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JP6636259B2 - Exhaust gas aftertreatment system and method for exhaust gas aftertreatment - Google Patents
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JP6636259B2 - Exhaust gas aftertreatment system and method for exhaust gas aftertreatment - Google Patents

Exhaust gas aftertreatment system and method for exhaust gas aftertreatment Download PDF

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JP6636259B2
JP6636259B2 JP2015081524A JP2015081524A JP6636259B2 JP 6636259 B2 JP6636259 B2 JP 6636259B2 JP 2015081524 A JP2015081524 A JP 2015081524A JP 2015081524 A JP2015081524 A JP 2015081524A JP 6636259 B2 JP6636259 B2 JP 6636259B2
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exhaust gas
gas
separator
heat exchanger
aftertreatment system
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JP2015203416A (en
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プラメン・トシェフ
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Everllence SE
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MAN Energy Solutions SE
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N5/00Exhaust or silencing apparatus combined or associated with devices profiting by exhaust energy
    • F01N5/02Exhaust or silencing apparatus combined or associated with devices profiting by exhaust energy the devices using heat
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01D53/02Separation 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 by adsorption, e.g. preparative gas chromatography
    • B01D53/06Separation 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 by adsorption, e.g. preparative gas chromatography with moving adsorbents, e.g. rotating beds
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
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    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9459Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts
    • B01D53/9477Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts with catalysts positioned on separate bricks, e.g. exhaust systems
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • B01D53/92Chemical or biological purification of waste gases of engine exhaust gases
    • B01D53/94Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
    • B01D53/9481Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start
    • B01D53/949Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start for storing sulfur oxides
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/02Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust
    • F01N3/021Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
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    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/10Exhaust 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
    • F01N3/18Exhaust 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
    • F01N3/20Exhaust 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
    • F01N3/2006Periodically heating or cooling catalytic reactors, e.g. at cold starting or overheating
    • F01N3/2013Periodically heating or cooling catalytic reactors, e.g. at cold starting or overheating using electric or magnetic heating means
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/10Exhaust 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
    • F01N3/18Exhaust 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
    • F01N3/20Exhaust 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
    • F01N3/2053By-passing catalytic reactors, e.g. to prevent overheating
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/08Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
    • F01N3/10Exhaust 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
    • F01N3/18Exhaust 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
    • F01N3/20Exhaust 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
    • F01N3/206Adding periodically or continuously substances to exhaust gases for promoting purification, e.g. catalytic material in liquid form, NOx reducing agents
    • F01N3/2066Selective catalytic reduction [SCR]
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • F01N2240/02Combination or association of two or more different exhaust treating devices, or of at least one such device with an auxiliary device, not covered by indexing codes F01N2230/00 or F01N2250/00, one of the devices being a heat exchanger
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Description

本発明は排気ガス後処理システムに関する。さらに、本発明は、排気ガス後処理のための方法に関する。   The present invention relates to an exhaust gas aftertreatment system. Furthermore, the invention relates to a method for exhaust gas aftertreatment.

例えば発電所で用いられる静置された内燃機関における燃焼過程、および、例えば船舶で用いられるに静置されていない内燃機関における燃焼過程の間、SOおよびSOなどの硫黄酸化物が生成され、これらの硫黄酸化物は、典型的には、石炭、坑口炭、褐炭、油、または重油などの硫黄含有化石燃料の燃焼の間に形成される。そのため、このような内燃機関には、具体的には、内燃機関を出て行く排気ガスの脱硫に役立つ排気ガス後処理システムが設けられる。 During the combustion process in a stationary internal combustion engine used for example in a power plant and in a non-stationary internal combustion engine used in a ship for example, sulfur oxides such as SO 2 and SO 3 are produced. These sulfur oxides are typically formed during the combustion of sulfur-containing fossil fuels such as coal, wellhead coal, lignite, oil, or heavy oil. Therefore, such internal combustion engines are specifically provided with an exhaust gas aftertreatment system which serves for desulfurization of the exhaust gases leaving the internal combustion engine.

排気ガスを脱硫するために、吸収剤として、生石灰(CaO)、消石灰(Ca(OH))、または炭酸カルシウム(CaCO)を主に使用する吸収による方法が、先行技術から主に知られている。過程では、粉末または粒状体が形成され、硫酸カルシウム粉末を排気ガスから除去するために、フィルタ装置が脱硫の下流に用いられる必要がある。 To desulfurize exhaust gas, as an absorbent, quick lime (CaO), slaked lime (Ca (OH) 2), or the method according to absorption primarily used calcium carbonate (CaCO 3) is known mainly from the prior art ing. In the process, a powder or granules are formed and a filter device needs to be used downstream of desulfurization to remove the calcium sulfate powder from the exhaust gas.

特許文献1から、二酸化窒素および粉末を含む排気ガスの処理のための方法および排気ガス後処理システムが知られている。   From US Pat. No. 6,037,098, a method and an exhaust gas aftertreatment system for the treatment of exhaust gases containing nitrogen dioxide and powder are known.

特許第3603365号公報Japanese Patent No. 3603365

このことから、本発明の目的は、新しい形の排気ガス後処理システムと、新しい形の排気ガス後処理のための方法とを作り出すことに基づいている。   Thus, it is an object of the present invention to create a new type of exhaust gas aftertreatment system and a method for a new type of exhaust gas aftertreatment.

この目的は、請求項1による排気ガス後処理システムによって解決される。本発明による内燃機関用の排気ガス後処理システムは、内燃機関の下流に配置された、硫黄酸化物を化学吸着するためのカルシウム含有粒状体を含む分離器を備える。さらに、本発明による排気ガス後処理システムは、内燃機関を出て行く排気ガスの温度を上昇させるために、一方で分離器を通って導かれた排気ガスが導かれ、他方で内燃機関を出て行く排気ガスが導かれ得るように通るガス−ガス熱交換器を備える。さらに、本発明による排気ガス後処理システムは、ガス−ガス熱交換器を通って導かれた排気ガスの温度をさらに上昇させるために、ガス−ガス熱交換器の下流で分離器の上流に配置された加熱装置を備える。   This object is solved by an exhaust gas aftertreatment system according to claim 1. An exhaust gas aftertreatment system for an internal combustion engine according to the present invention comprises a separator disposed downstream of the internal combustion engine and comprising calcium-containing particles for chemisorbing sulfur oxides. Furthermore, the exhaust gas aftertreatment system according to the present invention is directed on the one hand to the exhaust gas guided through the separator and on the other hand to leave the internal combustion engine in order to increase the temperature of the exhaust gas leaving the internal combustion engine. A gas-gas heat exchanger through which incoming exhaust gases can be directed. Furthermore, the exhaust gas aftertreatment system according to the invention is arranged downstream of the gas-gas heat exchanger and upstream of the separator in order to further increase the temperature of the exhaust gas guided through the gas-gas heat exchanger. Equipped heating device.

分離器を使用することで、硫酸カルシウムの粉末または粒状体を排気ガスから除去するためのフィルタ装置を省略することが可能である。硫黄酸化物は、分離器のカルシウム含有粒状体と反応し、粒状体として排出できる。ガス−ガス熱交換器と、ガス−ガス熱交換器の下流に配置された加熱装置とが、分離器を通って導かれる排気ガスを、分離器における排気ガスの脱硫に最適な温度へと温度制御することができ、ガス−ガス熱交換器における排気ガスの温度制御に続くため、加熱装置の回路が縮小できる。分離器を通って導かれる排気ガスを、分離器における排気ガスの脱硫に最適な温度へと温度制御することによって、分離器において排気ガスを脱硫することは短い反応時間で確保される。これによってさらに、分離器で排気ガスを脱硫することに関しては、必要とされるカルシウム含有粒状体が比較的少なくて済むことが保証される。   By using a separator, it is possible to omit a filter device for removing calcium sulfate powder or particulates from exhaust gas. The sulfur oxides react with the calcium-containing granules of the separator and can be discharged as granules. A gas-gas heat exchanger and a heating device arranged downstream of the gas-gas heat exchanger heat the exhaust gas guided through the separator to a temperature optimum for desulfurization of the exhaust gas in the separator. It can be controlled and follows the temperature control of the exhaust gas in the gas-gas heat exchanger, so that the circuit of the heating device can be reduced. By controlling the temperature of the exhaust gas led through the separator to a temperature optimum for the desulfurization of the exhaust gas in the separator, the desulfurization of the exhaust gas in the separator is ensured in a short reaction time. This further ensures that relatively little calcium-containing granules are required for desulfurizing the exhaust gas in the separator.

優先的には、ガス−ガス熱交換器は、内燃機関を出て行く排気ガスを、330℃と350℃との間の温度、好ましくは340℃と350℃との間の温度まで加熱する。加熱装置は、排気ガスを、375℃と450℃との間の温度、好ましくは400℃と450℃との間の温度、最も好ましくは360℃と420℃との間の温度まで加熱する。排気ガスのこの温度制御は、効果的であり、特に、分離器における排気ガスの脱硫に関して有利である。   Preferentially, the gas-gas heat exchanger heats the exhaust gas leaving the internal combustion engine to a temperature between 330 ° C and 350 ° C, preferably between 340 ° C and 350 ° C. The heating device heats the exhaust gas to a temperature between 375 ° C and 450 ° C, preferably between 400 ° C and 450 ° C, most preferably between 360 ° C and 420 ° C. This temperature control of the exhaust gas is effective and is particularly advantageous with regard to the desulfurization of the exhaust gas in the separator.

有利なさらなる発展形態によれば、SOをSOへと酸化するための酸化触媒コンバータが、加熱装置の下流で分離器の上流に位置付けられ、その酸化触媒コンバータを通って、加熱装置において加熱された排気ガスが、分離器の上流に導かれ得る。SOをSOへと酸化するための酸化触媒コンバータを使用することで、SOがSOよりも分離器のカルシウム含有粒状体とより素早く反応するため、分離器における排気ガスの滞留時間をずっと短くすることができる。これにより、排気ガスの特に効果的な脱硫を可能にする。 According to an advantageous further development, an oxidation catalytic converter for oxidizing SO 2 to SO 3 is located downstream of the heating device and upstream of the separator, through which the catalytic converter is heated. Exhausted exhaust gas may be directed upstream of the separator. By using an oxidation catalytic converter to oxidize SO 2 to SO 3 , the residence time of the exhaust gas in the separator is reduced because SO 3 reacts more quickly with the calcium-containing particulates of the separator than SO 2. Can be much shorter. This enables a particularly effective desulfurization of the exhaust gas.

さらに有利なさらなる発展形態によれば、加熱装置の下流で分離器の上流に装置が位置付けられ、その装置を通って、カルシウム含有および/またはナトリウム含有の粉末が、分離器の上流の加熱装置で加熱された排気ガスへと導入され得る。これにより、排気ガスの特に効果的な脱硫を可能にする。硫酸カルシウム粉末および/または硫酸ナトリウム粉末、あるいは、脱硫の間に形成される硫酸塩含有粒状体は、分離器を用いることで排気ガスから効果的に分離され得る。具体的には、カルシウム含有および/またはナトリウム含有の粉末または粒状体が、分離器の上流の加熱装置で加熱される排気ガスへと導入され得るように通る装置に加えて、酸化触媒コンバータも加熱装置の下流で分離器の上流に位置付けられる場合、カルシウム含有および/またはナトリウム含有の粉末または粒状体が排気ガスへと導入され得るように通る装置は、SOをSOへと酸化するための酸化触媒コンバータの下流で分離器の上流に位置付けられる。 According to a further advantageous further development, the device is located downstream of the heating device and upstream of the separator, through which the calcium- and / or sodium-containing powder is passed in the heating device upstream of the separator. It can be introduced into the heated exhaust gas. This enables a particularly effective desulfurization of the exhaust gas. Calcium sulfate powder and / or sodium sulfate powder, or sulfate-containing particulates formed during desulfurization, can be effectively separated from exhaust gas by using a separator. In particular, in addition to the device through which the calcium- and / or sodium-containing powder or granules can be introduced into the exhaust gas which is heated in the heating device upstream of the separator, the oxidation catalytic converter is also heated. If downstream of the device positioned upstream of the separator, apparatus through such calcium-containing and / or sodium-containing powder or granules can be introduced into the exhaust gas, for the oxidation and the sO 2 to sO 3 It is located downstream of the oxidation catalytic converter and upstream of the separator.

有利なさらなる発展形態によれば、排気ガス後処理システムはSCR触媒コンバータを備え、そのSCR触媒コンバータは、分離器の下流でガス−ガス熱交換器の上流に位置付けられるか、または、代替でガス−ガス熱交換器の下流に位置付けられるかのいずれかである。SCR触媒コンバータでは、排気ガスの脱窒と、それによる排気ガス排出物のさらなる低減とが行われる。   According to an advantageous further development, the exhaust gas aftertreatment system comprises an SCR catalytic converter, the SCR catalytic converter being located downstream of the separator and upstream of the gas-gas heat exchanger or alternatively of the gas-gas heat exchanger. -Either located downstream of the gas heat exchanger. In the SCR catalytic converter, denitrification of exhaust gas and thereby further reduction of exhaust gas emission are performed.

本発明による排気ガス後処理のための方法が、請求項12で定められている。   A method for exhaust gas aftertreatment according to the invention is defined in claim 12.

本発明の好ましいさらなる発展形態は、従属請求項および以下の説明から得られる。本発明の例示の実施形態が、図面を用いるが、これに限定されることなく、より詳細に説明される。   Preferred further developments of the invention follow from the dependent claims and the following description. BRIEF DESCRIPTION OF THE DRAWINGS Exemplary embodiments of the present invention will be described in more detail, using, but not limited to, the drawings.

本発明による第1の排気ガス後処理システムのブロック図である。1 is a block diagram of a first exhaust gas aftertreatment system according to the present invention. 本発明による第2の排気ガス後処理システムのブロック図である。FIG. 4 is a block diagram of a second exhaust gas aftertreatment system according to the present invention. 本発明による第3の排気ガス後処理システムのブロック図である。FIG. 4 is a block diagram of a third exhaust gas aftertreatment system according to the present invention. 本発明による第4の排気ガス後処理システムのブロック図である。FIG. 9 is a block diagram of a fourth exhaust gas aftertreatment system according to the present invention. 本発明によるさらなる排気ガス後処理システムのブロック図である。FIG. 4 is a block diagram of a further exhaust gas aftertreatment system according to the present invention.

本発明は、例えば、発電所に静置された内燃機関用、または、船舶の静置されていない内燃機関用といった、内燃機関用の排気ガス後処理システムに関する。   The present invention relates to an exhaust gas aftertreatment system for an internal combustion engine, for example, for an internal combustion engine that is stationary in a power plant or for an internal combustion engine that is not stationary on a ship.

具体的には、排気ガス後処理システムは、重油で運転される船舶用ディーゼル機関で用いられる。   Specifically, exhaust gas aftertreatment systems are used in marine diesel engines that operate on heavy oil.

図1は、内燃機関1の下流に配置された排気ガス後処理システム2の第1の例示の実施形態を示しており、本発明による排気ガス後処理システム2は、カルシウム含有粒状体または石灰に基づいた粒状体を含む分離器3を備えており、カルシウム含有粒状体または石灰に基づいた粒状体は、分離器3において硫黄酸化物を化学吸着するように作用する。分離器3は、いわゆる充填層反応器、または、いわゆる移動床反応器もしくは流動層反応器であってもよい。   FIG. 1 shows a first exemplary embodiment of an exhaust gas aftertreatment system 2 arranged downstream of an internal combustion engine 1, wherein the exhaust gas aftertreatment system 2 according to the invention reduces calcium-containing granules or lime. A separator 3 comprising granules based on calcium is provided, wherein the granules based on calcium or on lime act in the separator 3 to chemisorb sulfur oxides. The separator 3 may be a so-called packed bed reactor, or a so-called moving bed reactor or fluidized bed reactor.

硫黄酸化物を化学吸着するための分離器3で用いられる粒状体は、優先的には、CaOおよび/またはCa(OH)および/またはCaCOを含む。過程では、排気ガスの硫黄酸化物が、以下の反応式に従ってカルシウム含有粒状体と反応する。すなわち、Ca(OH)については、以下の反応式に従う。
Ca(OH)+SO⇔CaSO+H
Ca(OH)+SO+1/2O⇔CaSO+H
Ca(OH)+CO⇔CaCO+H
Ca(OH)+SO⇔CaSO+H
CaCOについては、以下の反応式に従う。
CaCO+SO⇔CaSO+CO
CaCO+SO+1/2O⇔CaSO+CO
CaCO+SO⇔CaSO+CO
Granules used in the separator 3 for chemisorption of sulfur oxides, Preferentially, including CaO and / or Ca (OH) 2 and / or CaCO 3. In the process, the sulfur oxides of the exhaust gas react with the calcium-containing granules according to the following reaction formula. That is, Ca (OH) 2 follows the following reaction formula.
Ca (OH) 2 + SO 2 ⇔CaSO 3 + H 2 O
Ca (OH) 2 + SO 2 + / O 2 ⇔CaSO 4 + H 2 O
Ca (OH) 2 + CO 2 ⇔CaCO 3 + H 2 O
Ca (OH) 2 + SO 3 ⇔CaSO 4 + H 2 O
For CaCO 3 , the following reaction equation follows.
CaCO 3 + SO 2 ⇔CaSO 3 + CO 2
CaCO 3 + SO 2 + / O 2 ⇔CaSO 4 + CO 2
CaCO 3 + SO 3 ⇔CaSO 4 + CO 2

分離器3を通って導かれた排気ガスは、後で分離器3を通って導かれる必要がある内燃機関1を出て行く排気ガスと同時に、排気ガス後処理システム2のガス−ガス熱交換器4を通って導かれ得る。分離器3において硫黄酸化物を化学吸着する間、熱が発熱反応の結果として発生し、その結果、分離器3を通ってすでに導かれた排気ガスは、内燃機関1を出て行く排気ガスより高い温度を有しており、その結果、ガス−ガス熱交換器4では、後で分離器3を通って導かれる必要がある内燃機関1を出て行く排気ガスは、分離器3を通ってすでに導かれた排気ガスによって加熱できる。ガス−ガス熱交換器4の下流で分離器3の上流に、本発明による排気ガス後処理システム2の加熱装置5が位置付けられ、加熱装置5は、ガス−ガス熱交換器4を通って導かれ、ガス−ガス熱交換器4ですでに加熱された排気ガスの温度をさらに上昇させるように機能する。   Exhaust gas led through the separator 3 is exhaust gas leaving the internal combustion engine 1 that needs to be later led through the separator 3 and at the same time gas-gas heat exchange of the exhaust gas aftertreatment system 2 Can be guided through the vessel 4. During the chemisorption of the sulfur oxides in the separator 3, heat is generated as a result of the exothermic reaction, so that the exhaust gas already led through the separator 3 is higher than the exhaust gas leaving the internal combustion engine 1. Exhaust gases leaving the internal combustion engine 1 which have a high temperature and consequently in the gas-gas heat exchanger 4, which later need to be led through the separator 3, pass through the separator 3 It can be heated by the exhaust gas already led. Downstream of the gas-gas heat exchanger 4 and upstream of the separator 3, a heating device 5 of the exhaust gas aftertreatment system 2 according to the invention is located, and the heating device 5 is guided through the gas-gas heat exchanger 4. This serves to further increase the temperature of the exhaust gas already heated in the gas-gas heat exchanger 4.

したがって、分離器3の上流で内燃機関1を出て行く排気ガスの加熱が、一方でガス−ガス熱交換器4において、そして、ガス−ガス熱交換器4の下流で加熱装置5においての2段階で起こる。ガス−ガス熱交換器4では、分離器3を通ってすでに導かれた排気ガスの上昇した温度が、内燃機関1を出て行く排気ガスを加熱するために利用される。内燃機関1を出て行く排気ガスは、典型的には、320℃未満の温度を有している。ガス−ガス熱交換器4によって、内燃機関1を出て行く排気ガスは、330℃と350℃との間の温度、好ましくは340℃と350℃との間の温度まで加熱され得る。分離器3の上流での排気ガスのさらなる加熱およびそれに伴う温度の上昇は、前記の温度の高さから開始して、ガス−ガス熱交換器4の下流に位置付けられた加熱装置5を介して起こり、加熱装置5は、排気ガスを、375℃と450℃との間の温度、好ましくは400℃と450℃との間の温度まで加熱する。   Thus, the heating of the exhaust gas leaving the internal combustion engine 1 upstream of the separator 3 takes place on the one hand in the gas-gas heat exchanger 4 and in the heating device 5 downstream of the gas-gas heat exchanger 4. Happens in stages. In the gas-gas heat exchanger 4, the increased temperature of the exhaust gas already led through the separator 3 is used to heat the exhaust gas leaving the internal combustion engine 1. The exhaust gas leaving the internal combustion engine 1 typically has a temperature of less than 320 ° C. By means of the gas-gas heat exchanger 4, the exhaust gas leaving the internal combustion engine 1 can be heated to a temperature between 330C and 350C, preferably between 340C and 350C. The further heating of the exhaust gas upstream of the separator 3 and the consequent increase in temperature, starting from the above-mentioned temperature height, via a heating device 5 located downstream of the gas-gas heat exchanger 4 As a result, the heating device 5 heats the exhaust gas to a temperature between 375 ° C and 450 ° C, preferably between 400 ° C and 450 ° C.

硫黄酸化物を化学吸着するために、排気ガスの硫黄酸化物が分離器3のカルシウム含有粒状体と反応する分離器3の上流での排気ガスの温度制御によって、排気ガスの硫黄酸化物は、分離器3における排気ガスの滞留時間が可能とされ得るように、最適な過程温度で分離器3のカルシウム含有粒状体と反応できる。さらに、具体的には、分離器3で処理される排気ガスが上記の排気ガス温度において分離器3を通って導かれるとき、比較的少ない還元剤、したがって、比較的少ないカルシウム含有粒状体が、硫黄酸化物を化学吸着するために、分離器3で必要とされる。したがって、全体として、分離器3において、非常に効果的な排気ガス後処理または排気ガスの脱硫が確保できる。   Due to the temperature control of the exhaust gas upstream of the separator 3 where the sulfur oxides of the exhaust gas react with the calcium-containing granules of the separator 3 in order to chemisorb the sulfur oxides, the sulfur oxides of the exhaust gas It can react with the calcium-containing granules of the separator 3 at an optimum process temperature so that the residence time of the exhaust gas in the separator 3 can be made possible. Furthermore, specifically, when the exhaust gas treated in the separator 3 is directed through the separator 3 at the above-mentioned exhaust gas temperature, a relatively small amount of reducing agent, and thus a relatively small amount of calcium-containing particles, Required in separator 3 to chemisorb sulfur oxides. Therefore, as a whole, a very effective exhaust gas after-treatment or exhaust gas desulfurization can be ensured in the separator 3.

すでに先に説明したように、分離器3における硫黄酸化物の化学吸着、つまり、分離器3におけるカルシウム含有粒状体との排気ガスの硫黄酸化物の反応は、分離器3を通って導かれる排気ガスに留意した発熱反応である。分離器3での発熱反応の間に放出されるこの熱エネルギーは、内燃機関1を出て行く排気ガスを中間温度へとすでに上昇させたものとするために、ガス−ガス熱交換器4で利用される。このため、優先的には、燃料運転される燃焼器、または、電気加熱装置であり得る加熱装置5が、小形化され得る。このため、本発明による排気ガス後処理システム2の効率が高められ得る。   As already explained above, the chemisorption of sulfur oxides in the separator 3, ie the reaction of the sulfur oxides of the exhaust gas with the calcium-containing particulates in the separator 3, This is an exothermic reaction taking gas into consideration. This thermal energy released during the exothermic reaction in the separator 3 is used in the gas-gas heat exchanger 4 in order to have already raised the exhaust gas leaving the internal combustion engine 1 to an intermediate temperature. Used. For this reason, preferentially, the heating device 5, which can be a fuel-operated combustor or an electric heating device, can be miniaturized. For this reason, the efficiency of the exhaust gas aftertreatment system 2 according to the present invention can be enhanced.

図1に示す例示の実施形態では、SCR触媒コンバータ6が、排気ガスを脱硫するように機能する分離器3の下流に位置付けられており、SCR触媒コンバータ6は、排気ガスを脱窒するように機能する。したがって、SCR触媒コンバータ6は、図1において、分離器3の下流でガス−ガス熱交換器4の上流に位置付けられている。   In the exemplary embodiment shown in FIG. 1, the SCR catalytic converter 6 is located downstream of the separator 3 which functions to desulfurize the exhaust gas, and the SCR catalytic converter 6 is configured to denitrify the exhaust gas. Function. Accordingly, the SCR catalytic converter 6 is positioned downstream of the separator 3 and upstream of the gas-gas heat exchanger 4 in FIG.

SCR触媒コンバータ6では、アンモニアが還元剤として利用されている。SCR触媒コンバータ6で利用されるアンモニアは、分離器3とSCR触媒コンバータ6との間のノズルによって、SCR触媒コンバータ6の上流で排気ガスへと直接噴射されてもよいし、代わりに、排気ガスにおいてアンモニアへと変換されるアンモニアの前駆物質が、分離器3の下流でSCR触媒コンバータ6の上流に導入されてもよい。このような前駆物質は、具体的には尿素である。   In the SCR catalytic converter 6, ammonia is used as a reducing agent. The ammonia utilized in the SCR catalytic converter 6 may be injected directly into the exhaust gas upstream of the SCR catalytic converter 6 by a nozzle between the separator 3 and the SCR catalytic converter 6, or alternatively, the exhaust gas May be introduced downstream of the separator 3 and upstream of the SCR catalytic converter 6. Such a precursor is specifically urea.

図1の例示の実施形態では、排熱回収装置7がガス−ガス熱交換器4の下流に位置付けられており、排気ガスの残留熱が、排気ガス後処理システム2の効率をさらに高めるために、および、おおよそ100℃の温度を有する排気ガスを排気ガス後処理システム2の下流の環境へと案内するために、ガス−ガス熱交換器4の下流で利用される。   In the exemplary embodiment of FIG. 1, the exhaust heat recovery device 7 is located downstream of the gas-gas heat exchanger 4, and the residual heat of the exhaust gas is used to further increase the efficiency of the exhaust gas aftertreatment system 2. And is utilized downstream of the gas-gas heat exchanger 4 to guide exhaust gases having a temperature of approximately 100 ° C. to the environment downstream of the exhaust gas aftertreatment system 2.

本明細書では、SCR触媒コンバータ6が、ガス−ガス熱交換器4の下流で排気ガス後処理装置7の上流に位置付けられてもよいことが注目される。この場合、分離器3を出て行く排気ガスは、最初にガス−ガス熱交換器4を通って、次にSCR触媒コンバータ6を通って導かれる。   It is noted here that the SCR catalytic converter 6 may be located downstream of the gas-gas heat exchanger 4 and upstream of the exhaust gas aftertreatment device 7. In this case, the exhaust gas leaving the separator 3 is directed firstly through the gas-gas heat exchanger 4 and then through the SCR catalytic converter 6.

図2は、内燃機関1の下流に配置された排気ガス後処理システム2の第2の例示の実施形態であり、図2の排気ガス後処理システム2は、図2の例示の実施形態では、酸化触媒コンバータ8が分離器3の上流で加熱装置5の下流に位置付けられている点において、図1の排気ガス後処理システム2と異なっている。   FIG. 2 is a second exemplary embodiment of an exhaust gas aftertreatment system 2 arranged downstream of the internal combustion engine 1, wherein the exhaust gas aftertreatment system 2 of FIG. 1 in that the oxidation catalytic converter 8 is positioned upstream of the separator 3 and downstream of the heating device 5.

酸化触媒コンバータ8では、以下の反応式に従って、SOがSOへと反応する。
2SO+O→2SO
In the oxidation catalytic converter 8, SO 2 reacts with SO 3 according to the following reaction formula.
2SO 3 + O 2 → 2SO 2

以下の化学元素が、SOをSOへと酸化するために、酸化触媒コンバータ8における活性成分として用いられている。すなわち、V(バナジウム)、および/または、白金/パラジウム、および/または、Fe(鉄)、および/または、Ce(セリウム)、および/または、Cs(セシウム)、および/または、これらの元素の酸化物である。バナジウム(V)の成分は、優先的には、5%超、好ましくは7%超、最も好ましくは9%超までとなる。 The following chemical elements, the SO 2 to oxidize to SO 3, are used as active ingredients in the oxidation catalytic converter 8. That is, V (vanadium), and / or platinum / palladium, and / or Fe (iron), and / or Ce (cerium), and / or Cs (cesium), and / or It is an oxide. The component of vanadium (V) is preferentially higher than 5%, preferably higher than 7% and most preferably higher than 9%.

基材として、酸化触媒コンバータ8は、WO(酸化タングステン)によって優先的に安定化されたTiO(酸化チタン)および/またはSiO(酸化ケイ素)を用いる。 As the base material, the oxidation catalytic converter 8 uses TiO 2 (titanium oxide) and / or SiO 2 (silicon oxide) that is preferentially stabilized by WO 3 (tungsten oxide).

SOがSOよりも素早く分離器3のカルシウム含有粒状体と反応するため、分離器3の上流に、SOをSOへと酸化するための酸化触媒コンバータ8が配置されることは有利である。このため、脱硫の効果が高められ得る。優先的には、酸化触媒コンバータ8においてSOをSOへと酸化することは、酸化触媒コンバータ8の下流で、排気ガスのすべての硫黄酸化物(SO)中のSOの成分が、少なくとも20%、好ましくは40%超、最も好ましくは60%超となるようなやり方で達成される。 Since SO 3 reacts with the calcium-containing granulate quickly separator 3 than SO 2, upstream of the separator 3, it is advantageous to the oxidation catalytic converter 8 for the oxidation and the SO 2 to SO 3 is arranged It is. For this reason, the effect of desulfurization can be enhanced. Preferentially, oxidizing SO 2 to SO 3 in oxidation catalytic converter 8 means that, downstream of oxidation catalytic converter 8, the component of SO 3 in all sulfur oxides (SO X ) of the exhaust gas is It is achieved in such a way that it is at least 20%, preferably more than 40%, most preferably more than 60%.

図3は、図1の例示の実施形態の代替の有利なさらなる発展形態を示しており、図3の排気ガス後処理システム2は、加熱装置5の下流で分離器3の上流に、装置9が位置付けられている点において、図1の排気ガス後処理システム2と異なっている。装置9を通って、カルシウム含有および/またはナトリウム含有の粉末が、カルシウム含有粒状体を含む分離器3の上流の加熱装置5で加熱された排気ガスへと導入され得る。   FIG. 3 shows an alternative advantageous further development of the exemplary embodiment of FIG. 1 in which the exhaust gas aftertreatment system 2 of FIG. 3 comprises a device 9 downstream of the heating device 5 and upstream of the separator 3. Is different from the exhaust gas after-treatment system 2 of FIG. Through the device 9, calcium- and / or sodium-containing powder can be introduced into the exhaust gas heated by the heating device 5 upstream of the separator 3 containing the calcium-containing granules.

図3の排気ガス後処理システム2の装置9は、カルシウム含有および/またはナトリウム含有の粉末を内燃機関1の排気ガスへと導入するように機能し、1mm未満の粒径、優先的には0.5mm未満の粒径、最も好ましくは0.25mm未満の粒径のカルシウム含有および/またはナトリウム含有の粉末を排気ガスへと導入し、カルシウム含有および/またはナトリウム含有の粉末のカルシウムおよび/またはナトリウムは、少なくとも酸化段階+1を有する。   The device 9 of the exhaust gas aftertreatment system 2 of FIG. 3 functions to introduce calcium- and / or sodium-containing powder into the exhaust gas of the internal combustion engine 1 and has a particle size of less than 1 mm, preferably A calcium- and / or sodium-containing powder having a particle size of less than 0.5 mm, most preferably less than 0.25 mm, is introduced into the exhaust gas and the calcium and / or sodium of the calcium- and / or sodium-containing powder is introduced. Has at least an oxidation step +1.

優先的には、カルシウム含有および/またはナトリウム含有の粉末は、CaOおよび/またはCa(OH)および/またはCaCOおよび/またはNaHCOを含んでいる。 Preferentially, the powder of the calcium-containing and / or sodium-containing includes CaO and / or Ca (OH) 2 and / or CaCO 3 and / or NaHCO 3.

装置9は、カルシウム含有および/またはナトリウム含有の粉末を、搬送ガスとして空気を用いるエアロゾルとして乾燥して、または、溶剤として水を用いるエマルションとして湿らせてかのいずれかで、排気ガスへと導入できる。   Apparatus 9 introduces the calcium- and / or sodium-containing powder into the exhaust gas either as an aerosol using air as a carrier gas or moistened as an emulsion using water as a solvent. it can.

このようなカルシウム含有および/またはナトリウム含有の粉末を吸着剤として使用すること、および、装置9を通じて排気ガスへとカルシウム含有および/またはナトリウム含有の粉末を上記のように導入することは、カルシウム含有および/またはナトリウム含有の粉末が、内燃機関1の排気ガスに含まれる硫黄酸化物と、つまり、SOおよびSOと反応するための大きな表面積を確保し、その結果、硫黄酸化物は、硫酸カルシウムCaSOおよび/または硫酸ナトリウムNaSOへと効果的に変換され得る。カルシウム含有および/またはナトリウム含有の粉末のSOおよびSOとの反応は、典型的には、以下の反応式に従ってもたらされる。すなわち、Ca(OH)については、以下の反応式に従う。
Ca(OH)+SO⇔CaSO+H
Ca(OH)+SO+1/2O⇔CaSO+H
Ca(OH)+CO⇔CaCO+H
Ca(OH)+SO⇔CaCO+H
CaCOについては、以下の反応式に従う。
CaCO+SO⇔CaSO+CO
CaCO+SO+1/2O⇔CaSO+CO
CaCO+SO⇔CaSO+CO
NaHCOについては、以下の反応式に従う。
2NaHCO→NaCO+CO+H
NaCO+SO+1/2O→NaSO+CO
NaCO+SO→NaSO+CO
The use of such calcium- and / or sodium-containing powder as an adsorbent and the introduction of calcium- and / or sodium-containing powder into the exhaust gas through the device 9 as described above comprises the calcium-containing and / or sodium-containing powder. And / or the sodium-containing powder secures a large surface area for reacting with sulfur oxides contained in the exhaust gas of the internal combustion engine 1, that is, with SO 2 and SO 3. It can be effectively converted to calcium CaSO 4 and / or sodium sulfate Na 2 SO 4 . The reaction of calcium- and / or sodium-containing powders with SO 2 and SO 3 is typically effected according to the following reaction formula: That is, Ca (OH) 2 follows the following reaction formula.
Ca (OH) 2 + SO 2 ⇔CaSO 3 + H 2 O
Ca (OH) 2 + SO 2 + / O 2 ⇔CaSO 4 + H 2 O
Ca (OH) 2 + CO 2 ⇔CaCO 3 + H 2 O
Ca (OH) 2 + SO 3 ⇔CaCO 4 + H 2 O
For CaCO 3 , the following reaction equation follows.
CaCO 3 + SO 2 ⇔CaSO 3 + CO 2
CaCO 3 + SO 2 + / O 2 ⇔CaSO 4 + CO 2
CaCO 3 + SO 3 ⇔CaSO 4 + CO 2
For NaHCO 3 , the following reaction equation follows.
2NaHCO 3 → Na 2 CO 3 + CO 2 + H 2 O
Na 2 CO 3 + SO 2 + 1 / 2O 2 → Na 2 SO 4 + CO 2
Na 2 CO 3 + SO 3 → Na 2 SO 4 + CO 2

分離器3の上流の装置9を介してカルシウム含有および/またはナトリウム含有の粉末を排気ガスへと導入することで、粉末の硫酸カルシウムCaSOおよび/または硫酸ナトリウムNaSOが形成され、移動床反応器または流動層反応器として形成された分離器3の粒状体と共に排出され得る。 By introducing the calcium- and / or sodium-containing powder into the exhaust gas via the device 9 upstream of the separator 3, the powdered calcium sulfate CaSO 4 and / or sodium sulfate Na 2 SO 4 is formed and moved It can be discharged with the granules of the separator 3 formed as a bed reactor or a fluidized bed reactor.

分離器3では、装置9を通って排気ガスへと導入されるカルシウム含有および/またはナトリウム含有の粉末と比較して、比較的大きな粒径、すなわち、2mm超の粒径、好ましくは3mm超の粒径、最も好ましくは4mm超の粒径を有する粒状体が用いられる。   The separator 3 has a relatively large particle size, ie a particle size of more than 2 mm, preferably more than 3 mm, as compared to calcium- and / or sodium-containing powder introduced into the exhaust gas through the device 9. Granules having a particle size, most preferably greater than 4 mm, are used.

分離器3の粒状体は、カルシウムを含むがナトリウムを含んではいない。したがって、分離器3の粒状体はNaHCOをまったく含んでいない。NaHCOは、せいぜい、分離器3の上流の装置9を通って、比較的細かい粒の粉末として排気ガスへと導入され得る。 The granules of the separator 3 contain calcium but not sodium. Therefore, the granules of the separator 3 do not contain any NaHCO 3 . At best, NaHCO 3 can be introduced into the exhaust gas as a relatively fine-grained powder through a device 9 upstream of the separator 3.

分離器3には、優先的には、粒状体を介して捕捉され、移動床反応器または流動床反応器として設計された分離器3から粒状体と共に排出される硫酸カルシウムを、移動床または流動床において粒状体から分離するために、図示されていない装置が設けられる。この装置は、例えば、ドラム剥離器、ドラムスクリーン、または粉砕器であり得る。これに続いて、硫酸カルシウムのなくなった粒状体が、粒状体回路を形成するために、および、粒状体を効果的に利用するために、移動床反応器または流動床反応器へと再び供給され得る。   The separator 3 preferentially receives calcium sulphate, which is captured via the granules and discharged together with the granules from the separator 3 designed as a moving bed reactor or a fluidized bed reactor, in a moving bed or in a fluidized bed. In order to separate from the granules on the floor, a device not shown is provided. The device can be, for example, a drum peeler, drum screen, or crusher. Following this, the granules depleted of calcium sulphate are fed back to a moving bed reactor or a fluidized bed reactor to form a granulate circuit and to make effective use of the granules. obtain.

内燃機関1の下流に配置された排気ガス後処理システム2のさらなる例示の実施形態が図4に示されており、図4の例示の実施形態は、図2および図3の例示の実施形態の組立体を組み合わせている。したがって、図4の排気ガス後処理システム2は、一方でSOをSOへと酸化するための酸化触媒コンバータ8と、他方でカルシウム含有および/またはナトリウム含有の粉末を排気ガスへと導入するための装置9とを備えている。図4によれば、装置9は、それを通ってカルシウム含有および/またはナトリウム含有の粉末が排気ガスへと導入でき、酸化触媒コンバータ8の下流に位置付けられている。したがって、酸化触媒コンバータ8は加熱装置5の下流に位置付けられており、装置9は、酸化触媒コンバータ8の下流で分離器3の上流に位置付けられている。 A further exemplary embodiment of an exhaust gas aftertreatment system 2 arranged downstream of the internal combustion engine 1 is shown in FIG. 4, which is an example of the exemplary embodiment of FIGS. 2 and 3. Assemblies are combined. Thus, the exhaust gas aftertreatment system 2 of FIG. 4 introduces, on the one hand, an oxidation catalytic converter 8 for oxidizing SO 2 to SO 3 and, on the other hand, calcium- and / or sodium-containing powder into the exhaust gas. And a device 9. According to FIG. 4, the device 9 is located downstream of the oxidation catalytic converter 8, through which calcium- and / or sodium-containing powder can be introduced into the exhaust gas. Thus, the oxidation catalytic converter 8 is located downstream of the heating device 5 and the device 9 is located downstream of the oxidation catalytic converter 8 and upstream of the separator 3.

内燃機関用の排気ガス後処理システム2のさらなる例示の実施形態が図5によって示されており、図5の排気ガス後処理システム2は、図2の排気ガス後処理システム2と同様に、酸化触媒コンバータ8を備え、さらにはガス状のアンモニア(NH)を排気ガスへと導入するための装置10も備えており、ガス状のNHを排気ガスへと導入するためのこの装置10は、酸化触媒コンバータ8の下流に配置されており、その結果、NHは、酸化触媒コンバータ8の上流で内燃機関1の排気ガスへと導入される。 A further exemplary embodiment of an exhaust gas aftertreatment system 2 for an internal combustion engine is illustrated by FIG. 5, wherein the exhaust gas aftertreatment system 2 of FIG. The apparatus 10 includes a catalytic converter 8 and further includes an apparatus 10 for introducing gaseous ammonia (NH 3 ) into exhaust gas. The apparatus 10 for introducing gaseous NH 3 into exhaust gas is provided. , Is arranged downstream of the oxidation catalytic converter 8, so that NH 3 is introduced into the exhaust gas of the internal combustion engine 1 upstream of the oxidation catalytic converter 8.

ここで、NHそのものをガス状の形態で排気ガス流へと直接的に導入すること、または、例えば尿素などのNH前駆物質を排気ガス流へと噴射し、排気ガス流でNH前駆物質をNHへと蒸発させることが、提供され得る。ガス状のNHを酸化触媒コンバータ8の上流への排気ガス流へと導入することは、これによって行われる排気ガスの脱窒によって、続く脱硫が改善され得るという利点を有している。 Here, NH 3 itself may be directly introduced into the exhaust gas stream in a gaseous form, or an NH 3 precursor such as urea may be injected into the exhaust gas stream, and the NH 3 precursor may be injected into the exhaust gas stream. Evaporating the material to NH 3 may be provided. The introduction of gaseous NH 3 into the exhaust gas stream upstream of the oxidation catalytic converter 8 has the advantage that the ensuing denitrification of the exhaust gas can improve the subsequent desulfurization.

図1から図5に示す排気ガス後処理システム2では、移動床反応器または流動床反応器として設計された多段分離器3が、硫酸カルシウムと、適切な場合には硫酸ナトリウムとの分離を改善するために用いられてもよく、具体的には、多段分離器3が使用される場合、異なる粒径の粒状体が、分離器3の個々の段で使用される。したがって、分離器3の個々の段では、粒状体の粒径が互いと異なっている。優先的には、直交流分離器として設計された分離器3が利用される。   In the exhaust gas aftertreatment system 2 shown in FIGS. 1 to 5, a multistage separator 3 designed as a moving bed reactor or a fluidized bed reactor improves the separation of calcium sulfate and, where appropriate, sodium sulfate. In particular, where a multi-stage separator 3 is used, granules of different particle sizes are used in individual stages of the separator 3. Thus, in the individual stages of the separator 3, the particle size of the granules is different from each other. Preference is given to using a separator 3 designed as a cross-flow separator.

本発明は、排気ガスターボ過給機を備える排気ガス過給内燃機関で用いられてもよい。したがって、このような場合、少なくとも粒子分離器3は、図示されていない排気ガスターボ過給機のタービンの下流に位置付けられることが、優先的に提供される。適切な場合には、酸化触媒コンバータ8は、タービンの上流にある高圧と排気流の高温とが酸化触媒コンバータ8におけるSOのSOへの酸化に好ましいため、優先的には、このようなタービンの上流に位置付けられる。 The present invention may be used in an exhaust gas supercharged internal combustion engine having an exhaust gas turbocharger. Thus, in such a case, it is preferentially provided that at least the particle separator 3 is located downstream of the turbine of the exhaust gas turbocharger, not shown. If appropriate, the oxidation catalytic converter 8 preferentially employs such a converter, since the high pressure upstream of the turbine and the high temperature of the exhaust stream favor the oxidation of SO 2 to SO 3 in the oxidation catalytic converter 8. Located upstream of the turbine.

本発明は、内燃機関用の排気ガス後処理システムと、内燃機関を出て行く排気ガスの排気ガス後処理のための方法とを提案し、排気ガスの脱硫が、カルシウム含有粒状体を備える分離器3で実施される。   The invention proposes an exhaust gas aftertreatment system for an internal combustion engine and a method for exhaust gas aftertreatment of exhaust gas leaving the internal combustion engine, wherein the desulfurization of the exhaust gas comprises a separation comprising calcium-containing particulates. This is performed in the vessel 3.

分離器3において最適な運転条件でこの脱硫を実施するために、内燃機関1を出て行く排気ガスが、分離器3の上流で、優先的には400℃と450℃との間のプロセス温度へと、つまり、多段において、最初にガス−ガス熱交換器4で次に加熱装置5において、加熱される。ガス−ガス熱交換器4は、内燃機関1を出て行く排気ガスを中間温度へと加熱するために、脱硫の間に分離器3で受け取った熱エネルギーを利用し、その結果として、加熱装置5の熱出力が低減できる。加熱装置5は、電気的に運転される加熱装置、または、具体的に重油といった、ガス状もしくは液状の燃料で運転される燃焼器であり得る。   In order to carry out this desulfurization in the separator 3 under optimal operating conditions, the exhaust gas leaving the internal combustion engine 1 has a process temperature upstream of the separator 3, preferentially between 400 ° C. and 450 ° C. , Ie, in multiple stages, heated first in the gas-gas heat exchanger 4 and then in the heating device 5. The gas-gas heat exchanger 4 utilizes the heat energy received at the separator 3 during the desulfurization to heat the exhaust gas leaving the internal combustion engine 1 to an intermediate temperature, and consequently the heating device 5, the heat output can be reduced. The heating device 5 can be an electrically operated heating device or, specifically, a combustor operated with a gaseous or liquid fuel, such as heavy oil.

すでに上記で説明したように、分離器3のカルシウム含有粒状体または石灰に基づいた粒状体での硫黄酸化物の化学吸着は、充填層反応器として、または、移動床反応器として具体化された、カルシウム含有粒状体を含む分離器3で起こり、この反応は発熱し、したがって熱エネルギーを放出する。分離器3は、分離器3での熱損失を低減するために二重壁で具体化され得る。したがって、分離器3は、内燃機関を出て行く排気ガスをガス−ガス熱交換器で加熱するための、発熱反応によって解放された熱エネルギーを、よりよく利用できる。   As already explained above, the chemisorption of sulfur oxides on the calcium-containing or lime-based granules of the separator 3 has been embodied as a packed bed reactor or as a moving bed reactor. Occur in the separator 3 containing the calcium-containing granules, the reaction being exothermic and thus releasing thermal energy. Separator 3 can be embodied with double walls to reduce heat loss in separator 3. Thus, the separator 3 can better utilize the heat energy released by the exothermic reaction for heating the exhaust gas leaving the internal combustion engine with the gas-gas heat exchanger.

分離器3の下流のSCR触媒コンバータ6の任意の利用は、排気ガスの脱窒を可能にし、具体的には、アンモニア前駆物質としての尿素は、分離器3の下流かつSCR触媒コンバータ6の上流で排気ガスへと導入されるとき、粒子分離器3の下流にある高い温度のため、尿素にとっての短い蒸発距離は適切である。すでに脱窒された排気ガスがSCR触媒コンバータ6を通って導かれるという事実のため、SCR触媒コンバータ6の目詰まりの危険性はない。   Optional use of the SCR catalytic converter 6 downstream of the separator 3 allows for denitrification of the exhaust gas, in particular urea as an ammonia precursor is downstream of the separator 3 and upstream of the SCR catalytic converter 6 Due to the high temperature downstream of the particle separator 3 when introduced into the exhaust gas at, a short evaporation distance for urea is appropriate. Due to the fact that already denitrified exhaust gases are led through the SCR catalytic converter 6, there is no risk of clogging the SCR catalytic converter 6.

すべての示した実施形態では、任意の排熱回収装置7が、ガス−ガス熱交換器4の下流に位置付けられている。これは、例えば、排気ガスの残留熱が電力を発生させるために利用される蒸気タービンであり得る。先に実施された排気ガスの脱硫のため、落下するHSOによる腐食が排熱回収装置7の領域で成長する危険性はない。 In all the illustrated embodiments, an optional waste heat recovery device 7 is located downstream of the gas-gas heat exchanger 4. This can be, for example, a steam turbine in which residual heat of the exhaust gas is used to generate power. Due to the desulfurization of the exhaust gas carried out earlier, there is no danger that the corrosion due to the falling H 2 SO 4 will grow in the area of the exhaust heat recovery device 7.

前述のように、本発明による排気ガス後処理システム2は、最適に適合された温度管理によって特徴付けられる。内燃機関1を出て行く排気ガスは、典型的には、320℃未満の温度を有している。内燃機関1を出て行く排気ガスの温度は、例えば、影響する排気ガスの絞り、または、ウェイストゲートによるといった、エンジン側での内燃機関1における干渉によって、ある程度まで上昇され得る。内燃機関1を出て行く排気ガスは、ガス−ガス熱交換器4を通って、おおよそ350℃の温度まで加熱され得る。加熱装置5の領域では、排気ガスは、分離器3で硫黄酸化物を化学吸着するための最適なプロセス温度を提供するために、優先的には、360℃と450℃との間の温度まで続いて加熱される。分離器3でのこの化学吸着は、発熱反応であり、分離器3を出て行く排気ガスはより高い温度を有する。すでに分離器3を通って導かれた排気ガスのこの上昇した温度は、ガス−ガス熱交換器4で利用される。任意で存在し、示した例示の実施形態では分離器3とガス−ガス熱交換器4との間に位置付けられたSCR触媒コンバータ6では、排気ガスの温度の小さな低下しか起こらない。ガス−ガス熱交換器4の下流では、排気ガスの残留熱が、電気エネルギーを発生するための排気ガス後処理装置7で有利に利用されている。排熱回収装置7の下流の温度は、最大でおおよそ120℃である。   As mentioned above, the exhaust gas aftertreatment system 2 according to the invention is characterized by an optimally adapted temperature control. The exhaust gas leaving the internal combustion engine 1 typically has a temperature of less than 320 ° C. The temperature of the exhaust gas leaving the internal combustion engine 1 can be increased to some extent by interference in the internal combustion engine 1 on the engine side, for example by restricting the affected exhaust gas or by a wastegate. Exhaust gas leaving the internal combustion engine 1 can be heated through the gas-gas heat exchanger 4 to a temperature of approximately 350 ° C. In the area of the heating device 5, the exhaust gas is preferentially up to a temperature between 360 ° C. and 450 ° C. in order to provide an optimum process temperature for the chemisorption of sulfur oxides in the separator 3. Subsequently, it is heated. This chemisorption at the separator 3 is an exothermic reaction and the exhaust gas leaving the separator 3 has a higher temperature. This increased temperature of the exhaust gas already led through the separator 3 is used in the gas-gas heat exchanger 4. The SCR catalytic converter 6, which is optionally present and is located between the separator 3 and the gas-gas heat exchanger 4 in the exemplary embodiment shown, causes only a small reduction in the temperature of the exhaust gas. Downstream of the gas-gas heat exchanger 4, the residual heat of the exhaust gas is advantageously used in an exhaust gas aftertreatment device 7 for generating electrical energy. The temperature downstream of the exhaust heat recovery device 7 is approximately 120 ° C. at the maximum.

1 内燃機関
2 排気ガス後処理システム
3 分離器
4 ガス−ガス熱交換器
5 加熱装置
6 SCR触媒コンバータ
7 排熱回収装置、排気ガス後処理装置
8 酸化触媒コンバータ
9 装置
10 装置
DESCRIPTION OF SYMBOLS 1 Internal combustion engine 2 Exhaust gas aftertreatment system 3 Separator 4 Gas-gas heat exchanger 5 Heating device 6 SCR catalytic converter 7 Exhaust heat recovery device, exhaust gas aftertreatment device 8 Oxidation catalytic converter 9 Device 10 Device

Claims (13)

内燃機関用の排気ガス後処理システム(2)であって、
内燃機関(1)の下流に配置された、硫黄酸化物を化学吸着するためのカルシウム含有粒状体を含む分離器(3)と、
ガス−ガス熱交換器であって、前記内燃機関(1)を出て行く排気ガスの温度を上昇させるために、一方で前記分離器(3)を通って導かれた排気ガスが当該ガス−ガス熱交換器を通って導かれ、他方で前記内燃機関(1)を出て行く前記排気ガスが導かれ得るように通る、ガス−ガス熱交換器(4)と、
前記ガス−ガス熱交換器(4)を通って導かれた前記排気ガスの温度をさらに上昇させるために、前記ガス−ガス熱交換器(4)の下流で前記分離器(3)の上流に配置された加熱装置(5)と
を備える排気ガス後処理システム。
An exhaust gas aftertreatment system (2) for an internal combustion engine,
A separator (3) disposed downstream of the internal combustion engine (1) and containing calcium-containing particulates for chemisorbing sulfur oxides;
A gas-gas heat exchanger, wherein the exhaust gas guided through the separator (3) is used to increase the temperature of the exhaust gas leaving the internal combustion engine (1). A gas-gas heat exchanger (4), which is conducted through a gas heat exchanger, while the exhaust gas leaving the internal combustion engine (1) passes therethrough.
Downstream of the gas-gas heat exchanger (4) and upstream of the separator (3) to further increase the temperature of the exhaust gas led through the gas-gas heat exchanger (4). An exhaust gas aftertreatment system comprising a heating device (5) arranged.
前記加熱装置(5)が、前記排気ガスを、375℃と450℃との間の温度まで加熱することを特徴とする、請求項1に記載の排気ガス後処理システム。 The heating device (5), the exhaust gas, characterized by heating in a warm Doma between 375 ° C. and 450 ° C., an exhaust gas aftertreatment system according to claim 1. 前記ガス−ガス熱交換器(4)が、前記排気ガスを、330℃と350℃との間の温度まで加熱することを特徴とする、請求項1または2に記載の排気ガス後処理システム。 The gas - gas heat exchanger (4), the exhaust gas, characterized by heating in a warm Doma between 330 ° C. and 350 ° C., the exhaust gas after-treatment according to claim 1 or 2 system. 前記分離器(3)の下流に、SCR触媒コンバータ(6)が位置付けられ、前記分離器(3)を出て行く排気ガスが、先ず前記SCR触媒コンバータ(6)を介して案内され、次に前記ガス−ガス熱交換器(4)を介して案内され得ることを特徴とする、請求項1から3のいずれか一項に記載の排気ガス後処理システム。   Downstream of the separator (3) is located an SCR catalytic converter (6), the exhaust gas leaving the separator (3) being first guided through the SCR catalytic converter (6), 4. The exhaust gas aftertreatment system according to claim 1, wherein the exhaust gas aftertreatment system can be guided via the gas-gas heat exchanger. 4. 前記ガス−ガス熱交換器(4)の上流に、SCR触媒コンバータ(6)が位置付けられ、前記分離器(3)を出て行く排気ガスが、先ず前記SCR触媒コンバータ(6)を介して案内され、次に前記ガス−ガス熱交換器(4)を介して案内され得ることを特徴とする、請求項1から3のいずれか一項に記載の排気ガス後処理システム。 An SCR catalytic converter (6) is located upstream of the gas-gas heat exchanger (4), and the exhaust gas leaving the separator (3) is first guided through the SCR catalytic converter (6). 4. The exhaust gas aftertreatment system according to claim 1, wherein the exhaust gas aftertreatment system is capable of being guided through the gas-gas heat exchanger . 前記ガス−ガス熱交換器(4)の下流に、排気ガス後処理装置(7)が位置付けられることを特徴とする、請求項1から5のいずれか一項に記載の排気ガス後処理システム。   The exhaust gas aftertreatment system according to any one of the preceding claims, characterized in that an exhaust gas aftertreatment device (7) is located downstream of the gas-gas heat exchanger (4). 前記加熱装置(5)の下流で前記分離器(3)の上流に、SOをSOへと酸化するための酸化触媒コンバータ(8)が位置付けられ、前記酸化触媒コンバータ(8)を通って、前記加熱装置(5)において加熱された前記排気ガスが、前記分離器(3)の上流に案内され得ることを特徴とする、請求項1から6のいずれか一項に記載の排気ガス後処理システム。 Upstream of the heating device the separator downstream of (5) (3), oxidation catalyst (8) is positioned to oxidize the SO 2 to SO 3, through the oxidation catalytic converter (8) 7. The exhaust gas according to claim 1, wherein the exhaust gas heated in the heating device (5) can be guided upstream of the separator (3). 8. Processing system. 前記加熱装置(5)の下流で前記分離器(3)の上流に装置(9)が位置付けられ、前記装置(9)を通って、カルシウム含有および/またはナトリウム含有の粉末が、前記分離器(3)の上流の前記加熱装置(5)で加熱された前記排気ガスへと導入され得ることを特徴とする、請求項1から7のいずれか一項に記載の排気ガス後処理システム。   A device (9) is located downstream of the heating device (5) and upstream of the separator (3), through which the calcium- and / or sodium-containing powder is passed through the separator (3). The exhaust gas aftertreatment system according to any of the preceding claims, characterized in that it can be introduced into the exhaust gas heated by the heating device (5) upstream of 3). カルシウム含有および/またはナトリウム含有の粉末が前記排気ガスへと導入され得るように通る装置(9)は、SOをSOへと酸化するための酸化触媒コンバータ(8)の下流で前記分離器(3)の上流に位置付けられることを特徴とする、請求項7または8に記載の排気ガス後処理システム。 Device through as powders of the calcium-containing and / or sodium-containing can be introduced into the exhaust gas (9), the separator SO 2 downstream of the oxidation catalytic converter (8) for the oxidation to SO 3 The exhaust gas aftertreatment system according to claim 7, wherein the exhaust gas aftertreatment system is positioned upstream of (3). 前記装置(9)を通って前記排気ガスの流れへと導入された前記カルシウム含有および/またはナトリウム含有の粉末が、CaOおよび/またはCa(OH)および/またはCaCOおよび/またはNaHCOを含み、前記装置(9)を通って前記排気ガスの流れへと導入される前記カルシウム含有および/またはナトリウム含有の粉末の粒径が、1mm未満となることを特徴とする、請求項8または9に記載の排気ガス後処理システム。 The device (9) powder of the said calcium being introduced into the flow of exhaust gases containing and / or sodium-containing through is, the CaO and / or Ca (OH) 2 and / or CaCO 3 and / or NaHCO 3 wherein, the particle size of the calcium-containing and / or sodium-containing powder is introduced into the device (9) through flow of the exhaust gas, characterized in that a 1mm less than, claim 8 or An exhaust gas aftertreatment system according to claim 9. 充填層反応器として、または、移動床反応器として優先的に設計された前記分離器(3)の粒状体が、CaOおよび/またはCa(OH)および/またはCaCOを含み、前記分離器(3)の粒状体の粒径が、2mm超となることを特徴とする、請求項1から10のいずれか一項に記載の排気ガス後処理システム。 As packed bed reactor, or, granules of a preferentially designed as a moving bed reactor wherein the separator (3) comprises CaO and / or Ca (OH) 2 and / or CaCO 3, wherein the separator The exhaust gas post-processing system according to any one of claims 1 to 10, wherein the particle size of the granular material (3) is more than 2 mm. 内燃機関を出て行く排気ガスの排気ガス後処理のための方法であって、
前記排気ガスが、硫黄酸化物を化学吸着するためのカルシウム含有粒状体を含む分離器を通って導かれ、
前記内燃機関を出て行く前記排気ガスの温度を上昇させるために、前記分離器を通って導かれた前記排気ガスと、他方で前記内燃機関を出て行く前記排気ガスとが、ガス−ガス熱交換器を通って導かれ、
前記ガス−ガス熱交換器で加熱された前記排気ガスが、温度をさらに上昇させるために、前記ガス−ガス熱交換器の下流で前記分離器の上流に配置された加熱装置を通るように導かれる方法。
A method for exhaust gas aftertreatment of exhaust gas leaving an internal combustion engine, comprising:
The exhaust gas is directed through a separator containing calcium-containing particulates for chemisorbing sulfur oxides;
In order to raise the temperature of the exhaust gas leaving the internal combustion engine, the exhaust gas guided through the separator and, on the other hand, the exhaust gas leaving the internal combustion engine are gas-gas Led through a heat exchanger,
The exhaust gas heated by the gas-gas heat exchanger is passed through a heating device located downstream of the gas-gas heat exchanger and upstream of the separator to further increase the temperature. How to be.
請求項1から11のいずれか一項に記載の排気ガス後処理システムを用いて同様に実施されることを特徴とする、請求項12に記載の方法。   13. The method according to claim 12, characterized in that it is likewise implemented with an exhaust gas aftertreatment system according to any of the preceding claims.
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