Thd
[0143] In this condition, the actual temperature of the HT-SCR is greater than its minimum operating temperature but less than the temperature threshold value. In this case, a proportionality factor which indicates the degree of opening of the flow valve can be determined from (T.sub.ThdT.sub.actual). In this case, the following boundary condition applies:
[0144] If
T.sub.actualT.sub.min and T.sub.ThdT.sub.actual0,
the bypass valve is 0% open, which is equivalent to 100% closed.
[0145]
[0146]
[0147]
[0148] At temperatures below the HT-SCR minimum temperature and thus also below the threshold value (EOP_01), no SO.sub.2 breakthrough can be observed for the test duration, which means good protection for the TT-SCR.
[0149] By increasing the temperature and/or the space velocity, the SO.sub.x trap efficiency decreases somewhat. However, since in this case the NO.sub.x conversion can be 100% (see
[0150]
[0151]
[0152]
EMBODIMENTS
Embodiment 1: HT-SCR1=V SCR
[0153] a) A commercially available titanium dioxide in anatase form doped with 5% by weight silica was dispersed in water, and vanadium dioxide (VO.sub.2) and tungsten trioxide (WO.sub.3) were subsequently added to such an amount that a catalyst of the composition 88.10% by weight TiO.sub.2, 4.60% by weight SiO.sub.2, 3.00% by weight V.sub.2O.sub.5, 4.30% by weight WO.sub.3 results. The mixture was stirred thoroughly and finally milled in a commercially available agitator bead mill. [0154] b) The dispersion obtained according to a) was coated onto a commercially available ceramic flow-through substrate with a volume of 0.5 l and a cell number of 62 cells per square centimeter at a wall thickness of 0.17 mm over its entire length with a washcoat loading of 160 g/l. Subsequently, drying took place at 90 C., and calcination took place at 600 C. for 2 hours. The catalyst obtained in this way is referred to below as HT-SCR1.
Embodiment 2: HT-SCR2=Fe SCR
[0155] a) A commercially available BEA-type zeolite with a SAR of 25 is mixed in water with a quantity of Fe(NO.sub.3).sub.3 corresponding to an iron content of 4.5% by weight (based on the iron-containing zeolite and calculated as Fe.sub.2O.sub.3) and stirred overnight. [0156] b) The dispersion obtained according to a) was coated onto a commercially available ceramic flow-through substrate with a volume of 0.5 l and a cell number of 62 cells per square centimeter at a wall thickness of 0.17 mm over its entire length with a washcoat loading of 220 g/l. The catalyst obtained (hereinafter referred to as HT-SCR2) is dried at 90 C., then calcined step-by-step in air at 350 C. and at 550 C.
Embodiment 3: HT-SCR3=Cu SCR
[0157] a) A commercially available CHA-type zeolite with a SAR of 30 is mixed in water with a quantity of CuSO.sub.4 corresponding to a copper content of 3.7% by weight (based on the copper-containing zeolite and calculated as CuO) and stirred overnight. [0158] b) The dispersion obtained according to a) was coated onto a commercially available ceramic flow-through substrate with a volume of 0.5 l and a cell number of 62 cells per square centimeter at a wall thickness of 0.17 mm over its entire length with a washcoat loading of 220 g/l. The catalyst obtained (hereinafter referred to as HT-SCR3) is dried at 90 C., then calcined step-by-step in air at 350 C. and at 550 C.
Embodiment 4: Determination of DeNOx Activity:
[0159] b) The DeNOx activity of the catalysts HT-SCR1 to HT-SCR3 was tested in a laboratory model gas system under the conditions given in the table below.
TABLE-US-00001 Gas/parameter Concentration/conditions NH.sub.3 1100 ppm NO 1000 ppm H.sub.2O 5% O.sub.2 10% N2 Remainder Temperature Cooling step-by-step 550 to 200 C. Space velocity 60.000 h.sup.1
[0160] During the measurement, the nitrogen oxide concentrations of the model gas were detected after flowing through the HT-SCR catalyst by means of FTIR (Fourier transform infrared spectrometry). The nitrogen oxide conversion, based on the ratio of NH.sub.3 to NO, over the catalyst for each temperature measuring point was calculated as follows from the known metered nitrogen oxide contents, which were verified during conditioning at the beginning of the respective test run with a pre-catalyst exhaust gas analysis, and the measured post-catalyst nitrogen oxide contents.
where
[0161] U.sub.NOx nitrogen oxide conversion
[0162] C.sub.Output concentration of the nitrogen oxides after flowing through the HT-SCR catalyst
[0163] C.sub.Input concentration of the nitrogen oxides before flowing through the HT-SCR catalyst
C.sub.Input/Output(NO.sub.x)=C.sub.Input/Output(NO)+C.sub.Input/Output(NO.sub.2)+C.sub.Input/Output(N.sub.2O)
[0164] The nitrogen oxide conversion values U.sub.NOx [%] obtained were applied as a function of the pre-catalyst temperature measured to evaluate the SCR activity of the materials investigated. This is shown in
TABLE-US-00002 TABLE 1 Nitrogen oxide conversion values of the three HT-SCR catalysts according to Exemplary Embodiments 1 to 3 U.sub.NOx [%] T [ C.] HT-SCR1 HT-SCR2 HT-SCR3 200 26.13 28.36 85.71 250 71.79 62.29 99.41 300 95.17 85.48 100.07 350 98.58 94.55 100.07 400 98.87 97.98 99.76 450 97.76 99.29 96.79 500 92.03 99.44 90.65 550 69.13 96.20 83.03
Embodiment 5: Analysis of Cu SCR: SO.SUB.x .Trap Function and HT-SCR:
[0165] The investigations of the HT-SCR3 with regard to its suitability as SCR catalyst for the medium to high temperature range and at the same time its suitability as SO.sub.x trap in the working range of the TT-SCR were carried out on the engine test bench. The catalyst volume used corresponded to the factor 2.26 of the engine cubic capacity or displacement. Customary analysis was used as analysis. For the NO.sub.x conversion determination, the pre-SCR and post-SCR NO.sub.x concentrations were measured by means of CLDs (chemiluminescence detectors). The conversion was calculated analogously to Example 4.
where
[0166] U.sub.NOx nitrogen oxide conversion
[0167] C.sub.Output concentration of the nitrogen oxides after flowing through the HT-SCR catalyst
[0168] C.sub.Input concentration of the nitrogen oxides before flowing through the HT-SCR catalyst
[0169] The SO.sub.x input and output concentrations were measured as SO.sub.2 by a mass spectrometer each at the DPF output and SCR output. The experiments were carried out in stationary operating mode. For this purpose, three different operating points were selected which differ with regard to their SCR inlet temperature and the exhaust gas mass flow or the SCR space velocity (GHSV or SV).
[0170] GHS stands for gas hourly space velocity and SV stands for space velocity.
[0171] Commercially available urea solution was used as reductant. An amount corresponding to an ammonia/NOX ratio of 1.2 was metered.
[0172] Table 2 compiles the points. Here, EOP stands for engine operating point.
TABLE-US-00003 TABLE 2 SCR inlet temperature and SCR space velocity for three EOPs examined T SCR in [ C.] SV [h.sup.1] EOP_01 190 7700 EOP_02 260 23100 EOP_03 260 34000
[0173] EOP_01 represents an operating point at which the exhaust gas temperature is below the threshold value and at the same time below the minimum temperature of the HT-SCR.
[0174] Wth regard to their temperature, EOP_02 and EOP_03 are above the minimum temperature.
[0175] For the sulfurization, B10 diesel fuel was used, which was additionally mixed with sulfur. Fuels of this type are commercially available. For all three operating points, the experiment was carried out until 2 g of sulfur (not SOx but S) per liter of SCR volume was emitted.
[0176] The SO2 curve after passage through the DPF is shown in
Embodiment 6: NOx Conversion and SO.SUB.2 .Trap Function of Cu HT-SCR and V HT-SCR
[0177] The comparison of a V SCR with a Cu SCR with regard to its suitability as a combined HT-SCR for the medium to high temperature range and as SO.sub.x trap in the working range of the TT-SCR was carried out on the engine test bench. The vanadium-containing V SCR (HT-SCR1) and the copper-containing Cu SCR (HT-SCR3) according to Exemplary Embodiments 1 and 3 were tested. The catalyst volume used corresponded to the factor 1.1 of the engine cubic capacity or displacement. For the NO.sub.x conversion determination, the pre-SCR and post-SCR NO.sub.x concentrations were measured by means of CLDs (chemiluminescence detectors). The conversion was calculated as in Example 5.
[0178] The SO.sub.x input and output concentrations were measured as SO.sub.2 by a mass spectrometer each at the DPF output and SCR output. The experiments were carried out in dynamic operating mode. To this end, a sequence of WHTC cycles (world harmonized transient cycles) was performed. WHTCs are legally predefined test cycles used for testing, qualifying and releasing heavy-duty/payload engines. The performance and design of a WHTC and the implementation of the test procedure are known to the person skilled in the art.
[0179] Commercially available urea solution was used as reductant. An amount corresponding to an ammonia/NO.sub.x ratio of 0.8 was metered. This is substoichiometric and the HT-SCR therefore cannot achieve 100% conversion. The theoretical maximum conversion would accordingly correspond to 80%.
[0180] For the sulfurization, B10 diesel fuel was used, which was additionally mixed with sulfur. Fuels of this type are commercially available. The sulfur emission per WHTC was 1375 mg.
[0181] The NO.sub.x conversion of the Cu HT-SCR is shown in
[0182] The sulfur breakdown curve from the dynamic engine test bench experiments for a V HT-SCR and the Cu HT-SCR is shown in
[0183]