AT527427A1 - Flue gas cleaning system for the reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a power plant - Google Patents
Flue gas cleaning system for the reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a power plant Download PDFInfo
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- AT527427A1 AT527427A1 ATA50585/2023A AT505852023A AT527427A1 AT 527427 A1 AT527427 A1 AT 527427A1 AT 505852023 A AT505852023 A AT 505852023A AT 527427 A1 AT527427 A1 AT 527427A1
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
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- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8621—Removing nitrogen compounds
- B01D53/8625—Nitrogen oxides
- B01D53/8628—Processes characterised by a specific catalyst
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- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
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- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
- B01D53/9413—Processes characterised by a specific catalyst
- B01D53/9418—Processes characterised by a specific catalyst for removing nitrogen oxides by selective catalytic reduction [SCR] using a reducing agent in a lean exhaust gas
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- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
- B01D53/9413—Processes characterised by a specific catalyst
- B01D53/9422—Processes characterised by a specific catalyst for removing nitrogen oxides by NOx storage or reduction by cyclic switching between lean and rich exhaust gases (LNT, NSC, NSR)
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- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9436—Ammonia
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- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/16—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/20—Vanadium, niobium or tantalum
- B01J23/22—Vanadium
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion
- F01N3/206—Adding periodically or continuously substances to exhaust gases for promoting purification, e.g. catalytic material in liquid form, NOx reducing agents
- F01N3/2066—Selective catalytic reduction [SCR]
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- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/206—Ammonium compounds
- B01D2251/2065—Ammonium hydroxide
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- B01D2255/207—Transition metals
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01D2258/0283—Flue gases
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- B01D53/34—Chemical or biological purification of waste gases
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Abstract
Rauchgasreinigungsanlage zur Reduktion von Stickstoffoxiden (NOx) und Oxidation von Kohlenstoffmonoxid (CO) aus dem Rauchgas einer Kraftwerksanlage Die Erfindung betrifft eine Rauchgasreinigungsanlage (1) und ein Verfahren zum Betrieb einer Rauchgasreinigungsanlage (1) zur selektiven katalytischen Reduktion von Stickstoffoxiden (NOx) und Oxidation von Kohlenstoffmonoxid (CO) aus dem Rauchgas (2) einer Kraftwerksanlage (3). Erfindungsgemäß umfasst die Rauchgasreinigungsanlage (1) einem Katalysator (4), der eine hochaktive Schicht (5) auf Basis von Vanadium ent- hält, und für Betriebstemperaturen bis 720°C ausgelegt ist.Flue gas cleaning system for reducing nitrogen oxides (NOx) and oxidizing carbon monoxide (CO) from the flue gas of a power plant. The invention relates to a flue gas cleaning system (1) and a method for operating a flue gas cleaning system (1) for the selective catalytic reduction of nitrogen oxides (NOx) and oxidizing carbon monoxide (CO) from the flue gas (2) of a power plant (3). According to the invention, the flue gas cleaning system (1) comprises a catalyst (4) which contains a highly active layer (5) based on vanadium and is designed for operating temperatures of up to 720°C.
Description
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Rauchgasreinigungsanlage zur Reduktion von Stickstoffoxiden und Oxidation von Kohlenstoffmonoxid aus dem Rauchgas einer Flue gas cleaning system for the reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a
Kraftwerksanlage power plant
Die vorliegende Erfindung betrifft eine Rauchgasreinigungsanlage sowie ein Verfahren zur Reduktion von Stickstoffoxiden (NOx) und Oxidation von Kohlenstoffmonoxid (CO) aus dem The present invention relates to a flue gas cleaning system and a method for reducing nitrogen oxides (NOx) and oxidizing carbon monoxide (CO) from the
Rauchgas einer Kraftwerksanlage. Flue gas from a power plant.
In vielen Länder schreibt der Gesetzgeber eine umfassende Behandlung von Rauchgasen aus Kraftwerksanlagen vor, insbesondere eine starke Reduzierung der giftigen NOx Gase, wie Stickstoffmonoxid (NO) und Stickstoffdioxid (NO02). Stickstoffoxide entstehen bei der Verbrennung von fossilen Brennstoffen und sind für die Luftverschmutzung und die Bildung von Smog verantwortlich. Daher wird in Rauchgasreinigungsanlagen das Rauchgas aus der Kraftwerksanlage zunächst durch einen Entstauber gereinigt, um Partikel abzuscheiden. Anschließend wird das entstaubte Rauchgas mit Ammoniak angereichert und durch den SCR-Katalysator geleitet, um den Anteil an Stick-In many countries, legislation requires comprehensive treatment of flue gases from power plants, in particular a strong reduction of toxic NOx gases such as nitrogen monoxide (NO) and nitrogen dioxide (NO02). Nitrogen oxides are produced when fossil fuels are burned and are responsible for air pollution and the formation of smog. In flue gas cleaning systems, the flue gas from the power plant is therefore first cleaned by a dust collector to separate particles. The dust-free flue gas is then enriched with ammonia and passed through the SCR catalyst to reduce the proportion of nitrogen.
oxiden zu reduzieren. oxides to reduce.
Rauchgasreinigungsanlagen weisen DeNOx-Katalysatoren auf, in denen Stickoxide durch selektive katalytische Reduktion reduziert und somit das schädliche NOx aus dem Rauchgas entfernt wird. Der SCR-Prozess basiert auf einer chemischen Reaktion, bei der Stickstoffoxide in Stickstoff und Wasser umgewandelt werden. Dabei wird Ammoniak (NH3) als Reduktionsmittel ver-Flue gas cleaning systems have DeNOx catalysts in which nitrogen oxides are reduced by selective catalytic reduction, thus removing the harmful NOx from the flue gas. The SCR process is based on a chemical reaction in which nitrogen oxides are converted into nitrogen and water. Ammonia (NH3) is used as a reducing agent.
wendet. turns.
Herkömmliche DeNOx-Katalysatoren sind für eine maximale Betriebstemperatur von ca. 420 °C ausgelegt. Wird die maximale Betriebstemperatur überschritten, kommt es zu einer Zerstörung des Katalysators. Um eine Zerstörung zu verhindern, werden herkömmliche DeNOx-Katalysatoren bei Temperaturen unter 420 °C betrieben. Conventional DeNOx catalysts are designed for a maximum operating temperature of around 420 °C. If the maximum operating temperature is exceeded, the catalyst will be destroyed. To prevent destruction, conventional DeNOx catalysts are operated at temperatures below 420 °C.
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Da das Rauchgas bei Eintritt in die Rauchgasreinigungsanlagen noch Temperaturen von um die 650 °C aufweist, ist eine Abkühlung erforderlich. Dies geschieht mittels quentschen des Rauchgases durch Zufuhr von Frischluft. Dabei wird das Rauchgas auf ca. 400 °C herabgekühlt. Die zusätzliche Einfuhr von Frischluft reduziert den Wirkungsgrad und die Betriebsflexibilität des Kraftwerks. Since the flue gas still has temperatures of around 650 °C when it enters the flue gas cleaning systems, cooling is necessary. This is done by quenching the flue gas with the supply of fresh air. The flue gas is cooled to around 400 °C. The additional supply of fresh air reduces the efficiency and operational flexibility of the power plant.
Es ist Aufgabe der Erfindung eine Rauchgasreinigungsanlage The object of the invention is to provide a flue gas cleaning system
zur Reduktion von Stickstoffoxiden und Oxidation von Kohlenstoffmonoxid aus dem Rauchgas einer Kraftwerksanlage anzugeben, die keinen Wirkungsgradverlust durch quenschen erleidet for the reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a power plant that does not suffer any loss of efficiency due to quenching
und trotzdem eine hohe Betriebsflexibilität aufweist. and yet offers a high level of operational flexibility.
Die auf eine Vorrichtung gerichtete Aufgabe der Erfindung wird gelöst durch eine Rauchgasreinigungsanlage zur selektiven katalytischen Reduktion von Stickstoffoxiden und Oxidation von Kohlenstoffmonoxid aus dem Rauchgas einer Kraftwerksanlage, mit einem Katalysator, der eine hochaktive Schicht auf Basis von Vanadium enthält, und für Betriebstem-The object of the invention, which is directed to a device, is achieved by a flue gas purification system for the selective catalytic reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a power plant, with a catalyst which contains a highly active layer based on vanadium and for operating temperatures
peraturen bis 720°C ausgelegt ist. temperatures up to 720°C.
Die hochaktive Schicht auf Basis von Vanadium wirkt als Katalysator, um die chemische Reaktion zwischen den Stickstoffoxiden und dem Ammoniak zu fördern. Durch den Kontakt mit dem Katalysator werden die Stickstoffoxide selektiv in Stickstoff und Wasser umgewandelt, wobei der Katalysator nicht be-The highly active vanadium-based layer acts as a catalyst to promote the chemical reaction between the nitrogen oxides and the ammonia. Through contact with the catalyst, the nitrogen oxides are selectively converted into nitrogen and water, without damaging the catalyst.
einträchtigt wird. is impaired.
Gleichzeitig findet in der Rauchgasreinigungsanlage auch die Oxidation von Kohlenstoffmonoxid statt. Kohlenstoffmonoxid ist ein giftiges Gas, das ebenfalls bei der Verbrennung von fossilen Brennstoffen entsteht. Der SCR-Katalysator mit der Vanadium-Beschichtung besitzt auch eine oxidierende Wirkung, die dazu führt, dass Kohlenstoffmonoxid in Kohlendioxid umge-At the same time, the oxidation of carbon monoxide also takes place in the flue gas cleaning system. Carbon monoxide is a poisonous gas that is also produced when fossil fuels are burned. The SCR catalyst with the vanadium coating also has an oxidizing effect, which leads to carbon monoxide being converted into carbon dioxide.
wandelt wird. is transformed.
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Die Verwendung einer Rauchgasreinigungsanlage mit einem Vanadium-basierten SCR-Katalysator ermöglicht es, den Ausstoß von Stickstoffoxiden und Kohlenstoffmonoxid signifikant zu reduzieren. Dadurch trägt die Anlage zur Verbesserung der Luftqualität und zur Verminderung der Umweltauswirkungen von The use of a flue gas cleaning system with a vanadium-based SCR catalyst makes it possible to significantly reduce the emissions of nitrogen oxides and carbon monoxide. The system therefore contributes to improving air quality and reducing the environmental impact of
Kraftwerken bei. power plants.
Die hochaktive Schicht besteht aus einem Trägermaterial mit einer hochaktiven Beschichtung auf Basis von Vanadium, oder aus einem Trägermaterial, welches mit Vanadium als katalytisch aktivem Material homogenisiert ist. Als Trägermaterial für den Katalysator kann homogen extrudierten Wabenkörper verwendet werden. Vanadium ist ein günstiges, und leicht zu beschaffenes Material zur selektiven katalytischen Reduktion The highly active layer consists of a carrier material with a highly active coating based on vanadium, or of a carrier material which is homogenized with vanadium as a catalytically active material. Homogenously extruded honeycomb bodies can be used as the carrier material for the catalyst. Vanadium is an inexpensive and easily obtained material for selective catalytic reduction.
von Stickstoffoxiden. of nitrogen oxides.
Der wesentliche Vorteil der Erfindung besteht darin, dass die Rauchgasreinigungsanlage für Betriebstemperaturen bis 720°C ausgelegt ist, und der Katalysator ohne Kühlung des Rauchgases direkt nach einer Gasturbine betrieben werden kann. Die Auslegung des Katalysators für Betriebstemperaturen bis 720°C erlauben eine flexible Betriebsweise, bei der es auch kurzzeitig zu höheren Temperaturen kommen kann. Durch die Erfindung kann eine Rauchgasreinigungsanlage gegenüber dem Stand der Technik wesentlich einfacher konstruiert und gebaut wer-The main advantage of the invention is that the flue gas cleaning system is designed for operating temperatures of up to 720°C and the catalyst can be operated directly after a gas turbine without cooling the flue gas. The design of the catalyst for operating temperatures of up to 720°C allows for flexible operation, which can also result in higher temperatures for short periods. The invention allows a flue gas cleaning system to be designed and built much more easily than the state of the art.
den. the.
Bei einer vorteilhaften Weiterentwicklung der Erfindung ist dem Katalysator zur selektiven katalytischen Reduktion von Stickstoffoxiden (NO0x) Ammoniakwasser (NH4,OH) als Reduktionsmittel zuführbar. Dies vereinfacht die Prozesskonfiguration, da bei diesem Ansatz keine Ammoniakwasser verdampft werden muss, bevor es in das Einspeisungsnetz geleitet wird. Das System wird dadurch einfacher zu steuern und zu warten, da In an advantageous further development of the invention, ammonia water (NH4,OH) can be fed as a reducing agent to the catalyst for the selective catalytic reduction of nitrogen oxides (NO0x). This simplifies the process configuration, since with this approach no ammonia water needs to be evaporated before it is fed into the feed network. The system is therefore easier to control and maintain, since
keine Abgasventilatoren mehr benötigt werden. exhaust fans are no longer required.
Vorteilhafterweise ist die Rauchgasreinigungsanlage für eine Advantageously, the flue gas cleaning system is designed for
Anwendung in Gas- und Dampf-Kraftwerken konzipiert, um den Designed for use in gas and steam power plants to
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Wirkungsgrad und die Betriebsflexibilität zu erhöhen. Der Ka-To increase efficiency and operational flexibility. The Ka-
talysator kommt direkt nach der Gasturbine zum Einsatz. The catalyst is used directly after the gas turbine.
Die auf ein Verfahren gerichtete Aufgabe ist gelöst durch ein Verfahren zur selektiven katalytischen Reduktion von Stickstoffoxiden (NOx) und Oxidation von Kohlenstoffmonoxid (CO) aus dem Rauchgas einer Kraftwerksanlage, mit einem Katalysator, der eine hochaktive Schicht auf Basis von Vanadium enthält, wobei der Katalysator bei Temperaturen bis 720°C be-The object directed to a process is achieved by a process for the selective catalytic reduction of nitrogen oxides (NOx) and oxidation of carbon monoxide (CO) from the flue gas of a power plant, with a catalyst containing a highly active layer based on vanadium, wherein the catalyst is operated at temperatures of up to 720°C.
trieben wird. is driven.
Die für die Vorrichtungsansprüche beschriebenen Vorteile gel-The advantages described for the device claims apply
ten gleichermaßen für die Verfahrensansprüche. equally for the process claims.
Bei einer vorteilhaften Weiterentwicklung des Verfahrens wird dem Katalysator zur selektiven katalytischen Reduktion von Stickstoffoxiden (NO0x) Ammoniakwasser (NH4,OH) als Reduktionsmittel zugeführt. In an advantageous further development of the process, ammonia water (NH4,OH) is fed to the catalyst as a reducing agent for the selective catalytic reduction of nitrogen oxides (NO0x).
Vorteilhafterweise kommt das Verfahren in Gas und DampfKraftwerken betrieben wird, um den Wirkungsgrad und die Be-The process is advantageously used in gas and steam power plants to increase the efficiency and
triebsflexibilität zu erhöhen. to increase operational flexibility.
Im Folgenden wird die Erfindung anhand von Figuren näher be-In the following, the invention is described in more detail with reference to figures.
schrieben. Darin zeigt: wrote. In it shows:
Figur 1 Eine schematische Darstellung einer Rauchgasreini Gungsanlage nach dem Stand der Technik. Figur 2 Ein Ausführungsbeispiel der erfindungsgemäßen Figure 1 A schematic representation of a flue gas cleaning system according to the state of the art. Figure 2 An embodiment of the inventive
Rauchgasreinigungsanlage. flue gas cleaning system.
Die Figur 1 zeigt eine schematische Darstellung einer Kraftwerksanlage 3 mit einer Rauchgasreinigungsanlage 1 zur Reinigung eines Rauchgases 2. Die Rauchgasreinigungsanlage 1 ist Figure 1 shows a schematic representation of a power plant 3 with a flue gas cleaning system 1 for cleaning a flue gas 2. The flue gas cleaning system 1 is
in den Rauchgaskanal 8 hinter einer Gasturbine 10 angeordnet, arranged in the flue gas duct 8 behind a gas turbine 10,
und ist Bestandteil eines Abhitzedampferzeugers 9. and is part of a heat recovery steam generator 9.
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Der Abhitzedampferzeuger 9 umfasst einen Katalysator 7 zur selektiven katalytischen Reduktion (SCR) von Stickoxiden, der im Rauchgaskanal 8, zwischen zwei Verdampferflächen des Wär-The waste heat steam generator 9 comprises a catalyst 7 for the selective catalytic reduction (SCR) of nitrogen oxides, which is installed in the flue gas duct 8, between two evaporator surfaces of the heat
metauschers 11 angeordnet ist. exchanger 11 is arranged.
Bei dem Katalysator 7 handelt es sich um einen konventionellen SCR-Katalysator nach dem Stand der Technik. Er ist für eine Betriebstemperatur bis zu 420 °C, und Ammoniak (NH3) als Reduktionsmittel ausgelegt, und ist zwischen den Verdampferheizflächen des Wärmetauschers 11 angeordnet. Um eine thermische Zerstörung des Katalysators 7 zu vermeiden, müssen Betriebstemperaturen unter 420°C sichergestellt werden. Da das Rauchgas bei Eintritt in den Abhitzedampferzeuger 9 noch Temperaturen von um die 650 °C aufweist, ist eine Abkühlung des Rausgases 2 erforderlich. Dies geschieht mittels quentschen des Rauchgases durch Zufuhr von Frischluft. Dabei wird das Rauchgas auf ca. 400 °C herabgekühlt. Die zusätzliche Einfuhr von Frischluft reduziert den Wirkungsgrad und die Betriebsflexibilität des Kraftwerks. The catalyst 7 is a conventional SCR catalyst according to the state of the art. It is designed for an operating temperature of up to 420 °C and ammonia (NH3) as a reducing agent, and is arranged between the evaporator heating surfaces of the heat exchanger 11. In order to avoid thermal destruction of the catalyst 7, operating temperatures below 420 °C must be ensured. Since the flue gas still has temperatures of around 650 °C when it enters the waste heat steam generator 9, the exhaust gas 2 must be cooled. This is done by quenching the flue gas by supplying fresh air. The flue gas is cooled down to approx. 400 °C. The additional supply of fresh air reduces the efficiency and operational flexibility of the power plant.
Figur 2 zeigt ein Ausführungsbeispiel der erfindungsgemäßen Figure 2 shows an embodiment of the inventive
Rauchgasreinigungsanlage. flue gas cleaning system.
Die Rauchgasreinigungsanlage 1 umfasst einen HochtemperaturDeNOx Katalysator 4 zur selektiven katalytischen Reduktion The flue gas cleaning system 1 comprises a high-temperature DeNOx catalyst 4 for selective catalytic reduction
von Stickstoffoxiden (NOx) und Oxidation von Kohlenstoffmonoxid (CO) aus dem Rauchgas 2. Um die hochtemperaturbeständigkeit zu erreichen, enthält der Katalysator 4 eine hochaktive Schicht 5 auf Basis von Vanadium, wodurch er für Betriebstem-of nitrogen oxides (NOx) and oxidation of carbon monoxide (CO) from the flue gas 2. In order to achieve high temperature resistance, the catalyst 4 contains a highly active layer 5 based on vanadium, which makes it suitable for operating temperatures
peraturen zwischen 420°C bis 720°C temperaturbeständig wird. temperatures between 420°C and 720°C.
Die hochaktive Schicht 5 auf Basis von Vanadium wirkt als Katalysator, um die chemische Reaktion zwischen den Stickstoffoxiden und dem Ammoniak zu fördern. Durch den Kontakt mit dem Katalysator 4 werden die Stickstoffoxide selektiv in Stickstoff und Wasser umgewandelt. Der Katalysator 4 kommt ohne Kühlung des Rauchgases 2 aus, und kann direkt nach einer The highly active layer 5 based on vanadium acts as a catalyst to promote the chemical reaction between the nitrogen oxides and the ammonia. Through contact with the catalyst 4, the nitrogen oxides are selectively converted into nitrogen and water. The catalyst 4 does not require cooling of the flue gas 2 and can be used directly after a
Gasturbine betrieben werden. gas turbine.
15 15
20 20
2023PF12152 2023PF12152
Bei einer vorteilhaften Weiterentwicklung der Erfindung ist dem Katalysator zur selektiven katalytischen Reduktion von Stickstoffoxiden (NO0x) Ammoniakwasser (NH4,OH) als Reduktionsmittel zuführbar. Das Reduktionsmittel 6 wird ohne Kühlung und Verdampfer verwendet. Dies vereinfacht die Prozesskonfiguration, da bei diesem Ansatz keine Ammoniakwasser verdampft werden muss, bevor es in das Einspeisungsnetz geleitet wird. Das System wird dadurch einfacher zu steuern und zu warten, In an advantageous further development of the invention, ammonia water (NH4,OH) can be fed as a reducing agent to the catalyst for the selective catalytic reduction of nitrogen oxides (NO0x). The reducing agent 6 is used without cooling and evaporator. This simplifies the process configuration, since with this approach no ammonia water has to be evaporated before it is fed into the feed network. The system is therefore easier to control and maintain.
da keine Abgasventilatoren mehr benötigt werden. because exhaust fans are no longer required.
In einer Situation der zunehmenden Durchdringung der Stromnetze mit erneuerbaren Energiequellen und der Umstellung auf Wasserstoffbasierte Energiespeichersysteme wird die Verbrennung von Gas in bestehenden Gasturbinenkraftwerken unweigerlich zu einem Anstieg der NOx-Emissionen führen. In diesem Fall wird die Nachrüstung solcher Kraftwerke mit dem Erfindungsgemäßen Katalysator eine einfache und kosteneffizi-In a situation of increasing penetration of the electricity grids with renewable energy sources and the transition to hydrogen-based energy storage systems, the combustion of gas in existing gas turbine power plants will inevitably lead to an increase in NOx emissions. In this case, retrofitting such power plants with the catalyst according to the invention will be a simple and cost-effective solution.
ente Lösung sein. be a solution.
Claims (6)
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| ATA50585/2023A AT527427A1 (en) | 2023-07-20 | 2023-07-20 | Flue gas cleaning system for the reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a power plant |
| PCT/EP2024/068319 WO2025016707A1 (en) | 2023-07-20 | 2024-06-28 | Flue gas cleaning system for reducing nitrogen oxides and oxidising carbon monoxide from the flue gas of a power plant |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| ATA50585/2023A AT527427A1 (en) | 2023-07-20 | 2023-07-20 | Flue gas cleaning system for the reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a power plant |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| AT527427A1 true AT527427A1 (en) | 2025-02-15 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| ATA50585/2023A AT527427A1 (en) | 2023-07-20 | 2023-07-20 | Flue gas cleaning system for the reduction of nitrogen oxides and oxidation of carbon monoxide from the flue gas of a power plant |
Country Status (2)
| Country | Link |
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| AT (1) | AT527427A1 (en) |
| WO (1) | WO2025016707A1 (en) |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE10015696A1 (en) * | 2000-03-27 | 2001-10-25 | Hyun Dai Heavy Ind Co Ltd | Catalyst for reducing nitric oxide to nitrogen and water in waste gases containing sulfur dioxide comprises titanium-pillared layered clay impregnated with vanadium pentoxide |
| AT409344B (en) * | 2000-12-11 | 2002-07-25 | Porzellanfabrik Frauenthal Gmb | Process for the catalytic treatment of flue gases, in particular nitrogen oxides, hydrocarbons and dioxins and furans |
| DE112014000588T5 (en) * | 2013-01-29 | 2015-12-24 | Johnson Matthey Public Limited Company | Ammonia oxidation catalyst |
| EP1680220B1 (en) * | 2003-09-27 | 2017-02-15 | Korea Power Engineering Company, Inc. | Vanadium/titania-based catalyst for removing nitrogen oxide at low temperature window, and process of removing nitrogen oxide using the same |
| CN106938200A (en) * | 2014-08-20 | 2017-07-11 | 清华大学苏州汽车研究院(吴江) | Vanadia-based SCR catalysts |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20110274607A1 (en) * | 2010-05-04 | 2011-11-10 | Technical University Of Denmark | Vanadia-supported zeolites for scr of no by ammonia |
| BR112013004709A2 (en) * | 2010-09-03 | 2016-05-10 | Univ Danmarks Tekniske | "heteropoly acid activated catalyst for nox ammonia scr" |
| PL2844372T3 (en) * | 2012-06-27 | 2017-04-28 | Siemens Aktiengesellschaft | Exhaust-gas purification device and method for the reduction of nitrogen oxides from an exhaust gas of a fossil-fired power plant |
| DE102015209988A1 (en) * | 2014-06-02 | 2015-12-03 | Johnson Matthey Public Limited Company | Coated articles with high KNOx / KSOx ratios for selective catalytic reduction |
-
2023
- 2023-07-20 AT ATA50585/2023A patent/AT527427A1/en unknown
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2024
- 2024-06-28 WO PCT/EP2024/068319 patent/WO2025016707A1/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE10015696A1 (en) * | 2000-03-27 | 2001-10-25 | Hyun Dai Heavy Ind Co Ltd | Catalyst for reducing nitric oxide to nitrogen and water in waste gases containing sulfur dioxide comprises titanium-pillared layered clay impregnated with vanadium pentoxide |
| AT409344B (en) * | 2000-12-11 | 2002-07-25 | Porzellanfabrik Frauenthal Gmb | Process for the catalytic treatment of flue gases, in particular nitrogen oxides, hydrocarbons and dioxins and furans |
| EP1680220B1 (en) * | 2003-09-27 | 2017-02-15 | Korea Power Engineering Company, Inc. | Vanadium/titania-based catalyst for removing nitrogen oxide at low temperature window, and process of removing nitrogen oxide using the same |
| DE112014000588T5 (en) * | 2013-01-29 | 2015-12-24 | Johnson Matthey Public Limited Company | Ammonia oxidation catalyst |
| CN106938200A (en) * | 2014-08-20 | 2017-07-11 | 清华大学苏州汽车研究院(吴江) | Vanadia-based SCR catalysts |
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| Publication number | Publication date |
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| WO2025016707A1 (en) | 2025-01-23 |
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